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Distribution of the Mycobacterium community and polycyclic aromatic hydrocarbons (PAHs) among different size fractions of a long-term PAH-contaminated soil

机译:长期被PAH污染的土壤中不同大小部分之间的分枝杆菌群落和多环芳烃(PAH)的分布

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摘要

Mycobacterium is often isolated from polycyclic aromatic hydrocarbon (PAH)-contaminated soil as degraders of PAHs. In model systems, Mycobacterium shows attachment to the PAH substrate source, which is considered to be a particular adaptation to low bioavailability as it results into increased substrate flux to the degraders. To examine whether PAH-degrading Mycobacterium in real PAH-contaminated soils, in analogy with model systems, are preferentially associated with PAH-enriched soil particles, the distribution of PAHs, of the PAH-mineralizing capacity and of Mycobacterium over different fractions of a soil with an aged PAH contamination was investigated. The clay fraction contained the majority of the PAHs and showed immediate pyrene- and phenanthrene-mineralizing activity upon addition of 14C-labelled pyrene or phenanthrene. In contrast, the sand and silt fractions showed a lag time of 15-26 h for phenanthrene and 3-6 days for pyrene mineralization. The maximum pyrene and phenanthrene mineralization rates of the clay fraction expressed per gram fraction were three to six times higher than those of the sand and silt fractions. Most-probable-number (MPN)-polymerase chain reaction demonstrated that Mycobacterium represented about 10% of the eubacteria in the clay fraction, while this was only about 0.1% in the sand and silt fractions, indicating accumulation of Mycobacterium in the PAH-enriched clay fraction. The Mycobacterium community composition in the clay fraction represented all dominant Mycobacterium populations of the bulk soil and included especially species related to Mycobacterium pyrenivorans, which was also recovered as one of the dominant species in the eubacterial communities of the bulk soil and the clay fraction. Moreover, Mycobacterium could be identified among the major culturable PAH-degrading populations in both the bulk soil and the clay fraction. The results demonstrate that PAH-degrading mycobacteria are mainly associated with the PAH-enriched clay fraction of the examined PAH-contaminated soil and hence, that also in the environmental setting of a PAH-contaminated soil, Mycobacterium might experience advantages connected to substrate source attachment.
机译:分枝杆菌通常从多环芳烃(PAH)污染的土壤中分离,作为PAHs的降解物。在模型系统中,分枝杆菌显示出对PAH底物来源的附着,这被认为是对低生物利用度的特殊适应,因为它导致增加了对降解物的底物通量。与模型系统类似,要检查在真实的受PAH污染的土壤中降解PAH的分枝杆菌是否优先与富含PAH的土壤颗粒,PAHs的分布,PAH矿化能力和分枝杆菌在土壤不同部分上的分布有关对PAH老化的污染物进行了调查。粘土级分包含大部分的PAH,并且在添加14C标记的pyr或菲后立即显示出pyr和菲的矿化活性。相反,菲沙的砂石和粉砂级分的滞后时间为15-26 h,pyr矿化的滞后时间为3-6天。每克级分表示的粘土级分的最大pyr和菲矿化速率比沙子和粉砂级分的最大pyr和菲矿化速率高三到六倍。最可能数(MPN)聚合酶链反应表明,分枝杆菌占粘土级分中真细菌的约10%,而在沙子和淤泥级分中仅占约0.1%,表明分枝杆菌在富含PAH的细菌中积累粘土分数。粘土级分中的分枝杆菌群落组成代表了整个土壤的所有主要分枝杆菌种群,并且特别包括与pyrenvorans分枝杆菌有关的物种,后者也被作为土壤和粘土级分的真细菌群落中的优势种之一而被回​​收。此外,在散装土壤和黏土组分中,主要可培养的降解PAH的种群中都可以鉴定到分枝杆菌。结果表明,降解多环芳烃的分枝杆菌主要与被检测的多环芳烃污染的土壤中富含多环芳烃的粘土部分有关,因此,在多环芳烃污染的土壤的环境中,分枝杆菌也可能会遇到与底物源附着相关的优势。

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