首页> 美国卫生研究院文献>Applied and Environmental Microbiology >Strong Impact on the Polycyclic Aromatic Hydrocarbon (PAH)-Degrading Community of a PAH-Polluted Soil but Marginal Effect on PAH Degradation when Priming with Bioremediated Soil Dominated by Mycobacteria
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Strong Impact on the Polycyclic Aromatic Hydrocarbon (PAH)-Degrading Community of a PAH-Polluted Soil but Marginal Effect on PAH Degradation when Priming with Bioremediated Soil Dominated by Mycobacteria

机译:以分枝杆菌为主的生物修复土壤引发土壤对PAH污染土壤的多环芳烃降解群落的强烈影响但对PAH降解的边际影响

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摘要

Bioaugmentation of soil polluted with polycyclic aromatic hydrocarbons (PAHs) is often disappointing because of the low survival rate and low activity of the introduced degrader bacteria. We therefore investigated the possibility of priming PAH degradation in soil by adding 2% of bioremediated soil with a high capacity for PAH degradation. The culturable PAH-degrading community of the bioremediated primer soil was dominated by Mycobacterium spp. A microcosm containing pristine soil artificially polluted with PAHs and primed with bioremediated soil showed a fast, 100- to 1,000-fold increase in numbers of culturable phenanthrene-, pyrene-, and fluoranthene degraders and a 160-fold increase in copy numbers of the mycobacterial PAH dioxygenase gene pdo1. A nonpolluted microcosm primed with bioremediated soil showed a high rate of survival of the introduced degrader community during the 112 days of incubation. A nonprimed control microcosm containing pristine soil artificially polluted with PAHs showed only small increases in the numbers of culturable PAH degraders and no pdo1 genes. Initial PAH degradation rates were highest in the primed microcosm, but later, the degradation rates were comparable in primed and nonprimed soil. Thus, the proliferation and persistence of the introduced, soil-adapted degraders had only a marginal effect on PAH degradation. Given the small effect of priming with bioremediated soil and the likely presence of PAH degraders in almost all PAH-contaminated soils, it seems questionable to prime PAH-contaminated soil with bioremediated soil as a means of large-scale soil bioremediation.
机译:由于引入的降解细菌的低存活率和低活性,对多环芳烃(PAHs)污染的土壤进行生物强化常常令人失望。因此,我们研究了通过添加2%具有高PAH降解能力的生物修复土壤来引发土壤中PAH降解的可能性。生物修复的引物土壤的可培养的PAH降解群落以分枝杆菌属为主。包含被PAHs人工污染并用生物修复的土壤引发的原始土壤的缩影显示可培养的菲,pyr和荧蒽的降解物数量快速增加100到1,000倍,分枝杆菌的拷贝数增加160倍PAH双加氧酶基因pdo1。用生物修复土壤引发的无污染缩影显示,在孵育的112天中,引入的降解菌群落具有很高的存活率。包含人工污染过PAHs的原始土壤的无底漆对照微观世界显示,可培养的PAH降解物的数量仅增加很少,而没有pdo1基因。在引发的微观世界中,最初的PAH降解速率最高,但随后,在引发和未引发的土壤中,降解速率相当。因此,引入的,适应土壤的降解剂的增殖和持久性仅对PAH降解产生很小的影响。鉴于用生物修复土壤引发的影响很小,而且几乎所有受PAH污染的土壤中都可能存在PAH降解剂,因此用生物修复土壤引发PAH污染的土壤作为大规模土壤生物修复的方法似乎是有问题的。

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