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两相液膜生物反应器中来自农业土壤和污染土壤的土著菌降解多环芳烃的潜力。

PAHs biodegradation potential of indigenous consortia from agricultural soil and contaminated soil in two-liquid-phase bioreactor (TLPB).

机构信息

State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.

出版信息

J Hazard Mater. 2010 Apr 15;176(1-3):41-7. doi: 10.1016/j.jhazmat.2009.10.123. Epub 2009 Nov 6.

Abstract

Estimation of PAHs degradation potential of indigenous consortia is essential for remediation of polluted soils. In this study, the biodegradation of a mixture of 11 PAHs was compared using a long-term PAH-contaminated soil (CS) and an unpolluted agricultural soil (AS) as inocula in a two-liquid-phase bioreactor (TLPB). In the TLPB, silicone oil was used as the organic phase to increase the PAHs bioavailability. The microbial numbers were also determined during the biodegradation. The results demonstrated that naphthalene, fluorene, phenanthrene, anthracene, fluoranthene and pyrene could be completely biodegraded in both soils within 4-50 days. With the exception of dibenzo(a,h)anthrancene, the other PAHs including benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene and benzo(k)fluoranthene were degraded to different extents in both soils at the end of 170 days. Complete biodegradation of benzo(a)anthracene and benzo(b)fluoranthene only occurred in CS. During the process, microbial growth was highly correlated to the biodegradation of PAHs. Sequential utilization of PAHs showed a competitive-inhibition in the multi-substrate system. The half-life times of PAHs obtained here were much shorter than those reported previously in soils, indicating that indigenous microbes in both soils had high PAHs degradation potential, facilitated by TLPB.

摘要

评估土著菌群落对多环芳烃(PAHs)的降解潜力对于污染土壤的修复至关重要。在这项研究中,使用长期受到 PAHs 污染的土壤(CS)和未受污染的农业土壤(AS)作为接种物,在两相生物反应器(TLPB)中比较了 11 种 PAHs 的生物降解情况。在 TLPB 中,硅油被用作有机相以增加 PAHs 的生物利用度。在生物降解过程中还测定了微生物数量。结果表明,萘、芴、菲、蒽、荧蒽和芘在两种土壤中均能在 4-50 天内完全降解。除了二苯并(a,h)蒽之外,其他 PAHs,包括苯并(a)蒽、苯并(a)芘、苯并(b)荧蒽和苯并(k)荧蒽,在 170 天结束时在两种土壤中均有不同程度的降解。苯并(a)蒽和苯并(b)荧蒽仅在 CS 中完全生物降解。在此过程中,微生物生长与 PAHs 的生物降解高度相关。多底物系统中 PAHs 的顺序利用表现出竞争抑制。这里获得的 PAHs 的半衰期远短于以前在土壤中报道的半衰期,表明两种土壤中的土著微生物具有较高的 PAHs 降解潜力,这得益于 TLPB。

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