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Tenax TA 萃取法了解 PAH 污染土壤中甲基-β-环糊精强化生物修复的限速因素。

Tenax TA extraction to understand the rate-limiting factors in methyl-β-cyclodextrin-enhanced bioremediation of PAH-contaminated soil.

机构信息

Key Laboratory of Soil Environment and Pollution Remediation, Institute of Soil Science, Chinese Academy of Sciences, Nanjing, 210008, China.

出版信息

Biodegradation. 2013 Jun;24(3):365-75. doi: 10.1007/s10532-012-9593-2. Epub 2012 Sep 22.

Abstract

The effectiveness of many bioremediation systems for PAH-contaminated soil may be constrained by low contaminant bioaccessibility due to limited aqueous solubility or large sorption capacity. Information on the extent to which PAHs can be readily biodegraded is of vital importance in the decision whether or not to remediate a contaminated soil. In the present study the rate-limiting factors in methyl-β-cyclodextrin (MCD)-enhanced bioremediation of PAH-contaminated soil were evaluated. MCD amendment at 10 % (w/w) combined with inoculation with the PAH-degrading bacterium Paracoccus sp. strain HPD-2 produced maximum removal of total PAHs of up to 35 %. The desorption of PAHs from contaminated soil was determined before and after 32 weeks of bioremediation. 10 % (w/w) MCD amendment (M2) increased the Tenax extraction of total PAHs from 12 to 30 % and promoted degradation by up to 26 % compared to 6 % in the control. However, the percentage of Tenax extraction for total PAHs was much larger than that of degradation. Thus, in the control and M2 treatment it is likely that during the initial phase the bioaccessibility of PAHs is high and biodegradation rates may be limited by microbial processes. On the other hand, when the soil was inoculated with the PAH-degrading bacterium (CKB and MB2), the slowly and very slowly desorbing fractions (F sl and F vl ) became larger and the rate constants of slow and very slow desorption (k sl and k vl ) became extremely small after bioremediation, suggesting that desorption is likely rate limiting during the second, slow phase of biotransformation. These results have practical implications for site risk assessment and cleanup strategies.

摘要

许多用于受多环芳烃污染土壤的生物修复系统的有效性可能受到污染物生物可利用性低的限制,这是由于其有限的水溶性或较大的吸附容量所致。了解多环芳烃易于生物降解的程度对于是否要修复受污染的土壤至关重要。在本研究中,评估了在甲基-β-环糊精(MCD)增强的多环芳烃污染土壤生物修复中,限制因素的程度。在添加 10%(w/w)MCD 并接种多环芳烃降解菌 Paracoccus sp. strain HPD-2 的情况下,多环芳烃的总去除率最高可达 35%。在生物修复前和 32 周后测定了受污染土壤中多环芳烃的解吸情况。与对照相比,添加 10%(w/w)MCD (M2)使总多环芳烃的 Tenax 提取量从 12%增加到 30%,并促进了高达 26%的降解。然而,Tenax 提取的总多环芳烃百分比远大于降解的百分比。因此,在对照和 M2 处理中,在初始阶段,多环芳烃的生物可利用性可能很高,而生物降解速率可能受到微生物过程的限制。另一方面,当用多环芳烃降解菌(CKB 和 MB2)接种土壤时,缓慢和非常缓慢解吸的部分(F sl 和 F vl )变得更大,并且缓慢和非常缓慢解吸的速率常数(k sl 和 k vl )在生物修复后变得极小,这表明解吸可能是在生物转化的第二阶段,即缓慢阶段中限速的。这些结果对场地风险评估和清理策略具有实际意义。

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