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利用生物双层渗透屏障修复甲基叔丁基醚污染地下水的实验室柱实验研究

Laboratory column study for remediation of MTBE-contaminated groundwater using a biological two-layer permeable barrier.

作者信息

Liu She-Jiang, Jiang Bin, Huang Guo-Qiang, Li Xin-Gang

机构信息

School of Chemical Engineering and Technology, Tianjin University, Tianjin 300072, PR China.

出版信息

Water Res. 2006 Oct;40(18):3401-8. doi: 10.1016/j.watres.2006.07.015. Epub 2006 Sep 7.

Abstract

In this study, an in situ biological two-layer permeable reactive barrier system consisting of an oxygen-releasing material layer followed by a biodegradation layer was designed to evaluate the remediation effectiveness of MTBE-contaminated groundwater. The first layer containing calcium peroxide (CaO(2)) and other inorganic salts is to provide oxygen and nutrients for the immobilized microbes in the second layer in order to keep them in aerobic condition and maintain their normal metabolism. Furthermore, inorganic salts such as potassium dihydrogen phosphate (KH(2)PO(4)) and ammonium sulphate ((NH(4))(2)SO(4)) can also decrease the high pH caused by the alkali salt degraded from CaO(2). The second layer using granular expanded perlite as microbial carrier is able to biodegrade MTBE entering the barrier system. Batch experiments were conducted to identify the appropriate components of oxygen-releasing materials and the optimum pH value for the biodegradation of MTBE. At pH=8.0, the biodegradation efficiency of MTBE is the maximum and approximately 48.9%. A laboratory-scale experiment using two continuous upflow stainless-steel columns was then performed to evaluate the feasibility of this designed system. The fist column was filled with oxygen-releasing materials at certain ratio by weight. The second column was filled with expanded perlite granules immobilizing MTBE-degrading microbial consortium. Simulated MTBE-contaminated groundwater, in which dissolved oxygen (DO) content was 0mg/L, was pumped into this system at a flow rate of 500mL/d. Samples from the second column were analyzed for MTBE and its major degradation byproduct. Results showed that MTBE could be removed, and its metabolic intermediate, tert-butyl alcohol (TBA), could also be further degraded in this passive system.

摘要

在本研究中,设计了一种原位生物双层渗透反应屏障系统,该系统由一个释氧材料层和一个生物降解层组成,用于评估对受甲基叔丁基醚(MTBE)污染的地下水的修复效果。第一层包含过氧化钙(CaO₂)和其他无机盐,其作用是为第二层中的固定化微生物提供氧气和养分,以使它们保持有氧状态并维持其正常代谢。此外,诸如磷酸二氢钾(KH₂PO₄)和硫酸铵((NH₄)₂SO₄)等无机盐还可以降低由CaO₂降解产生的碱盐所导致的高pH值。第二层使用颗粒膨胀珍珠岩作为微生物载体,能够对进入屏障系统的MTBE进行生物降解。进行了批次实验以确定释氧材料的合适成分以及MTBE生物降解的最佳pH值。在pH = 8.0时,MTBE的生物降解效率最高,约为48.9%。然后进行了一项使用两个连续上流式不锈钢柱的实验室规模实验,以评估该设计系统的可行性。第一个柱按一定重量比例填充释氧材料。第二个柱填充固定有MTBE降解微生物群落的膨胀珍珠岩颗粒。将溶解氧(DO)含量为0mg/L的模拟MTBE污染地下水以500mL/d的流速泵入该系统。对第二个柱的样品进行MTBE及其主要降解副产物分析。结果表明,在这个被动系统中MTBE可以被去除,其代谢中间体叔丁醇(TBA)也可以进一步降解。

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