Center of Health & Bioresources, Bioresources, AIT Austrian Institute of Technology GmbH, Konrad-Lorenz-Strasse 24, 3430, Tulln a.d. Donau, Austria.
Quality Management, AIT Austrian Institute of Technology GmbH, 2444, Seibersdorf, Austria.
N Biotechnol. 2020 Jul 25;57:34-44. doi: 10.1016/j.nbt.2020.02.005. Epub 2020 Apr 1.
Perchloroethene (PCE) is a hazardous and persistent groundwater pollutant. Both treatment with nanoscaled zero-valent iron (nZVI) and biological degradation by bacteria have downsides. Distribution of nZVI underground is difficult and a high percentage of injected nZVI is consumed by anaerobic corrosion, forming H rather than being available for PCE dechlorination. On the other hand, microbial PCE degradation can suffer from the absence of H. This can cause the accumulation of the hazardous metabolites cis-1,2-dichloroethene (DCE) or vinylchloride (VC). The combination of chemical and biological PCE degradation is a promising approach to overcome the disadvantages of each method alone. In this lysimeter study, artificial aquifers were created to test the influence of nZVI on anaerobic microbial PCE dechlorination by a commercially available culture containing Dehalococcoides spp. under field-like conditions. The effect of the combined treatment was investigated with molasses as an additional electron source and after cessation of molasses addition. The combination of nZVI and the Dehalococcoides spp. containing culture led to a PCE discharge in the lysimeter outflow that was 4.7 times smaller than that with nZVI and 1.6 times smaller than with bacterial treatment. Moreover, fully dechlorinated end-products showed an 11-fold increase compared to nZVI and a 4.2-fold increase compared to the microbial culture. The addition of nZVI to the microbial culture also decreased the accumulation of hazardous metabolites by 1.7 (cis-DCE) and 1.2 fold (VC). The stimulatory effect of nZVI on microbial degradation was most obvious after the addition of molasses was stopped.
全氯乙烯 (PCE) 是一种危险且持久的地下水污染物。纳米零价铁 (nZVI) 处理和细菌生物降解都有其缺点。nZVI 在地下的分布困难,注入的 nZVI 很大一部分被厌氧腐蚀消耗,形成 H,而不是可用于 PCE 脱氯。另一方面,微生物 PCE 降解可能会因 H 的缺乏而受到影响。这可能导致危险代谢物顺-1,2-二氯乙烯 (DCE) 或氯乙烯 (VC) 的积累。化学和生物 PCE 降解的组合是克服每种方法单独使用的缺点的一种有前途的方法。在这项淋溶试验研究中,人工含水层是为了在类似于现场的条件下,通过一种含有 Dehalococcoides spp. 的商业可用培养物,测试 nZVI 对厌氧微生物 PCE 脱氯的影响而创建的。研究了在添加糖蜜作为额外电子源和停止添加糖蜜后的联合处理的效果。nZVI 与含有 Dehalococcoides spp. 的培养物的组合导致淋溶流出物中的 PCE 排放量比单独使用 nZVI 时小 4.7 倍,比单独使用细菌处理时小 1.6 倍。此外,与 nZVI 相比,完全脱氯的终产物增加了 11 倍,与微生物培养物相比增加了 4.2 倍。向微生物培养物中添加 nZVI 还将危险代谢物的积累减少了 1.7 倍(顺-DCE)和 1.2 倍(VC)。停止添加糖蜜后,nZVI 对微生物降解的刺激作用最为明显。