Chemical Engineering Department, Research Institute for Chemical and Environmental Technology (ITQUIMA), University of Castilla-La Mancha, 13071 Ciudad Real, Spain.
Chemical Engineering Department, Research Institute for Chemical and Environmental Technology (ITQUIMA), University of Castilla-La Mancha, 13071 Ciudad Real, Spain.
Sci Total Environ. 2019 Feb 10;650(Pt 2):1961-1968. doi: 10.1016/j.scitotenv.2018.09.338. Epub 2018 Oct 1.
Oxyfluorfen is a non-polar herbicide that may cause severe soil pollution. The present work studies the possible improvement due to surfactant addition in the efficiency of electro-bioremediation of a clay soil polluted which such a non-polar, low-mobility pollutant. Two-week-long batch electro-bioremediation experiments were performed in a bench-scale device. Oxyfluorfen-polluted soil (20 mg kg) was inoculated with an acclimated microbial culture, and several experiments were performed using different surfactant concentrations in the electrode wells (0.0, 2.5, 5.0, 10.0 and 20.0 g L of SDS, sodium dodecyl sulphate). Experiments were performed under 1.0 V cm and electrode polarity reversal. It was observed that the electro-osmotic flow (EOF) increased with SDS concentration and that SDS was successfully distributed across the soil, probably improving the oxyfluorfen mobility. Additionally, microbiological activity was fully maintained during the experiments. Electro-bioremediation without SDS removed 14% of the oxyfluorfen, while under 2.5 g L SDS, the efficiency increased to 22% because of an expected improvement in the contact between the different species in the soil. However, higher SDS concentrations (between 10.0 and 20.0 g L) caused a decrease in the oxyfluorfen removal efficiency, as SDS is an easily biodegradable compound and was preferably used as substrate by the microbial culture instead of oxyfluorfen. Additionally, the use of high concentrations of SDS was clearly inefficient, as high amounts of the surfactant were lost through the EOF, and even low amounts of oxyfluorfen were removed to the electrode wells, which means that ex situ treatment of the polluted water would be needed.
氟氧氟草醚是一种非极性除草剂,可能会造成严重的土壤污染。本工作研究了在电生物修复过程中添加表面活性剂以提高低迁移性非极性污染物的修复效率的可能性。在实验室规模的设备中进行了为期两周的批处理电生物修复实验。将受氟氧氟草醚污染的土壤(20mgkg)接种到驯化的微生物培养物中,并在电极井中使用不同的表面活性剂浓度(0.0、2.5、5.0、10.0 和 20.0gLSDS,十二烷基硫酸钠)进行了多次实验。实验在 1.0Vcm 和电极极性反转下进行。结果表明,电渗流(EOF)随 SDS 浓度的增加而增加,SDS 成功地分布在土壤中,可能提高了氟氧氟草醚的迁移性。此外,在实验过程中微生物活性得到了完全维持。无 SDS 的电生物修复去除了 14%的氟氧氟草醚,而在 2.5gL SDS 下,由于土壤中不同物种之间的接触得到改善,效率提高到 22%。然而,更高浓度的 SDS(10.0 至 20.0gL)会降低氟氧氟草醚的去除效率,因为 SDS 是一种容易生物降解的化合物,更容易被微生物培养物用作基质而不是氟氧氟草醚。此外,高浓度 SDS 的使用显然效率不高,因为大量表面活性剂通过电渗流流失,即使只有少量的氟氧氟草醚被去除到电极井中,这意味着需要对污染水进行异位处理。