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Surface catalyzed Fenton treatment of bis(2-chloroethyl) ether and bis(2-chloroethoxy) methane

机译:双(2-氯乙基)醚和双(2-氯乙氧基)甲烷的表面催化Fenton处理

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This study examined the feasibility of using surface catalyzed Fenton treatment to remediate soil and groundwater contaminated by the chlorinated ethers, bis(2-chloroethyl) ether (BCEE) and bis(2-chloroethoxy) methane (BCEM). Parameters that affect the contaminant loss rate such as porewater pH, hydrogen peroxide concentration, and solid/water ratio were systematically evaluated. Batch reactors were set-up utilizing either contaminated or uncontaminated soil, obtained from an industrial site in Moss Point, MS, that was mixed with synthetic groundwater containing the contaminants of interest. The results show an increase in contaminant reduction with a decrease in pH, an increase in hydrogen peroxide concentration, or an increase in the solid/water ratio. For a similar set of conditions, contaminant reduction was greater for systems utilizing contaminated soil as compared to the systems containing uncontaminated soil. In addition, specific oxygen uptake rates (SOURs) were measured for biomass, collected from an activated sludge plant, exposed to different dilutions of untreated and surface catalyzed Fenton treated water to evaluate whether residual BCEE, BCEM, and their co-contaminants as well as their oxidation by-products were potentially inhibitory or can potentially serve as a substrate for the biomass. The measured SOURs show that the surface catalyzed Fenton treatment enhanced the biodegradability of the contaminated groundwater and served as a substrate for the biomass.
机译:这项研究检验了使用表面催化的Fenton处理来修复被氯化醚,双(2-氯乙基)醚(BCEE)和双(2-氯乙氧基)甲烷(BCEM)污染的土壤和地下水的可行性。系统地评估了影响污染物损失率的参数,例如孔隙水pH值,过氧化氢浓度和固水比。使用从密苏里州莫斯波因特的工业基地获得的受污染或未受污染的土壤设置间歇式反应器,将其与含有目标污染物的合成地下水混合。结果表明,随着pH的降低,过氧化氢浓度的增加或固/水比的增加,污染物减少的增加。在一组类似的条件下,与含有未污染土壤的系统相比,利用污染土壤的系统减少的污染物更大。此外,还测量了从活性污泥厂收集的生物质的特定氧气吸收率(SOURs),将其暴露于未经稀释的Fenton处理过的和表面催化的Fenton处理过的不同稀释液中,以评估是否残留BCEE,BCEM及其共污染物以及它们的氧化副产物可能具有抑制作用,或可能充当生物质的底物。测得的SOURs表明,表面催化的Fenton处理增强了被污染地下水的生物降解能力,并作为生物质的底物。

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