4.7 Article

Preferential removal of benzene, toluene, ethylbenzene, and xylene (BTEX) by persulfate in ethanol-containing aquifer materials

期刊

ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH
卷 29, 期 12, 页码 17617-17625

出版社

SPRINGER HEIDELBERG
DOI: 10.1007/s11356-021-16926-4

关键词

BTEX; Ethanol; Persulfate; In situ chemical oxidation; Bioremediation; Groundwater

资金

  1. Projects of National Natural Science Foundation of China [41967028]
  2. Guangxi Natural Science Foundation [2019GXNSFDA245030]

向作者/读者索取更多资源

This study investigated the batch experiment with different aquifer materials using persulfate as a chemical oxidant to oxidize organic contaminants. The results showed that BTEX could be preferentially removed with the addition of persulfate, while ethanol could compete with sulfate radical and potentially inhibit the biodegradation of BTEX.
The effective approaches to eliminate impacts of ethanol on the biodegradation of benzene, toluene, ethylbenzene, and xylene (BTEX) are concerned in the bioremediation of groundwater contaminated with ethanol-blended gasoline. In situ chemical oxidation (ISCO) is a common technique widely used for the remediation of contaminated groundwater. However, the selectivity of ISCO for BTEX and ethanol removal is poorly understood. Therefore, a batch experiment was performed with different aquifer materials, including calcareous soil, basalt soil, granite soil, dolomite, and sand. Gasoline was used to provide dissolved BTEX and ethanol reagent was used as additive to improve the quality of gasoline and to reduce the possibility of air pollution caused by gasoline. Persulfate (PS) was used as a chemical oxidant to oxidize organic contaminants. The target concentrations of BTEX and ethanol were 20 mg/L and 1000 mg/L, respectively. The results showed that ethanol could be preferentially degraded in the absence of PS and inhibit BTEX biodegradation. However, BTEX could be preferentially removed prior to ethanol in all aquifer materials used at ambient temperature, when PS was added at a PS/BTEX molar ratio of 150. Over 94% BTEX in sand, dolomite, and granite soil was preferentially removed with the first-order decay rate constants of 0.890-2.703 day(-1) within the first similar to 10 days, followed by calcareous and basalt soil at the constants of 0.123-0.371 day(-1). Ethanol could compete with BTEX for sulfate radical at the first-order decay rate constants of 0.005-0.060 day(-1) for the first 25 days, which was slower than that of BTEX. The pH quickly decreased to < 2.5 in dolomite, sand, and granite soil, but maintained > 6.2 in calcareous soil. Rich organic matter in calcareous and basalt soil had an inhibition effect on BTEX oxidation by PS. The pH buffer in calcareous soil may imply the potential of PS oxidation combined with bioremediation in carbonate rock regions.

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