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采用过硫酸盐修饰的铁改性反应性活性炭从水中及水/土壤泥浆中去除全氟烷基和多氟烷基物质。

Removal of perfluoroalkyl and polyfluoroalkyl substances in water and water/soil slurry using Fe -modified reactive activated carbon conjugated with persulfate.

机构信息

Department of Civil Engineering, The University of Texas at Arlington, Arlington, Texas, USA.

Ramboll Americas Engineering, Syracuse, New York, USA.

出版信息

Water Environ Res. 2022 Jan;94(1):e1671. doi: 10.1002/wer.1671. Epub 2021 Dec 15.

Abstract

Treatment of highly persistent perfluoroalkyl and polyfluoroalkyl substances (PFAS) has been a challenging but significant task. Herein, we propose adsorption-mediated chemical decomposition of PFAS implemented by using granular activated carbon (GAC) impregnated with zerovalent nanoiron (ZVI, Fe ), so-called reactive activated carbon (RAC). The effects of reaction temperature, injection of persulfate (PS), and presence of soil on removal of PFAS in water were evaluated. Results showed that RAC conjugated with PS at 60°C exhibited decomposition of PFAS, exclusively all three carboxylic PFAS tested, obviously producing various identifiable short-chain PFAS. Carboxylic PFAS were removed via physical adsorption combined with chemical decomposition while sulfonic PFAS were removed via solely adsorption mechanism. The presence of soil particles did not greatly affect the overall removal of PFAS. Carbon mass balance suggested that chemical oxidation by radical mechanisms mutually influences, in a complex manner, PFAS adsorption to GAC, ZVI and its iron derivatives, and soil particles. Nonetheless, all tested six PFAS were removed significantly. If successfully developed, the adsorption-mediated decomposition strategy may work for treatment of complex media containing PFAS and co-contaminants under different environmental settings. PRACTITIONERS POINTS: Treatment of persistent per- and polyfluoroalkyl substances (PFAS) was addressed. Activated carbon with zerovalent iron was examined in the presence of persulfate. The system significantly removed and decomposed PFAS in water and soil mixture.

摘要

处理持久性全氟烷基和多氟烷基物质(PFAS)一直是一项具有挑战性但意义重大的任务。在此,我们提出了一种通过使用负载零价纳米铁(Fe)的颗粒活性炭(GAC),即反应性活性炭(RAC)来实现的吸附介导的 PFAS 化学分解方法。评估了反应温度、过硫酸盐(PS)注入和土壤存在对水中 PFAS 去除的影响。结果表明,在 60°C 下,RAC 与 PS 结合表现出 PFAS 的分解作用,仅对三种测试的羧酸 PFAS 明显产生各种可识别的短链 PFAS。羧酸 PFAS 通过物理吸附与化学分解去除,而磺酸 PFAS 通过仅吸附机制去除。土壤颗粒的存在并没有极大地影响 PFAS 的整体去除。碳质量平衡表明,自由基机制的化学氧化以复杂的方式相互影响 PFAS 在 GAC、ZVI 及其铁衍生物和土壤颗粒上的吸附。尽管如此,所有测试的六种 PFAS 都被显著去除。如果成功开发,这种吸附介导的分解策略可能适用于在不同环境条件下处理含有 PFAS 和共存污染物的复杂介质。

实践者要点

处理持久性全氟烷基和多氟烷基物质(PFAS)。

在过硫酸盐存在下检查负载零价铁的活性炭。

该系统显著去除和分解了水和土壤混合物中的 PFAS。

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