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利用 UV/亚硫酸盐工艺在复杂水基质中还原降解全氟辛酸。

Reductive degradation of perfluorooctanoic acid in complex water matrices by using the UV/sulfite process.

机构信息

Chemical Process Engineering, University of Oulu, P.O. Box 4300, Oulu FIN-90014, Finland.

Department of Biochemistry and Biocenter, University of Oulu, Oulu FIN-99020, Finland.

出版信息

Water Res. 2021 Oct 15;205:117676. doi: 10.1016/j.watres.2021.117676. Epub 2021 Sep 22.

Abstract

Hydrated electrons (eE= -2.9 V) generated by advanced reduction processes (ARPs) have been proved to be a promising approach to eliminate various per- and polyfluoroalkyl substances (PFASs) in water. In this study, the decomposition of perfluorooctanoic acid (PFOA) in a complex water matrix by e generated from the UV/sulfite process was investigated. The effect of pH (9-12) and co-existing compounds (chloride, nitrate, phosphate, carbonate and humic acid) on PFOA degradation efficiency was studied. In addition, the intermediates and possible degradation pathways were analyzed by ultra-high performance liquid chromatography-tandem mass spectrometry (UPLC-MS). The results showed that the concentration of PFOA was below the detection limit (10 μg/L) after 1 h (conditions: C 10 mg/L, initial pH = 10, sulfite 10 mM) while 89% defluorination was achieved after 24 h. Using a higher initial pH (pH = 12) greatly enhanced the PFOA degradation as 100% degradation and 98% defluorination were achieved after 24 h. The presence of carbonate (> 5 mM), nitrate (> 2 mM) and humic acid (> 25 mg/L) showed a significant negative effect on PFOA degradation via a UV blocking effect or quenching of hydrated electrons while the presence of chloride and phosphate had a smaller effect on PFOA degradation. Even at extremely high concentrations of chloride (1.709 M, pH = 11.25), the defluorination ratio reached 97% after 24 h of reaction time. During the process, short-chain perfluorinated carboxylic acids (PFCAs, C < 7) and hydrogen substituted compounds were detected, which implies that chain-shortening and H/F change reactions had occurred. Moreover, this confirmed the generation of sulfonated and unsaturated intermediates during the process, which disclosed valuable new mechanistic insights into PFOA degradation.

摘要

水合电子(eE=-2.9V)是通过先进的还原过程(ARPs)产生的,已被证明是消除水中各种全氟和多氟烷基物质(PFASs)的一种很有前途的方法。在本研究中,研究了由 UV/亚硫酸盐过程产生的 e 还原水中全氟辛酸(PFOA)的情况。考察了 pH 值(9-12)和共存化合物(氯离子、硝酸盐、磷酸盐、碳酸盐和腐殖酸)对 PFOA 降解效率的影响。此外,通过超高效液相色谱-串联质谱(UPLC-MS)分析了中间产物和可能的降解途径。结果表明,在 1 小时(条件:C10mg/L,初始 pH=10,亚硫酸盐 10mM)后,PFOA 的浓度低于检测限(10μg/L),而在 24 小时后达到 89%的除氟率。使用较高的初始 pH 值(pH=12)可极大地增强 PFOA 的降解效果,在 24 小时后可达到 100%的降解率和 98%的除氟率。当存在碳酸盐(>5mM)、硝酸盐(>2mM)和腐殖酸(>25mg/L)时,由于紫外线阻断作用或水合电子的猝灭,对 PFOA 的降解会产生明显的负面影响,而氯离子和磷酸盐的存在对 PFOA 的降解影响较小。即使在氯离子浓度极高的情况下(1.709M,pH=11.25),反应 24 小时后除氟率仍达到 97%。在此过程中,检测到短链全氟羧酸(PFCAs,C<7)和氢取代化合物,这意味着发生了链缩短和 H/F 取代反应。此外,这证实了在该过程中生成了磺化和不饱和中间产物,这为 PFOA 降解提供了有价值的新机制见解。

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