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一种新型太阳能激活二氧化氯工艺,用于饮用水中莠去津的降解。

A novel solar-activated chlorine dioxide process for atrazine degradation in drinking water.

机构信息

Ministry of Education Key Laboratory of Integrated Regulation and Resource Development on Shallow Lakes, Hohai University, Nanjing 210098, PR China; College of Environment, Hohai University, Nanjing 210098, PR China.

Ministry of Education Key Laboratory of Integrated Regulation and Resource Development on Shallow Lakes, Hohai University, Nanjing 210098, PR China; College of Environment, Hohai University, Nanjing 210098, PR China.

出版信息

Water Res. 2023 Jul 1;239:120056. doi: 10.1016/j.watres.2023.120056. Epub 2023 May 6.

Abstract

New technologies using advanced oxidation processes (AOPs) with low energy-input to address the presence of micro-contaminants and the formation of disinfection byproducts (DBPs) are required for drinking water safety. In this work, the activation of chlorine dioxide with solar (solar/ClO process), a type of renewable and inexhaustible energy, was developed to degrade atrazine (ATZ) and control the formation of DBPs. Results revealed that solar/ClO process was effective in degrading ATZ. Hydroxyl radicals (•OH) and chlorine radicals (Cl•) produced in solar/ClO process were found to be the predominant agents for ATZ degradation with contribution rates of 55.9% and 44.1%, respectively, based on radical quenching tests and competition kinetics. Reaction pH did not affect the total amount of Cl• and •OH (i.e., [•OH]) and [Cl•]), while the conversion of Cl• to •OH was responsible for the depressed ATZ degradation efficiency with the increasing pH in solar/ClO process. The presence of bicarbonate (HCO), chloride (Cl) and humic acid (HA) retarded the ATZ degradation mainly due to they decreased [•OH]) and [Cl•]. Using the UPLC-MS/MS analysis, six degradation intermediates of ATZ were tentatively identified, and the three-stage degradation pathway as well as the stepwise detoxification of ATZ were confirmed by the condensed Fukui function (CFF) calculation and ECOSAR prediction. Applying solar/ClO as a pretreatment of HA-containing water, the formation of DBPs during post-chlorination was significantly reduced. However, the presence of ATZ during solar/ClO pretreatment of HA significantly lowered the control efficiency of DBPs. The major degradation intermediate, i.e., deethyldeisopropylhydroxyatrazine (DEIHA), of ATZ could incorporate into HA and therefore providing more precursors for DBPs. The acute toxicity recorded by the behavior of zebrafish larvae revealed that using chloramine instead of chlorine downstream the solar/ClO pretreatment of ATZ and HA could significantly reduce the acute toxicity by decreasing the formation of total DBPs. This study demonstrated the great potential of applying solar/ClO process followed by chloramination to simultaneously degrade micro-contaminants and reduce DBPs formation as well as toxic risk in practical applications.

摘要

需要利用低能耗的先进氧化工艺(AOPs)新技术来解决微污染物的存在和消毒副产物(DBPs)的形成问题,以确保饮用水安全。在这项工作中,利用太阳能(太阳能/ClO 工艺)激活二氧化氯,作为一种可再生和取之不尽的能源,来降解莠去津(ATZ)并控制 DBPs 的形成。结果表明,太阳能/ClO 工艺能有效降解 ATZ。通过自由基猝灭实验和竞争动力学,发现太阳能/ClO 工艺中产生的羟基自由基(•OH)和氯自由基(Cl•)是 ATZ 降解的主要因素,其贡献分别为 55.9%和 44.1%。反应 pH 不影响 Cl•和•OH(即[•OH])和[Cl•]的总量,但随着太阳能/ClO 工艺 pH 的增加,Cl•向•OH 的转化导致 ATZ 降解效率降低。碳酸氢根(HCO)、氯离子(Cl)和腐殖酸(HA)的存在主要由于它们降低了[•OH]和[Cl•],从而阻碍了 ATZ 的降解。通过 UPLC-MS/MS 分析,初步鉴定了 ATZ 的 6 种降解中间产物,并通过凝聚福井函数(CFF)计算和 ECOSAR 预测,确认了 ATZ 的三阶段降解途径和逐步解毒。将太阳能/ClO 作为含 HA 水的预处理方法,可以显著降低后续氯化过程中 DBPs 的形成。然而,在太阳能/ClO 预处理 HA 的过程中存在 ATZ 会显著降低 DBPs 的控制效率。ATZ 的主要降解中间产物,即去乙基去异丙基羟基莠去津(DEIHA),可以与 HA 结合,从而为 DBPs 的形成提供更多的前体。通过斑马鱼幼虫的行为记录的急性毒性表明,在太阳能/ClO 预处理 ATZ 和 HA 之后,使用氯胺而不是氯气,可以通过减少总 DBPs 的形成,显著降低急性毒性。本研究表明,在实际应用中,采用太阳能/ClO 工艺后再接氯胺处理,同时降解微污染物和减少 DBPs 形成以及降低毒性风险具有很大的潜力。

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