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受藻类污染的氯化水的毒性:消毒副产物的形成与藻毒素的减少。

Toxicity of chlorinated algal-impacted waters: Formation of disinfection byproducts vs. reduction of cyanotoxins.

机构信息

Key Laboratory of Drinking Water Science and Technology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing, 100085, China; Department of Environmental Engineering and Earth Sciences, Clemson University, Anderson, SC, 29625, USA.

Department of Environmental Engineering and Earth Sciences, Clemson University, Anderson, SC, 29625, USA.

出版信息

Water Res. 2020 Oct 1;184:116145. doi: 10.1016/j.watres.2020.116145. Epub 2020 Jul 9.

Abstract

Seasonal algal blooms in surface waters can impact water quality through an input of algal organic matter (AOM) to the pool of dissolved organic matter as well as the release of cyanotoxins. The formation and speciation of disinfection byproducts (DBPs) during chlorination of algal-impacted waters, collected from growth of Microcystis aeruginosa were studied. Second-order rate constants for the reactions of microcystins (MCs) with chlorine and bromine were determined. Finally, the toxicity of chlorinated algal-impacted waters was evaluated by Chinese hamster ovary (CHO) cytotoxicity and genotoxicity assays. Under practical water treatment conditions, algal-impacted waters produced less regulated trihalomethanes (THMs) and haloacetic acids (HAAs), haloacetonitriles (HANs), and total organic halogen (TOX) than natural organic matter (NOM). For example, the weight ratios of DBP formation from AOM to NOM (median levels) were approximately 1:5, 1:3, 1:2 and 1:3 for THMs, HAAs, HANs, and TOX, respectively. Increasing initial bromide level significantly enhanced THM and HAN concentrations, and therefore unknown TOX decreased. The second-order rate constant for the reactions of MC-LR (the most common MC species) with chlorine was 60 M s at pH 7.5 and 21 °C, and the rate constants for MC congeners follow the order: MC-WR > MC-LW > MC-YR > MC-LY > MC-LR ≈ MC-RR. The reaction rate constant of bromine with MC-LR is two orders of magnitude higher than that of chlorine. Unchlorinated algal-impacted waters were toxic owning to the presence of MCs, and chlorination enhanced their cytotoxicity and genotoxicity due to the formation of toxic halogenated DBPs. However, the toxicity of treated waters depended on the evolution of cyanotoxins and formation of DBPs (particularly unknown or emerging DBPs).

摘要

季节性藻类水华会通过输入藻类有机物质(AOM)到溶解有机物质池中以及释放蓝藻毒素来影响水质。研究了从铜绿微囊藻生长中收集的受藻类影响的水在氯化过程中消毒副产物(DBP)的形成和形态。确定了微囊藻毒素(MCs)与氯和溴的二级反应速率常数。最后,通过中国仓鼠卵巢(CHO)细胞毒性和遗传毒性测定评估了氯化藻类影响水的毒性。在实际水处理条件下,受藻类影响的水产生的法规三卤甲烷(THMs)和卤乙酸(HAAs)、卤乙腈(HANs)和总有机卤素(TOX)比天然有机物(NOM)少。例如,DBP 形成的重量比(中值水平)从 AOM 到 NOM 分别约为 1:5、1:3、1:2 和 1:3,分别用于 THMs、HAAs、HANs 和 TOX。初始溴化物水平的增加显著提高了 THM 和 HAN 的浓度,因此未知的 TOX 减少了。MC-LR(最常见的 MC 物种)与氯的反应二级速率常数在 pH 7.5 和 21°C 时为 60 M s,MC 同系物的速率常数顺序为:MC-WR>MC-LW>MC-YR>MC-LY>MC-LR≈MC-RR。溴与 MC-LR 的反应速率常数比氯高两个数量级。未氯化的受藻类影响的水因存在 MCs 而具有毒性,氯化由于形成有毒的卤代 DBP,增强了其细胞毒性和遗传毒性。然而,处理水的毒性取决于藻毒素的演变和 DBP 的形成(特别是未知或新兴的 DBP)。

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