Instrumental Analytical Chemistry, University of Duisburg-Essen, Universitätsstr. 5, 45141 Essen, Germany; Centre for Water and Environmental Research (ZWU), University of Duisburg-Essen, Universitätsstr. 2, 45141 Essen, Germany.
Instrumental Analytical Chemistry, University of Duisburg-Essen, Universitätsstr. 5, 45141 Essen, Germany.
Sci Total Environ. 2021 Apr 15;765:142727. doi: 10.1016/j.scitotenv.2020.142727. Epub 2020 Oct 6.
Micropollutants reach the aquatic environment through wastewater treatment plant effluents. Ozonation, applied in wastewater treatment for micropollutants abatement, can yield transformation products (TP), which might be of ecotoxicological concern. Previous studies on TP formation were mostly performed in ultrapure water. However, the water matrix can have a substantial influence and lead to unpredictable yields of TPs with toxicological potential. In this study the acute toxicity (immobilization) of the parent substances (isoproturon and metoprolol) and also of available TPs of isoproturon, metoprolol and diclofenac towards Daphnia magna (D. magna) were investigated. Further, the acute toxicity of TP mixtures, formed during ozonation of isoproturon, metoprolol and diclofenac was evaluated in the following systems: in the presence of radical scavengers (tert-butanol and dimethyl sulfoxide) and in the presence of hypobromous acid (HOBr), a secondary oxidant in ozonation. For all tested substances and TP standards, except 2,6-dichloroaniline (EC 1.02 mg/L (48 h)), no immobilization of D. magna was detected. Ozonated pure water and wastewater did not show an immobilization effect either. After ozonation of diclofenac in the presence of dimethyl sulfoxide 95% (48 h) of the daphnids were immobile. Ozonation of parent substances, after the reaction with HOBr, showed no effect for isoproturon but a high effect on D. magna for diclofenac (95% immobilization (48 h)) and an even higher effect for metoprolol (100% immobilization (48 h)). These results emphasize that complex water matrices can influence the toxicity of TPs as shown in this study for D. magna.
微污染物通过污水处理厂的废水进入水生环境。臭氧化处理应用于微污染物的去除,会产生转化产物 (TP),可能具有生态毒理学关注。以前关于 TP 形成的研究主要在超纯水中进行。然而,水基质会产生实质性的影响,并导致具有潜在毒性的 TP 的产量不可预测。在这项研究中,研究了母体物质(异丙隆和甲氧普隆)以及异丙隆、甲氧普隆和双氯芬酸的可用 TP 对大型溞(Daphnia magna)的急性毒性(固定化)。此外,还评估了在以下系统中形成的 TP 混合物对臭氧氧化的异丙隆、甲氧普隆和双氯芬酸的急性毒性:存在自由基清除剂(叔丁醇和二甲亚砜)和存在次溴酸(HOBr)时,臭氧氧化中的一种次要氧化剂。除 2,6-二氯苯胺(EC 1.02 mg/L(48 h))外,所有测试的物质和 TP 标准均未检测到 D. magna 的固定化。臭氧氧化的纯水和废水也没有显示出固定化作用。在二甲亚砜存在下臭氧氧化双氯芬酸后,95%(48 h)的大型溞不能固定。母体物质与 HOBr 反应后的臭氧氧化对异丙隆没有影响,但对双氯芬酸对 D. magna 有很高的影响(95%固定化(48 h)),对甲氧普隆的影响甚至更高(100%固定化(48 h))。这些结果强调了复杂的水基质可以影响 TP 的毒性,正如本研究中对 D. magna 所显示的那样。