Yang Shuai, Shi Yang, Wang Xinhao, Liu Yang, Ren Yi, Li Wei, Zhang Heng, Dai Xiaoqiang, Sun Weiyi, Lai Bo
State Key Laboratory of Hydraulics and Mountain River Engineering, College of Architecture and Environment, Sichuan University, Chengdu 610065, China; Sino-German Centre for Water and Health Research, Sichuan University, Chengdu 610065, China.
State Key Laboratory of Hydraulics and Mountain River Engineering, College of Architecture and Environment, Sichuan University, Chengdu 610065, China; Sino-German Centre for Water and Health Research, Sichuan University, Chengdu 610065, China; Water Safety and Water Pollution Control Engineering Technology Research Center in Sichuan Province, Haitian Water Group, China.
Water Res. 2023 Aug 15;242:120317. doi: 10.1016/j.watres.2023.120317. Epub 2023 Jul 5.
Natural organic matter, specifically ortho-quinones organics among them, was considered can participate in the transformation of sulfonamide antibiotics (SAs). Herein, based on targeted oxidizing for ortho-dihydroxyl structures (catechol as the model) upon periodate, an efficient approach for SAs elimination was introduced. Results first indicated the generation of ortho-benzoquinone (o-BQ) within periodate/catechol system progresses readily (the energy barriers for 9.6854 kcal/mol). The near-complete eliminations were observed towards sulfamethoxazole (SMX) in periodate/catechol system (with the rate of 0.4229 min) as well as other SAs and exhibited unprecedented resistance to operating parameters. Besides, periodate converts little into toxic low-valent iodate species during the reaction process, and both the cytotoxicity and acute toxicity assays revealed a significant decline in antibiotics bioactivity. Mechanistic insight revealed that o-BQ dominated the degradation process, comprehensive analysis further confirmed Michael addition reaction was the first degradation stage, in which electrons flow from o-BQ to SMX and form covalent bonds upon aniline. Furthermore, several catechol derivatives were used to verify the universality of the mechanism, and their wide distribution in both subsurface and wastewater implies the potential applications. Overall, the mechanisms elucidated behind this research proposed an efficient strategy for eliminating trace SAs in aqueous environments and selectively removing SAs from complex wastewater matrices.
天然有机物,特别是其中的邻醌类有机物,被认为可以参与磺胺类抗生素(SAs)的转化。在此,基于高碘酸盐对邻二羟基结构(以儿茶酚为模型)的靶向氧化,引入了一种高效去除SAs的方法。结果首先表明,高碘酸盐/儿茶酚体系中邻苯醌(o-BQ)的生成进展顺利(能垒为9.6854千卡/摩尔)。在高碘酸盐/儿茶酚体系中观察到对磺胺甲恶唑(SMX)以及其他SAs的近乎完全去除(速率为0.4229分钟),并且对操作参数表现出前所未有的抗性。此外,在反应过程中高碘酸盐几乎不会转化为有毒的低价碘酸盐物种,细胞毒性和急性毒性试验均表明抗生素的生物活性显著下降。机理研究表明,o-BQ主导了降解过程,综合分析进一步证实迈克尔加成反应是第一个降解阶段,其中电子从o-BQ流向SMX并在苯胺上形成共价键。此外,使用了几种儿茶酚衍生物来验证该机理的普遍性,它们在地下和废水中的广泛分布意味着潜在的应用。总体而言,本研究阐明的机理提出了一种在水环境中去除痕量SAs以及从复杂废水基质中选择性去除SAs的有效策略。