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反渗透会改变氯胺的形态,导致污水回用过程中 NDMA 的重新形成。

Reverse Osmosis Shifts Chloramine Speciation Causing Re-Formation of NDMA during Potable Reuse of Wastewater.

机构信息

Department of Civil and Environmental Engineering, Stanford University , Stanford, California 94305, United States.

Orange County Water District , Fountain Valley, California 92708, United States.

出版信息

Environ Sci Technol. 2017 Aug 1;51(15):8589-8596. doi: 10.1021/acs.est.7b01641. Epub 2017 Jul 18.

Abstract

UV-based advanced oxidation processes (AOPs) effectively degrade N-nitrosodimethylamine (NDMA) passing through reverse osmosis (RO) units within advanced treatment trains for the potable reuse of municipal wastewater. However, certain utilities have observed the re-formation of NDMA after the AOP from reactions between residual chloramines and NDMA precursors in the AOP product water. Using kinetic modeling and bench-scale RO experiments, we demonstrate that the low pH in the RO permeate (∼5.5) coupled with the effective rejection of NH promotes conversion of the residual monochloramine (NHCl) in the permeate to dichloramine (NHCl) via the reaction: 2 NHCl + H ↔ NHCl + NH. Dichloramine is the chloramine species known to react with NDMA precursors to form NDMA. After UV/AOP, utilities generally use lime or other techniques to increase the pH of the finished water to prevent distribution system corrosion. Modeling indicated that, while the increase in pH halts dichloramine formation, it converts amine-based NDMA precursors to their more reactive, neutral forms. With modeling, and experiments at both bench-scale and field-scale, we demonstrate that reducing the time interval between RO treatment and final pH adjustment can significantly reduce NDMA re-formation by minimizing the amount of dichloramine formed prior to reaching the final target pH.

摘要

基于紫外线的高级氧化工艺 (AOP) 可有效降解通过反渗透 (RO) 单元的 N-亚硝基二甲胺 (NDMA),这些反渗透单元位于市政污水饮用再利用的高级处理系统中。然而,某些公用事业公司在 AOP 之后观察到 NDMA 的重新形成,这是由于 AOP 产物水中残留的氯胺与 AOP 产物水中的 NDMA 前体之间的反应所致。通过使用动力学建模和台式 RO 实验,我们证明了 RO 渗透物中的低 pH 值(约 5.5)以及 NH 的有效截留促进了残留的一氯胺(NHCl)通过反应转化为二氯胺(NHCl):2 NHCl + H ↔ NHCl + NH。二氯胺是已知与 NDMA 前体反应形成 NDMA 的氯胺物质。在 UV/AOP 之后,公用事业公司通常使用石灰或其他技术来提高产水的 pH 值,以防止分配系统腐蚀。建模表明,尽管 pH 值的升高会阻止二氯胺的形成,但会将基于胺的 NDMA 前体转化为更具反应性的中性形式。通过建模以及台式和现场规模的实验,我们证明通过在达到最终目标 pH 值之前最小化形成的二氯胺量,可以显著减少 NDMA 的重新形成,从而减少 RO 处理和最终 pH 调整之间的时间间隔。

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