热激活过硫酸盐在水生环境中降解人工甜味剂糖精的功效和机制

IF 4.3 3区 材料科学 Q1 ENGINEERING, ELECTRICAL & ELECTRONIC ACS Applied Electronic Materials Pub Date : 2024-07-11 DOI:10.1039/D4EW00357H
Webber Wei-Po Lai and Chia-Ming Chang
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摘要

人工甜味剂可能对生态系统构成威胁,是水生环境中普遍存在的新污染物。本研究首次探讨了热激活过硫酸盐处理(热/过硫酸盐)降解糖精的功效和机理。在以下条件下,糖精降解遵循伪一阶动力学,kobs 值为 0.023 min-1:[糖精]0 = 5 mg L-1,[过硫酸盐]0 = 100 mg L-1,温度 = 70 °C,溶液 pH = 7.0。最佳的糖精降解发生在中性和弱酸性 pH 条件下(pH 值为 7 和 5),计算得出的糖精表观活化能为 113.3 kJ mol-1。清除剂实验和电子顺磁共振鉴定的结果表明,SO4˙- 和 -OH 是参与糖精降解的主要自由基物种,其中 -OH 可能起主要作用。HCO3-、NO3-和溶解的有机物与糖精竞争自由基,降低了糖精的降解速率;然而,Cl-具有积极的作用。糖精降解包括单羟基化和二羟基化,并分别产生 TP1 和 TP2。在处理过程中,TOC 降低了 35%,Microtox® 的毒性先增加后降低,这表明糖精及其转化副产物发生了矿化和解毒作用。糖精在实际水基质中的降解率低于去离子水。总之,这项工作全面研究了热活化过硫酸盐处理对糖精的降解,为今后在水/废水处理中的应用提供了参考。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

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Efficacy and mechanism of the artificial sweetener saccharin degradation by thermally activated persulfate in aquatic environments†

Artificial sweeteners, which potentially pose threats to ecosystems, are prevalent emerging contaminants in aquatic environments. This study explored the efficacy and mechanism underlying the degradation of saccharin by thermally activated persulfate treatment (thermal/persulfate) for the first time. Saccharin degradation followed pseudo-first-order kinetics, with a kobs value of 0.023 min−1 under the following conditions: [saccharin]0 = 5 mg L−1, [persulfate]0 = 100 mg L−1, temperature = 70 °C and solution pH = 7.0. Optimal saccharin degradation occurred under neutral and weakly acidic pH conditions (pH 7 and 5), and the calculated apparent activation energy of saccharin was 113.3 kJ mol−1. The results from the scavenger experiments and electron paramagnetic resonance identification revealed that SO4˙ and ·OH were the predominant radical species involved in saccharin degradation, with ·OH likely playing the major role. HCO3, NO3, and dissolved organic matter competed with saccharin for free radicals, decreasing the saccharin degradation rate; however, Cl had a positive effect. Saccharin degradation involved monohydroxylation and dihydroxylation and produced TP1 and TP2, respectively. During treatment, 35% TOC reduction was achieved, and the Microtox® toxicity initially increased and then decreased, suggesting that saccharin and its transformation byproducts undergo mineralization and detoxification. The saccharin degradation rate was lower in actual water matrices than in deionized water. In conclusion, this work comprehensively investigated the degradation of saccharin by thermally activated persulfate treatment for future applications in water/wastewater treatment.

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567
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