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在 Fe(III)-EDDS 活化过硫酸盐体系中磺胺嘧啶的光降解性能和机制。

Photodegradation performance and mechanism of sulfadiazine in Fe(III)-EDDS-activated persulfate system.

机构信息

School of Resources, Environment and Materials, Guangxi University, Nanning, People's Republic of China.

Guangxi Bossco Environmental Protection Technology Co., Ltd, Nanning, People's Republic of China.

出版信息

Environ Technol. 2023 Sep;44(23):3518-3531. doi: 10.1080/09593330.2022.2064238. Epub 2022 Apr 25.

Abstract

In order to overcome the shortcomings in the traditional Fenton process, Fe(III)-EDDS-activated persulfate advanced oxidation process under irradiation is carried out as a promising technology. The photodegradation of sulfadiazine (SD) in Fe(III)-EDDS-activated persulfate system was investigated in this paper. The results showed that SD could be effectively degraded in Fe(III)-EDDS//hv system. The effects of Fe(III):EDDS molar ratio, the concentration of Fe(III)-EDDS, and the concentration of on SD degradation were explored. At neutral pH, when Fe(III):EDDS = 1:1, Fe(III)-EDDS = 0.1 mM,  = 1.5 mM, the best SD degradation was achieved. The experiment of external influence factors showed that the degradation of SD could be obviously inhibited by the presence of , , whereas the degradation of SD was almost unaffected by the addition ofCl. The degradation of SD could be slightly inhibited by the presence of humic acid and NO. The effect of pH on SD degradation was investigated, and SD could be degraded effectively in the pH range of 3-9. ESR proved that O, ·OH, , and O were produced in the process. and ·OH were identified as the main radicals while O also played non-ignorable role. Eleven intermediate products of SD were analysed. The C = N, S-N, and S-C bonds of SD were attacked by radicals firstly, leading to a series of reactions that eventually resulted in the destruction of SD molecules and the formation of small organic molecules.

摘要

为了克服传统芬顿工艺的缺点,在辐照下进行了 Fe(III)-EDDS 激活过硫酸盐高级氧化工艺,这是一种很有前途的技术。本文研究了 Fe(III)-EDDS 激活过硫酸盐体系中磺胺嘧啶(SD)的光降解。结果表明,SD 可在 Fe(III)-EDDS//hv 体系中有效降解。探讨了 Fe(III):EDDS 摩尔比、Fe(III)-EDDS 浓度和 浓度对 SD 降解的影响。在中性 pH 值下,当 Fe(III):EDDS=1:1,Fe(III)-EDDS=0.1 mM,=1.5 mM 时,SD 降解效果最佳。外加影响因素实验表明,存在、、时,SD 的降解明显受到抑制,而添加 Cl 时,SD 的降解几乎不受影响。腐殖酸和 NO 对 SD 的降解略有抑制。考察了 pH 值对 SD 降解的影响,SD 可在 pH 3-9 范围内有效降解。ESR 证明过程中产生了 O、·OH、、和 O。和·OH 被鉴定为主要自由基,而 O 也发挥了不可忽视的作用。分析了 SD 的 11 个中间产物。SD 的 C=N、S-N 和 S-C 键首先受到自由基的攻击,导致一系列反应,最终导致 SD 分子的破坏和小分子有机化合物的形成。

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