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利用热激活过硫酸盐氧化法在耕地土壤中降解莠去津、西玛津和莠灭净:优化、动力学和降解途径。

Degradation of Atrazine, Simazine and Ametryn in an arable soil using thermal-activated persulfate oxidation process: Optimization, kinetics, and degradation pathway.

机构信息

College of Resources and Environmental Sciences, Nanjing Agricultural University, Nanjing, 210095, China.

College of Resources and Environmental Sciences, Nanjing Agricultural University, Nanjing, 210095, China.

出版信息

J Hazard Mater. 2020 Dec 5;400:123201. doi: 10.1016/j.jhazmat.2020.123201. Epub 2020 Jun 16.

DOI:10.1016/j.jhazmat.2020.123201
PMID:32947740
Abstract

This study examined the feasibility of applying thermal-activated persulfate (PS) oxidation for remediation of soil co-contaminated with s-triazine herbicides including Atrazine (ATZ), Simazine (SIM) and Ametryn (AME). Homogeneous activation using heating method (50 °C) was selected. Results showed that thermal-activated PS oxidation process may successfully degrade ATZ in soil and degradation efficiency was increased along the arising activation temperature. Higher PS dosages and depressed initial pH were beneficial for degradation while increasing initial ATZ concentration may hamper the degradation. The oxidation process may lead to changes of surface functional groups on soil. The presence of Cl, HCO and HPO at both of low and high concentrations may inhibit the degradation of ATZ. Soil depths may apparently influence the ATZ degradation which followed 0-10 < 10-30 < 30-60 cm mainly depending on the soil organic matter (SOM) contents. Thermal-activated PS may effectively degrade ATZ, SIM and AME under co-contaminated condition and the more favorable of ethyl group towards SO than isopropyl and methylation groups was detected. Both of SO and HO were identified to be responsible for degradation. Finally, degradation intermediates of ATZ, SIM and AME were identified by LC-Q-TOF-MS and detailed transformation pathways for three pesticides were proposed, respectively.

摘要

本研究考察了热活化过硫酸盐 (PS) 氧化应用于修复同时污染三嗪类除草剂(包括莠去津 (ATZ)、西玛津 (SIM) 和莠灭净 (AME))的土壤的可行性。选择了使用加热法(50°C)进行均相活化。结果表明,热活化过硫酸盐氧化过程可以成功降解土壤中的 ATZ,降解效率随着活化温度的升高而增加。较高的 PS 剂量和降低的初始 pH 值有利于降解,而增加初始 ATZ 浓度可能会阻碍降解。氧化过程可能导致土壤表面官能团的变化。Cl、HCO 和 HPO 的存在,无论是在低浓度还是高浓度下,都可能抑制 ATZ 的降解。土壤深度明显影响 ATZ 的降解,其降解顺序为 0-10 < 10-30 < 30-60 cm,主要取决于土壤有机质 (SOM) 含量。热活化 PS 可在共存污染条件下有效降解 ATZ、SIM 和 AME,检测到乙基基团比异丙基和甲基基团对 SO 的亲和力更强。SO 和 HO 都被认为是负责降解的基团。最后,通过 LC-Q-TOF-MS 鉴定了 ATZ、SIM 和 AME 的降解中间产物,并分别提出了三种农药的详细转化途径。

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