Institute of Environmental Engineering, School of Metallurgy and Environment, Central South University, Changsha, 410083, China.
Chinese National Engineering Research Center for Control & Treatment of Heavy Metal Pollution, Changsha, 410083, China.
Environ Sci Pollut Res Int. 2020 Nov;27(32):40504-40511. doi: 10.1007/s11356-020-10072-z. Epub 2020 Jul 14.
Hydroxyl radical (OH)-based advanced oxidation technologies (AOTs) is an effective and clean way to remove sulfonamide antibiotics in water at ambient temperature and pressure. In this study, we systematically investigated the degradation kinetics of sulfamethazine (SMT) by OH with a combination of experimental and theoretical approaches. The second-order rate constant (k) of SMT with OH was experimentally determined to be 5.27 ± 0.06 × 10 M s at pH 4.5. We also calculated the thermodynamic and kinetic behaviors for the reactions by density functional theory (DFT) using the B3LYP/6-31G*. The results revealed that OH addition pathways at the methylene (C4) site on the pyridine ring and the ortho sites (C12 and C14) of the amino group on the benzene ring dominate the reaction, especially C14 site on the benzene ring accounted for 43.95% of SMT degradation kinetics. The theoretical k value which was calculated by conventional transition state theory is 3.96 × 10 M s, indicating that experimental observation (5.27 ± 0.06 × 10) is correct. These results could further help AOTs design in treating sulfonamide during wastewater treatment processes.
羟基自由基(OH)基高级氧化技术(AOTs)是在环境温度和压力下有效且清洁地去除水中磺胺类抗生素的方法。在这项研究中,我们结合实验和理论方法系统地研究了 OH 对磺胺甲噁唑(SMT)的降解动力学。通过实验确定 OH 与 SMT 的二级反应速率常数(k)在 pH 4.5 时为 5.27±0.06×10 M s。我们还通过密度泛函理论(DFT)使用 B3LYP/6-31G*计算了反应的热力学和动力学行为。结果表明,在吡啶环的亚甲基(C4)位和苯环上氨基的邻位(C12 和 C14)上的 OH 加成途径主导反应,特别是苯环上的 C14 位占 SMT 降解动力学的 43.95%。通过传统过渡态理论计算得到的理论 k 值为 3.96×10 M s,表明实验观察(5.27±0.06×10)是正确的。这些结果可以进一步帮助在废水处理过程中设计 AOTs 处理磺胺类抗生素。