Interactions between the antibiotic tetracycline and humic acid: Examination of the binding sites, and effects of complexation on the oxidation of tetracycline

化学 腐植酸 四环素 溶解有机碳 傅里叶变换红外光谱 降级(电信) 背景(考古学) 激进的 结合位点 离子强度 核化学 无机化学 光化学 有机化学 环境化学 生物化学 水溶液 抗生素 古生物学 电信 生物 物理 量子力学 肥料 计算机科学
作者
Bo Yang,Chengjin Wang,Xin Cheng,Yongli Zhang,Wei Li,Jingquan Wang,Zixin Tian,Wenhai Chu,Gregory V. Korshin,Hongguang Guo
出处
期刊:Water Research [Elsevier]
卷期号:202: 117379-117379 被引量:124
标识
DOI:10.1016/j.watres.2021.117379
摘要

The binding between dissolved organic matter (DOM) and micro-pollutants (MPs) results in significant impacts on their migration, transformation and degradation. However, the role of the DOM/MP binding on their oxidative transformation remains poorly studied. The binding of MPs by DOM, in combination with DOM's roles as a photosensitizer and/or a competitor for free radicals, needs to be considered in the context of understanding the DOM's impacts on the oxidative degradation of MPs. This study aims to explore this aspect of DOM/MP interactions based on the quantitation of humic acid (HA) and tetracycline (TET) complexation and its role in TET removal. This study also compared the degradation of free TET versus that bound in HA-TET complexes in different oxidation processes. Fourier transform infrared (FTIR) data show that the carboxyl and phenolic hydroxyl groups in HA are the main binding sites of TET, while nuclear magnetic resonance (NMR) analysis shows the binding of TET engages its -N(CH3)2 groups, and two-dimensional correlation spectroscopy (2D-COS) data show that the carboxyl groups in DOM are sensitive than phenolic groups in the binding of TET. The difference between the degradation rates (Δkobs) of the free and bound TET decreased with the increase of ionic strength using sodium nitrate, but increased with the introduction of Ca2+ and Mg2+ due to the formation of TET-Ca2+/Mg2+ complexes. Quenching experiments showed that the free radicals (•OH and •SO4−), PMS oxidant and UV light were the main contributors to the TET degradation in UV/PS, UV/PMS and UV/H2O2 processes, respectively. In-situ fluorescence time scanning and differential absorbance spectra showed that free TET was preferentially oxidized over the bound TET in all the tested treatments except UV/PS. These results provide new insights into the role of DOM/MP complexation in the degradation of MPs in natural and engineered systems.
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