State Key Laboratory of Pollution Control and Resources Reuse, Key Laboratory of Yangtze Water Environment, Ministry of Education, College of Environmental Science and Engineering, Tongji University, Shanghai, 200092, PR China; College of Biological and Environmental Engineering, Guiyang University, Guiyang, 550005, PR China.
State Key Laboratory of Pollution Control and Resources Reuse, Key Laboratory of Yangtze Water Environment, Ministry of Education, College of Environmental Science and Engineering, Tongji University, Shanghai, 200092, PR China; Shanghai Institute of Pollution Control and Ecological Security, Shanghai, 200092, PR China.
Chemosphere. 2021 Jun;272:129568. doi: 10.1016/j.chemosphere.2021.129568. Epub 2021 Jan 7.
Iopamidol is a commonly used iodinated X-ray contrast media in medical field, and its residue in water can react with disinfectants to form highly toxic iodinated disinfection by-products (I-DBPs). This study investigated the degradation of iopamidol and formation of DBPs, especially iodinated trihalomethanes (I-THMs), during ferrate (Fe(VI)) pre-oxidation and subsequent chlor(am)ination under raw water background. It was found that iopamidol degradation efficiency in raw water by Fe(VI) at pH 9 could reach about 80%, which was much higher than that at pH 5 and pH 7 (both about 25%). With Fe(VI) dose increasing, iopamidol removal efficiency increased obviously. During the iopamidol degradation by Fe(VI), IO was the dominant product among all the iodine species. After pre-treated by Fe(VI), yields of THM4 and I-THMs can be reduced in subsequent chlor(am)ination. Besides, pH was a crucial factor for Fe(VI) pre-oxidition controlling DBPs. With the pH increasing from 5 to 9, the yield of THM4 kept increasing in subsequent chlorination but showed the highest amount at pH 6 in subsequent chloramination. The yield of I-THMs increased first and then decreased with the increase of pH in both subsequent chlorination and chloramination. I-THM concentrations in chlorinated samples were lower than chloraminated ones under acidic conditions but became higher under neutral and alkaline conditions. The total CTI of THMs during Fe(VI)-chloramination was higher than that during Fe(VI)-chlorination under neutral condition, but sharply decreased under alkaline conditions. In summary, Fe(VI)-chloramination subsequent treatment under alkaline conditions should be an effective method for iopamidol removal and DBP control.
碘帕醇是一种常用的医用碘造影剂,其在水中的残留与消毒剂反应会生成具有高毒性的含碘消毒副产物(I-DBPs)。本研究考察了高铁酸盐(Fe(VI))预氧化及原水背景下后续氯化(氨)过程中碘帕醇的降解和消毒副产物,特别是含碘三卤甲烷(I-THMs)的形成。结果表明,pH 值为 9 时,Fe(VI)对原水中碘帕醇的降解效率可达约 80%,显著高于 pH 值为 5 和 7 时的约 25%。随着 Fe(VI)剂量的增加,碘帕醇的去除效率明显提高。在 Fe(VI)降解碘帕醇的过程中,IO 是所有碘形态中的主要产物。经 Fe(VI)预处理后,后续氯化(氨)过程中 THM4 和 I-THMs 的生成量会降低。此外,pH 值是控制 Fe(VI)预氧化生成 DBPs 的关键因素。随着 pH 值从 5 增加到 9,后续氯化过程中 THM4 的生成量持续增加,但在后续氯化氨化过程中在 pH 值为 6 时达到最高。在后续氯化和氯化氨化过程中,随着 pH 值的增加,I-THMs 的生成量先增加后减少。在酸性条件下,氯化样品中 I-THMs 的浓度低于氯化氨化样品,但在中性和碱性条件下则较高。在中性条件下,Fe(VI)-氯化氨化过程中的总三卤甲烷 CTI 高于 Fe(VI)-氯化过程,但在碱性条件下急剧下降。综上所述,在碱性条件下进行 Fe(VI)-氯化氨化后续处理,是去除碘帕醇和控制 DBPs 的有效方法。