Center for Radiation Chemistry Research, Idaho National Laboratory, ID, P.O. Box 1625, Idaho Falls 83415, USA.
Center for Radiation Chemistry Research, Idaho National Laboratory, ID, P.O. Box 1625, Idaho Falls 83415, USA.
Water Res. 2020 Nov 1;186:116314. doi: 10.1016/j.watres.2020.116314. Epub 2020 Aug 18.
The successful use of advanced oxidation processes to treat aqueous solutions containing undesirable organic species requires the degradation of these species to lower molecular weight, lower hazard compounds. Safe application of this technology requires a thorough understanding of the mechanisms of degradation. These oxidative transformations are mainly initiated by the reactions of reactive oxygen species, particularly hydroxyl radicals. These react with organic molecules to generate carbon-centered radicals. In the presence of dissolved oxygen, the carbon-centered radicals are next converted to peroxyl radicals, which then decay to lower molecular weight species by multiple mechanistic pathways. Formic acid and its conjugate base formate are the last stable chemical species produced immediately before the complete mineralization of any organic molecule undergoing oxidative degradation in aqueous solution. Once understood, the radical-induced chemistry of formic acid/formate under these conditions has wide applicability in all advanced oxidation technologies. To develop this quantitative knowledge, we have performed a series of Co gamma irradiation studies on aqueous formic acid/formate over different pH and solution conditions. The measured species concentration changes, as a function of applied dose, are compared with the predictions of a kinetic computer model constructed from literature reactions and reported rate coefficients. The excellent agreement found between the results and modeling gives confidence in the mechanism presented here and provide the first complete computer model for the radiolytic degradation of formic acid in water.
成功地使用高级氧化工艺处理含有不良有机物种的水溶液需要将这些物种降解为低分子量、低危害的化合物。安全应用这项技术需要对降解机制有透彻的了解。这些氧化转化主要是由活性氧物种(特别是羟基自由基)的反应引发的。这些自由基与有机分子反应生成碳中心自由基。在溶解氧存在下,碳中心自由基接下来被转化为过氧自由基,然后通过多种机制途径衰变为低分子量物质。在水溶液中进行氧化降解的任何有机分子完全矿化之前,立即产生的最后稳定的化学物质是甲酸及其共轭碱甲酸盐。一旦理解了这些条件下甲酸/甲酸盐的自由基诱导化学,它在所有高级氧化技术中都具有广泛的适用性。为了发展这种定量知识,我们在不同的 pH 值和溶液条件下对甲酸/甲酸盐进行了一系列 Coγ辐照研究。将测量的物种浓度变化与从文献反应和报告的速率系数构建的动力学计算机模型的预测进行比较。结果与模型之间的良好一致性证明了这里提出的机制的可靠性,并提供了甲酸在水中辐射降解的第一个完整计算机模型。