School of Environmental Science and Engineering, Huazhong University of Science and Technology, Wuhan 430074, PR China.
Department of Environmental and Occupational Health, School of Public Health, Texas A&M University, College Station, TX 77843, United States.
Sci Total Environ. 2022 Mar 20;813:152647. doi: 10.1016/j.scitotenv.2021.152647. Epub 2021 Dec 27.
Permanganate has been widely used in the remediation of contaminated water due to its relatively strong oxidation properties and ease of use. The ubiquitous dissolved organic matter (DOM) in natural waters causes a significant sink of permanganate in treatments, which further impacts the photoformation of reactive species and the removal of trace pollutants by DOM. Significantly, the effect of permanganate oxidation on the photoreactivity of DOM remains unknown. The present paper investigated for the first time the photophysical and photochemical properties variation of DOM from different sources after permanganate oxidation. Results showed that the permanganate oxidation caused a decrease in UV absorbance, fluorescence intensity, aromaticity, and molecular weight for all tested DOM samples, as well as photoformation rate of DOM triplet states (DOM), singlet oxygen (O), and hydroxyl radical (OH) under simulated sunlight. Quantum yield of O showed positively linear correlations with both triplet quantum yield coefficient (f) and E2/E3 (ratio of absorbance at 254 and 365 nm) for all the DOM samples before and after permanganate oxidation. The quantum yield of OH exhibited no significant correlation with f or E2/E3. Permanganate oxidation inhibited the DOM-photosensitized indirect photodegradation of pollutants that do not absorb sunlight (e.g., decreased by 15-29%). For the tested pollutants that undergo direct photolysis under sunlight, their photodegradation was promoted (e.g., increased by 1-19%) in the permanganate oxidized DOM solutions due to the decrease of light-screening effect by DOM. These findings suggest that permanganate oxidation affects the photoreactivity of DOM and the corresponding photochemical fate of organic pollutants in natural waters.
高锰酸盐由于其较强的氧化性能和使用方便而被广泛应用于受污染水的修复。天然水中普遍存在的溶解有机物质(DOM)会导致高锰酸盐在处理过程中大量消耗,这进一步影响了反应性物质的光形成和 DOM 对痕量污染物的去除。值得注意的是,高锰酸盐氧化对 DOM 光反应性的影响尚不清楚。本研究首次考察了高锰酸盐氧化后不同来源 DOM 的光物理和光化学性质变化。结果表明,高锰酸盐氧化导致所有测试的 DOM 样品的紫外吸光度、荧光强度、芳香度和分子量降低,以及模拟太阳光下 DOM 三重态(DOM)、单线态氧(O)和羟基自由基(OH)的光形成速率降低。O 的量子产率与所有 DOM 样品氧化前后的三重态量子产率系数(f)和 E2/E3(254nm 和 365nm 处吸光度的比值)呈正线性相关。OH 的量子产率与 f 或 E2/E3 均无显著相关性。高锰酸盐氧化抑制了不吸收太阳光的污染物的 DOM 敏化间接光降解(例如,减少了 15-29%)。对于在阳光下进行直接光解的测试污染物,由于 DOM 的光屏蔽效应降低,它们在高锰酸盐氧化 DOM 溶液中的光降解得到促进(例如,增加了 1-19%)。这些发现表明,高锰酸盐氧化会影响 DOM 的光反应性以及天然水中有机污染物的相应光化学命运。