State Key Laboratory of Urban Water Resource and Environment, School of Environment, Harbin Institute of Technology, Harbin 150090, China.
State Key Laboratory of Urban Water Resource and Environment, School of Environment, Harbin Institute of Technology, Harbin 150090, China.
Water Res. 2021 Apr 1;193:116860. doi: 10.1016/j.watres.2021.116860. Epub 2021 Jan 20.
After reaction with permanganate or ferrate, the resulted Mn-loaded and Fe-loaded biochar (MnOx/biochar and FeOx/biochar) exhibited excellent catalytic ozonation activity. O (2.5 mg/L) eliminated 48% of atrazine (ATZ, 5 μM) within 30 min at pH 7.0, while under identical conditions, ozonation efficiency of ATZ increased to 83% and 100% in MnOx/biochar and FeOx/biochar (20 mg/L) heterogeneous catalytic systems, respectively. Radical scavenger experiment and electron paramagnetic resonance (EPR) analysis confirmed that hydroxyl radical (•OH) was the dominant oxidant. Total Lewis acid sites on MnOx/biochar and FeOx/biochar were 3.5 and 4.1 times of that on the raw biochar, which induced enhanced adsorption of O and its subsequent decomposition into •OH. Electron transfer via redox pairs on MnOx/biochar and FeOx/biochar was observed by cyclic voltammetry scans, which also functioned in the improved catalytic capacity. Degradation pathways of ATZ in MnOx/biochar and FeOx/biochar ozonation systems were proposed, with 34.6% and 44.8% of dechlorination effect accomplished within 30 min of reaction, which was improved by 4.1 and 5.3 times compared to pure ozonation. After 12-hour treatment, acute toxicity of ATZ oxidation products was reduced from 38.3% of pure ozonation system to 14.5% and 6.3% of activated ozonation systems with MnOx/biochar and FeOx/biochar, respectively. Mn-loaded biochar and Fe-loaded biochar have great potential for heterogeneous catalytic ozonation of polluted water.
高锰酸盐或高铁酸盐反应后,负载 Mn 和 Fe 的生物炭(MnOx/生物炭和 FeOx/生物炭)表现出优异的催化臭氧化活性。在 pH 值为 7.0 时,2.5mg/L 的 O(氧气)在 30 分钟内消除了 48%的莠去津(ATZ,5μM),而在相同条件下,MnOx/生物炭和 FeOx/生物炭(20mg/L)非均相催化体系中,ATZ 的臭氧化效率分别提高到 83%和 100%。自由基捕获实验和电子顺磁共振(EPR)分析证实,羟基自由基(•OH)是主要氧化剂。MnOx/生物炭和 FeOx/生物炭上的总路易斯酸位是原始生物炭的 3.5 和 4.1 倍,这导致 O 的吸附增强及其随后分解为•OH。通过循环伏安扫描观察到 MnOx/生物炭和 FeOx/生物炭上的氧化还原对之间的电子转移,这也提高了催化能力。提出了在 MnOx/生物炭和 FeOx/生物炭臭氧化体系中 ATZ 的降解途径,在 30 分钟的反应时间内,脱氯率达到 34.6%和 44.8%,比纯臭氧化提高了 4.1 和 5.3 倍。经过 12 小时处理,ATZ 氧化产物的急性毒性从纯臭氧化体系的 38.3%降低到负载 Mn 和 Fe 的生物炭处理的臭氧化体系的 14.5%和 6.3%。负载 Mn 的生物炭和负载 Fe 的生物炭在受污染水的非均相催化臭氧化方面具有巨大的潜力。