Degradation of Phenol by Peroxymonosulfate Catalyzed by Cerium-doped amino-functionalized metal-organic frameworks (NH2-MIL-101 (Fe, Ce))

苯酚 降级(电信) 催化作用 金属有机骨架 化学 兴奋剂 核化学 金属 无机化学 有机化学 材料科学 电信 光电子学 吸附 计算机科学
作者
Lijie Mo,Guangzhou Chen,Biao Xu
出处
期刊:Journal of environmental chemical engineering [Elsevier]
卷期号:12 (4): 113256-113256 被引量:2
标识
DOI:10.1016/j.jece.2024.113256
摘要

As an organic pollutant difficult to be degraded in water bodies, phenol is toxic even at low concentrations. Therefore, studying the degradation technology of phenol is of great significance. In order to investigate the effect of transition metal doping on the performance of oxidative degradation of phenol by the persulfate activated by metal-organic frameworks, the different doping levels of Ce were tested based on the NH2-MIL-101(Fe). Then, NH2-MIL-101(Fe,Ce) with different Fe/Ce ratios was successfully prepared by solvothermal method. They were characterized by means of XRD, SEM, TEM, XPS and FT-IR. Selecting phenol as the target pollutant, the NH2-MIL-101(Fe,Ce)/PMS system was constructed to study the degradation rate. The factors of the different temperature, initial pH, anions, Ce doping ratios, catalyst dosage and PMS concentration were investigated. The mechanism of degradation of phenol for the above system was analyzed through free radical burst test, and the metal ion dissolution of catalytic materials in actual wastewater treatment process was monitored by ICP-OES instrument. Finally, the intermediate products of phenol in the degradation process were inferred using LC-MS method. The results showed that when the molar ratio of Ce/(Ce+Fe) was 15%, under the same reaction conditions, NH2-MIL-101(Fe,Ce)-15% ( referred to as NM-15%) had the highest degradation rate for phenol. After the 50 minutes, phenol could be completely removed, with K value of 0.059 min-1. This system could achieve the efficient degradation of phenol under the range of pH values (pH=3-9). The results of the free radical burst test and the free radical trapping test showed that the dominant oxidising groups were SO4•−, •OH, •O2− and non-free radical 1O2.
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