Enhanced photo-Fenton degradation of tetracycline hydrochloride by 2, 5-dioxido-1, 4-benzenedicarboxylate-functionalized MIL-100(Fe)

被引:22
|
作者
Li, Mingyu [1 ,2 ]
Ma, Yuhan [1 ,2 ]
Jiang, Jingjing [1 ,2 ]
Li, Tianren [1 ,2 ]
Zhang, Chongjun [3 ]
Han, Zhonghui [1 ,2 ]
Dong, Shuangshi [1 ,2 ]
机构
[1] Jilin Univ, Key Lab Groundwater Resources & Environm, Minist Educ, Changchun 130021, Jilin, Peoples R China
[2] Jilin Univ, Jilin Prov Key Lab Water Resources & Environm, Changchun 130021, Jilin, Peoples R China
[3] Northeast Normal Univ, Sch Environm, Engn Lab Water Pollut Control & Resources Recovery, Changchun 130117, Peoples R China
基金
中国国家自然科学基金;
关键词
H2DOBDC-Functionalized MIL-100(Fe); Photo-Fenton; Contaminant removal; Degradation mechanism; WATER; MIL-53(FE);
D O I
10.1016/j.envres.2022.113399
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Heterogeneous photo-Fenton technology has drawn tremendous attention for removal of recalcitrant pollutants. Fe-based metal-organic frameworks (Fe-MOFs) are regarded to be superior candidates in wastewater treatment technology. However, the central metal sites of the MOFs are coordinated with the linkers, which reduces active site exposure and decelerates H2O2 activation. In this study, a series of 2, 5-dioxido-1, 4-benzenedicarboxylate (H2DOBDC)-functionalized MIL-100(Fe) with enhanced degradation performance was successfully constructed via solvothermal strategy. The modified MIL-100(Fe) displayed an improvement in photo-Fenton behaviors. The photocatalytic rate constant of optimized MIL-100(Fe)-1/2/3 are 2.3, 3.6 and 4.4 times higher compared with the original MIL-100(Fe). The introduced H2DOBDC accelerates the separation and transfer in photo-induced charges and promotes Fe(II)/Fe(III) cycle, thus improving the performance. center dot OH and center dot O-2(-) are main reactive radicals in tetracycline (TCH) degradation. Dealkylation, hydroxylation, dehydration and dealdehyding are the main pathways for TCH degradation.
引用
收藏
页数:9
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