MOF-derived N-Co/Fe-PC composite as heterogeneous electro-Fenton catalysis combined with electrocoagulation process for enhanced degradation of Cu-CIP complexes from wastewater

被引:37
|
作者
Sun, Chengye [1 ]
Wang, Jun [1 ]
Gu, Cheng [2 ]
Wang, Chao [2 ]
Sun, Shuai [1 ]
Song, Peipei [1 ]
机构
[1] Shandong Agr Univ, Coll Resources & Environm, Key Lab Agr Environm, Natl Engn Res Ctr Efficient Utilizat Soil & Ferti, Tai An 271018, Peoples R China
[2] Nanjing Univ, State Key Lab Pollut Control & Resource Reuse, Sch Environm, Nanjing 210023, Peoples R China
基金
中国国家自然科学基金;
关键词
Metal-organic frameworks; N-Co/Fe-PC; Cu-ciprofloxacin; Heterogeneous electro-Fenton; Electrocoagulation Removal mechanism; METAL-ORGANIC FRAMEWORKS; CIPROFLOXACIN; NANOPARTICLES; WASTEWATERS; INSIGHTS; REMOVAL;
D O I
10.1016/j.cej.2022.139592
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Recently, heavy metal-antibiotic complexes have been frequently detected in wastewater, posing a serious threat to the human health. In this study, a novel combination of heterogeneous electro-Fenton (hetero-EF) and electrocoagulation process was developed for efficient removal of Cu-ciprofloxacin complexes (Cu-CIP). As hetero-EF cathode catalyst, N doped porous carbon loaded with Co/Fe sites (N-Co/Fe-PC) was innovatively synthesized, and Fe/Co-N-C structure was formed. The homogeneous mixing of Fe3C and Co3Fe7 resulted in the electron transfer and accumulation on Fe3C, which optimized the active substance and facilitated the oxygen reduction reaction. The effects of current, electrolyte type, pH, and concentration were comprehensively investigated, and the optimum removal efficiency of Cu, CIP, and TOC were 99.69 %, 96.40 %, and 83.62 %, respectively. Besides, it revealed that center dot O-2(-) was the dominant contributor to the Cu-CIP degradation. As a result, Cu-CIP complexes were degraded into small molecules and released Cu2+ with the ring-opening demethylation of the piperazine ring, cleavage and demethylation of carboxyl group, hydroxylation of the piperazine ring, and beta-cleavage reactions of cyclopropyl group. Meanwhile, they were also adsorbed by aluminum hydroxide/hydroxyl oxides especially gamma-AlOOH generated from the anode and finally coprecipitated. This study will provide a novel technology and theoretical basis for enhanced degradation of heavy metal-antibiotic complexes from wastewater.
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页数:13
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