Sulfidated nanoscale zero-valent iron derived from iron sludge for tetracycline removal: Role of sulfur and iron in reactivity and mechanisms

被引:6
|
作者
Zhu, Shijun [1 ,2 ]
Yang, Kaida [1 ]
Wang, Tenghui [1 ]
He, Sijia [1 ]
Ma, Xin [1 ]
Deng, Jing [1 ]
Shao, Penghui [3 ]
Li, Xueyan [4 ]
Ma, Xiaoyan [1 ]
机构
[1] Zhejiang Univ Technol, Coll Civil Engn, Zhejiang Key Lab Civil Engn Struct & Disaster Prev, Hangzhou 310023, Peoples R China
[2] Mizuda Grp Co LTD, Huzhou 313000, Peoples R China
[3] Nanchang Hangkong Univ, Natl Local Joint Engn Res Ctr Heavy Met Pollutants, Key Lab Jiangxi Prov Persistent Pollutants Control, Nanchang 330063, Peoples R China
[4] Suzhou Univ Sci & Technol, Sch Environm Sci & Engn, Suzhou 215009, Peoples R China
基金
中国国家自然科学基金;
关键词
Sulfidated nanoscale zero valent iron(S-nFe(0)); Iron sludge; Oxygenation; Aerobic conditions; Tetracycline (TC); REDUCTIVE DECHLORINATION; OXIDATION; NANOPARTICLES; DEGRADATION; ANTIBIOTICS; PH; TRICHLOROETHYLENE; PEROXYMONOSULFATE; TRANSFORMATION; ADSORPTION;
D O I
10.1016/j.envpol.2024.123305
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Iron sludge, produced during the drinking water treatment process, can be recycled as potential iron resource to create environmental functional material. In this study, sulfur-iron composites derived from iron sludge (S-Fe composites) was synthesized through sulfidation and carbonization, and used for the tetracycline (TC) removal under aerobic and anoxic conditions. The reactivities of these as-prepared products were strongly depended on pyrolysis temperatures. In particular, sulfidated nanoscale zero-valent iron loaded on carbon (S-nFe(0)@CIS) carbonized at 800 degrees C exhibited the highest TC removal efficiency with 86.6% within 30 min at circumneutral pH compared with other S-Fe composites. The crystalline structure of alpha-Fe-0, FeSx and S-0 as main active sites in S-nFe(0)@CIS promoted the degradation of TC. Moreover, the Fe/S molar ratios significantly affected the TC removal rates, which reached the best value as the optimal S/Fe of 0.27. The results illustrated that the optimized extent of sulfidation could facilitate electron transfer from nFe(0) towards contaminants and accelerate Fe(III)/Fe(II) cycle in reaction system compared to bared nFe(0)@CIS. We revealed that removal of TC by S-nFe(0)@CIS in the presence of dissolved oxygen (DO) is mainly attributed to oxidation, adsorption and reduction pathways. Their contribution to TC removal were 31.6%, 25.2% and 28.8%, respectively. Furthermore, this adsorption-oxygenation with the formation of S-nFe(0)@CIS-TC* complexes was a surface-mediated process, in which DO was transformed by the structural FeSx on complex surface to center dot OH with the generation of H2O2 intermediate. The intermediates of TC and toxicity analysis indicate that less toxicity products generated through degradation process. This study provides a new reclamation of iron sludge and offers a new insight into the TC removal by S-nFe(0)@CIS under aerobic conditions.
引用
收藏
页数:12
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