Synergistic effect and mechanism of Cd(II) and As(III) adsorption by biochar supported sulfide nanoscale zero-valent iron

被引:60
作者
Zheng, Xiaoyu [1 ]
Wu, Qiuju [1 ]
Huang, Chao [1 ]
Wang, Ping [1 ]
Cheng, Hao [1 ]
Sun, Chengyou [1 ]
Zhu, Jian [1 ]
Xu, Haiyin [1 ]
Ouyang, Ke [1 ]
Guo, Jing [2 ]
Liu, Zhiming [3 ]
机构
[1] Cent South Univ Forestry & Technol, Coll Environm Sci & Engn, Changsha 410004, Peoples R China
[2] Hunan Agr Univ, Coll Resources & Environm, Changsha 410128, Hunan, Peoples R China
[3] Eastern New Mexico Univ, Dept Biol, Portales, NM 88130 USA
基金
中国国家自然科学基金;
关键词
Biochar; S-nZVI@BC; Cadmium; Arsenic; Synergistic effect; SURFACE COMPLEXATION; AQUEOUS-SOLUTION; ZEROVALENT IRON; METAL-IONS; REMOVAL; CADMIUM; REMEDIATION; INSIGHT; SEQUESTRATION; NANOPARTICLES;
D O I
10.1016/j.envres.2023.116080
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Biochar derived from bamboo was used to support sulfide nanoscale zero-valent iron (S-nZVI@BC) for simul-taneous removal of Cd(II) and As (III) from aqueous media. Scanning electron microscopy (SEM) and X-ray diffraction spectroscopy (XRD) characterization confirmed the successful synthesis of the S-nZVI@BC. Adsorp-tion kinetics and isotherms indicated that co-adsorption of Cd(II) and As(III) onto S-nZVI@BC was well repre-sented by pseudo-second-order model (R2Cd(II) = 0.990, Rns(III) = 0.995) and Langmuir model (R2Cd(II) = 0.954, Rns (III) = 0.936). The maximum adsorption was 162.365 and 276.133 mg/g for Cd(II) and As(III), respectively, in a co-adsorption system, which was significantly higher than that in a single adsorption system (103.195 and 223.736 mg/g, respectively). Batch experiments showed that the Cd(II)-to-As(III) concentration ratio signifi-cantly affected the co-adsorption with the optimal ratio of 1:2. Ca2+ and Mg2+ significantly inhibited Cd(II) removal. In contrast, phosphate and humic acid significantly inhibited As(III) removal. Electrochemical analysis indicated S-nZVI@BC had a lower corrosion potential and resistance than nZVI@BC, making it more conducive to electron transfer and chemical reaction. Electrostatic adsorption, complexation, co-precipitation, and redox were the primary mechanisms for Cd(II) and As(III) removal. Overall, the present study provides new insights into the synergistic removal of Cd(II) and As(III) by S-nZVI@BC, which is a very promising adsorbent for the effective removal of Cd(II) and As(III) from contaminated wastewater.
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页数:10
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