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生物炭负载硫化纳米零价铁对 Cd(II)和 As(III)吸附的协同效应及机制。

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

机构信息

College of Environmental Science and Engineering, Central South University of Forestry and Technology, Changsha, 410004, China.

College of Environmental Science and Engineering, Central South University of Forestry and Technology, Changsha, 410004, China.

出版信息

Environ Res. 2023 Aug 15;231(Pt 1):116080. doi: 10.1016/j.envres.2023.116080. Epub 2023 May 8.

Abstract

Biochar derived from bamboo was used to support sulfide nanoscale zero-valent iron (S-nZVI@BC) for simultaneous 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. Adsorption kinetics and isotherms indicated that co-adsorption of Cd(II) and As(III) onto S-nZVI@BC was well represented by pseudo-second-order model (R = 0.990, R = 0.995) and Langmuir model (R = 0.954, R = 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 significantly affected the co-adsorption with the optimal ratio of 1:2. Ca and Mg 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.

摘要

竹基生物炭负载纳米零价铁(S-nZVI@BC)协同去除水中的 Cd(II) 和 As(III)。扫描电子显微镜(SEM)和 X 射线衍射光谱(XRD)分析证实了 S-nZVI@BC 的成功合成。吸附动力学和等温线表明,Cd(II)和 As(III)在 S-nZVI@BC 上的共吸附可以用伪二级动力学模型(R=0.990,R=0.995)和 Langmuir 模型(R=0.954,R=0.936)很好地描述。在共吸附体系中,Cd(II)和 As(III)的最大吸附量分别为 162.365 和 276.133 mg/g,显著高于单一吸附体系(分别为 103.195 和 223.736 mg/g)。批实验表明,Cd(II)-As(III)浓度比对共吸附有显著影响,最佳比例为 1:2。Ca 和 Mg 显著抑制了 Cd(II)的去除。相比之下,磷酸盐和腐殖酸显著抑制了 As(III)的去除。电化学分析表明,S-nZVI@BC 的腐蚀电位和电阻均低于 nZVI@BC,更有利于电子转移和化学反应。静电吸附、络合、共沉淀和氧化还原是去除 Cd(II)和 As(III)的主要机制。总之,本研究为 S-nZVI@BC 协同去除 Cd(II)和 As(III)提供了新的见解,S-nZVI@BC 是一种很有前途的吸附剂,可有效去除受污染废水中的 Cd(II)和 As(III)。

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