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首页> 外文期刊>Journal of Molecular Liquids >g-C3N4 modified magnetic Fe3O4 adsorbent: Preparation, characterization, and performance of Zn(II), Pb(II) and Cd(II) removal from aqueous solution
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g-C3N4 modified magnetic Fe3O4 adsorbent: Preparation, characterization, and performance of Zn(II), Pb(II) and Cd(II) removal from aqueous solution

机译:G-C3N4改性磁FE3O4吸附剂:Zn(II),Pb(II)和Cd(II)的制备,表征和性能从水溶液中除去

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摘要

A novel magnetic carbon nitrogen adsorbent (Fe3O4&g-C3N4) was first prepared by one step method and applied to remove Zn(II), Pb(II) and Cd(II) from aqueous solution. Scanning electron microscope (SEM), transmission electron microscope (TEM), fourier transform infrared spectroscopy (FT-IR), X-ray diffraction (XRD), thermo-gravimetric analyzer (TGA), X-Ray fluorescence (XRF) and vibrating sample magnetometer (VSM) were used to character Fe3O4&g-C3N4. The adsorption performance of Fe3O4&g-C3N4 was evaluated by batch experiments with different pH, contact time, initial concentration and ionic strength. Pseudo-second-order model and intraparticle diffusion mode can well describe the adsorption kinetics data. Isothermal adsorption data was best fitted by Freundlich model and the adsorption capacity were 45, 137 and 102 mg/g (initial concentration: 200 mg/L) for Zn(II), Pb(II) and Cd(II), respectively. The result of X-ray photoelectron spectroscopy (XPS) survey spectrum suggested that the formation of conjugation of Fe3O4&g-C3N4 with heavy metal ions is the main adsorption mechanism for heavy metal ions on Fe3O4&g-C3N4. Moreover, the metal ions adsorbed Fe3O4&g-C3N4 could be regenerated by EDTA and the adsorption capacity of regenerative Fe3O4&g-C3N4 could maintain 88.9% after five cycles. Therefore, the Fe3O4&g-C3N4 is a potential adsorbent for separating Zn(II), Pb(II) and Cd(II) from wastewater. (C) 2018 Elsevier B.V. All rights reserved.
机译:首先通过一种步骤方法制备新的磁性碳氮吸附剂(Fe 3 O 4&G-C3N4),并施加来自水溶液的Zn(II),Pb(II)和Cd(II)。扫描电子显微镜(SEM),透射电子显微镜(TEM),傅里叶变换红外光谱(FT-IR),X射线衍射(XRD),热重分析仪(TGA),X射线荧光(XRF)和振动样品磁力计(VSM)用于符号Fe3O4&G-C3N4。通过具有不同pH,接触时间,初始浓度和离子强度的分批实验评估Fe3O4&G-C3N4的吸附性能。伪二阶模型和桐穴扩散模式可以很好地描述吸附动力学数据。等温吸附数据最适合由Freundlich模型安装,并且吸附能力分别为Zn(II),Pb(II)和CD(II)的45,137和102mg / g(初始浓度:200mg / L)。 X射线光电子能谱(XPS)测量光谱的结果表明,Fe3O4&G-C3N4与重金属离子的缀合是Fe3O4&G-C3N4中重金属离子的主要吸附机制。此外,吸附的Fe3O4&G-C3N4可以通过EDTA再生金属离子,再生Fe3O4&G-C3N4的吸附能力在五个循环后可以保持88.9%。因此,Fe 3 O 4&G-C3N4是用于分离废水的Zn(II),Pb(II)和Cd(II)的潜在吸附剂。 (c)2018年elestvier b.v.保留所有权利。

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