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磁性核壳 FeO@普鲁士蓝去除微污染水中的 Cd(II)。

Removal of Cd(II) from Micro-Polluted Water by Magnetic Core-Shell FeO@Prussian Blue.

机构信息

College of Resources and Environment, University of Chinese Academy of Sciences, Huaibei Town 380, Huairou District, Beijing 101408, China.

Key Laboratory of Groundwater Circulation and Evolution, School of Water Resources and Environment, China University of Geosciences, No. 29 Xueyuan Road, Haidian District, Beijing 100083, China.

出版信息

Molecules. 2021 Apr 25;26(9):2497. doi: 10.3390/molecules26092497.

Abstract

A novel core-shell magnetic Prussian blue-coated FeO composites (FeO@PB) were designed and synthesized by in-situ replication and controlled etching of iron oxide (FeO) to eliminate Cd (II) from micro-polluted water. The core-shell structure was confirmed by TEM, and the composites were characterized by XRD and FTIR. The pore diameter distribution from BET measurement revealed the micropore-dominated structure of FeO@PB. The effects of adsorbents dosage, pH, and co-existing ions were investigated. Batch results revealed that the Cd (II) adsorption was very fast initially and reached equilibrium after 4 h. A pH of 6 was favorable for Cd (II) adsorption on FeO@PB. The adsorption rate reached 98.78% at an initial Cd (II) concentration of 100 μg/L. The adsorption kinetics indicated that the pseudo-first-order and Elovich models could best describe the Cd (II) adsorption onto FeO@PB, indicating that the sorption of Cd (II) ions on the binding sites of FeO@PB was the main rate-limiting step of adsorption. The adsorption isotherm well fitted the Freundlich model with a maximum capacity of 9.25 mg·g of Cd (II). The adsorption of Cd (II) on the FeO@PB was affected by co-existing ions, including Cu (II), Ni (II), and Zn (II), due to the competitive effect of the co-adsorption of Cd (II) with other co-existing ions.

摘要

一种新型核壳结构磁性普鲁士蓝包覆的 FeO 复合材料(FeO@PB)通过原位复制和氧化铁(FeO)的控制刻蚀设计和合成,用于从微污染水中去除 Cd(II)。TEM 证实了核壳结构,通过 XRD 和 FTIR 对复合材料进行了表征。BET 测量的孔径分布揭示了 FeO@PB 的微孔主导结构。考察了吸附剂用量、pH 值和共存离子的影响。批量实验结果表明,Cd(II)的吸附最初非常快,4 小时后达到平衡。pH 值为 6 时有利于 FeO@PB 对 Cd(II)的吸附。在初始 Cd(II)浓度为 100μg/L 时,吸附率达到 98.78%。吸附动力学表明,伪一阶和 Elovich 模型可以最好地描述 Cd(II)在 FeO@PB 上的吸附,表明 Cd(II)离子在 FeO@PB 的结合位点上的吸附是吸附的主要限速步骤。吸附等温线很好地符合 Freundlich 模型,最大 Cd(II)容量为 9.25mg·g。由于 Cd(II)与其他共存离子的共吸附竞争效应,共存离子(包括 Cu(II)、Ni(II)和 Zn(II))对 FeO@PB 上 Cd(II)的吸附有影响。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/956a/8123264/943cba14baf7/molecules-26-02497-g001.jpg

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