Preparation of MIL-53(Cr) and MIL-101(Cr)/reduced graphene oxide/polyaniline composites for Cr(VI) adsorption

IF 2.5 4区 材料科学 Q2 CHEMISTRY, APPLIED
Zhuannian Liu, Xiaolei Shi, Benlong Wei, Sheng Liao
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引用次数: 0

Abstract

The rapid development of industrialization has brought a series of difficulties and challenges to mankind, especially the heavy metal Cr(VI) pollution in water, which has become an important research topic. In the study, the reduced graphene oxide/polyaniline (rGO/PANI) material was synthetically synthesized by in-situ polymerization of polyaniline (PANI) with reduced graphene oxide (rGO) for adsorption of Cr(VI) in simulated wastewater. The Cr(VI) adsorbed on the layer of rGO/PANI utilized as metal ion center, MIL-53(Cr)/rGO/PANI (M-53/G-P) and MIL-101(Cr)/rGO/PANI (M-101/G-P) composites were prepared by hydrothermal method. The prepared composite adsorbs Cr(VI) again, and the composites were characterized by XRD, XPS, BET, and FTIR before and after adsorption, and the adsorption mechanism was elucidated by XPS. Results indicate: compared with rGO/PANI (38.98 m2·g−1), the M-53/G-P (137.87 m2·g−1) and M-101/G-P (70.91 m2·g−1) show higher BET surface area. When pH is 2, initial concentration is 100 mg L−1 and dosage is 0,10 g (per 100 mL), the maximum adsorption capacities of M-53/G-P and M-101/G-P composite materials for Cr(VI) are 81.58 and 77.76 mg·g−1, respectively. The adsorption kinetics of Cr(VI) on the two composites conform to the pseudo-second-order kinetic model and the adsorption isotherm follows the Freundlich model. The adsorption mechanisms of Cr(VI) by the two materials involve electrostatic attraction, ion exchange, and complexation. This study found that M-53/G-P has promising applications in removing contaminants and purifying wastewater compared to M-101/G-P.

MIL-53(Cr)和MIL-101(Cr)/还原氧化石墨烯/聚苯胺复合材料吸附Cr(VI)的制备
工业化的快速发展给人类带来了一系列的困难和挑战,尤其是水体中重金属Cr(VI)的污染问题,已成为一个重要的研究课题。本研究通过聚苯胺(PANI)与还原氧化石墨烯(rGO)原位聚合,合成了还原氧化石墨烯/聚苯胺(rGO/PANI)材料,用于吸附模拟废水中的Cr(VI)。将吸附在氧化石墨烯/苯胺层上的Cr(VI)作为金属离子中心,通过水热法制备了MIL-53(Cr)/氧化石墨烯/苯胺(M-53/G-P)和MIL-101(Cr)/氧化石墨烯/苯胺(M-101/G-P)复合材料。制备的复合材料再次吸附Cr(VI),通过吸附前后的XRD、XPS、BET和FTIR对复合材料进行了表征,并通过XPS对吸附机理进行了阐述。结果表明:与rGO/PANI (38.98 m2·g−1)相比,M-53/ g - p (137.87 m2·g−1)和M-101/ g - p (70.91 m2·g−1)具有更高的BET表面积;当pH = 2,初始浓度为100 mg L−1,投加量为0.10 g(每100 mL)时,M-53/ g - p和M-101/ g - p复合材料对Cr(VI)的最大吸附量分别为81.58和77.76 mg·g−1。两种复合材料对Cr(VI)的吸附动力学符合拟二级动力学模型,吸附等温线符合Freundlich模型。两种材料对Cr(VI)的吸附机理包括静电吸引、离子交换和络合作用。研究发现,与M-101/G-P相比,M-53/G-P在去除污染物和净化废水方面具有广阔的应用前景。
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来源期刊
Journal of Porous Materials
Journal of Porous Materials 工程技术-材料科学:综合
CiteScore
4.80
自引率
7.70%
发文量
203
审稿时长
2.6 months
期刊介绍: The Journal of Porous Materials is an interdisciplinary and international periodical devoted to all types of porous materials. Its aim is the rapid publication of high quality, peer-reviewed papers focused on the synthesis, processing, characterization and property evaluation of all porous materials. The objective is to establish a unique journal that will serve as a principal means of communication for the growing interdisciplinary field of porous materials. Porous materials include microporous materials with 50 nm pores. Examples of microporous materials are natural and synthetic molecular sieves, cationic and anionic clays, pillared clays, tobermorites, pillared Zr and Ti phosphates, spherosilicates, carbons, porous polymers, xerogels, etc. Mesoporous materials include synthetic molecular sieves, xerogels, aerogels, glasses, glass ceramics, porous polymers, etc.; while macroporous materials include ceramics, glass ceramics, porous polymers, aerogels, cement, etc. The porous materials can be crystalline, semicrystalline or noncrystalline, or combinations thereof. They can also be either organic, inorganic, or their composites. The overall objective of the journal is the establishment of one main forum covering the basic and applied aspects of all porous materials.
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