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制备生物炭互穿海藻酸铁水凝胶作为一种对pH不敏感的吸附剂用于去除Cr(VI)和Pb(II)。

Preparation of biochar-interpenetrated iron-alginate hydrogel as a pH-independent sorbent for removal of Cr(VI) and Pb(II).

作者信息

Zhao Chenhao, Hu Linlin, Zhang Changai, Wang Shengsen, Wang Xiaozhi, Huo Zhongyang

机构信息

College of Environmental Science and Engineering, Yangzhou University, Yangzhou, 225127, PR China; Jiangsu Key Laboratory of Crop Genetics and Physiology/Jiangsu Co-Innovation Center for Modern Production Technology of Grain Crops/Agricultural College, Yangzhou University, Yangzhou, 225009, PR China.

College of Water Conservancy and Civil Engineering, Shandong Agricultural University, Taian, 271018, PR China.

出版信息

Environ Pollut. 2021 Oct 15;287:117303. doi: 10.1016/j.envpol.2021.117303. Epub 2021 May 10.

Abstract

Herein, a pH-independent interpenetrating polymeric networks (Fe-SA-C) were fabricated from graphitic biochar (BC) and iron-alginate hydrogel (Fe-SA) for removal of Cr(VI) and Pb(II) in aqueous solution. Fourier transform infrared spectroscopy (FTIR), Raman spectroscopy and scanning electron microscope (SEM) results demonstrated that graphitic BC interpenetration increased surface porosity and distorted surfaces of Fe-SA, which boosted availability of hydroxyl (-OH) group. Fe as a cross-linking agent of the alginate endowed Fe-SA-C with positive surfaces (positive zeta potential) and excellent pH buffering capacity, while excessive Fe was soldered on Fe-SA-C matrix as FeO(OH) and FeO. Cr(VI) removal at pH of 3 by Fe-SA-C (20.3 mg g) were 30.3% and 410.6% greater than that by Fe-SA and BC, respectively. Fe-SA-C exhibited minor pH dependence over pH range of 2-7 towards Cr(VI) retention. Greater zeta potential of Fe-SA-C over Fe-SA conferred a better electrostatic attraction with Cr(VI). FTIR and XPS of spent sorbents confirmed the reduction accounted for 98.5% for Cr(VI) removal mainly due to participation of -OH. Cr(VI) reduction was further favored by conductive carbon matrix in Fe-SA-C, as evidenced by more negative Tafel corrosion potential. Reductively formed Cr(III) was subsequently complexed with carboxylic groups originating from oxidation of -OH. Thus, Cr(VI) removal invoked electrostatic attraction, reduction, and surface complexation mechanisms. Pb(II) removal with excellent pH independence was mainly ascribed to surface complexation and possible precipitation. Thus, the functionalized, conductive, and positively-charged Fe-SA-C extended its applicability for Cr(VI) and Pb(II) removal from aqueous solutions in a wide pH range. This research could expand the application of hydrogel materials for removal of both cationic and anionic heavy metals in solutions over an extended pH range.

摘要

在此,通过石墨化生物炭(BC)和铁-海藻酸盐水凝胶(Fe-SA)制备了一种pH值不依赖的互穿聚合物网络(Fe-SA-C),用于去除水溶液中的Cr(VI)和Pb(II)。傅里叶变换红外光谱(FTIR)、拉曼光谱和扫描电子显微镜(SEM)结果表明,石墨化BC的互穿增加了Fe-SA的表面孔隙率并使表面变形,这提高了羟基(-OH)基团的可用性。Fe作为海藻酸盐的交联剂赋予Fe-SA-C正表面(正zeta电位)和优异的pH缓冲能力,而过量的Fe以FeO(OH)和FeO的形式焊接在Fe-SA-C基质上。在pH为3时,Fe-SA-C对Cr(VI)的去除量(20.3 mg g)分别比Fe-SA和BC高30.3%和410.6%。Fe-SA-C在2-7的pH范围内对Cr(VI)保留表现出较小的pH依赖性。Fe-SA-C比Fe-SA具有更高的zeta电位,与Cr(VI)具有更好的静电吸引力。废吸附剂的FTIR和XPS证实,Cr(VI)去除中98.5%归因于还原,主要是由于-OH的参与。Fe-SA-C中的导电碳基质进一步促进了Cr(VI)的还原,更负的塔菲尔腐蚀电位证明了这一点。还原形成的Cr(III)随后与源自-OH氧化的羧基络合。因此,Cr(VI)的去除涉及静电吸引、还原和表面络合机制。对Pb(II)的去除具有优异的pH不依赖性,主要归因于表面络合和可能的沉淀。因此,功能化、导电且带正电的Fe-SA-C扩展了其在宽pH范围内从水溶液中去除Cr(VI)和Pb(II)的适用性。本研究可以扩展水凝胶材料在扩展pH范围内去除溶液中阳离子和阴离子重金属的应用。

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