首页> 外文期刊>Applied Geochemistry: Journal of the International Association of Geochemistry and Cosmochemistry >Removal of hazardous hexavalent chromium from aqueous phase using zirconium oxide-immobilized alginate beads
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Removal of hazardous hexavalent chromium from aqueous phase using zirconium oxide-immobilized alginate beads

机译:使用氧化锆固定的海藻酸盐珠粒从水相中除去危险六价铬

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The present study addresses the aqueous phase removal of hexavalent chromium [Cr(VI)] using a composite adsorbent. An adsorbent was prepared by immobilizing hydrous zirconium oxide (HZO) into alginate beads (HZO@AB). The material was characterized via scanning electron microscopy (SEM), which showed an increase in surface roughness after HZO immobilization. The impregnation of alginate beads with HZO and successful adsorption of Cr(VI) onto HZO@AB were analyzed by X-ray photoelectron spectroscopy (XPS). The adsorption of Cr(VI) was well described by a pseudo-second-order kinetic model (R-2 0.99). The Langmuir model provided the best correlation with adsorption of Cr(VI) on HZO@AB (R-2 0.99), supporting the nature of adsorption as a monolayer. The adsorption of Cr(VI) [as CrO42- and HCrO4-)] was effective between pH 3 and 6 and decreased at higher pH. The maximum equilibrium sorption capacity of HZO@AB for Cr(VI) was 9.8 mg g(-1) at pH 5. The thermodynamic parameters (Delta G degrees, Delta H degrees, Delta S degrees) were evaluated, and the process of Cr(VI) adsorption on HZO@AB was identified as endothermic, thermodynamically feasible, and spontaneous (-Delta G degrees). The adsorbent was satisfactorily reused for three consecutive cycles. The adsorption capacity of regenerated composite adsorbent for Cr(VI) was 6.92 mg g(-1) in the third cycle, and the adsorbent retained approximately 73% of its original Cr(VI) adsorption capacity. The results of this study indicate that the developed adsorbent (HZO@AB) could be a potential candidate for treating wastewater containing Cr(VI). (C) 2017 Elsevier Ltd. All rights reserved.
机译:本研究通过复合吸附剂解决了六价铬[Cr(VI)]的水相去除。通过将含水锆氧化锆(HZO)固定到海藻酸盐珠粒(HZO @ AB)中制备吸附剂。通过扫描电子显微镜(SEM)表征该材料,其显示在HZO固定后的表面粗糙度增加。通过X射线光电子能谱(XPS)分析用HZO与HZO的浸渍和成功吸附Cr(VI)的浸渍和将Cr(VI)的吸附性成功吸附在HZO @ AB上。 Cr(VI)的吸附是通过伪二阶动力学模型(R-2> 0.99)很好的描述。 Langmuir模型提供了与HZO @ AB(R-2> 0.99)上的Cr(VI)的吸附的最佳相关性,支持吸附作为单层的吸附性质。 Cr(VI)的吸附[作为CRO42-和HCRO 4-)]在pH 3和6之间有效,并在更高的pH下降低。 HZO @ AB的最大平衡吸附容量在pH 5时为9.8mg g(-1)。评估热力学参数(Delta g型,δH度,δ谱),以及Cr的过程(VI)HZO @ AB上的吸附被识别为吸热,热力学可行和自发性(-Delta G度)。吸附剂令人满意地重复使用三个连续循环。在第三个循环中,Reenerated复合吸附剂的吸附容量为Cr(VI)为6.92mg g(-1),吸附剂保留约73%的原始Cr(VI)吸附能力。该研究的结果表明,发育的吸附剂(HZO @ AB)可以是用于治疗含Cr(VI)的废水的潜在候选物。 (c)2017 Elsevier Ltd.保留所有权利。

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