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Journal ArticleDOI

Slow Adsorption Reaction between Arsenic Species and Goethite (α-FeOOH): Diffusion or Heterogeneous Surface Reaction Control

Junshe Zhang, +1 more
- 25 Feb 2005 - 
- Vol. 21, Iss: 7, pp 2895-2901
TLDR
DMA desorbed completely and rapidly when the pH was raised, in contrast to the slow adsorption kinetics, indicating that the slow Adsorption step is not due to intraparticle diffusion.
Abstract
The slow stage of phosphate or arsenate adsorption on hydrous metal oxides frequently follows an Elovich equation. The equation can be derived by assuming kinetic control by either a diffusion process (either interparticle or intraparticle) or a heterogeneous surface reaction. The aim of this study is to determine whether the slow stage of arsenic adsorption on goethite is more consistent with diffusion or heterogeneous surface reaction control. Adsorption kinetics of arsenate and dimethylarsinate (DMA) on goethite (alpha-FeOOH) were investigated at different pH values and inert electrolyte concentrations. Their adsorption kinetics was described and compared using Elovich (Gamma vs ln time) plots. Desorption of arsenate and DMA was studied by increasing the pH of the suspension from pH 4.0 to pH 10.0 or 12.0. The effective particle sizes and zeta-potential of goethite were also determined. Effective particle size increased rapidly as the pH approached pH(IEP), both in the absence and presence of arsenic. Inert electrolyte concentrations and pH had no effect on the slow stage of arsenate adsorption on goethite, while the kinetics of DMA adsorption on goethite was influenced by both parameters. The slow stage of arsenate adsorption on goethite follows an Elovich equation. Since effective particle size changes with both pH and inert electrolyte concentrations, and effective particle size influences interparticle diffusion, the arsenate adsorption kinetics indicate that the slow adsorption step is not due to interparticle diffusion. DMA also has complex adsorption kinetics with a slow adsorption stage. DMA desorbed completely and rapidly when the pH was raised, in contrast to the slow adsorption kinetics, indicating that the slow adsorption step is not due to intraparticle diffusion. The slow adsorption is not the result of diffusion, but rather is due either to the heterogeneity of the surface site bonding energy or to other reactions controlling arsenic removal from solution.

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Citations
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Arsenic removal from water/wastewater using adsorbents—A critical review

TL;DR: Strong acids and bases seem to be the best desorbing agents to produce arsenic concentrates, and some commercial adsorbents which include resins, gels, silica, treated silica tested for arsenic removal come out to be superior.
Journal ArticleDOI

Kinetics and thermodynamic study of phosphate adsorption on iron hydroxide-eggshell waste

TL;DR: In this paper, the feasibility of using waste iron hydroxide-eggshell as an adsorbent for the removal of phosphate under different experimental conditions was explored and the results showed that the sorption capacity increases with an increase in solution temperature from 20 to 45 C at the initial phosphate solution concentration.
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Functionalized graphene sheets for arsenic removal and desalination of sea water

TL;DR: In this paper, the authors have synthesized the graphene sheets by hydrogen induced exfoliation of graphitic oxide followed by functionalization, and these functionalized graphene sheets were used for simultaneous removal of high concentration of inorganic species of arsenic (both trivalent and pentavalent) and sodium from aqueous solution using supercapacitor based water filter.
Journal ArticleDOI

Iron and aluminium based adsorption strategies for removing arsenic from water.

TL;DR: This review briefly presents iron and aluminium based adsorbents for arsenic removal and point-of-use adsorptive remediation methods indicate that Sono Arsenic filter and Kanchan™ ArsenIC filter are in operation at various locations of Bangladesh and Nepal.
Journal ArticleDOI

Vanadium removal by metal (hydr)oxide adsorbents.

TL;DR: Knowing vanadium occurrence in North American groundwater is summarized and vanadium removal by three commercially available metal oxide adsorbents with different mineralogies is assessed; GFH has the highest adsorption capacity, followed by GTO and E-33, and results indicate that all adsorbent remove vanadium.
References
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Journal ArticleDOI

Arsenite and Arsenate Adsorption on Ferrihydrite: Kinetics, Equilibrium, and Adsorption Envelopes

TL;DR: In this paper, the authors compared the adsorption behavior of arsenite and arsenate on ferrihydrite, under carefully controlled conditions, with regard to adaption kinetics and the influence of pH.
Journal ArticleDOI

Mechanisms of Arsenic Adsorption on Amorphous Oxides Evaluated Using Macroscopic Measurements, Vibrational Spectroscopy, and Surface Complexation Modeling.

TL;DR: In this study in situ Raman and Fourier transform infrared (FTIR) spectroscopic methods were combined with sorption techniques, electrophoretic mobility measurements, and surface complexation modeling to study the interaction of As(III) and As(V) with amorphous oxide surfaces.
Journal ArticleDOI

A surface structural approach to ion adsorption : The charge distribution (CD) model

TL;DR: In this paper, an ion adsorption model for metal hydroxides has been developed which deals with the observation that in the case of inner sphere complex formation only part of the surface complex is incorporated into the surface by a ligand exchange reaction while the other part is located in the Stern layer.
Journal ArticleDOI

Arsenate and Chromate Retention Mechanisms on Goethite. 1. Surface Structure

TL;DR: In this paper, the authors used Extended X-ray absorption fine structure (EXAFS) spectroscopy to deduce the local coordination environment of two environmental contaminants, arsenate and chromate, on the mineral goethite (α-FeOOH).
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