铁酸盐的制备和表征:从水溶液中去除砷的应用

Rasmane Tiendrebéogo, Yacouba Sanou, S. Paré, Aboubacar Senou
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摘要

由于砷对人类健康和水资源的影响,砷污染是布基纳法索的一个公共卫生隐患。为了减轻这种污染,人们合成了无水亚铁材料,并对其进行了表征,将其用作去除水溶液中砷的吸附剂。这项研究的目的是利用无水亚铁去除水中的砷,为改善清洁饮用水的获取做出贡献。砷物种如 As(III) 和 As(V) 是通过批量吸附去除的。实验采用砷水溶液批处理模式进行。使用扫描电子显微镜(SEM)结合能量色散光谱(EDX)、X 射线衍射(XRD)、红外线(IR)和布鲁纳尔-艾美特-泰勒(BET)对无定形和微孔 2 线无水亚铁进行的表征显示,无水亚铁是一种无定形和微孔 2 线无水亚铁。总比表面积和零电荷点的 pH 值(pHpzc)分别为 184.518 m²/g 和 9.41。As (V) 的最佳吸附剂剂量为 4 g/L,As (III) 的最佳吸附剂剂量为 8 g/L。吸附 As (V) 和 As (III) 的最佳 pH 值范围为 2 至 10,随着浓度在 2 至 16 mg/L 之间的增加,As(V) 的最大吸附容量为 15.07 mg/g,As(III) 的最大吸附容量为 13.01 mg/g。As (V) 和 As (III) 在铁水石上的平衡时间分别为 720 分钟和 960 分钟。砷(Ⅴ)和砷(Ⅲ)在铁酸盐上的吸附符合 Langmuir 单层模型。砷的吸附是自发的化学反应。砷的去除是在单层上按照假二阶动力学进行的。
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Preparation and Characterization of Ferrihydrite: Application in Arsenic Removal from Aqueous Solutions
Arsenic pollution is a public health hazard in Burkina Faso due to its impact on human health and water resources. To mitigate this pollution, ferrihydrite material has been synthesized and characterized to be used as adsorbent for arsenic removal in aqueous solutions. This study aimed to contribute to improve of access to clean drinking water by removing arsenic from water using ferrihydrite. Arsenic species such as As(III) and As(V) were removed through batch adsorption. Experiments were carried out in batch mode using arsenic aqueous solutions. The characterization of ferrihydrite using Scanning Electron Microscopy (SEM) coupled with Energy Dispersive Spectroscopy (EDX), X-ray Diffraction (XRD), Infrared (IR), and Brunauer Emmett Teller (BET) showed that an amorphous and microporous 2-line ferrihydrite. The total specific surface area and pH at point of zero charge (pHpzc) were 184.518 m²/g and 9.41, respectively. The optimal adsorbent doses were 4 g/L for As (V) and 8 g/L for As (III). The optimum pH range for the adsorption of As (V) and As (III) was between 2 and 10, The maximum adsorption capacity was 15.07 mg/g for As(V) and 13.01 mg/g for As(III) with increasing concentration between 2 and 16 mg/L. Equilibrium time for As (V) and  As (III) on ferrihydrite was found to be 720 min and 960 min, respectively. The adsorption of As(V) and As(III) was consistent with the Langmuir monolayer model on ferrihydrite. Arsenic adsorption was occurred according to spontaneous chemical reaction. Arsenic removal was occurred on a monolayer following the pseudo-second order kinetic.
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