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首页> 外文期刊>Chemical engineering journal >Removal of arsenic(III) from aqueous solution using a low-cost by-product in Fe-removal plants—Fe-based backwashing sludge
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Removal of arsenic(III) from aqueous solution using a low-cost by-product in Fe-removal plants—Fe-based backwashing sludge

机译:去除铁工厂中低成本的副产品从水溶液中去除砷(III)-铁基反冲洗污泥

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This study investigated the elemental composition and distribution of the Fe-based backwashing sludge (FBBS), and studied its adsorption behaviors and mechanisms towards arsenite [As(III)]. The characterization results of EDS, XPS, and XRF corroborated that the valuable constituents within FBBS are ferric oxhy-droxide (γ-FeOOH) and sulfate inter-layered Fe hydroxide [Fe(SO4)OH]. The zeta'potential results indicated a pH_(ZPC) value of 7.7. The adsorption equilibrium could be reached within 18 h, and the kinetics data were well described by the Elovich and Power models due to the heterogeneous surfaces of FBBS. The isotherm experimental results suggested that the maximum adsorption amount of As(III) was around 59.7 mg/g (initial As(III) = 1-120 mg/L, pH = 7.0, T= 25 °C), which is higher than most of other low-cost adsorbents, The uptake of As(III) onto FBBS would increase with an increase in temperatures, inferring that it is an endothermic process. The optimal initial solution pH for As(III) removal was around pH 8.0. The release of sulfate from FBBS after As(III) adsorption implied the occurrence of ligand exchanges, while the mechanism of Fe(III) precipitation might be also involved. The spectra of FTIR and XPS revealed that the surface hydroxyl groups played an important role in the adsorption of As(III), and the oxidation state of As(III) was not changed. Moreover, phosphates (>1 mM) could strongly inhibit the removal of As(III). The desorption results indicated that the release of As caused by alkali or phosphate eluent should be avoided for the scrutiny of waste landfill.
机译:这项研究调查了铁基反冲洗污泥(FBBS)的元素组成和分布,并研究了其吸附行为以及对砷[As(III)]的吸附机理。 EDS,XPS和XRF的表征结果证实了FBBS中有价值的成分是羟基氧化铁(γ-FeOOH)和硫酸盐层间氢氧化铁[Fe(SO4)OH]。 ζ电位结果表明pH_(ZPC)值为7.7。吸附平衡可在18 h内达到,并且由于FBBS的表面不均匀,动力学数据已被Elovich和Power模型很好地描述。等温线实验结果表明,As(III)的最大吸附量约为59.7 mg / g(初始As(III)= 1-120 mg / L,pH = 7.0,T = 25°C),高于在大多数其他低成本吸附剂中,随着温度的升高,As(III)在FBBS上的吸收会增加,从而推断这是一个吸热过程。去除As(III)的最佳初始溶液pH约为pH 8.0。 As(III)吸附后,FBBS中的硫酸盐释放暗示了配体交换的发生,而Fe(III)沉淀的机理也可能参与其中。 FTIR和XPS光谱表明,表面羟基在As(III)的吸附中起重要作用,As(III)的氧化态没有改变。此外,磷酸盐(> 1 mM)可以强烈抑制As(III)的去除。解吸结果表明,应避免对碱,磷酸盐洗脱液引起的砷的释放进行仔细检查。

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