A crystalline polyferric sulfate(PFS) adsorbent was synthesized by oxidizing and precipitating ferrous ions in air atmospheric conditions. The morphology, structure, specific surface area(SSA), and adsorptive efficacy...A crystalline polyferric sulfate(PFS) adsorbent was synthesized by oxidizing and precipitating ferrous ions in air atmospheric conditions. The morphology, structure, specific surface area(SSA), and adsorptive efficacy of the adsorbent to As(Ⅲ) were characterized by scanning electron microscope(SEM) and transmission electron microscopy(TEM) images, X-ray diffraction(XRD) patterns, Fourier-transform infrared(FTIR) spectra, BET SSA analyses, and adsorption experiments. The adsorbent showed a near-spherical aggregate structure and had good crystallinity. A significant amount of α-goethite co-precipitated with PFS in the case of the initial ferrous concentration of 1 mol/L and increased SSA of the adsorbent. The stability region of ferric compounds in the process was drawn and applied to analyze the iron behavior during the synthesis. The adsorption of As(Ⅲ) in high As(Ⅲ)-containing solutions fitted the Langmuir isotherm model adequately. The absorbent with co-precipitation of α-goethite showed good adsorbability for As(Ⅲ) and good filtering performance in the high As(Ⅲ)-containing solution of 10–100 mg/L under acidic, neutral, and alkaline conditions(pH 2.09–9.01). After the adsorption process, the stability of the residues bearing As(Ⅲ) was evaluated by toxic characteristic leaching procedure(TCLP) tests. The results indicated that the residues were extremely stable, and the concentrations of arsenic in the leaching solutions were less than 0.01 mg/L.展开更多
研究海藻酸钠-钙凝胶球、海藻酸钠-铁(Ⅲ)凝胶球对废水中的铬(Ⅵ)的去除效果。结果表明:对50 m L(10 mg/L)的模拟废水进行吸附,海藻酸钠-铁(Ⅲ)凝胶球的吸附效果较好,而海藻酸钠-钙凝胶球对铬(Ⅵ)几乎不发生吸附作用。铬(Ⅵ)的去除率随...研究海藻酸钠-钙凝胶球、海藻酸钠-铁(Ⅲ)凝胶球对废水中的铬(Ⅵ)的去除效果。结果表明:对50 m L(10 mg/L)的模拟废水进行吸附,海藻酸钠-铁(Ⅲ)凝胶球的吸附效果较好,而海藻酸钠-钙凝胶球对铬(Ⅵ)几乎不发生吸附作用。铬(Ⅵ)的去除率随吸附时间的增加而提高,吸附240 min后,海藻酸钠-铁(Ⅲ)凝胶球对铬(Ⅵ)的去除率可达99%以上,海藻酸钠-铁(Ⅲ)凝胶球在酸性条件下比较稳定,在强碱性条件下易被分解,海藻酸钠-铁(Ⅲ)凝胶球吸附铬(Ⅵ)的吸附等温线符合Langmuir型,最大吸附量为11.827 mg/g。利用海藻酸钠-铁(Ⅲ)凝胶球去除废水中的铬(Ⅵ)具有工艺简单、处理效率高、速度快等优点。展开更多
基金financially supported by the National Natural Science Foundation of China(No.51574285)
文摘A crystalline polyferric sulfate(PFS) adsorbent was synthesized by oxidizing and precipitating ferrous ions in air atmospheric conditions. The morphology, structure, specific surface area(SSA), and adsorptive efficacy of the adsorbent to As(Ⅲ) were characterized by scanning electron microscope(SEM) and transmission electron microscopy(TEM) images, X-ray diffraction(XRD) patterns, Fourier-transform infrared(FTIR) spectra, BET SSA analyses, and adsorption experiments. The adsorbent showed a near-spherical aggregate structure and had good crystallinity. A significant amount of α-goethite co-precipitated with PFS in the case of the initial ferrous concentration of 1 mol/L and increased SSA of the adsorbent. The stability region of ferric compounds in the process was drawn and applied to analyze the iron behavior during the synthesis. The adsorption of As(Ⅲ) in high As(Ⅲ)-containing solutions fitted the Langmuir isotherm model adequately. The absorbent with co-precipitation of α-goethite showed good adsorbability for As(Ⅲ) and good filtering performance in the high As(Ⅲ)-containing solution of 10–100 mg/L under acidic, neutral, and alkaline conditions(pH 2.09–9.01). After the adsorption process, the stability of the residues bearing As(Ⅲ) was evaluated by toxic characteristic leaching procedure(TCLP) tests. The results indicated that the residues were extremely stable, and the concentrations of arsenic in the leaching solutions were less than 0.01 mg/L.
