高温煅烧稀土矿渣对水体中磷的吸附过程与机理

    Adsorption of Phosphorus in Aqueous Solution by Calcined Rare Earth Slag and Its Mechanism

    • 摘要: 将稀土矿渣废弃物煅烧制备成具有优良吸附脱磷性能的低成本吸附剂(CRES)。通过扫描电镜(SEM)、红外光谱(FTIR)、X 射线荧光光谱(XRF)、比表面与孔分析(BET?BJH)、热重分析(TGA)等手段对制备的CRES 进行系统表征。研究了CRES 对磷吸附–解吸附过程的吸附等温线和吸附动力学,并考察了溶液pH 值对磷吸附的影响。结果表明,CRES 具有较好的孔隙结构,表面含有Ba、V、Si、Y、Ca、Fe、Yb 等金属和类金属元素化合物,溶液pH 值(2. 2~10.0)对磷吸附无明显影响。Langmuir 模型能较好拟合等温吸附数据(R =0. 932 5, =5),CRES 对磷酸根的最大吸附能力达152 mg·g-1,高于普遍报道的除磷吸附剂的吸附能力。吸附动力学试验表明,吸附过程在4~6 min 就达到平衡,准二级动力学模型很好地描述了吸附过程,表明化学吸附起到主导作用;物理吸附过程主要存在于吸附的初始阶段,这与CRES 表面含有多种金属和类金属元素以及良好的孔隙系统有关。

       

      Abstract: Rare earth slag fromSouth Jiangxi,China, was prepared into a promising low-cost adsorbent (CRES) through carcination for phosphorus removal in phosphorus over-loaded wastewater. To characterize CRES systematically, a number of modern equipment, such as Scanning Electron Microscope (SEM), Infrared Spectroscopy (FTIR), X-ray Fluorescence (XRF), Specific Surface Area Analyze (BET-BJH) and Thermogravimetric Analysis (TGA) were used. Phosphorus adsorption and desorption processes of CRES were studies by means of adsorption isotherm and adsorption kinetics.Effect of pH of the solution on P adsorption by CRES was also explored. Results show that CRES has a well-developed porous structure, containing various metal elements and metalloid element compounds, such as Ba, V, Si, Y, Ca, Fe, Yb, etc., on its surface. Solution pH, ranging from 2.2 to 10.0, did not affect much on its P adsorption capacity. Additionally, desorption of phosphorus-loaded CRES was investigated in different aqueous solutions. It was found that the P desorption rate was much higher in HCl solution than in any other others.The Langmuir modelwas found to be good in describing the P adsorption isotherm (R2 = 0.9325,n = 5) of CRES. Themaximum PO43-adsorption capacityof CREScould be as high as 152 mg•g-1, higher than any other adsorbents’ previously reported. P adsorption kinetics tests reveal that the P adsorption reached equilibrium pretty soon, only after 4 - 6 min, of which the process could be well described with Ho’s pseudo-second-order kinetic model, implying that chemisorption was the dominant mechanism of the P adsorption. Chemisorption was related to surface functional groups of CRES and coordination effect. Further, physisorption was also involved in this adsorption process, but mainly occurred at the initial stage of the adsorption process. Physisorption was related to various metal/metalloid elements contained in the surface as well as the well developed porous structure of CRES.

       

    /

    返回文章
    返回