Tamura Hiroki
Laboratory of Materials Chemistry, Graduate School of Engineering, Hokkaido University, Sapporo 060-8628, Japan.
J Colloid Interface Sci. 2004 Nov 1;279(1):1-22. doi: 10.1016/j.jcis.2004.07.010.
Ion-exchange reactions are naturally occurring at soil and sediment/water interphases, determining soil fertility and water quality. These ion-exchange reactions with inorganic and organic exchangers are applied to chemical analysis, recovery of useful ions from low-grade ores (potentially from sea water), water purification including the preparation of "ultrapure" water, production of foods and medicines, therapy, and other uses. It is important to theorize about or to model ion-exchange reactions for quantitative explanations of ion-exchange phenomena and for efficient operation of ion-exchange processes. This paper describes the modeling of ion-exchange equilibria for hydroxyl sites on metal oxides and carboxyl sites in resins with monovalent cations (alkali metal ions), a monovalent anion (nitrate ion), and divalent heavy metal ions. The procedure of modeling is as follows: the stoichiometry and material balance equations of the respective ion-exchange reactions were established based on findings here and by others. The equilibrium conditions were given by the Frumkin equation, where the mass-action relation is modified with lateral interactions between species at the interphase. The model equations were fitted to the measured data and model parameter values were determined by nonlinear regression analysis. The formation of bonds between ions and exchanger sites was evaluated by the equilibrium constant and the suppression of bond formation by electrostatic, geometric, and other lateral interactions was evaluated by the interaction constant. It was established that the properties of ions are determined by the valence, size, and hydration state of the ions. Monovalent ions (anions and cations) react with oxide surface hydroxyl and resin carboxyl sites as hydrated ions and form loose ion-site pairs by a weak electrostatic bond (nonspecific adsorption). However, the lateral interactions are large because of a large polarization of the ion-site pairs. When the monovalent cations are dehydrated to react with carboxyl sites in narrow resin nanopores, the bond formation is difficult because energy for dehydration is necessary. The suppressive lateral interactions here are small because of a small polarization of the dehydrated ion-site pairs that are in direct contact. Divalent heavy metal ions react with oxide hydroxyl sites by replacing their hydrated water molecules and form ion-site pairs in direct strong contact (specific adsorption). The bond formation becomes easier with increasing charge density of the ions evaluated by the charge/radius ratio, agreeing with the order of these ions to form hydroxo complexes in solution. The suppressive lateral interaction is, however, small for ions with large charge densities, because a strong contact bond reduces the polarization of ion-site pairs by neutralization. The properties of exchangers are functions of the molecular and pore environments around the functional groups. The acid-base nature of oxide surface-hydroxyl groups is determined by the electronegativity of surrounding lattice metal ions, and that of resin carboxyl groups by the electron-repelling effect of adjacent methyl groups. Pores in oxides have diameters sufficient to accommodate hydrated ions, and the suppression is large because of repulsion from ions adsorbed on opposite pore walls (across-pore interaction). Pores in resins differentiate ions that can access or not access sites on the internal surfaces of the pores. Narrow nanopores with diameters less than those of the hydrated ions require ions to dehydrate before they can enter. The ion-exchange reactivity here is small, as described above for dehydrated monovalent ions. In wide nanopores where hydrated ions can enter, bond formation is easier, but suppression is greater because of a larger polarization of hydrated ion-site pairs and also of the across-pore interaction. Macropores have diameters much larger than those of the hydrated ions and the bond formation is the same as that in wide nanopores, but the suppression is smaller because of the absence oe of the absence of the across-pore interaction. Finally, this paper attempts a formulation of activity coefficients of exchanging sites and adsorbed ion-site pairs and compares the proposed activity coefficients of interphase species with that of solution species given by the Debye-Hückel equation.
离子交换反应自然发生在土壤以及沉积物/水的界面,决定着土壤肥力和水质。这些与无机和有机交换剂发生的离子交换反应被应用于化学分析、从低品位矿石(可能来自海水)中回收有用离子、水净化(包括制备“超纯水”)、食品和药品生产、治疗以及其他用途。为了对离子交换现象进行定量解释以及使离子交换过程高效运行,对离子交换反应进行理论推导或建模很重要。本文描述了金属氧化物上羟基位点以及树脂中羧基位点与单价阳离子(碱金属离子)、单价阴离子(硝酸根离子)和二价重金属离子之间的离子交换平衡建模。建模过程如下:基于此处及其他研究结果建立了各自离子交换反应的化学计量和物料平衡方程。平衡条件由弗鲁姆金方程给出,其中质量作用关系通过界面处物种间的横向相互作用进行修正。将模型方程与测量数据拟合,并通过非线性回归分析确定模型参数值。通过平衡常数评估离子与交换剂位点之间键的形成,通过相互作用常数评估静电、几何和其他横向相互作用对键形成的抑制作用。已确定离子的性质由离子的价态、大小和水合状态决定。单价离子(阴离子和阳离子)以水合离子的形式与氧化物表面羟基和树脂羧基位点反应,并通过弱静电键(非特异性吸附)形成松散的离子 - 位点对。然而,由于离子 - 位点对的大极化,横向相互作用很大。当单价阳离子脱水以与狭窄树脂纳米孔中的羧基位点反应时,由于需要脱水能量,键的形成很困难。此处抑制性横向相互作用较小,因为直接接触的脱水离子 - 位点对的极化较小。二价重金属离子通过取代其水合水分子与氧化物羟基位点反应,并形成直接紧密接触的离子 - 位点对(特异性吸附)。随着通过电荷/半径比评估的离子电荷密度增加,键的形成变得更容易,这与这些离子在溶液中形成羟基配合物的顺序一致。然而,对于电荷密度大的离子,抑制性横向相互作用较小,因为强接触键通过中和减少了离子 - 位点对的极化。交换剂的性质是官能团周围分子和孔环境的函数。氧化物表面羟基基团的酸碱性质由周围晶格金属离子的电负性决定,树脂羧基基团的酸碱性质由相邻甲基的电子排斥效应决定。氧化物中的孔直径足以容纳水合离子,并且由于来自吸附在相对孔壁上的离子的排斥(跨孔相互作用),抑制作用很大。树脂中的孔区分了能够进入或无法进入孔内表面位点的离子。直径小于水合离子直径的狭窄纳米孔要求离子在进入之前脱水。如上述脱水单价离子的情况,此处的离子交换反应性较小。在水合离子可以进入的宽纳米孔中,键的形成更容易,但由于水合离子 - 位点对以及跨孔相互作用的更大极化,抑制作用更大。大孔的直径比水合离子的直径大得多,键的形成与宽纳米孔中的情况相同,但由于不存在跨孔相互作用,抑制作用较小。最后,本文尝试对交换位点和吸附的离子 - 位点对的活度系数进行公式化,并将所提出的界面物种活度系数与德拜 - 休克尔方程给出的溶液物种活度系数进行比较。