Abstract

A Gibbs energy minimization (GEM) approach to calculate chemical equilibria involving surface complexation at the mineral-water interfaces is presented, permitting the whole continuum “aqueous speciation - heterogeneous adsorption - surface (co)precipitation - solid solution” to be modeled only in elemental stoichiometry, without additional material balance constraints for the total number of surface sites. The thermodynamic stability of surface-bound species is considered in a way similar to that of the solid-solution endmembers, gases, and aqueous species. This consideration is made possible by introducing: (1) the standard and reference states of surface species involving a single value of reference site density Γ<sub>o</sub>; (2) an expression of (electro)chemical potential linking quantities of the surface species with the amount and specific surface area of the sorbent; (3) activity/concentration relationships between aqueous sorbates and surface species, based on the surface activity terms (SAT) as functions of the maximum site densities Γ<sub>max</sub>; (4) the surface type area fractions φ<sub>α,t</sub> for describing faces or patches on heterogeneous surface of multi-site-surface sorption mineral phases; (5) an elemental stoichiometry and standard partial molal properties of the amphoteric neutral surface functional group ≡OH and derived surface complexes at ambient conditions, comparable between all (hydr)oxide mineral surfaces. For the ;OH group (in 2pK<sub>A</sub> surface complexation models), a O<sub>0.5</sub>H<sup>o</sup> stoichiometry is conventionally defined from a reaction 0.5H<sub>2</sub>O<sub>aq</sub> = &gt;O<sub>0.5</sub>H<sup>o</sup>, with logK<sub>n</sub> = 1.74436 (at Γ<sub>o</sub> = 20 μmol · m<sup>−2</sup>) which is independent of temperature, pressure, pH, fO<sub>2</sub>, amount and specific surface area of the sorbent, aqueous speciation, and surface speciation. It follows that all the non-reacted &gt;O<sub>0.5</sub>H<sup>o</sup> groups have constant activity in the presence of liquid H<sub>2</sub>O and are thus macroscopically indistinguishable. The surface heterogeneity is described via standard thermodynamic properties of the surface complexes (reacted groups), such as “surface hydronium” &gt;O<sub>0.5</sub>H<sub>2</sub><sup>+</sup>, “surface hydroxyl” &gt;O<sub>0.5</sub><sup>−</sup>, adsorbed cations or anions, as well as through φ<sub>α,t</sub> and the common or individual Γ<sub>t,max</sub> parameters. Theoretical findings, implemented in the GEM-Selektor code, are illustrated by modeling the literature potentiometric titration and adsorption data for silica and rutile in NaCl solutions with the triple-layer (TLM), the generalized double-layer (DLM), and the non-electrostatic (NEM) surface complexation models (SCM). Some examples were also calculated with the FITEQL3.2 code to check for compatibility. It is shown: (1) how approximate conversions between partial molal properties of surface species and intrinsic adsorption constants can be performed for different total site densities Γ<sub>C</sub> ≠ Γ<sub>o</sub>; (2) what are the regions of “geometrically ideal” and “non-ideal” adsorption behavior for the chosen SCM and how they are controlled by the SAT = f(Γ<sub>max</sub>) on heterogeneous surfaces; and (3) why different sets of TLM parameters are not thermodynamically equivalent, and how a meaningful “optimal” set can be determined from titration data. Due to the separation of Γ<sub>max</sub> parameters from Γ<sub>o</sub> and, hence, from thermodynamic constants, the thermodynamic SCMs (in GEM implementation) can provide more insight into the relationships between surface types, complexes, bulk mineral sorbent, and aqueous sorbates, therefore permitting a more thorough use of microscopic/spectroscopic data in sorption modeling than has ever been possible.

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