The conceptual and mathematical basis for a new general-composite modeling
approach for ion binding to environmental sorbents is presented. The work e
xtends the Simple Metal Sorption (SiMS) model previously presented for meta
l and proton binding to humic substances (Ganguly et al., 1999). A surface
complexation modeling approach is presented, where metal ion binding is con
ceptualized as occurring at a single (diprotic) binding site with variable
reactivity. The overall sorption constant (K-ads) is represented as the pro
duct of three terms: K-ads = K-chem K-coul K-het. The chemical contribution
to metal binding is included in K-chem, while K-coul and K-het define coul
ombic and/or heterogeneity effects, and are approximated by empirical power
functions of Hf and metal to site concentration ratio (M-T/S-T), respectiv
ely. Because of the difficulty in separating electrostatic and heterogeneit
y effects for field sorbents, the model is applied first to synthetic data
where these effects can be examined separately and cumulatively. The diffus
e double layer model (DDLM) is used as a basis of comparison for single and
multiple sorbents; a discrete affinity distribution model is used to explo
re heterogeneity effects in the absence of electrostatics, The variable rea
ctivity model then is applied to the experimental data reported by Wen et n
l. (1998) for proton and metal binding to river sediment. These application
s illustrate the underlying physical and chemical properties embodied in mo
del parameters as well as the ability of the model to simulate sorption dat
a for an environmental sorbent. Model attributes and limitations are discus
sed.