Adsorption of anthropogenically released toxic metals such as Ni and Zn to
goethite effects their mobility and bioavailability in aquatic environments
. In this research sorption studies were conducted to understand competitiv
e adsorption of environmentally important metals such as Ni, Zn, and Ca ont
o the goethite surface. Adsorption edges conducted as a function of ionic s
trength suggest that these metals are chemisorbed to the goethite surface.
Furthermore, the adsorption affinity follows the order of the inverse of th
e hydrated radii multiplied by the number of waters in the primary solvatio
n shell: Zn > Ni > Ca. Isotherm studies revealed a linear relation between
the amount of metal adsorbed and the aqueous bulk phase concentrations, whe
re site saturation was obtained by reducing the goethite concentration to 0
.1 g 1(-1). Accordingly the single-site Langmuir model provided a good fit;
equilibrium constants were found to be independent of pH indicative of one
type of adsorption reaction. The equilibrium constants for both transition
metals (Ni and Zn) were greater than that of Ca, suggesting that transitio
n metals have a greater affinity for the surface. Analyses of site densitie
s revealed two types of sites on the surface of goethite: high affinity one
s to which transition metals bind, and low affinity sites that comprise 100
x that of the high affinity ones. From the isotherm studies, it appears th
at only the alkaline earth metals such as Ca adsorb to this lower affinity
site. The single-site Langmuir model was able to accurately describe adsorp
tion competition between Ni and Zn for the goethite surface. In contrast, n
o competitive effects were observed in Ni-Ca and Zn-Ca binary systems. (C)
2001 Elsevier Science B.V. All rights reserved.