EARTH scientists have long recognized(1-4) that the soluble organic ac
ids excreted by soil biota enhance rates of mineral weathering, thereb
y chemically stratifying the soil and affecting the biodegradation pat
hways of organic matter, including pollutants(5). Multidentate organic
ligands(6,7) also exist in industrial waste waters(8) and can enhance
the mobility of heavy elements, including radionuclides(9). Here we e
xamine whether rate coefficients for ligand-promoted disolution of min
erals can be predicted from existing studies of dissolved metal comple
xes. We have performed dissolution experiments on bunsenite (NiO) to c
ompare with published studies of ligand exchange around dissolved Ni(l
I)-ligand complexes(10-12). The hypothesis is confirmed with surprisin
g detail: the dissolution rate coefficient increases with the number o
f ligand functional groups coordinated to the surface metal, as do the
exchange rate coefficients(10-12). Furthermore, we find that the diss
olution rate coefficients can be predicted from the equilibrium consta
nts for metal complexation in solution, indicating that the activated
surface complexes resemble the corresponding dissolved complexes in im
portant ways.