Recent studies have shown that aging or increased residence time can reduce
the availability of trace element cations sorbed to common soil minerals.
Numerous explanations have been given to explain the observed residence tim
e effect. However, most of these studies begin only with sorbed species and
not surface precipitates. The formation of Ni2+ surface precipitates on co
mmon soil minerals has been observed in the laboratory by a number of resea
rchers. Accordingly, the influence residence time on the sorption/desorptio
n kinetics of Ni2+ on kaolinite was examined. Nickel sorption kinetics were
conducted at three aqueous concentrations (0.10, 0.50, 0.75 mM) of Ni2+ in
the presence of 25 g L-1 kaolinite at pH 7.5. More than 99% of the Ni2+ wa
s sorbed to the kaolinite surface at the end of 14 days for all aqueous con
centrations of Ni2+ Adsorption was characterized by an initial fast reactio
n followed by a slower reaction. Both reactions followed first order kineti
cs. Based on previous spectroscopic studies, the fast reaction was attribut
ed to chemisorption, whereas the slow reaction was attributed to nucleation
and surface precipitation of a Ni-AL layered double-hydroxide (LDH). Desor
ption experiments were conducted on kaolinite samples after 14 days (short-
term) and 20 weeks (long-term) in the presence of 1 mM oxalate at pH 6.0. S
imilar to adsorption kinetics, desorption kinetics were characterized by an
initial rapid reaction followed by a slower reaction, both of which follow
ed first order kinetics. For all surface coverages the total quantity of Ni
2+ desorbed and the desorption rate coefficients (k(1) and k(2)) were great
er for the short-term than for the long-term experiments. It is suggested t
hat the residence time effect observed for the slow desorption/dissolution
reaction was caused by an increase in crystallinity of the LDH surface prec
ipitate and, to a lesser extent, phase transformation into a Ni-Al phyllosi
lciate. In contrast, several processes may be responsible for the residence
time effect observed for the fast desorption/dissolution reaction, includi
ng movement of weakly bound Ni2+ to a more strongly bound phase (eg, change
in the type of surface complex), diffusion into micropores or intraparticl
e spaces, or an increase in crystallinity (eg, Ostwald ripening) of weakly
precipitated Ni2+ The above results demonstrate and suggest potential mecha
nisms for the long-term natural attenuation of trace metal cations such as
Ni2+ adsorbed to mineral surfaces.