Cadmium (Cd) is of no known essential biological function and is toxic
to plants and animals. Leaching of Cd through soil profiles has impli
cations for both its accumulation in subsoil or contamination of groun
d-water. We measured adsorption and transport of Cd in the presence of
Ca and Na salts of varying ionic strengths using batch and miscible d
isplacement techniques. Two variable charge soils, an Oxisol and an Al
fisol, were used in this study. The Alfisol, despite its lower clay co
ntent, showed an adsorption coefficient (K) that was four times higher
than the clay-rich Oxisol. Such a difference in adsorption was attrib
uted to the presence of 2:1 layer silicate minerals in the Alfisol and
the consequent high surface negative charge density. Zn column experi
ments, a marked effect of ionic strength on the breakthrough curves (B
TCs) of Cd was observed when the concentrations of NaNO3 were increase
d from 0.03 M to 0.15 M in the background solutions. This increase cau
sed nearly four times faster movement of Cd through the Oxisol soil co
lumn. The effect of increasing Ca(NO3)(2) concentration on Cd adsorpti
on and transport was relatively less pronounced than that recorded for
the NaNO3 solution. In the Alfisol, the increase in Ca(NO,), ionic st
rength from 0.05 M to 0.25 M resulted in four-fold smaller adsorption
coefficient. For both soils, the movement of Cd at a constant ionic st
rength was, however, an order of magnitude faster in the presence of C
a(NO,), than that in the presence of NaNO3. To describe the combined e
ffect of ionic strength and pH, we used the K values calculated from t
he BTCs with CXTFIT model to develop a simple theoretical relationship
between Cd adsorption and [H+], [Ca2+] and [Cd2+] in solution. The re
lation was found to be consistent with other published studies. The st
udy demonstrated that Cd mobility in soils is strongly affected by the
soil solution composition (ionic strength and type of cations). (C) 1
998 Elsevier Science B.V. All rights reserved.