Equilibrium batch measurements were made of the adsorption of Cd(II) o
n 15 New Jersey soils. The soils were characterized in terms of surfac
e properties and chemical composition, particularly organic matter and
metal oxides. The adsorption of Cd(II) followed the Langmuir relation
and increased with increasing pH between pH 3 and pH 10. At constant
pH and metal concentration, greater adsorption was observed for soils
with higher organic matter content. To better understand the mechanism
of adsorption, the experimental results for the adsorption of Cd by t
he 15 soils were tested using a partition coefficient model that relat
ed the adsorption of the Cd(II) to the soil components: organic matter
, iron oxides, aluminum oxides, and manganese oxides. This model was n
ot successful when applied to measurements at the natural soil pH beca
use of the competition of protons with Cd(II) for available sites. How
ever, at constant pH, partition coefficients obtained from experimenta
l data were highly correlated with those calculated for a partition co
efficient between Cd(II) and organic matter alone. Normalization of th
e partition coefficients, K-d, for the organic matter content of the s
oils, K-om, greatly improved the relationship between the partition co
efficient and pH (R(2) increased from 0.799 to 0.927). This suggests t
hat the surficial adsorption sites are principally composed of organic
matter. For the 24-h equilibration period employed, diffusion of Cd(I
I) through this superficial organic matter coating to underlying sorpt
ive materials, including metal oxides, is unimportant in the partition
ing of Cd(II).