Abstract

Soils of central and southern Jordan Valley (JV) are partially irrigated with waste waters relatively enriched with heavy metals, such as Pb and Cd. A composite surface soil sample (0–25 cm) was collected from a central JV field of Deir‐Alla. The clay fraction (reference clay: <2 μm primarily of carbonate, mica, and kaolinite minerals) was fractionated from a subsample and employed in studying Cd adsorption isotherms (10, 20, or 30° C) from 0.05 M NaCl (Cd 2+ and CdCl+ chemical species) or NaClO4(Cd 2+ species only) background solutions. Twelve Cd initial concentrations ranging between 0.4 and 10 mg L ‐1 were employed in the adsorption study. Cadmium adsorption onto OM‐free or CO3‐free clay suspensions in 0.05 M NaClO4 background solutions was also studied. Equilibrium Cd concentrations were determined using Differential Pulse Anodic Stripping Voltammetry. For the reference clay suspensions in NaClO4 or NaCl solutions. Cd2+ adsorption isotherms conformed to linear Langmuir plot. Maximum adsorption capacity (B) from the ClO4 background solutions increased slightly with increasing temperature from 1020 (at 10° C) to 1099 μg g‐1 clay (at 30° C). This was accompanied by a respective increase in the Langmuir's affinity constant (K) from 16.0 to 30.3. Changing the background solution to NaCl resulted in a marked increase in B values and decrease in K values with increasing temperature. This was attributed to concurrent adsorption of CdCl+ and Cd2+ ionic species from the Cl solutions. Adsorption of CdCl+ species decreased from 367 to 254 μg g‐1 with increasing temperature from 20 to 30° C due to decreasing stability of that complex ion. Removal of organic matter slightly increased the B values of Cd2+ due to the exposure of internal surfaces as a result of deflocculation of clay particles. To the contrary, acid removal of CaCO3 caused a substantial reduction in the adsorption capacity of Cd2+ due to flocculation of clay particles by Ca2+.

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