CALCIUM: ALUMINIUM EXCHANGE EQUILIBRIA IN CLAY MINERALS AND ACID SOILS 1
Brian Coulter, O. Talibudeen
Abstract
Brian Coulter, O. Talibudeen
Abstract
Summary Exchange reactions between 0.0 in AlCl 3 solutions of different pH and Ca‐saturated montmorillonite, vermiculite, illite, and soils from the Park Grass Experiment at Rothamsted and the Deerpark Experiment, Wexford, Ireland, showed that Al 3+ and Al(OH) 2 + were adsorbed from solutions of pH > 4.0 and Al 3+ and H + from solutions of pH < 3.0. When Al was adsorbed, the cation exchange capacity of Ca‐saturated soils and clays increased. Conventional Ca: Al exchange isotherms showed that Al 3+ was strongly preferred to Ca 2+ on all soils and clays. The equilibrium constant for Ca: Al exchange, K , was identical for soils before and after oxidizing their organic matter and did not vary, for any exchanger, with Al‐saturation or the initial pH of the AlCl 3 solution. This proved the validity of the procedure used for calculating exchangeable Al 3+ . K values for Ca:Al exchange favoured Al 3+ in the order: vermiculite > Park Grass soil > Deerpark soil > illite > montmorillonite. The influence of surface‐charge densities of the clay minerals on this order is discussed and a method proposed and tested for calculating the K value of a soil from its mineralogical composition.
OpenAlex reports 22 citations for this work. Citation counts describe recorded attention and do not establish research quality.
A contribution statement is not available in the OpenAlex record.
Method details are not available in the OpenAlex metadata.
Findings are not separately available in the OpenAlex metadata.
Limitations are not available in the OpenAlex metadata.
Application details are not available in the OpenAlex metadata.
Summary Exchange reactions between 0.0 in AlCl 3 solutions of different pH and Ca‐saturated montmorillonite, vermiculite, illite, and soils from the Park Grass Experiment at Rothamsted and the Deerpark Experiment, Wexford, Ireland, showed that Al 3+ and Al(OH) 2 + were adsorbed from solutions of pH > 4.0 and Al 3+ and H + from solutions of pH < 3.0. When Al was adsorbed, the cation exchange capacity of Ca‐saturated soils and clays increased. Conventional Ca: Al exchange isotherms showed that Al 3+ was strongly preferred to Ca 2+ on all soils and clays. The equilibrium constant for Ca: Al exchange, K , was identical for soils before and after oxidizing their organic matter and did not vary, for any exchanger, with Al‐saturation or the initial pH of the AlCl 3 solution. This proved the validity of the procedure used for calculating exchangeable Al 3+ . K values for Ca:Al exchange favoured Al 3+ in the order: vermiculite > Park Grass soil > Deerpark soil > illite > montmorillonite. The influence of surface‐charge densities of the clay minerals on this order is discussed and a method proposed and tested for calculating the K value of a soil from its mineralogical composition.
Key concepts: Vermiculite, Illite, Montmorillonite, Cation-exchange capacity, Soil water, Chemistry, Clay minerals, Oxidizing agent