Cation Exchange

Definitions

cation: An ion that carries a positive electrical charge (e.g. the metallic element of salt compounds). A cation can combine with certain anions (which have negative charges).

cation exchange: A process in which cations in solution are exchanged with cations held on the exchange sites of mineral and organic matter, particularly on the surfaces of colloids of clay and humus.

cation exchange capacity: The total amount of exchangeable cations that a particular material or soil can adsorb at a given pH. Exchangeable cations are held mainly on the surface of colloids of clay and humus and are measured in centimoles of charge per kilogram (cmolc/kg) of soil (or of other adsorbing material such as clay).

Concepts

Soil colloids have a net negative charge, therefore these particles are surrounded by a swarm of cations. The concentration of the cations is the highest in the Stern layer at surface of the clay particle, decreases in the Gouy layer and is the lowest in the bulk solution (Fig. 6.12).

Clay
Fig. 6.12. Impact of soil colloid (clay mineral) on the distribution of cation and anions in soil.

It is important to note that atoms of an element can exist in different form in soil. For example, aluminum is in a bound form in the crystal lattice (integral component of the octahedral layer and may be a substitute for silicon in the tetrahedral layer) and can be present as exchangeable cation and in soil bulk solution at certain soil pHs.

Table 6.4. Exchangeable cations and their ionic radius

Cation Ionic radius
(nm or 10-9 m)
Al3+ 0.051
Fe3+ 0.064
Mg2+ 0.066
Zn2+ 0.074
Fe2+ 0.070
Na+ 0.097
Ca2+ 0.099
K+ 0.133

The valance and ionic radius of exchangeable cations is presented in Table 6.4. The strength of the attractive force between a cation and a micelle depends on the charge of the cation, the charge density of micelle, and how close the cation can get to the micelle. The sequence of relative attractive forces, reflecting both the number of charges and the hydrated radius is Al3+ > Ca2+ > Mg2+ > NH4+ ~ K+ > Na+ . This list, sometimes called the lyotrophic series, may be considered as a preferential adsorption sequence. Cation exchange sites adsorb more of an ion early in the sequence than of one later in the sequence of the two are present in equal amounts. Preferential adsorption, however, can be overcome by an ion that is much more concentrated than others in soil solution (Thompson and Troeh, 1973).

Cation Exchange

The interchange between a cation in solution and one on a colloid must be chemically balanced (Fig. 6.13):

Cation

Fig 6.13. Dynamics of cation exchange

The exchange of cation is a dynamic and a rapid process. In order to assess the cation exchange capacity (CEC), it is necessary to determine the sum of exchangeable cations that a material (soil) can adsorb at a specific pH. The CEC is expressed in cmol (+)/kg soil. It yields a measure of the capacity of a soil to hold nutrients against leaching and the amount of negative charge of a soil sample.

Cations such as Ca2+, Mg2+, K+ and Na+ are basic while Al3+ and H+ are acidic. Therefore, the base saturation in soil is a measure of the proportion of basic cations occupying the exchange sites of a soil.

Base saturation (%) = Equation x 100

The percent base saturation is related to the pH, chemistry of dominant soil and soil formation. The relative amounts of cations impact the behavior of mineral and organic colloids in soil. For example, in soils have a relatively high proportion of Na+, dispersion occurs because Na+ has a single charge and a large hydrated ionic radius.

Sodium Clay
Fig. 6.14. Dispersion of clay particles in soils with a relatively high concentration of sodium ions.

In Ca-saturated systems, the attractive forces are greater than repulsive forces because Ca2+ has a small hydrated ionic radius. The clay particle flocculate due to gravity (Fig. 6.15).

Calcium Clay
Fig. 6.15. Flocculation of clay particles in soils with a relatively high concentration of calcium ions.

It is important that colloids do have small amount of positive charges through broken edges and pH-dependent charge. Therefore, anions can be exchanged in the same way as cations on soil colloids.

Anion Exchange


Format for citing this page:
Juma, N. G. The Pedosphere and its Dynamics: Mineralogy, 6.5 Cation Exchange [Online]. (1998, October 19). Available HTTP: http://www.soils.rr.ualberta.ca/pedosphere/content/section06/page05.cfm.