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).

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):

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 (%) = |
 |
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.

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).

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.
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. |