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Introduction to Soil Chemistry

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distribution between soil solids and soil solution 83<br />

Many other methods of determining soil pH and exchangeable pro<strong>to</strong>ns are<br />

described in the soils literature. Among these are a number of methods<br />

designed <strong>to</strong> determine a fac<strong>to</strong>r called the soil buffer pH, which is determined<br />

by adding a highly buffered solution <strong>to</strong> the soil and measuring the change in<br />

its pH. This change can then be related back <strong>to</strong> a property called the <strong>to</strong>tal<br />

acidity in soil. It is also used as the basis for making liming recommendations<br />

in agriculture. See Chapter 5, Section 5.3.1, for a detailed discussion of pH<br />

electrodes for measuring soil pH.<br />

It is often tempting <strong>to</strong> design a new pro<strong>to</strong>col or change an existing method<br />

for pH determination. Keep in mind that when or if this is done, it will change<br />

all the analytical methods that use pH as an important component such as the<br />

determination of CEC as discussed above. It will also change the interpretation<br />

of analytical results and the recommendations for applications of some agricultural<br />

amendments (see Chapter 10). Such a change is probably not advisable<br />

unless there is some highly significant improvement in the new method.<br />

4.10. THE SOIL SOLUTION AROUND PARTICLES<br />

Dissolved ions and molecules are evenly distributed throughout a pure solution.<br />

In soil, this does not take place because soil particles, particularly colloidal<br />

particles, both clay and carbon, have sorbed, exchangeable, and<br />

peripherally attracted components associated with them.<br />

Cations attracted <strong>to</strong> colloid surfaces through their waters of hydration are<br />

outer-sphere species, whereas those that react directly with the oxygens<br />

present in the surface are inner-sphere species. Of the two, the latter species<br />

will be more strongly bonded and harder <strong>to</strong> extract.<br />

Cations form a diffuse layer of ions called the diffuse double layer or the<br />

electrical double layer around soil particles as depicted in Figure 4.8. The existence<br />

of the diffuse double layer means that the ions are not evenly distributed<br />

throughout the solution; rather, they are more concentrated close <strong>to</strong> soil<br />

particle surfaces and less concentrated farther away. This phenomenon must<br />

be kept in mind, particularly when electrochemical analytical methods of<br />

analysis are developed [5,6].<br />

4.11. DISTRIBUTION BETWEEN SOIL SOLIDS AND SOIL SOLUTION<br />

All components in the soil solution are <strong>to</strong> a greater or lesser extent distributed<br />

unevenly between the solid and liquid phases. Anions are generally only<br />

weakly attracted <strong>to</strong> soil solids, if at all. Cations are attracted <strong>to</strong> the soil colloids,<br />

while the interaction between soil solids and organic compounds is<br />

complex, depending on the structure and functional groups of the organic<br />

compound and the nature of the soil solids. However, measuring the attraction<br />

or having a measure of the distribution between the two phases is<br />

extremely important in understanding the movement of material in soil. It will

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