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Introduction to Soil Chemistry

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82 soil basics iv<br />

ionized will be determined by the pK a of the acid or phenol or in the case of<br />

amines, their pK b. The solubility of organic molecules that contain ionizable<br />

groups is greatly increased once they become ionized.<br />

Once ionized, the acid molecule carries a negative charge and can thus<br />

attract cations and participate in the cation exchange capacity of soil. The contribution<br />

of this source of negative charge will depend on the pH of the soil<br />

solution and will change as the pH changes. This is thus a variable or pH<br />

dependent cation exchange capacity (CEC).<br />

Because of the variability of this component of soil, the CEC determined<br />

at two different pHs should expectedly result in different CEC values; this can<br />

also happen if two different labora<strong>to</strong>ries determine the CEC. For this reason<br />

it is essential that CEC always be measured in the same way, taking care <strong>to</strong><br />

define the pH of the solutions used in its determination.<br />

4.9. SOIL pH<br />

In any aqueous solution the pH is a measure of the hydrogen ion or pro<strong>to</strong>n<br />

activity. However, in many if not most cases, pH is treated as the concentration<br />

of pro<strong>to</strong>ns in solution rather that their activity. The soil solution is no different<br />

except that the measurement is much more complex. The complexity<br />

arises from two sources:<br />

1. An electrical potential develops at all interfaces. In soil, there are interfaces<br />

between solids and solution, solution and suspension, suspension<br />

and the electrode surface, and the reference electrode and all these<br />

interfaces.<br />

2. The concept of activity is extremely important in soil. Pro<strong>to</strong>ns or hydronium<br />

ions attracted <strong>to</strong> exchange sites or other components in the system<br />

will not be measured as part of the solution composition.<br />

For these reasons, a standard method of measuring soil pH is chosen and all<br />

phenomena related <strong>to</strong> pH or involving pH is related <strong>to</strong> this “standardized” pH<br />

measurement. The most common method is <strong>to</strong> use a 1:1 ratio of soil <strong>to</strong> water,<br />

typically 10mL of distilled water and 10g of soil. In this method, the soil and<br />

water are mixed and allowed <strong>to</strong> stand for 10min and the pH determined using<br />

a pH meter.<br />

This method does not measure exchangeable pro<strong>to</strong>ns attached <strong>to</strong> cation<br />

exchange sites; therefore, it is also common <strong>to</strong> use a salt solution (either KCl<br />

or CaCl2) instead of distilled water in determining soil pH. The K + or Ca 2+ in<br />

the solution exchanges with exchangeable hydronium, thus bringing it in<strong>to</strong><br />

solution where it can be measured. These procedures therefore usually give a<br />

pH that is less, more acidic, than that obtained using distilled water. The justification<br />

for this approach is that it is thought <strong>to</strong> more closely relate <strong>to</strong> the<br />

pH experienced by plant roots.

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