Many nutrients required by plants exist in soil as basic cations: Mg2+, Mn2, and Ca2. A soil's cation-exchange capacity is a measure of its ability to adsorb these basic cations as well as exchangeable hydrogen and aluminum ions. The cation-exchange capacity of soil is derived from two sources: small clay particles called micelles consisting of alternating layers of alumina and silica crystals, and organic colloids.
Replacement of A13+ and Si4+ by other cations of lower valence creates a net negative charge within the inner layers of the micelles. This is called the soil's permanent charge. For example, replacement of an atom of aluminum by calcium within a section where the net charge was previously zero, as shown below, produces a net charge of -1, to which other cations can become adsorbed.

Figure 1
A pH-dependent charge develops when hydrogen dissociates from hydroxyl moieties on the outer surfaces of
the clay micelles. This leaves negatively-charged oxygen atoms to which basic cations may adsorb. Likewise, a large pH-dependent charge develops when hydrogen dissociates from carboxylic acids and phenols in organic matter.
In most clays, permanent charges brought about by substitution account for anywhere from half to nearly all of the total cation-exchange capacity. Soils very high in organic matter contain primarily pH-dependent charges.
In a research study, three samples of soil were leached with a 1 N solution of neutral KCl, and the displaced A13+ and basic cations measured. The sample was then leached again with a buffered solution of BaCl2 and triethanolamine at pH 8.2, and the displaced H+ measured. Table 1 gives results for three soils tested by this method.
Table 1

Due to the buffering effect of the soil's cation exchange capacity, just measuring the soil solution's pH will not indicate how much base is needed to change the soil pH. In another experiment, measured amounts of acid and base were added to 10-gram samples of well-mixed soil that had been collected from various locations in a field. The volumes of the samples were equalized by adding water. The results were recorded in Figure 2.

Figure 2
What would be the effect of leaching the three soil samples in Table 1 with a buffered BaCl2 solution at pH 9.5 instead of 8.3?
- The measured permanent charge would be greater.
- The measured pH-dependent charge would be greater.
- The measured permanent charge would be smaller.
- The measured pH-dependent charge would be smaller.
Answer(s): B
Explanation:
You are told in the passage that the pH-dependent charge of soil is created when hydrogen dissociates from hydroxyl moieties found in organic matter and on the surface of the soil micelles. Remember that hydrogen does not normally dissociate from a hydroxyl or carboxyl group under acidic or neutral conditions. Under alkaline conditions, the hydrogen from a hydroxyl or carboxyl group may be pulled away from the oxygen by hydroxide ions in the solution. Thus, the more basic the leaching solution, the more hydrogen is likely to be released. This will result in a larger reading for the pH-dependent charge.
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