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Introduction to Soil Chemistry

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organic ions in solution 81<br />

consequence is that anions will pass through soil and not be adsorbed or even<br />

retarded. For the simple anions and some of the oxyanions, this is exactly what<br />

happens. All the halides, nitrite, nitrate, bicarbonate, and carbonate act in this<br />

fashion. However, there are some oxyanions that do not act as expected, and<br />

chief among them is phosphate.<br />

Monobasic (H2PO 4 - ), dibasic (HPO4 2- ), and tribasic (PO4 3- ) phosphates react<br />

with iron and aluminum at low pH <strong>to</strong> form insoluble phosphates. In a similar<br />

fashion, calcium reacts with phosphate at high pH <strong>to</strong> form insoluble calcium<br />

phosphates. In addition, phosphates will react with clay minerals and organic<br />

matter <strong>to</strong> form insoluble compounds. For these reasons phosphate seldom<br />

moves in soil. Exceptions occur when phosphate is associated with some kinds<br />

of organic matter, which is moving through the soil and where there is a large<br />

excess of phosphate in soil such as in areas where phosphate is mined, such as<br />

around the Florida phosphate mines. Other oxyanions will also behave like<br />

phosphate, although the exact nature of the reactions leading <strong>to</strong> their attraction<br />

<strong>to</strong> soil particles and organic matter is not well unders<strong>to</strong>od.<br />

Some soils, particularly those in the tropics, have significant anion exchange<br />

capacity. For these soils, there is an attraction between soil colloids and the<br />

simple halogen and nitrate anions. Bringing these anions in<strong>to</strong> solution for<br />

analysis will require an extraction or replacing anion just as does the analysis<br />

of exchangeable cations.<br />

4.8. ORGANIC IONS IN SOLUTION<br />

There are three types of organic functional groups—acid, phenolic, and nitrogen—which<br />

are commonly ionized in soil (Figure 4.7). Whether the group is<br />

H<br />

C<br />

H<br />

H<br />

O<br />

C<br />

OH<br />

Carboxylic acid<br />

Phenol<br />

OH<br />

C N<br />

R<br />

H R<br />

+ H +<br />

H<br />

C<br />

H<br />

O<br />

C<br />

O –<br />

Carboxylate ion<br />

Phenoxy ion<br />

H<br />

H<br />

C N<br />

R<br />

H R<br />

+<br />

O –<br />

+ H +<br />

+ H +<br />

3 o Amine<br />

4 o Alkyl ammonium ion<br />

Figure 4.7. Reactions leading <strong>to</strong> the formation of charged organic species in soil. Note that the<br />

unsatisfied bond on the left is attached <strong>to</strong> some larger organic component in soil.

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