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Introduction to Soil Chemistry

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phosphorus 205<br />

<strong>to</strong> soil cation exchange sites and be an exchangeable cation. In the fine-grained<br />

mica-type clays, ammonia can be trapped between clay sheets. In this condition<br />

the ammonium is not available <strong>to</strong> plants and is seldom biologically available.<br />

The third group is amino acids and proteins. While amino acids are soluble<br />

in water and thus are expected <strong>to</strong> move readily, they are also zwitterions<br />

(having both positive and negative charges) and thus may interact with charges<br />

on soil particles, depending on the pH, and move slowly or not at all. Proteins<br />

are polymers of amino acid and may or may not be soluble but can have<br />

charges as do amino acids. There are also a large number of other types of<br />

nitrogen containing compounds, for example, amino sugars and nitrogen<br />

containing lipids, present in soil, and some will be soluble while others are<br />

insoluble.<br />

Otherwise, nitrogen moves between the various soil compartments easily,<br />

depending on the soil environmental conditions. These movements are often<br />

outlined as the nitrogen cycle (which can be found in the text by Coyne [24]).<br />

The slowest and most energy-intensive part of the cycle is the “fixation” of<br />

nitrogen gas (N 2) forming various nitrogen compounds with either oxygen,<br />

forming oxyanions (hydrogen), forming ammonia, or with carbon <strong>to</strong> form<br />

amino acids. Once these initial compounds are formed, subsequent changes in<br />

nitrogen species are fairly rapidly and easily accomplished.<br />

Ammonium (NH 4 + ) may be added as a fertilizer or released during organic<br />

matter decomposition. It is the chief species present immediately after the<br />

injection of anhydrous ammonium in<strong>to</strong> soil (as a fertilizer). Ammonium will<br />

be present in solution, as a cation, attracted <strong>to</strong> the cation exchange sites, and<br />

it may also become trapped between clay layers. It is labile in soil in that, under<br />

aerobic, moist, moderate temperature conditions, it is rapidly oxidized <strong>to</strong><br />

nitrite and nitrate. Ammonia may also be volatilized from the soil solution,<br />

particularly under basic soil conditions.<br />

Oxidized species, chiefly nitrite and nitrate, of nitrogen occur in all soils in<br />

the soil solution. Although nitrite in the environment is of concern, its occurrence<br />

is usually limited because the oxidation of nitrite <strong>to</strong> nitrate is more rapid<br />

than the oxidation of ammonia <strong>to</strong> nitrite. Both nitrite and nitrate move readily<br />

in soil, and nitrate is available <strong>to</strong> plants as a source of nitrogen and can move<br />

<strong>to</strong> plant roots with water.<br />

As a result of these reactions and volatilization, nitrogen species concentrations<br />

are expected <strong>to</strong> change during sampling and sample s<strong>to</strong>rage. This<br />

is particularly true if precautions are not taken <strong>to</strong> limit this eventuality<br />

[2,23,25–27].<br />

10.4. PHOSPHORUS<br />

To understand the occurrence of phosphate oxyanions in soil, the titration of<br />

phosphoric acid is instructive. Phosphoric acid is triprotic, and each of the<br />

pro<strong>to</strong>ns has a different pKa. Thus the titration curve has three inflections

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