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Introduction to Soil Chemistry

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40 soil basics ii<br />

NH4<br />

Nitrosomonas spp.<br />

NO 2 –<br />

(2.3)<br />

When observing the oxidation of ammonia <strong>to</strong> nitrite in soil, it is found <strong>to</strong> be<br />

a slower reaction than is the oxidation of nitrite <strong>to</strong> nitrate. When the energy<br />

available from each of these reactions is considered [see (2.3)], it is obvious<br />

that this observation is directly related <strong>to</strong> the amount of energy available.<br />

In this case nitrite is not expected <strong>to</strong> occur or build up <strong>to</strong> appreciable levels<br />

in the environment. Nitrobacter species must use approximately 3.6 times as<br />

much nitrogen in terms of nitrogen a<strong>to</strong>ms <strong>to</strong> obtain the same amount of energy<br />

as Nitrosomonas spp.Thus it can be expected <strong>to</strong> take up nitrite at a higher rate<br />

<strong>to</strong> compete. This type of energy calculation is simply done by fac<strong>to</strong>ring in the<br />

amount or energy required for bond breaking and the amount released<br />

in bond making. Alternatively, the energy can be measured directly by<br />

calorimetry.<br />

2.8. ALL FACTORS TOGETHER<br />

In a purely chemical approach <strong>to</strong> how reactions take place, all of these fac<strong>to</strong>rs<br />

come <strong>to</strong>gether; specifically, the rate is related <strong>to</strong> <strong>to</strong>tal energy used and released,<br />

the energy of activation required, steric effects, and the types of bonds<br />

being broken and formed. For this reason it is most common <strong>to</strong> measure<br />

the energy and rate quantities directly for the conditions of the reaction.<br />

Because of the complexity of soil, it is even more important <strong>to</strong> measure these<br />

directly.<br />

2.9. MICELLES<br />

Nitrobacter spp.<br />

+ –<br />

NH4 + 1.5O2 NO2 + H2O + 2H +<br />

Nitrosomonas spp.<br />

Nitrobacter spp.<br />

–<br />

NO2 + 0.5O2 –<br />

NO3 +<br />

Difference<br />

NO 3 –<br />

275 kJ<br />

76 kJ<br />

3.62 ¥<br />

In Chapter 1 it is observed that sand, silt and clay do not act independently of<br />

each other. In a similar fashion clay particles alone do not act independently<br />

of each other; rather, they form groups of particles called micelles. The model<br />

for a micelle is a group of long-chain fatty acid salts in water. The hydrophobic<br />

ends are associated with the ionic “salt” end exposed <strong>to</strong> water. An idealized<br />

micelle with some associated water is shown in Figure 2.6. The structure<br />

is often described as being a ball-like. This ideal is hard <strong>to</strong> visualize when<br />

looking at the typical shape and size of a clay particle. However, it is possible<br />

<strong>to</strong> envision individual clay crystals associated with each other through hydro-<br />

(a)<br />

(b)

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