Introduction to Soil Chemistry
Introduction to Soil Chemistry
Introduction to Soil Chemistry
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
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)