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Diploma thesis in Physics submitted by Florian Freundt born in ...

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2.3. Soil atmosphere composition 2 Theory<br />

2.3 Soil atmosphere composition<br />

2.3.1 Sources, s<strong>in</strong>ks and profiles of O2 and CO2<br />

The most important subsurface source of CO2 and s<strong>in</strong>k of O2 is soil respiration, which summarizes<br />

the production of CO2 caused <strong>by</strong> root respiration and microbiological processes. How<br />

important each process is <strong>in</strong> a given soil is hard to estimate and varies with many parameters.<br />

Usually the fraction of CO2 production caused <strong>by</strong> root respiration is given as rang<strong>in</strong>g from 0<br />

– 50 % [Amundson and Davidson, 1990; Scheffer and Schachtschabel, 2010]. Tang et al. [2005]<br />

give an annual mean of 44 % and a grow<strong>in</strong>g season average of 56 % <strong>in</strong> a forest soil.<br />

In the presence of O2, CO2 is produced <strong>by</strong> aerobic bacteria ga<strong>in</strong><strong>in</strong>g energy from the decomposition<br />

of glucose:<br />

C6H12O6 + 6 O2 −→ 6 CO2 + 6 H2O + 2800 kJ/mol (2.26)<br />

This reaction produces equimolar amounts of gas and therefore does not <strong>in</strong>fluence the partial<br />

pressure equilibrium of the soil atmosphere directly as the sum of O2 and CO2 should still be<br />

20.9 Vol%. The produced CO2 has a much higher solubility <strong>in</strong> water than O2, lead<strong>in</strong>g to a<br />

reduction of CO2 partial pressure. In acidic soils (pH < 5) this removal of CO2 from the gaseous<br />

phase is generally described <strong>by</strong> the follow<strong>in</strong>g equilibrium reaction [Yamaguchi et al., 1967]:<br />

CO2(g) + H2O ⇋ H2CO3 ⇋ HCO − 3 + H+ ⇋ CO 2−<br />

3<br />

+ 2 H+<br />

(2.27)<br />

Oxygen depletion <strong>by</strong> microbial activity can therefore lead to a deficit <strong>in</strong> partial pressure, which<br />

is the basis for the proposed OD model presented <strong>in</strong> Section 2.1.3.<br />

When O2 is not available (close to the water table or under waterlogged conditions), anaerobic<br />

<strong>in</strong>stead of aerobic bacteria flourish, lead<strong>in</strong>g to different carbohydrate decomposition processes.<br />

In the absence of O2 the oxidation of glucose<br />

C6H12O6 −→ 2 CH3 CO COOH + 4 H + + 4 e −<br />

(2.28)<br />

requires a match<strong>in</strong>g reduction reaction to be provided <strong>by</strong> the microorganism, lead<strong>in</strong>g to various<br />

possible reactions [Rowell, 1997] such as denitrification or the production of methane:<br />

2 NO − 3 + 12 H+ + 10 e − −→ N2 + 6 H2O (2.29)<br />

CO2 + 8 H + + 8 e − −→ CH4 + 2 H2O (2.30)<br />

Another anaerobic process is given <strong>by</strong> Scheffer and Schachtschabel [2010] as<br />

C6H12O6 −→ 3 CO2 + 3 CH4 + 188 kJ/mol (2.31)<br />

Anaerobic processes are mostly non-equimolar regard<strong>in</strong>g the gas phase, lead<strong>in</strong>g to an <strong>in</strong>crease of<br />

gas concentration and therefore a partial pressure gradient. In the case of waterlogged marshes<br />

this can cause significant flow and emissions of CH4 from the soil.<br />

In general, microbial activity reduces the amount of O2 <strong>in</strong> the soil and <strong>in</strong>creases the amount of<br />

CO2, CH4 and of some nitrogenous gases. The ma<strong>in</strong> source for O2 is the atmosphere, result<strong>in</strong>g <strong>in</strong><br />

28

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