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Introduction to Soil Chemistry

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potentiometry (electrodes in soil measurements) 97<br />

trode potentials for the oxidation of oxygen and the reduction of hydrogen at<br />

common soil pH levels.<br />

Although the reduction of hydrogen and the oxidation of oxygen determine<br />

the lower and upper limits of electrochemical redox measurements in soil, it<br />

is still possible <strong>to</strong> have both hydrogen and oxygen produced by biological<br />

processes. Pho<strong>to</strong>synthetic production of oxygen by algae and pho<strong>to</strong>trophic<br />

bacteria occurs in all soils. Likewise, the biological production of hydrogen gas<br />

occurs under anaerobic conditions. Thus it is possible <strong>to</strong> find oxygen and/or<br />

hydrogen gas being produced in soil.<br />

In soil analysis, pH, selective ion, oxidation–reduction (redox), electrical<br />

conductivity cells, and oxygen electrodes are commonly used. For each of these<br />

measurements a different specific electrode along with a separate or integral<br />

reference electrode will be needed. In some cases, with extended use or long<br />

exposure <strong>to</strong> soil or soil–water suspensions, electrodes may become polarized.<br />

When this happens, erroneous results will be obtained and depolarization will<br />

need <strong>to</strong> be carried out using the electrode manufacturers’ directions [3].<br />

5.3.1. pH<br />

In soil one can conceive of the presence of three “types” of pro<strong>to</strong>ns (see<br />

Chapter 6, p. 116). However, those in solution, associated with water molecules<br />

forming hydronium ions, are the only measurable pro<strong>to</strong>ns. Other pro<strong>to</strong>ns will<br />

be associated with cation exchange sites, are exchangeable, and contribute <strong>to</strong><br />

soil buffering. They cannot be measured directly but can be exchanged with<br />

cations from salts or buffer solutions, and once in solution they can be measured.<br />

The third “type” of pro<strong>to</strong>n is bonded <strong>to</strong> either inorganic or organic soil<br />

components and normally will be regarded as being covalently bonded.<br />

However, they may be part of a functional group from which they may be<br />

easily removed and thus become part of the pro<strong>to</strong>ns in solution. Both organic<br />

acid and phenolic groups are examples of compounds, which have pro<strong>to</strong>ns,<br />

that fall in<strong>to</strong> this category.<br />

The absolute pH of soil cannot be known absolutely; however, standardized<br />

methods for measuring soil pH have been developed.<br />

A combination pH electrode, as illustrated in Figure 5.4 and shown in<br />

Figure 5.5 (A), is most commonly used in determining soil pH. However, two<br />

separate electrodes, one pH sensing (i.e., the H + glass bulb in Figure 5.5) and<br />

the other a reference electrode, may be used and may be best in cases where<br />

fouling of the reference electrode is a particular problem. Care must always<br />

be taken <strong>to</strong> avoid scratching or breaking the pH sensing bulb when making a<br />

pH measurement, because while some pH electrodes have robust pH sensing<br />

electrodes, others are quite delicate. Figure 5.6 shows a pH electrode in a soil<br />

suspension, which is connected through a card, which is a pH meter, <strong>to</strong> a lap<strong>to</strong>p<br />

computer that provides data output.<br />

Electrodes may be attached <strong>to</strong> a pH meter, which can be analog, digital, or,<br />

as mentioned above, <strong>to</strong> a computer. Several different connec<strong>to</strong>rs are used

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