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Introduction to Soil Chemistry

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conclusions 207<br />

situ, thus removing problems associated with sampling and extraction. This<br />

approach, although optimal, is feasibly in only a few instances. The second<br />

approach is <strong>to</strong> make the analysis as quickly after sampling as possible, preferably<br />

in the field, so as <strong>to</strong> eliminate s<strong>to</strong>rage problems. In this case minutes or<br />

seconds between sampling and analysis are desirable.<br />

When these approaches are not possible, steps must be taken <strong>to</strong> account<br />

for changes occurring during sampling and s<strong>to</strong>rage. These can be in either<br />

direction; that is, the concentration of a species may increase or decrease or<br />

be converted <strong>to</strong> an entirely different species. It is not possible <strong>to</strong> give a prescription<br />

for sampling or s<strong>to</strong>rage that will guarantee the stability of a soil<br />

species over a period of time. Some species will be sensitive <strong>to</strong> oxidation while<br />

others will be changed by the lack of oxygen. In some cases species will be<br />

stable in air dry soil while others will be more stable in moist soil. In some<br />

cases refrigeration at 0°C is best while other species will require s<strong>to</strong>rage at<br />

-40°C or even lower temperatures. In yet other cases s<strong>to</strong>rage at room temperature<br />

will be sufficient. The solution <strong>to</strong> sampling and s<strong>to</strong>rage problems is<br />

<strong>to</strong> study the stability of the species of interest under various sampling and<br />

s<strong>to</strong>rage conditions and thus determine which is best.<br />

Some generalized sampling and s<strong>to</strong>rage recommendations, however, can be<br />

made. During sampling and s<strong>to</strong>rage samples must be kept under the same<br />

oxygen concentration, temperature, and pressure conditions occurring in the<br />

field, if species integrity is <strong>to</strong> be maintained. Samples taken from anaerobic,<br />

low- or high-temperature, or high-pressure conditions should be maintained<br />

under these conditions during sampling, s<strong>to</strong>rage, and until actual analysis<br />

is carried out. A sample taken from the bot<strong>to</strong>m of a lake will be under<br />

pressure and low-oxygen or anaerobic conditions. It may also be at a significantly<br />

lower temperature than surface water, air, or soil temperatures. To<br />

maintain sample integrity, it must be kept under these conditions [2].<br />

10.6. CONCLUSIONS<br />

This discussion is not intended <strong>to</strong> be a comprehensive discussion of all the elements,<br />

cations, anions, and organic species present in soil. It includes a range<br />

of such species that illustrate the common situations related <strong>to</strong> the analysis of<br />

cations, anions, and oxyanions in soil. Different species have different biological<br />

reactivity and availability, and thus it is important <strong>to</strong> know which species<br />

is present. Cations have water molecules surrounding them, and some cations<br />

react with water, forming oxy and hydroxy cations. Other cations can be<br />

present in multiple oxidation states and may be present in mixtures of these<br />

oxidation states. Some species added <strong>to</strong> soil will rapidly be converted <strong>to</strong> other<br />

species, such as the conversion of Cr 6+ <strong>to</strong> Cr 3+ , such that analysis for the original<br />

species may be fruitless, especially if the soil sample has been s<strong>to</strong>red for<br />

any length of time. All species may be associated in various ways with the inorganic,<br />

organic, and colloidal components of soil <strong>to</strong> form species of interest.

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