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Introduction to Soil Chemistry

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122 titrimetric measurement<br />

6.6. NITRITE AND NITRATE<br />

Both nitrite and nitrate are highly mobile in soil and easy <strong>to</strong> extract. However,<br />

it is also possible <strong>to</strong> reduce each individually <strong>to</strong> ammonia and subsequently<br />

steam-distill the ammonia, capturing and titrating it as described above for<br />

ammonia. If this procedure is <strong>to</strong> be followed, naturally occurring ammonia in<br />

soil must first be determined as described above. After this step, a reducing<br />

agent is placed in the flask and nitrite and nitrate reduced <strong>to</strong> ammonia. The<br />

soil is then rendered basic again and the ammonia steam-distilled and titrated.<br />

If both nitrate and nitrite are reduced at the same time, the combined amount<br />

of both is obtained. At this point selective reduction of either nitrate or nitrite<br />

with subsequent distillation and titration will allow for calculation of the<br />

amounts of all three forms of nitrogen in the soil sample.<br />

The determination of nitrite and nitrite in soil can be accomplished by<br />

reactions carried out before digestion or steam distillation <strong>to</strong> oxidize nitrite <strong>to</strong><br />

nitrate and <strong>to</strong> reduce nitrate <strong>to</strong> ammonia. Alternately, nitrite can be reacted<br />

with an organic compound, typically salicylic acid and subsequently digested<br />

in a typical kjeldahl procedure. This procedure starts with an organic molecule<br />

that reacts with nitrite <strong>to</strong> form a nitro compound that is subsequently reduced<br />

<strong>to</strong> an amine. The amine is then subject <strong>to</strong> digestion just as with organic matter<br />

in soil. In this way the <strong>to</strong>tal nitrogen content in soil can be determined. Also,<br />

when this procedure is combined with those described above, the amounts of<br />

the various forms of nitrogen in soil—organic, ammonia, nitrite, and nitrate—<br />

can be determined. This is thus an extremely powerful method for elucidating<br />

the nitrogen status of soils. Figure 6.7 gives a flow diagram for determining<br />

nitrite and nitrate in soil using a kjeldahl apparatus.<br />

The procedures described above determine soil nitrogen that is often taken<br />

<strong>to</strong> be the <strong>to</strong>tal nitrogen in soil. Because very few other organic or inorganic<br />

nitrogen compounds are commonly found in soil, there is little call for additional<br />

analytical procedures. However, there are some exceptions <strong>to</strong> this. It<br />

may be necessary <strong>to</strong> determine the gaseous oxides of nitrogen, formed during<br />

denitrification. This is typically accomplished using gas chroma<strong>to</strong>graphy (see<br />

Chapter 9). Also, using simple steam distillation ammonia trapped in clay<br />

structures will not be determined. Such determination requires complete<br />

destruction of soil minerals and the subsequently released ammonia<br />

determined.<br />

Although kjeldahl procedures are capable of providing information about<br />

all the common nitrogen components in soil, it is a time-, labor-, equipment-,<br />

and reagent-intensive procedure. Typically kjeldahl equipment, namely, a<br />

digestion–steam distillation apparatus, can accommodate 6, 12, or more<br />

digestion tubes or flasks and distillation, and titration can be done quickly;<br />

however, it will take hours <strong>to</strong> do any significant number of samples. For 15 N<br />

work, additional steps, time, and money are required <strong>to</strong> convert ammonia <strong>to</strong><br />

nitrogen gas and determination of 15 N by mass spectrometry (see Chapter 8)<br />

[6].

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