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Factors affecting nitric oxide and nitrous oxide emissions from ...

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NH 4 + -N (g g -1 dry soil)<br />

1000<br />

800<br />

600<br />

400<br />

200<br />

0<br />

35<br />

30<br />

25<br />

20<br />

15<br />

Days<br />

10<br />

5<br />

0<br />

4.5<br />

5.0<br />

5.5<br />

6.0<br />

6.5<br />

7.0<br />

7.5<br />

Initial soil pH<br />

Figure 4.2 Mesh plot of soil NH4 + -N concentrations over time versus initial soil pH for the<br />

urine treated soils.<br />

4.3.2 Soil NO2 - -N concentrations<br />

Without urine application, mean soil NO2 - -N concentrations ranged <strong>from</strong> 0.93 to 2.39 µg<br />

g -1 dry soil while in the urine treated soils they ranged <strong>from</strong> 0.79 to 3.56 µg g -1 dry soil. The<br />

initial soil pH had no significant effect on soil NO2 - -N concentrations (P = 0.15) at day 7, but<br />

on days 14 <strong>and</strong> 21 higher NO2 - -N concentrations occurred at soil pH 7.6 with no significant<br />

differences among the other treatments (Fig. 4.3). With sampling time as a factor, soil NO2 - -N<br />

concentrations decreased significantly as time progressed (r = -0.64, P < 0.01) (Fig. 4.2).<br />

There was no interaction between initial soil pH treatment <strong>and</strong> time (P = 0.69) (Fig. 4.4).<br />

When data <strong>from</strong> all sampling dates were pooled soil NO2 - -N concentrations correlated with<br />

soil NH4 + -N concentrations (r = 0.43, P < 0.01) but the only correlation between these two<br />

variables at any individual sampling day occurred on day 21 (Table, 4.3-4.6) .<br />

31

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