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

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<strong>from</strong> the deposition of NO2 on the plant surface <strong>and</strong> diffusion of NO2 through stomata<br />

following oxidation of NO by O3 within the canopy. This adsorption of NOx onto the plant<br />

canopy may reduce global NOx <strong>emissions</strong> to the atmosphere to as low as 13 Tg N yr -1<br />

compared to 21 Tg N yr -1 of the net ecosystem <strong>emissions</strong> to the atmosphere (Davidson &<br />

Kingerlee, 1997). Yienger <strong>and</strong> Levy (1995) suggested that canopy recapture of NO is an<br />

important correction to be made to global estimates of soil NO <strong>emissions</strong>.<br />

In addition to canopy effects on NOx <strong>emissions</strong>, plants add carbon (C) to the soil in the form<br />

of root exudates which, when decomposed become part of the soil organic-C. These C inputs<br />

may affect soil microbial N transformation processes such as denitrification (Firestone &<br />

Davidson, 1989). During plant root respiration oxygen (O2) is consumed <strong>and</strong> CO2 is released<br />

by plant roots. Plant roots have been shown to create anaerobic conditions in soils <strong>and</strong><br />

provided substrates such as easily decomposable root exudates for the soil microorganism<br />

resulting in enhanced denitrification (Mahmood et al., 1997; Nykanen et al., 1995). Carbon<br />

regulates NO production primarily due to its effect on denitrification (section 9.5). In<br />

addition, soil C inputs increase denitrification under anaerobic conditions (Baumgartner &<br />

Conrad, 1992; Drury et al., 1991)). For example, Schuster <strong>and</strong> Conrad (1992) showed that<br />

glucose addition increased NO production under anaerobic conditions by a factor of 6.6<br />

compared to a control soil. Venterea <strong>and</strong> Rolston (2000a) found that a positive correlation<br />

was obtained between soil organic C <strong>and</strong> NO production in agricultural soils (sterile soils).<br />

These workers showed that it was due to the reaction of nitrification derived NO2 - with H +<br />

concentrations at low soil pH levels. Stevenson (1994) reported that reactions of HNO2 with<br />

phenolic <strong>and</strong> other constituents of soil organic matter promoted NO production.<br />

However, with respect to the urine patch, previous studies have shown that solubilization of<br />

soil organic matter occurs as a result of the high soil pH induced following hydrolysis<br />

reactions. This may assist in the production of NOx <strong>emissions</strong> if denitrification is a dominant<br />

production pathway.<br />

2.7 Research Objectives<br />

In view of the shortcomings in the current underst<strong>and</strong>ing of urine induced NOx fluxes a<br />

sequence of controlled laboratory studies were also conceived in order to examine the effects<br />

of soil moisture <strong>and</strong> temperature, soil pH <strong>and</strong> urine-N rate on the subsequent NOx <strong>emissions</strong>.<br />

Further in situ studies were also performed to examine urine-N rate <strong>and</strong> in situ seasonal<br />

effects on NOx <strong>emissions</strong> <strong>from</strong> urine patches.<br />

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