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THE FLORIDA STATE UNIVERSITY ARTS AND SCIENCES ...

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1.3.2. Mass Balance Approach<br />

Mass balance has long been used to estimate various terrestrial N fluxes at the field scale<br />

and more recently at stream reach, watershed, or regional scales (Groffman et al., 2006).<br />

In some studies, denitrification is estimated using literature values and is one component<br />

of the mass balance (Hantzche & Finnemore, 1992); others estimate denitrification by the<br />

difference in the mass balance (e.g., David & Gentry, 2000, Tesoriero et al., 2000 Pribyl<br />

et al., 2004).<br />

As this method can be applied at a range of scales, from small plots to large watersheds,<br />

lakes, estuaries, and open marine systems, it is a useful method to assess denitrification.<br />

However, in order to estimate denitrification by mass balance, direct measurements or<br />

estimates of all other N fluxes and changes in storage for the system are needed. The use<br />

of this method requires the assumption of a steady state system and only inputs and<br />

outputs are quantified. Major inputs to terrestrial systems typically include fertilizer,<br />

biological N2 fixation, and atmospheric deposition, with outputs including crop or<br />

biomass harvest and export from the area or leaching, runoff and riverine export.<br />

(Groffman et al., 2006). These assumptions place a limitation on the usefulness of mass<br />

balance as a predictive tool.<br />

While certainly useful in providing some insight into the potential importance of<br />

denitrification, the mass balance approximations can be improved if multiple years of<br />

data are used and averaged. This method is perhaps better suited to verify the validity of<br />

new methods of measuring the rate of denitrification.<br />

1.3.3. Isotopes<br />

Kinetic isotopic fractionation of<br />

−<br />

NO 3 during bacterial denitrification has been<br />

documented in laboratory and field studies (Mariotti 1981; Mariotti et al., 1988; Altabet<br />

et al., 1995; Barford et al., 1999; Voss et al., 2001). The bacteria responsible for<br />

denitrification preferentially utilize the lighter isotopes than the heavier isotopes during<br />

denitrification, thus leaving the remaining elements in the system enriched in the heavier<br />

isotopes.<br />

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