Wj. Parton et al., GENERALIZED-MODEL FOR N-2 AND N2O PRODUCTION FROM NITRIFICATION AND DENITRIFICATION, Global biogeochemical cycles, 10(3), 1996, pp. 401-412
We describe a model of N-2 and N2O gas fluxes from nitrification and d
enitrification. The model was developed using laboratory denitrificati
on gas flux data and field-observed N2O gas fluxes from different site
s. Controls over nitrification N2O gas fluxes are soil texture, soil N
H4, soil water-filled pore space, soil N turnover rate, soil pH, and s
oil temperature. Observed data suggest that nitrification N2O gas flux
es are proportional to soil N turnover and that soil NH4 levels only i
mpact N2O gas fluxes with high levels of soil NH4 (>3 mu g N g(-1)). T
otal denitrification (N-2 plus N2O) gas fluxes are a function of soil
heterotrophic respiration rates, soil NO3, soil water content, and soi
l texture. N-2:N2O ratio is a function of soil water content, soil NO3
, and soil heterotrophic respiration rates. The denitrification model
was developed using laboratory data [Weier et al., 1993] where soil wa
ter content, soil NO3, and soil C availability were varied using a ful
l factorial design. The Weier's model simulated observed N-2 and N2O g
as fluxes for different soils quite well with r(2) equal to 0.62 and 0
.75, respectively. Comparison of simulated model results with field N2
O data for several validation sites shows that the model results compa
re well with the observed data (r(2)=0.62). Winter denitrification eve
nts were poorly simulated by the model. This problem could have been c
aused by spatial and temporal variations in the observed soil water da
ta and N2O fluxes. The model results and observed data suggest that ap
proximately 14% of the N2O fluxes for a shortgrass steppe are a result
of denitrification and that this percentage ranged from 0% to 59% for
different sites.