Ecological controls on N<sub>2</sub>O emission in surface litter and near-surface soil of a managed grassland: modelling and measurements

Large variability in N<sub>2</sub>O emissions from managed grasslands may occur because most emissions originate in surface litter or near-surface soil where variability in soil water content (<i>θ</i>) and temperature (<i>T</i><sub>s</sub>) is greates...

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Bibliographic Details
Main Authors: R. F. Grant, A. Neftel, P. Calanca
Format: Article
Language:English
Published: Copernicus Publications 2016-06-01
Series:Biogeosciences
Online Access:http://www.biogeosciences.net/13/3549/2016/bg-13-3549-2016.pdf
Description
Summary:Large variability in N<sub>2</sub>O emissions from managed grasslands may occur because most emissions originate in surface litter or near-surface soil where variability in soil water content (<i>θ</i>) and temperature (<i>T</i><sub>s</sub>) is greatest. To determine whether temporal variability in <i>θ</i> and <i>T</i><sub>s</sub> of surface litter and near-surface soil could explain this in N<sub>2</sub>O emissions, a simulation experiment was conducted with <i>ecosys</i>, a comprehensive mathematical model of terrestrial ecosystems in which processes governing N<sub>2</sub>O emissions were represented at high temporal and spatial resolution. Model performance was verified by comparing N<sub>2</sub>O emissions, CO<sub>2</sub> and energy exchange, and <i>θ</i> and <i>T</i><sub>s</sub> modelled by <i>ecosys</i> with those measured by automated chambers, eddy covariance (EC) and soil sensors on an hourly timescale during several emission events from 2004 to 2009 in an intensively managed pasture at Oensingen, Switzerland. Both modelled and measured events were induced by precipitation following harvesting and subsequent fertilizing or manuring. These events were brief (2–5 days) with maximum N<sub>2</sub>O effluxes that varied from  &lt;  1 mg<mspace linebreak="nobreak" width="0.125em"/>N<mspace linebreak="nobreak" width="0.125em"/>m<sup>−2</sup><mspace linebreak="nobreak" width="0.125em"/>h<sup>−1</sup> in early spring and autumn to  &gt;  3 mg<mspace linebreak="nobreak" width="0.125em"/>N<mspace width="0.125em" linebreak="nobreak"/>m<sup>−2</sup><mspace linebreak="nobreak" width="0.125em"/>h<sup>−1</sup> in summer. Only very small emissions were modelled or measured outside these events. In the model, emissions were generated almost entirely in surface litter or near-surface (0–2 cm) soil, at rates driven by N availability with fertilization vs. N uptake with grassland regrowth and by O<sub>2</sub> supply controlled by litter and soil wetting relative to O<sub>2</sub> demand from microbial respiration. In the model, NO<sub><i>x</i></sub> availability relative to O<sub>2</sub> limitation governed both the reduction of more oxidized electron acceptors to N<sub>2</sub>O and the reduction of N<sub>2</sub>O to N<sub>2</sub>, so that the magnitude of N<sub>2</sub>O emissions was not simply related to surface and near-surface <i>θ</i> and <i>T</i><sub>s</sub>. Modelled N<sub>2</sub>O emissions were found to be sensitive to defoliation intensity and timing which controlled plant N uptake and soil <i>θ</i> and <i>T</i><sub>s</sub> prior to and during emission events. Reducing leaf area index (LAI) remaining after defoliation to half that under current practice and delaying harvesting by 5 days raised modelled N<sub>2</sub>O emissions by as much as 80 % during subsequent events and by an average of 43 % annually. Modelled N<sub>2</sub>O emissions were also found to be sensitive to surface soil properties. Increasing near-surface bulk density by 10 % raised N<sub>2</sub>O emissions by as much as 100 % during emission events and by an average of 23 % annually. Relatively small spatial variation in management practices and soil surface properties could therefore cause the large spatial variation in N<sub>2</sub>O emissions commonly found in field studies. The global warming potential from annual N<sub>2</sub>O emissions in this intensively managed grassland largely offset those from net C uptake in both modelled and field experiments. However, model results indicated that this offset could be adversely affected by suboptimal land management and soil properties.
ISSN:1726-4170
1726-4189