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Denitrification losses in response to N fertiliser rates - a synthesis of high temporal resolution N2O, in-situ 15N2O and 15N2 measurements and fertiliser 15N recoveries in intensive sugarcane systems
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  • Naoya Takeda,
  • Johannes Friedl,
  • Robert Kirkby,
  • David Rowlings,
  • Clemens Scheer,
  • Daniele De Rosa,
  • Peter R Grace
Naoya Takeda
Queensland University of Technology

Corresponding Author:n3.takeda@qut.edu.au

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Johannes Friedl
Queensland Institute of Technology
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Robert Kirkby
Queensland University of Technology
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David Rowlings
Queensland University of Technology
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Clemens Scheer
IMK-IFU, Karlsruhe Institute of Technology
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Daniele De Rosa
European Commission, Joint Research Centre (JRC), Sustainable Resources Directorate, Land Resources Unit
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Peter R Grace
Queensland University of Technology
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Abstract

Denitrification is a key process in the global nitrogen (N) cycle, causing both nitrous oxide (N2O) and dinitrogen (N2) emissions. However, estimates of seasonal denitrification losses (N2O+N2) are scarce, reflecting methodological difficulties in measuring soil-borne N2 emissions against the high atmospheric N2 background and challenges regarding their spatio-temporal upscaling. This study investigated N2O+N2 losses in response to N fertiliser rates (0, 100, 150, 200 and 250 kg N ha-1) on two intensively managed tropical sugarcane farms in Australia, by combining automated N2O monitoring, in-situ N2 and N2O measurements using the 15N gas flux method and fertiliser 15N recoveries at harvest. Dynamic changes in the N2O/(N2O+N2) ratio (< 0.01 to 0.768) were explained by fitting generalised additive mixed models (GAMMs) with soil factors to upscale high temporal-resolution N2O data to daily N2 emissions over the season. Cumulative N2O+N2 losses ranged from 12 to 87 kg N ha-1, increasing non-linearly with increasing N fertiliser rates. Emissions of N2O+N2 accounted for 31–78% of fertiliser 15N losses and were dominated by environmentally benign N2 emissions. The contribution of denitrification to N fertiliser loss decreased with increasing N rates, suggesting increasing significance of other N loss pathways including leaching and runoff at higher N rates. This study delivers a blueprint approach to extrapolate denitrification measurements at both temporal and spatial scales, which can be applied in fertilised agroecosystems. Robust estimates of denitrification losses determined using this method will help to improve cropping system modelling approaches, advancing our understanding of the N cycle across scales.