Abstract

Nitrous oxide (N2O) is a potent greenhouse gas, and drained tropical/subtropical wetland soils that are high in carbon (C) make a substantial contribution to global anthropogenic N2O emissions. However, we previously reported negligible N2O emissions from an acidic, C-rich Gleysol under aerobic rice (Oryza sativa L.) production in the subtropics despite ample moisture and fertiliser nitrogen (N). In a field experiment, seasonal cumulative N2O emissions in the field following the application of 90 kg ha−1 N as urea were low (0.15 kg N2O-N ha−1·season−1). An incubation study examining the effects of temperature (20 °C, 25 °C and 30 °C) and water-filled pore space (WFPS; 40% vs. 60%) on N transformations showed that incubation temperature had a larger influence on nitrification than WFPS (40% vs. 60%). There was limited nitrification at 20 °C at either WFPS over 30 days, but low concentrations of NO3− (<100 mg kg−1) began to accumulate between 16–23 days at 30 °C and between 23–30 days at 25 °C. Liming soil resulted in nitrification after 10 days, while only minor nitrification was evident in the unlimed soil. The presence of the nitrification inhibitor 3,4-dimethylpyrazole phosphate (DMPP) with urea delayed nitrification for up to 4 days in the limed soil, suggesting such inhibitors may not provide substantial benefits in high C soils. Our results suggest that a low soil pH contributes to impaired nitrification in the C-rich Gleysol examined, which is associated with low fluxes of N2O in the field. We suggest that soil pH could potentially be manipulated to sustain low rates of nitrification and lower N losses, without compromising crop growth.

Highlights

  • The global demand for fertiliser nitrogen (N) has grown in recent years from 110.03 Mt N in 2015 to a projected 118.76 Mt N in 2020 [1]

  • Well recognised that N fertiliser application to soil can result in the production and loss to the atmosphere of nitrous oxide (N2 O), a greenhouse gas with a global warming potential of 300 times that of carbon dioxide (CO2 ) on a 100 year timescale and that is of major importance for stratospheric ozone depletion [3]

  • When drained for agricultural purposes, peat soils become a source of both CO2 and nitrous oxide (N2 O) and make a substantial contribution to agricultural greenhouse gas emissions [6]

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Summary

Introduction

The global demand for fertiliser nitrogen (N) has grown in recent years from 110.03 Mt N in 2015 to a projected 118.76 Mt N in 2020 [1] This rising demand for fertiliser N is closely related to the rising demand for food, fibre and biofuels [2]. It is, well recognised that N fertiliser application to soil can result in the production and loss to the atmosphere of nitrous oxide (N2 O), a greenhouse gas with a global warming potential of 300 times that of carbon dioxide (CO2 ) on a 100 year timescale and that is of major importance for stratospheric ozone depletion [3]. When drained for agricultural purposes, peat soils become a source of both CO2 and nitrous oxide (N2 O) and make a substantial contribution to agricultural greenhouse gas emissions [6]

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