Abstract

Abstract. A field study was conducted to determine the effect of the nitrification inhibitor dicyandiamide (DCD) on N2O and N2 emissions after cattle slurry (CS) application in the presence of nitrate (NO3) fertiliser on seven different occasions (between March 2009 and March 2011). N2O emissions from CS in the presence of NO3 fertiliser were very high (0.4–8.7% of applied N) over a 20-day period, under mild moist conditions. Emissions were significantly larger from the CS treatment compared to an NH4+-N source, supplying the same rate of N as in the slurry. This study supports the view that organic fertilisers should not be applied at the same time as nitrate-based fertilisers, as significant increases in N2O emissions occur. The average N2O mole fraction (N2O/(N2O + N2)) over all seven application dates was 0.34 for CSNO3 compared to 0.24 for the NH4ClNO3 treatment, indicating the dominance of N2 emissions. The rate of nitrification in CSNO3 was slower than in NH4ClNO3, and DCD was found to be an effective nitrification inhibitor in both treatments. However, as N2O emissions were found to be predominantly associated with the NO3 pool, the effect of DCD in lowering N2O emissions is limited in the presence of a NO3 fertiliser. To obtain the maximum cost-benefit of DCD in lowering N2O emissions, under mild moist conditions, it should not be applied to a nitrate containing fertiliser (e.g. ammonium nitrate or calcium ammonium nitrate), and therefore the application of DCD should be restricted to ammonium-based organic or synthetic fertilisers.

Highlights

  • Ammonium nitrate (AN) and calcium ammonium nitrate (CAN) are the dominant forms of fertiliser applied to grassland in UK and Ireland

  • N2O and N2 cumulative emissions were expressed as a percentage of the applied N

  • Over the seven treatment dates, between 0.4–8.7 % of the applied N (NH+4 and NO−3 ) was lost as N2O and between 2.1–23.2 % was lost as N2 in the CSNO3 treatment

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Summary

Introduction

Ammonium nitrate (AN) and calcium ammonium nitrate (CAN) are the dominant forms of fertiliser applied to grassland in UK and Ireland. AN contains nitrogen as NH+4 -N and NO−3 -N, and CAN contains in addition dolomite or limestone. Fertiliser usage for grassland has been declining since the mid-1980s by 38 % in UK and 33 % in Ireland. Spiralling fertiliser prices (Farmers Weekly, 2012) and nitrate regulations have mostly caused the observed decline. There is more of an incentive to use organic fertilisers to supply nitrogen (N) in a nutrient management plan on farms, and cattle slurry is by far the most common form of organic fertiliser. On-farm nutrient management planning encourages the integrated use of both cattle slurry and inorganic fertilisers. The practice of cattle slurry being applied in the presence of NO3 is regionally relevant

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