Abstract

Urine patches and dung pats from grazing livestock create hotspots for production and emission of the greenhouse gas, nitrous oxide (N2O), and represent a large proportion of total N2O emissions in many national agricultural greenhouse gas inventories. As such, there is much interest in developing country specific N2O emission factors (EFs) for excretal nitrogen (EF3, pasture, range and paddock) deposited during gazing. The aims of this study were to generate separate N2O emissions data for cattle derived urine and dung, to provide an evidence base for the generation of a country specific EF for the UK from this nitrogen source. The experiments were also designed to determine the effects of site and timing of application on emissions, and the efficacy of the nitrification inhibitor, dicyandiamide (DCD) on N2O losses. This co-ordinated set of 15 plot-scale, year-long field experiments using static chambers was conducted at five grassland sites, typical of the soil and climatic zones of grazed grassland in the UK. We show that the average urine and dung N2O EFs were 0.69% and 0.19%, respectively, resulting in a combined excretal N2O EF (EF3), of 0.49%, which is <25% of the IPCC default EF3 for excretal returns from grazing cattle. Regression analysis suggests that urine N2O EFs were controlled more by composition than was the case for dung, whilst dung N2O EFs were more related to soil and environmental factors. The urine N2O EF was significantly greater from the site in SW England, and significantly greater from the early grazing season urine application than later applications. Dycandiamide reduced the N2O EF from urine patches by an average of 46%. The significantly lower excretal EF3 than the IPCC default has implications for the UK's national inventory and for subsequent carbon footprinting of UK ruminant livestock products.

Highlights

  • Grazed grasslands support a significant proportion of sheep and cattle production throughoutEurope and other parts of the World, converting human-inedible plant biomass into human edible animal products but with generally low nitrogen (N) use efficiencies

  • It is well documented that urine additions to grassland soils result in significant quantities of N2O production and emission, mainly due to the soil microbial processes of nitrification and denitrification (Selbie et al, 2015), following the addition of readily available N and carbon (C), and the effects of significantly increased percentage of water filled pore space (WFPS) within the urine patch

  • In this paper we summarise the results of the first co-ordinated set of plot-based experiments aimed at generating new N2O emissions data for disaggregated urine and dung deposition to soil, from which country specific N2O emission factors (EFs) can be derived that are relevant to UK soils and climate

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Summary

Introduction

Grazed grasslands support a significant proportion of sheep and cattle production throughout. Europe and other parts of the World, converting human-inedible plant biomass into human edible animal products but with generally low nitrogen (N) use efficiencies. It is well documented that urine additions to grassland soils result in significant quantities of N2O production and emission, mainly due to the soil microbial processes of nitrification and denitrification (Selbie et al, 2015), following the addition of readily available N and carbon (C), and the effects of significantly increased percentage of water filled pore space (WFPS) within the urine patch (van der Weerden et al, 2012). Deposition of N in urine patches can represent an equivalent application rate of 200-2000 kg. A meta-analysis by Selbie et al (2015) indicates average urine patch N loading rates for dairy cows and beef cattle of 613 kg N ha-1 and 345 kg N ha-1, respectively

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