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Deposition of urine and dung in pasture-based livestock production systems is a major source of ammonia ( NH3) volatilization, contributing to the eutrophication and acidification of water bodies and to indirect nitrous oxide emissions. The objectives of this study were to (i) measure NH3 volatilization from dung and urine in three seasons, (ii) test the effect of spiking urine with the nitrification inhibitor dicyandiamide ( DCD) on NH3 volatilization and (iii) generate NH3 emission factors ( EFs) for dung, urine and urine + DCD in temperate maritime grassland. Accordingly, simulated dung, urine and urine spiked with DCD (at 30 kg DCD/ha equivalent rate) patches were applied to temperate grassland. Treatments were applied three times in 2014 with one measurement of NH3 loss being completed in spring, summer and autumn. The NH3-N EF was highest in spring, which was most likely due to the near absence of rainfall throughout the duration of loss measurement. The EFs across the experiments ranged between 2.8 and 5.3% (mean 3.9%) for dung, 8.7 and 14.9% (mean 11.2%) for urine and 9.5 and 19.5% (mean 12.9%) for urine + DCD, showing that ammonia loss from dung was significantly lower than from urine. Aggregating country-specific emission data such as those from the current experiment with data from climatically similar regions (perhaps in a weighted manner which accounts for the relative abundance of certain environmental conditions) along with modelling is a potentially resource-efficient approach for refining national ammonia inventories. [ABSTRACT FROM AUTHOR]

A small proportion (15–35%) of nitrogen (N) entering pasture-based livestock production systems is converted to tradable agricultural products. The majority of remaining N (surplus N) is largely unaccounted for. While some surplus N is retained in the system, which can be beneficial, most is lost through a range of pathways with potential environmental consequences. The objectives of this study were to (i) account for the N entering a pasture-based dairy production system by determining the amount of N exiting in products and lost to the wider environment and (ii) determine the relative importance of the components of this balance sheet. Detailed measurements and estimates of N entering and exiting a pasture-based dairy production system in Ireland (52°51′N, 08°21′W) was completed in 2011 and 2012. Total N entering and exiting the system was 245 kg ha −1 and 269 kg ha −1 , respectively, averaged over both years. The latter being comprised of N exiting in products: 79 kg ha −1 and losses to the wider environment: 190 kg ha −1 . The N use efficiency of the system was 29% and 37% in 2011 and 2012, respectively. The system N balance (mean ± 95% confidences intervals) was –50 ± 82 kg ha −1 in 2011 and +1 ± 22 kg ha −1 in 2012 and, hence, came close to equality between N entering and existing the system. Of N lost by various pathways, 6.1% was lost to groundwater, 41.6% as ammonia, 8.0% as nitrous oxide and 43.7% as dinitrogen gas. Although N surpluses on pasture based livestock production systems can be substantial, the results of this study suggest that a high proportion of surplus N was lost as environmentally benign dinitrogen gas. This study also highlights that emphasis should be on ammonia and nitrous oxide to minimise environmentally damaging N losses and improve the N-efficiency of such systems of dairy production. [ABSTRACT FROM AUTHOR]

Cattle and cow slurry storage is a significant source of agricultural greenhouse gas (GHG) and ammonia (NH3) emissions. While acidification has been demonstrated to significantly reduce these emissions, a knowledge gap exists to identify a range of chemical amendments that are safe, suitable and cost effective to mitigate both GHG and NH 3 gases simultaneously. The current study showed that ferric chloride, sulphuric acid, alum and acetic acid were extremely effective at abating emissions, with NH 3 reduced by 96%, 85%, 82% and 73%, respectively. In terms of methane (CH 4), ferric chloride, alum, sulphuric acid and acetic acid reduced emissions by 98%, 96%, 95% and 94%, respectively. Previous studies have found that the reduction of >pH 6 can inhibit the release of these gases; however, the effectiveness can vary depending on each amendment's composition. The cost benefit analysis, assessed the amendments in terms of both gaseous emissions reduction and net cost. Sulphuric acid, acetic acid, ferric chloride and alum ranked best, respectively. Currently, the cost of implementing these amendments is, at best, cost neutral. Therefore, incentivising chemical amendments for the abatement of GHG and NH 3 gases from slurry storage is needed. This incubation experiment is an effective means of pre-screening amendments before they are explored at pilot or full scale with subsequent field application. Future research should consider the assessment of cheaper on- and off-farm alternative waste streams as slurry amendment. Image 1 • Acidification of cattle and dairy slurry was investigated. • Target pH of 5.5 resulted in a 96% reduction in NH 3 and 98% reduction in CH 4. • Ferric chloride reductions were independent of pH value. • Cost analysis revealed financial incentives are needed for scaled implementation. [ABSTRACT FROM AUTHOR]