381-9 Does Drainage of Poorly Drained Soils Affect Their Nitrogen Attenuation Capacity? Evidence from Six Dairy Farms in South Ireland.

See more from this Division: SSSA Division: Soil and Water Management and Conservation
See more from this Session: Soil and Water Managment and Conservation Oral IV

Wednesday, November 9, 2016: 10:50 AM
Phoenix Convention Center North, Room 127 A

Elisa Clagnan, Groundwater Protection and Restoration Group, Kroto Research Institute, University of Sheffield, Sheffield, UNITED KINGDOM, Steven F Thornton, Groundwater Protection and Restoration Group, Kroto Research Institute, University of Sheffield, sheffield, United Kingdom, Stephen A Rolfe, Department of Animal and Plant Science, University of Sheffield, sheffield, United Kingdom, Naomi S Wells, Department of Catchment Hydrology, Helmholtz Centre for Environmental Research – UFZ,, Halle (Saale), Germany, Kay Knoeller, Department of Catchment Hydrology, Helmholtz Centre for Environmental Research – UFZ, Halle (Saale), Germany, John Murphy, Environmental Research Centre, teagasc, Wexford, Ireland, Patrick Tuohy, Animal and Grassland Research and Innovation Centre, Teagasc, Moorepark, Ireland and Owen Fenton, Environmental Research Centre, teagasc, wexford, Ireland
Abstract:
In Ireland a high reliance on grazing and reduced mechanisation allows Irish milk to have the lowest carbon footprint within the European Union (EU). However, the efficiency of nitrogen (N) use within Irish pasture-based systems is variable and N leaching occurs. Heterogeneous soils create high and low denitrification areas, with attenuation capacity increasing with decreasing drainage class. However, to facilitate dairy expansion, poorly or imperfectly-drained soils are the first to be artificially drained. A major knowledge gap is whether such intervention disrupts natural attenuation capacity or simply transports attenuated water along the transfer continuum. The present multi-farm study (1 research and 5 commercial farms) was conducted on extensive monitoring networks (in-field drains, open ditches and groundwater). Water samples were taken for NO3-15N, NO3-18O, NH4+15N, N2O-δ15N, dissolved-N2O and excess-N2 at multiple locations and allowed elucidation of N speciation, sources and transformational processes across these networks.

Organic NO3--N sources dominated monitoring points across all farms. On the research farm long term groundwater samples (2005-2014) exhibited high spatial NO3--N (0-25 mg/l) and NH4+-N (0-23 mg/l) differences while concentrations in drainage systems were below EU standards. “Remediation” was shown with main transformational process indicative of denitrification but with a wide range of values (54.9-6.2‰, δ15N-NO3-; 28.2‰-2.3‰, δ18O-NO3-) suggesting variable attenuation and completeness. Commercial farms showed high NH4+-N concentration (0-1.3 mg/l) but no NO3--N/l contamination (0-4.13 mg/l), again main transformational process was denitrification (nitrification on one farm) with smaller intra-farm ranges.

In conclusion across six sites artificial drainage systems installed in poorly or imperfectly-drained soils did not disrupt their inherently high attenuation capacity but instead acted as a conduit transporting attenuated water. However, some NH4+-N breaches occurred, which need to be investigated further.

Future installation of land drainage should be guided by such information, avoiding areas of low attenuation capacity.

See more from this Division: SSSA Division: Soil and Water Management and Conservation
See more from this Session: Soil and Water Managment and Conservation Oral IV