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Coupling of surface water and groundwater nitrate-N dynamics in two permeable agricultural catchments

Published online by Cambridge University Press:  05 March 2014

P.-E. MELLANDER ,
A. R. MELLAND ,
P. N. C. MURPHY ,
D. P. WALL ,
G. SHORTLE  and
P. JORDAN
P.-E. MELLANDER*
Affiliation:
Agricultural Catchments Programme, Teagasc, Johnstown Castle Environment Research Centre, Wexford, Co. Wexford, Ireland
A. R. MELLAND
Affiliation:
Agricultural Catchments Programme, Teagasc, Johnstown Castle Environment Research Centre, Wexford, Co. Wexford, Ireland
P. N. C. MURPHY
Affiliation:
Agricultural Catchments Programme, Teagasc, Johnstown Castle Environment Research Centre, Wexford, Co. Wexford, Ireland
D. P. WALL
Affiliation:
Crops, Environment and Land Use Programme, Teagasc, Johnstown Castle Environment Research Centre, Wexford, Co. Wexford, Ireland
G. SHORTLE
Affiliation:
Agricultural Catchments Programme, Teagasc, Johnstown Castle Environment Research Centre, Wexford, Co. Wexford, Ireland
P. JORDAN
Affiliation:
School of Environmental Sciences, University of Ulster, Coleraine, Northern Ireland
*
*To whom all correspondence should be addressed. Email: Per-Erik.Mellander@teagasc.ie
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Summary

The current study investigated the coupling of groundwater and surface water nitrogen (N) dynamics over 3 years, and considered intensive agricultural land-management influences over this period where the risk of N loss to water was considered high. Groundwater N (as nitrate) was monitored monthly in different strata and zones in four hillslopes, two in each of two agricultural catchments of c. 10 km2, and stream water N flux was monitored sub-hourly in the catchment outlets. Field nutrient sources were connected to surface water via groundwater; the groundwater along hillslopes was seen to be influenced spatially and temporally by management, geology and weather as observed in the concentration variability of nitrate in groundwater. Based on spatio-temporal averages of nitrate-N concentration, groundwater status was considered good (at least below a maximum acceptable concentration (MAC) of 11·3 mg/l). However, zones coincident with land-use change (ploughing and reseeding, typical of a management event in intensive landscapes), showed high spatio-temporal variability in nitrate-N concentration, exceeding the MAC temporarily, before recovering. This spatio-temporal variability highlighted the need for insight into these differences when interpreting groundwater quality data from a limited number of basin-scale sampling points and occasions. In both catchments the 3-year mean nitrate-N concentration in stream water was similar to the spatio-temporal mean concentration in groundwater. The magnitude and variability of loads, however, were more related to changes in annual runoff rather than changes in annual groundwater nitrate-N status. In one wet year, nitrate-N loads exceeded 48 kg/ha from an Arable catchment and 45 kg/ha from a grassland catchment (close to double the loss in a dry year).

Type
Nitrogen Workshop Special Issue Papers
Information
The Journal of Agricultural Science , Volume 152 , Supplement S1: Special Issue from the 17th International Nitrogen Workshop , December 2014 , pp. 107 - 124
Copyright
Copyright © Cambridge University Press 2014 

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References

REFERENCES

Anon. (2010). Food Harvest 2020. A Vision for Irish Agri-food and Fisheries. Dublin, Ireland: Department of Agriculture, Fisheries and Food.Google Scholar
Baily, A., Watson, C. J., Laughlin, R., Matthews, D., McGeough, K. & Jordan, P. (2012). Use of the 15 N gas flux method to measure the source and level of N2O and N2 emissions from grazed grassland. Nutrient Cycling in Agroecosystems 94, 287–298.CrossRefGoogle Scholar
Batson, J. A., Mander, U. & Mitsch, W. J. (2012). Denitrification and nitrogen budget of created riparian wetlands. Journal of Environmental Quality 41, 2024–2032.CrossRefGoogle ScholarPubMed
Conley, D. J., Paerl, H. W., Howarth, R. W., Boesch, D. F., Seitzinger, S. P., Havens, K. E., Lancelot, C. & Likens, G. E. (2009). Controlling eutrophication: nitrogen and phosphorus. Science 323, 1014–105.CrossRefGoogle ScholarPubMed
Council Of The European Communities (CEC) (1991). Council Directive 91/676/EEC of 12 December 1991 concerning the protection of waters against pollution caused by nitrates from agricultural sources. Official Journal of the European Community L375, 0001–0008.Google Scholar
Council of the European Communities (CEC) (2000). Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for community action in the Field of Water Policy. Official Journal of the European Communities L237, 1–72.Google Scholar
Doney, S. C., Mahowald, N., Lima, I., Feely, R. A., Mackenzie, F. T., Lamarque, J.-F. & Rasch, P. J. (2007). Impact of anthropogenic atmospheric nitrogen and sulfur deposition on ocean acidification and the inorganic carbon system. Proceedings of the National Academy of Sciences of the United States 104, 14580–14585.Google Scholar
Fealy, R. M., Buckley, C., Mechan, S., Melland, A., Mellander, P.-E., Shortle, G., Wall, D. & Jordan, P. (2010). The Irish Agricultural Catchments Programme: catchment selection using spatial multi-criteria decision analysis. Soil Use and Management 26, 225–236.Google Scholar
Fenton, O., Schulte, R. P. O., Jordan, P., Lalor, S. T. J. & Richards, K. G. (2011). Time lag: a methodology for the estimation of vertical and horizontal travel and flushing timescales to nitrate threshold concentration in Irish aquifers. Environmental Science and Policy 14, 419–431.Google Scholar
Gruber, N. & Galloway, J. N. (2008). An Earth-system perspective of the global nitrogen cycle. Nature 451, 293–296.CrossRefGoogle ScholarPubMed
Healey, M. G., Ibrahim, T. G., Lanigan, G. J., Serrenho, A. J. & Fenton, O. (2012). Nitrate removal rate, efficiency and pollution swapping potential of different organic carbon media in laboratory denitrification bioreactors. Ecological Engineering 40, 198–209.Google Scholar
Howden, N. J. K., Burt, T. P., Worrall, F., Whelan, M. J. & Bieroza, M. (2010). Nitrate concentrations and fluxes in the River Thames over 140 years (1868–2008): are increases irreversible? Hydrological Processes 24, 2657–2662.Google Scholar
Hubbard, R. K., Sheridan, J. M., Lowrance, R., Bosch, D. D. & Vellidis, G. (2004). Fate of nitrogen from agriculture in the southeastern Coastal Plain. Journal of Soil and Water Conservation 59, 72–86.Google Scholar
Humphreys, J., Casey, I. A., Darmody, P., O'Connell, K., Fenton, O. & Watson, C. J. (2008). Quantities of mineral N in soil and concentrations of nitrate-N in groundwater in four grassland-based systems of dairy production on a clay-loam soil in a moist temperate climate. Grass and Forage Science 63, 481–494.CrossRefGoogle Scholar
Jordan, P., Melland, A. R., Mellander, P.-E., Shortle, G. & Wall, D. (2012). The seasonality of phosphorus transfers from land to water: implications for trophic impacts and policy evaluation. Science of the Total Environment 434, 101–109.Google Scholar
Jordan, P., Cassidy, R., Macintosh, K. A. & Arnscheidt, J. (2013). Field and laboratory tests of flow-proportional passive samplers for determining average phosphorus and nitrogen concentration in rivers. Environmental Science and Technology 47, 2331–2338.Google Scholar
Kelso, B., Smith, R. V., Laughlin, R. J. & Lennox, S. D. (1997). Dissimilatory nitrate reduction in anaerobic sediments leading to river nitrite accumulation. Applied and Environmental Microbiology 63, 4679–4685.Google Scholar
Kim, S. & Dale, B. E. (2008). Effects of nitrogen fertilizer application on greenhouse gas emissions and economics of corn production. Environmental Science and Technology 42, 6028–6033.CrossRefGoogle ScholarPubMed
King, K. W., Hughes, K. L., Balogh, J. C., Fausey, N. R. & Harmel, R. D. (2006). Nitrate-nitrogen and dissolved reactive phosphorus in subsurface drainage from managed turfgrass. Journal of Soil and Water Conservation 61, 31–40.Google Scholar
King, K. W., McDonald, J., Moore, J. F., Agrawal, S. G., Fischer, E. N. & Balogh, J. C. (2010). Nutrient and pesticide removal from laboratory-simulated tile drainage discharge. Transactions of the American Society of Agricultural and Biological Engineers 53, 769–777.Google Scholar
Majumdar, D. (2003). The Blue Baby Syndrome: nitrate poisoning in humans. Resonance 8, 20–30.Google Scholar
McGarrigle, M., Lucey, J. & Ó Cinnéide, M. (2010). Water Quality in Ireland 2007–2009. Wexford, Ireland: Environmental Protection Agency.Google Scholar
Melland, A. R., Mellander, P.-E., Murphy, P. N. C., Wall, D. P., Mechan, S., Shine, O., Shortle, G. & Jordan, P. (2012). Stream water quality in intensive cereal cropping catchments with regulated nutrient management. Environmental Science and Policy 24, 58–70.Google Scholar
Mellander, P.-E., Melland, A. R., Jordan, P., Wall, D. P., Murphy, P. N. C. & Shortle, G. (2012). Quantifying nutrient transfer pathways in agricultural catchments using high temporal resolution data. Environmental Science and Policy 24, 44–57.CrossRefGoogle Scholar
Molénat, J., Gascuel-Odoux, C., Ruiz, L. & Gruau, G. (2008). Role of water table dynamics on stream nitrate export and concentration in agricultural headwater catchment (France). Journal of Hydrology 348, 363–378.Google Scholar
Paerl, H. (2009). Controlling eutrophication along the freshwater–marine continuum: dual nutrient (N and P) reductions are essential. Estuaries and Coasts 32, 593–601.CrossRefGoogle Scholar
Rouxel, M., Molénat, J., Ruiz, L., Legout, C., Faucheux, M. & Gascuel-Odoux, C. (2011). Seasonal and spatial variation in groundwater quality along the hillslope of an agricultural research catchment (Western France). Hydrological Processes 25, 831–841.CrossRefGoogle Scholar
Sleeman, A. G. & Pracht, M. (1995). Geology of South Cork, Sheet 25. Dublin, Ireland: Geological Survey of Ireland.Google Scholar
Statutory Instruments (2009). S.I. No. 272 of 2009. European Communities Environmental Objectives (Surface Waters) Regulations. Dublin, Ireland: the Stationery Office.Google Scholar
Statutory Instruments (2010). S.I. No. 9 of 2010. European Communities Environmental Objectives (Groundwater) Regulations. Dublin, Ireland: the Stationery Office.Google Scholar
Sutton, M. A., Oenema, O., Erisman, J. W., Leip, A., Grinsven, H. V. & Winiwarter, W. (2011). Too much of a good thing. Nature 472, 159–161.CrossRefGoogle ScholarPubMed
Tesoriero, A. J., Duff, J. H., Wolock, D. M., Spahr, N. E. & Almendinger, J. E. (2009). Identifying pathways and processes affecting nitrate and orthophosphate inputs to streams in agricultural watersheds. Journal of Environmental Quality 38, 1892–1900.CrossRefGoogle ScholarPubMed
Tesoriero, A. J., Duff, J. H., Saad, D. A., Spahr, N. E. & Wolock, D. M. (2013). Vulnerability of streams to legacy nitrate sources. Environmental Science and Technology 47, 3623–3629.Google Scholar
Tietzsch-Tyler, D., Sleeman, A. G., McConnell, B. J., Daly, E. P., Flegg, A. M., O'Connor, P. J. & Warren, W. P. (1994). Geology of Carlow-Wexford, Sheet 19. Dublin, Ireland: Geological Survey of Ireland.Google Scholar
Wall, D., Jordan, P., Melland, A. R., Mellander, P.-E., Buckley, C., Reaney, S. & Shortle, G. (2011). Using the nutrient transfer continuum concept to evaluate the European Union Nitrates Directive National Action Programme. Environmental Science and Policy 14, 664–674.Google Scholar
Wall, D. P., Murphy, P. N. C., Melland, A. R., Mechan, S., Shine, O., Buckley, C., Mellander, P.-E., Shortle, G. & Jordan, P. (2012). Evaluating nutrient source regulations at different scales in five agricultural catchments. Environmental Science and Policy 24, 34–43.Google Scholar
World Health Organisation (2011). Nitrate and Nitrite in Drinking-Water – Background Document for Development of WHO Guidelines for Drinking-Water Quality. Geneva: WHO Press.Google Scholar