Groundwater Contribution to Surface Water Contamination in a North German Low Land Catchment with Intensive Agricultural Land Use — Oak Academic Publishing
Research ArticleOpen AccessGoogle Scholar indexed
Groundwater Contribution to Surface Water Contamination in a North German Low Land Catchment with Intensive Agricultural Land Use
Faculty of Agriculture and Environmental Sciences, Universität Rostock, Rostock, Germany
,
Faculty of Agriculture and Environmental Sciences, Universität Rostock, Rostock, Germany
,
Faculty of Agriculture and Environmental Sciences, Universität Rostock, Rostock, Germany
1 Faculty of Agriculture and Environmental Sciences, Universität Rostock, Rostock, Germany
2 Faculty of Agriculture and Environmental Sciences, Universität Rostock, Rostock, Germany
3 Faculty of Agriculture and Environmental Sciences, Universität Rostock, Rostock, Germany
The contribution of groundwater (GW) to the nitrate loads in surface waters (SW) was exemplarily studied for the river Augraben with a catchment area of 89.9 km 2 , located in north eastern Germany. The study uses available GW and SW quality data in order to develop a relationship between SW and GW in the Augraben catchment. The calculated ratio of base flow varies from 40% to 80% using various filtering methods of hydrograph separation methods ( without taking into account the drainage ) in comparison to a calculated GW infiltration of 5% - 7% applying Darcy’s law ( upper unconfined aquifer ). Drainage was estimated as the difference in base flow obtained through filtering methods of hydrograph separation and the Darcy’s law. Results on the basis of monitoring data and hydrograph separation in quick flow and base flow showed that during winter periods, high concentration in SW has been found parallel to periods of higher GW flow with a strong correlation between SW and GW concentrations. These findings also coincided with the non-vegetation period, i.e. low nitrogen uptake by plants. Overall, nitrate-nitrogen loads at the SW monitoring point (Bei Lindenberg represents the 85% area of the catchment) were 193.5, 97.72, and 122 tons for the year 2010, 2011 and 2012 respectively. Measured GW concentrations in the catchment differ strongly, depending on land use, with elevated concentrations in agricultural areas compared to monitoring points in grass land and in forest areas. In one GW monitoring station, NO 3 concentrations exceed the maximum permissible limits (MPL) according to EU water quality standards (MPL = 50 mg/l NO 3 ), up to factor two. High ammonia concentrations at another station may be due to excessive application of manure. The contribution of the different sub-catchments to nitrate load in SW can be ranked in decreasing order in Zone B, D, A and C. Drainage and interflow proved to be a major contributor with 55% - 65% of total load in SW. With the applied method a robust estimation of GW contribution to nitrate loads is feasible using typically available monitoring data of German environmental authorities.
KeywordsBase Flow SeparationDiffuse pollutionDrainage and InterflowGroundwater NitrogenGehmkow Augraben
Novotny, V. and Chesters, G. (1981) Handbook of Nonpoint Pollution: Sources and Management. Van Nostrand-Reinhold, New York.
Ritter, W.F. and Shirmohammadi, A. (2001) Agricultural Nonpoint Source Pollution. Lewis, Boca Raton, London, New York, Washington DC.
Heathwaite, L., Sharpley, A. and Gburek, W. (2000) A Conceptual Approach for Integrating Phosphorus and Nitrogen Management at Watershed Scales. Journal of Environmental Quality, 29, 158-166. https://doi.org/10.2134/jeq2000.00472425002900010020x
Spalding, R.F. and Exner, M.E. (1993) Occurrence of Nitrate in Groundwater—A Review. Journal of Environmental Quality, 22, 392-402. https://doi.org/10.2134/jeq1993.00472425002200030002x
Campling, P., Terres, J.M., Vande Walle, S., Van Orshoven, J. and Crouzet, P. (2005) Estimation of Nitrogen Balances from Agriculture for EU-15: Specialisation of Estimates to River Basins using the CORINE Land Cover. Physics and Chemistry of the Earth, 30, 25e34.
Nitratbericht (2016) Gemeinsamer Bericht der Bundesministerien für Umwelt, Naturschutz, Bau und Reaktorsicherheit sowie für Ernährung und Landwirtschaft.
Randall, D.J. and Tsui, T.K.N. (2002) Ammonia Toxicity in Fish. Marine Pollution Bulletin, 45, 17-23. https://doi.org/10.1016/S0025-326X(02)00227-8
Haralambous, A., Maliou, E. and Malamis, M. (1992) The Use of Zeolite for Ammonium Uptake. Water Science & Technology, 25, Article ID: 139145.
Ip, Y.K., Chew, S.F. and Randall, D.J. (2001) Ammonia Toxicity, Tolerance, and Excretion. Fish Physiology, 20, 109-148. https://doi.org/10.1016/S1546-5098(01)20005-3
Van der Molen, D.T., Breeuwsma, A. and Boers, P.C.M. (1998) Agricultural Nutrient Losses to Surface Water in the Netherlands: Impact, Strategies, and Perspectives. Journal of Environmental Quality, 27, 4e11.
Oenema, O. and Roest, C.W.J. (1998) Nitrogen and Phosphorus Losses from Agriculture into Surface Waters; The Effects of Policies and Measures in the Netherlands. Water Science and Technology, 37, 19e30.
Oenema, O., Van Liere, L. and Schoumans, O. (2005) Effects of Lowering Nitrogen and Phosphorus Surpluses in Agriculture on the Quality of Groundwater and Surface Water in the Netherlands. Journal of Hydrology, 304, 289e301.
Addiscott, T.M. and Wagenet, R.J. (1985) Concepts of Solute Leaching in Soils: A Review of Modelling Approaches. Journal of Soil Science, 36, 411-424. https://doi.org/10.1111/j.1365-2389.1985.tb00347.x
HELCOM (2010) Ecosystem Health of the Baltic Sea—HELCOM Initial Holistic Assessment. Baltic Sea Environment Proceedings No. 122, 63 p.
HELCOM (2013) Taking Further Action to Implement the Baltic Sea Action Plan—Reaching Good Environmental Status for a Healthy Baltic Sea. Copenhagen, 19.
Saaltink, R., van der Velde Ype Dekker, S.C., Lyon, S.W. and Dahlke, H.E. (2014) Societal: Land Cover and Climatic Controls on River Nutrient Flows into the Baltic Sea. Journal of Hydrology: Regional Studies, 1, 44-56.
Hinsby, K., Markager, S., Kronvang, B., Windolf, J., Sonnenborg, T.O. and Thorling, L. (2012) Threshold Values and Management Options for Nutrients in a Catchment of a Temperate Estuary with Poor Ecological Status. Hydrology and Earth System Sciences, 16, 2663-2683. https://doi.org/10.5194/hess-16-2663-2012
Wendland, F., Keller, L., Kuhr, P., Kunkel, R. and Tetzlaff, B. (2015) Regional Differenzierte Quantifizierung der Nährstoffeinträge in das Grundwasser und in die Oberflächengewässer Mecklenburg-Vorpommerns unter Anwendung der Modellkombination Growadenuz-Weku-MEPhos, Endbericht, Herausgeber: LUNG Güstrow.
Brook Zarnow gauging station Zarnow basin, Germany. http://ne-friend.bafg.de/servlet/is/17796/Zarnow.pdf
Koch, F. (2014) Diffuse Nährstoffbelastungen in Oberflächengewässern und im Grundwasser, 19. Gewässersymposium, 19.11.2014 Güstrow.
Rostock. Meeresbiolog. Beitr (2004) Nährstoffausträge in die Ostsee aus diffusen Quellen Mecklenburg-Vorpommerns und Schleswig-Holsteins Nutrient emissions from diffuse sources of Mecklenburg-West Pomerania and Schleswig-Holstein to the Baltic Sea.
McLay, C.D.A., Dragten, R., Sparling, G. and Selvarajah, N. (2001) Predicting Groundwater Nitrate Concentrations in a Region of Mixed Agricultural Land Use: A Comparison of Three Approaches. Environmental Pollution, 115, 191-204. https://doi.org/10.1016/S0269-7491(01)00111-7
Methods for Estimating Groundwater Discharge to Streams—Summary of Field Trials. http://www.environment.gov.au%2Fsystem%2ffiles%2Fpages%2Ff4c0c901-66bc-46ba-94cb-056dfb54b69d%2Ffiles%2Fmethods-estimating-groundwater-discharge-streams.doc&usg=AFQjCNHYTL-YQN4tMfyks65LLi_pr2-qjQ
Nikkarinen, M., Kauniskangas, E. and Nenonen, K. (1996) Use of Geological and Geochemical Data for the Derivation of Maps for Environmental Planning in Iisalmi, Finland. Applied Geochemistry, 11, 261-270. https://doi.org/10.1016/0883-2927(95)00038-0
Canter, L.W., Knox, R.C. and Fairchild, D.M. (1988) Ground Water Quality Protection. Lewis Publishers, Chelsea, 562 p.
Lee, S.H. and Kim, Y.L. (1996) The Management of Groundwater Contamination in Seoul using GIS. Proceedings of Journal of the Korean Society of Groundwater Environment, 40-44.
BIOTA (2012) überarbeitung und Aktualisierung der Karte der mittleren Abflüsse und mittleren Niedrigwasserabflüsse für Mecklenburg-Vorpommern. biota Institut für ökologische Forschung und Planung GmbH im Auftrag des Landesamtes für Umwelt, Naturschutz und Geologie Mecklenburg-Vorpommern, 97 S.
Tallaksen, L.M. and Van Lanen, H.A. (2004) Hydrological Drought: Processes and Estimation Methods for Streamflow and Groundwater. Vol. 48, Elsevier, Amsterdam.
Sloto, R.A. and Crouse, M.Y. (1996) HYSEP, a Computer Program for Streamflow Hydrograph Separation and Analysis. US Department of the Interior, US Geological Survey.
Hall, F.R. (1968) Base Flow Recessions—A Review. Water Resources Research, 4, 973-983. https://doi.org/10.1029/WR004i005p00973
Arnold, J.G. and Fohrer, N. (2005) SWAT2000: Current Capabilities and Research Opportunities in Applied Watershed Modeling. Hydrological Processes, 19, 563-572. https://doi.org/10.1002/hyp.5611
Lyne, V. and Hollick, M. (1979) Stochastic Time-Variable Rainfall-Runoff Modeling. Institute of Engineers Australia National Conference, 89-93.
Gregor, M. (2010) BFI+ 3.0.
Nathan, R.J. and Mcmahon, T.A. (1990) Evaluation of Automated Techniques for Base Flow and Recession Analyses. Water Resources Research, 26, 1465-1473.
Welderufael, W.A., Le Roux, P.A.L. and Hensley, M. (2009) Quantifying Rainfall Runoff Relationships on the Melkassa Hypo Calcic Regosol Ecotope in Ethiopia. Water SA, 35, 639-648. https://doi.org/10.4314/wsa.v35i5.49189
Growing Season in Germany. https://en.wikipedia.org/wiki/Growing_season
WHO (1985) Guidelines for the Study of Dietary Intake of Chemical Contaminants. World Health Organization, Geneva, WHO Offset Publication No. 87.
WHO (1985) Health Hazards from Nitrate in Drinking-Water. Report, WHO Meeting, Copenhagen, 5-9 March 1984, Environmental Health Series No. 1.
OGewV (2015) Verordnung zum Schutz der Oberflächengewässer. https://www.gesetze-im-internet.de/ogewv_2016/BJNR137310016.html