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                                                          Groundwater pollution remediation and protection  269



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                     The Drastrup Project, north Jutland, Denmark
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                     A unique example of spatial planning to achieve sustainable land  cover with low intensity grazing (Fig. 1). Planting began in the late
                     use in a groundwater catchment area with the aim of improving  1990s and the new forest was inaugurated in September 2001
                     and protecting groundwater quality is provided by the Drastrup  (Municipality of Aalborg 2001).
                     Project in north Jutland, Denmark. The motivation for the project  The initial preparation of soil in the new forest area by deep
                     was decreasing water quality from the diffuse input of nitrate and  ploughing caused an initial flush of nitrate (up to 40 mg L −1  as N)
                     pesticides, with concentrations of nitrate up to 125 mg L −1  in  but it is considered that as the trees grow, soil nitrate concentra-
                     groundwater. The Drastrup area, covering about 870 ha, is one   tions will begin to decline after 4–6 years. Trees demand a high
                     of two large groundwater catchment areas for the city of Aalborg,  nitrogen uptake during the first 15 years of growth, and so effect-
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                     contributing 20%, or approximately 1.7 × 10 m , of the annual  ively reduce soil nitrate leaching, but later soil nitrate concentra-
                     municipal water supply demand (Fig. 1).    tions may increase as a result of atmospheric inputs of nitrogen to
                      To protect the underlying Chalk aquifer and demonstrate the  the ageing forest canopy. In areas of grassland, soil monitoring
                     effects of land use change on nitrate leaching, it was decided to  has shown that conversion to grassland quickly reduces nitrate
                     apply a municipal planning act to execute voluntary land distribu-  concentrations to effectively zero within the first 2–3 years of con-
                     tion among farmers in the groundwater catchment area near Frejlev  version (Fig. 2a).
                     and Drastrup. The farm owners received compensation in the form  Since the implementation of land-use change in 1994, depth
                     of either payments or as land outside of the groundwater catch-  sampling of groundwater may now be showing signs of improve-
                     ment area. The project also had the objective of establishing a   ment in water quality, although further years of monitoring
                     recreational area close to Aalborg for the benefit of its citizens  are required to identify unambiguously an improvement in water
                     through the creation of a new, 230-ha recreational forest compris-  quality from natural background variation in nitrate content
                     ing a non-rotation, mixed age forest with some permanent grass  (Fig. 2b).






































                     Fig. 1 The Drastrup area, Denmark, showing the area of new forest planted to protect groundwater from the leaching of nitrate.
                     After the Municipality of Aalborg (2001).
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