Lake restoration in Denmark

Lake restoration in Denmark has involved the use of several different restoration techniques, all aiming to improve lake water quality and establishing clear-water conditions. The most frequently used method, now used in more than 20 lakes, is the reduction of zooplanktivorous and benthivorous fish (especially roach (Rutilus rutilus) and bream (Abramis brama)) with the objective of improving the growth conditions for piscivores, large-sized zooplankton species, benthic algae and submerged macrophytes. Piscivore stocking (mainly Esox lucius (pike)), aiming especially at reducing the abundance of young-of-the-year fish, has been used in more than 10 lakes and frequently as a supplement to fish removal. Hypolimnetic oxidation, with oxygen and nitrate, has been undertaken in a few stratified lakes and sediment dredging, with the purpose of diminishing the internal phosphorus loading, has been experimented with in one large, shallow lake. Submerged macrophyte implantation has been conducted in some of the biomanipulated lakes to increase macrophyte abundance and distribution. Overall, the results from lake restoration projects, in the mainly shallow Danish lakes, show that external nutrient loading must be reduced to a level below 0.05–0.1 mg P L–1 under equilibrium conditions to gain permanent effects on lake water quality. By using fish removal, at least 80% of the fish stock should be removed over a period of not more than 1–2 years to obtain a substantial effect on lower trophic levels and to avoid regrowth of the remaining fish stock. Stocking of piscivores requires high densities (>0.1 individuals m–2) if an impact on the plankton level is to be obtained and stocking should be repeated yearly until a stable clear-water state is reached. The experiments with hypolimnetic oxygenation and sediment dredging confirm that internal phosphorus loading can be reduced. Experience from macrophyte implantation experiments indicates that protection against grazing by herbivorous waterfowl may be useful in the early phase of recolonization.

[1]  Martin W. Marsden,et al.  Lake restoration by reducing external phosphorus loading: the influence of sediment phosphorus release , 1989 .

[2]  E. Jeppesen,et al.  Impact of submerged macrophytes on fish-zooplankton-phytoplankton interactions : large-scale enclosure experiments in a shallow eutrophic lake , 1995 .

[3]  E. Jeppesen,et al.  Colonization of submerged macrophytes in shallow fish manipulated Lake Væng: impact of sediment composition and waterfowl grazing , 1993 .

[4]  Fish manipulation as a lake restoration tool in shallow, eutrophic, temperate lakes 2: threshold levels, long-term stability and conclusions , 1990 .

[5]  L. Hansson Effects of competitive interactions on the biomass development of planktonic and periphytic algae in lakes1 , 1988 .

[6]  T. Aldenberg,et al.  A model study on the stability of the macrophyte-dominated state as affected by biological factors. , 1998 .

[7]  E. Jeppesen,et al.  Hypolimnetic Nitrate Treatment to Reduce Internal Phosphorus Loading in a Stratified Lake , 2000 .

[8]  T. V. Madsen,et al.  The impact of grazing waterfowl on submerged macrophytes: In situ experiments in a shallow eutrophic lake , 1996 .

[9]  E. Jeppesen,et al.  Macrophyte-Waterfowl Interactions: Tracking a Variable Resource and the Impact of Herbivory on Plant Growth , 1998 .

[10]  Åge Brabrand,et al.  Relative Importance of Phosphorus Supply to Phytoplankton Production: Fish Excretion versus External Loading , 1990 .

[11]  Brian Kronvang,et al.  Lake and catchment management in Denmark , 1999 .

[12]  E. Jeppesen,et al.  The importance of macrophyte bed size for cladoceran composition and horizontal migration in a shallow lake , 1996 .

[13]  Erik Jeppesen,et al.  Biomanipulation as an Application of Food-Chain Theory: Constraints, Synthesis, and Recommendations for Temperate Lakes , 1998, Ecosystems.

[14]  Erik Jeppesen,et al.  Changes in nitrogen retention in shallow eutrophic lakes following a decline in density of cyprinids , 1998 .

[15]  Marten Scheffer,et al.  Biomanipulation in shallow lakes in The Netherlands: an evaluation of 18 case studies , 1999 .

[16]  B. Kronvang,et al.  Nationwide monitoring of nutrients and their ecological effects: state of the Danish aquatic environment , 1993 .

[17]  M. Scheffer,et al.  Alternative stable states. , 1998 .

[18]  S. Born Lake rehabilitation: A status report , 1979 .

[19]  The restoration of shallow eutrophic lakes, and the role of northern pike, aquatic vegetation and nutrient concentration , 1990 .

[20]  K. Havens Fish-induced sediment resuspension: effects on phytoplankton biomass and community structure in a shallow hypereutrophic lake , 1991 .

[21]  L. Greenberg,et al.  Complex trophic interactions in freshwater benthic food chains , 1997 .

[22]  Erik Jeppesen,et al.  Trophic structure, species richness and biodiversity in Danish lakes: changes along a phosphorus gradient , 2000 .

[23]  L. Persson Food consumption and competition between age classes in a perch Perca fluviatilis population in a shallow eutrophic lake , 1983 .

[24]  S. Diehl Effects of habitat structure on resource availability, diet and growth of benthivorous perch, Perca fluviatilis , 1993 .

[25]  M. Scheffer,et al.  Alternative equilibria in shallow lakes. , 1993, Trends in ecology & evolution.

[26]  J. K. Breteler,et al.  Effects of benthivorous bream (Abramis brama) and carp (Cyprinus carpio) on sediment resuspension and concentrations of nutrients and chlorophyll a , 1994 .

[27]  L. Greenberg,et al.  Interspecific and intraspecific size-class competition affecting resource use and growth of perch (Perca fluviatilis ) , 1990 .