Multiplicity of stable states in freshwater systems

It is shown with the use of minimal models that several ecological relationships in freshwater systems potentially give rise to the existence of alternative equilibria over a certain range of nutrient values. The existence of alternative stable states has some implications for the management of such systems. An important consequence is that signs of eutrophication are only apparent after the occurrence of changes that are very difficult to reverse. Reduction of the nutrient level as a measure to restore such systems gives poor results, but biomanipulation as an additional measure can have significant effects, provided that the nutrient level has been reduced enough to allow the existence of a stable alternative clear water equilibrium.

[1]  R. Macarthur,et al.  Graphical Representation and Stability Conditions of Predator-Prey Interactions , 1963, The American Naturalist.

[2]  C. S. Holling,et al.  Qualitative Analysis of Insect Outbreak Systems: The Spruce Budworm and Forest , 1978 .

[3]  M. Rosenzweig,et al.  Exploitation in Three Trophic Levels , 1973, The American Naturalist.

[4]  S. Diehl Foraging efficiency of three freshwater fishes: effects of structural complexity and light , 1988 .

[5]  D. Spence,et al.  zonation of plants in freshwater lakes , 1982 .

[6]  I. Noy-Meir,et al.  Stability of Grazing Systems: An Application of Predator-Prey Graphs , 1975 .

[7]  B. Moss,et al.  Prevention of growth of potentially dense phytoplankton populations by zooplankton grazing, in the presence of zooplanktivorous fish, in a shallow wetland ecosystem , 1984 .

[8]  X. Lazzaro A review of planktivorous fishes: Their evolution, feeding behaviours, selectivities, and impacts , 1987, Hydrobiologia.

[9]  M. Meijer,et al.  Is reduction of the benthivorous fish an important cause of high transparency following biomanipulation in shallow lakes , 1990 .

[10]  B. Moss,et al.  The River Bure, United Kingdom: Patterns of change in chemistry and phytoplankton in a slow-flowing fertile river: With 5 figures and 1 table in the text , 1984 .

[11]  S. H. Hosper Biomanipulation, new perspectives for restoration of shallow, eutrophic lakes in The Netherlands , 1989, Hydrobiological Bulletin.

[12]  M. P. Grimm Northern pike (Esox lucius L.) and aquatic vegetation, tools in the management of fisheries and water quality in shallow waters , 1989, Hydrobiological Bulletin.

[13]  M. P. Grimm,et al.  Food web manipulation in Lake Zwemlust: Positive and negative effects during the first two years , 1989, Hydrobiological Bulletin.

[14]  R. Holt Predation, apparent competition, and the structure of prey communities. , 1977, Theoretical population biology.

[15]  J. Benndorf,et al.  Manipulation of the Pelagic Food Web by Stocking with Predacious Fishes , 1984 .

[16]  G. Andersson,et al.  Effects of planktivorous and benthivorous fish on organisms and water chemistry in eutrophic lakes , 1978, Hydrobiologia.

[17]  S. Wium-Andersen Allelopathy among aquatic plants , 1987 .

[18]  R. May Thresholds and breakpoints in ecosystems with a multiplicity of stable states , 1977, Nature.

[19]  Sergio Rinaldi,et al.  Some models of catastrophic behavior in exploited forests , 1987 .

[20]  A. Crivelli The destruction of aquatic vegetation by carp , 1983, Hydrobiologia.

[21]  L. Oksanen,et al.  Exploitation Ecosystems in Gradients of Primary Productivity , 1981, The American Naturalist.

[22]  M. Rosenzweig Paradox of Enrichment: Destabilization of Exploitation Ecosystems in Ecological Time , 1971, Science.

[23]  M. Scheffer,et al.  Alternative stable states in eutrophic, shallow freshwater systems: A minimal model , 1989, Hydrobiological Bulletin.

[24]  René Thom,et al.  Structural stability and morphogenesis - an outline of a general theory of models , 1977, Advanced book classics.