Paradox of enrichment

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The paradox of enrichment is a term from population ecology coined by Michael Rosenzweig in 1971. He described an effect in six predator–prey models where increasing the food available to the prey caused the predator's population to destabilize. A common example is that if the food supply of a prey such as a rabbit is overabundant, its population will grow unbounded and cause the predator population (such as a lynx) to grow unsustainably large. That may result in a crash in the population of the predators and possibly lead to local eradication or even species extinction.

The term 'paradox' has been used since then to describe this effect in slightly conflicting ways. The original sense was one of irony; by attempting to increase the carrying capacity in an ecosystem, one could fatally imbalance it. Since then, some authors have used the word to describe the difference between modelled and real predator–prey interactions.

Rosenzweig used ordinary differential equation models to simulate the prey population that represented only prey populations. Enrichment was taken to be increasing the prey carrying capacity and showing that the prey population destabilized, usually into a limit cycle.

The cycling behavior after destabilization was more thoroughly explored in a subsequent paper (May 1972) and discussion (Gilpin and Rozenzweig 1972).

Model and exception[edit]

Many studies have been done on the paradox of enrichment since Rosenzweig, and some have shown that the model initially proposed does not hold in all circumstances, as summarised by Roy and Chattopadhyay in 2007, such as these exceptions:

  • Inedible prey: if there are multiple prey species and not all are edible, some may absorb nutrients and stabilise cyclicity.
  • Invulnerable prey: even with a single prey species, if there is a degree of temporal or spatial refuge (the prey can hide from the predator), destabilisation may not happen.
  • Unpalatable prey: if prey do not fulfil the nutritional preferences of the predator to as great an extent at higher densities, as with some algae and grazers, there may be a stabilising effect.
  • Heterogeneous environment: the model for enrichment follows an assumption of environmental homogeneity. If a spatiotemporally chaotic, heterogeneous environment is introduced, cyclic patterns may not arise.
  • Induced defense: if there is a predation-dependent response from prey species, it may act to decelerate the downward swing of population caused by the boom in predator population. An example is of Daphnia and fish predators.
  • Autotoxins and other predator density-dependent effects: if predator density cannot increase in proportion to that of prey, destabilising periodicities may not develop.
  • Prey toxicity: if there is a significant cost to the predator of consuming the (now very dense) prey species, predator numbers may not increase sufficiently to give periodicity.

Link with Hopf bifurcation[edit]

The paradox of enrichment can be accounted for by the bifurcation theory. As the carrying capacity increases, the equilibrium of the dynamical system becomes unstable.

The bifurcation can be obtained by modifying the Lotka–Volterra equation. First, one assumes that the growth of the prey population is determined by the logistic equation. Then, one assumes that predators have a nonlinear functional response, typically of type II. The saturation in consumption may be caused by the time to handle the prey or satiety effects.

Thus, one can write the following (normalized) equations:

  • x is the prey density;
  • y is the predator density;
  • K is the prey population's carrying capacity;
  • γ and δ are predator population's parameters (rate of decay and benefits of consumption, respectively).

The term represents the prey's logistic growth, and the predator's functional response.

The prey isoclines (points at which the prey population does not change, i.e. dx/dt = 0) are easily obtained as and . Likewise, the predator isoclines are obtained as and , where . The intersections of the isoclines yields three equilibrium states:

The first equilibrium corresponds to the extinction of both predator and prey, the second one to the extinction of the predator and the third to co-existence.

By the Hartman–Grobman theorem, one can determine the stability of the steady states by approximating the nonlinear system by a linear system. After differentiating each and with respect to and in a neighborhood of , we get:

It is possible to find the exact solution of this linear system, but here, the only interest is in the qualitative behavior. If both eigenvalues of the community matrix have negative real part, then by the stable manifold theorem the system converges to a limit point. Since the determinant is equal to the product of the eigenvalues and is positive, both eigenvalues have the same sign. Since the trace is equal to the sum of the eigenvalues, the system is stable if

At that critical value of the parameter K, the system undergoes a Hopf bifurcation. It comes as counterintuitive (hence the term 'paradox') because increasing the carrying capacity of the ecological system beyond a certain value leads to dynamic instability and extinction of the predator species.

Arguments against paradox[edit]

A credible, simple alternative to the Lotka–Volterra predator–prey model and its common prey dependent generalizations is the ratio dependent or Arditi–Ginzburg model.[1] The two are the extremes of the spectrum of predator interference models. According to the authors of the alternative view, the data show that true interactions in nature are so far from the Lotka–Volterra extreme on the interference spectrum that the model can simply be discounted as wrong. They are much closer to the ratio dependent extreme so if a simple model is needed one can use the Arditi–Ginzburg model as the first approximation.[2]

The presence of the paradox is strongly dependent on the assumption of the prey dependence of the functional response; because of this the ratio dependent Arditi–Ginzburg model does not have the paradoxical behavior. The authors claim that the paradox is absent in nature (simple laboratory systems may be the exception) is in fact a strong argument for their alternative view of the basic equations.[3]

See also[edit]


  1. ^ Arditi, R. and Ginzburg, L.R. (1989) "Coupling in predator–prey dynamics: ratio dependence" Journal of Theoretical Biology, 139: 311–326.
  2. ^ Arditi, R. and Ginzburg, L.R. (2012) How Species Interact: Altering the Standard View on Trophic Ecology Oxford University Press. ISBN 9780199913831.
  3. ^ Jensen, C. XJ., and Ginzburg, L.R. (2005) "Paradoxes or theoretical failures? The jury is still out." Ecological Modelling, 118:3–14.

Other reading[edit]

  • Gilpin, Michael and Michael Rosenzweig. 1972. "Enriched Predator–Prey Systems: Theoretical Stability" Science Vol. 177, pp. 902–904.
  • May, Robert. 1972. "Limit Cycles in Predator–Prey Communities" Science Vol. 177, pp. 900–902.
  • Rosenzweig, Michael. 1971. "The Paradox of Enrichment" Science Vol. 171: pp. 385–387
  • Kot, Mark. 2001. "Elements of Mathematical Ecology" Cambridge University Press
  • Roy, Shovonlal; J Chattopadhyay (2007). "The stability of ecosystems: A brief overview of the paradox of enrichment". Journal of Biosciences. 32 (2): 421–428. doi:10.1007/s12038-007-0040-1. ISSN 0250-5991. Retrieved 2010-12-08.