Vacant niches

From Wikipedia, the free encyclopedia

You have new messages (last change).

A vacant niche can be defined as the possibility that in ecosystems or habitats more species could exist than are present at a particular point in time, because many possibilities are not used by potentially existing species (Rohde 2005b). [1]

Contents

[edit] History of the concept

Hutchinson (1957) [2] was apparently the first who considered the possibility of vacant niches. He writes: (p.424): “The question raised by cases like this is whether the three Nilghiri Corixinae fill all the available niches……….. or whether there are really empty niches.”…….“The rapid spread of introduced species often gives evidence of empty niches, but such rapid spread in many instances has taken place in disturbed areas.” Since then, the concept “vacant niche” or “empty niche” has been used regularly in the scientific literature. Some of the many examples are Elton (1958, pp.135-136) [3], Rohde (1977, 1979, 1980) [4][5][6] Lawton (1984) [7], Price (1984) [8], Compton et al. (1989) [9], Begon et al. (1990) [10] and Cornell (1999). [11] Further examples, some of them in great detail, are discussed in Rohde (2005b). [1]

[edit] Causes of vacant niches

Vacant niches can have several causes.

One cause is radical disturbances in a habitat. For example, droughts or forest fires can destroy a flora and fauna partially or completely. However, in such cases species suitable for the habitat usually survive in the neighbourhood and colonize the vacated niches, leading to a relatively fast re-establishment of the original conditions.

Further causes of vacant niches are radical and long-lasting changes in the environment, such as ice ages.

Vacant niches can also be due to evolutionary contingencies: suitable species did not evolve for usually unknown reasons.

[edit] Demonstration of vacant niches

Vacant niches can best be demonstrated by considering the spatial component of niches in simple habitats. For example, Lawton and collaborators compared the insect fauna of the bracken Pteridium aquilinum, a widely distributed species, in different habitats and geographical regions and found vastly differing numbers of insect species. They concluded that many niches remain vacant (e.g., Lawton 1984). [12]

Rohde and collaborators have shown that the number of ectoparasitic species on the gills of different species of marine fishes varies from 0 to about 30, even when fish of similar size and from similar habitats are compared. Assuming that the host species with the largest number of parasite species has the largest possible number of parasite species, only about 16% of all niches are occupied. However, the maximum may well be greater, since the possibility cannot be excluded that even on fish with a rich parasite fauna, more species could be accommodated (recent review in Rohde 2005b). [1]

Using similar reasoning, Walker und Valentine (1984) [13] estimated that 12-54% of niches for marine invertebrates are empty.

The ground breaking theoretical investigations of Kauffman (1993) [14] and Wolfram (2002) [15] also suggest the existence of a vast number of vacant niches. Using different approaches, both have shown that species rarely if ever reach global adaptive optima. Rather, they get trapped in local optima from which they cannot escape, i.e., they are not perfectly adapted. As the number of potential local optima is almost infinite, the niche space is largely unsaturated and species have little opportunity for interspecific competition. Kauffman (p.19) writes: “ ..many conceivable useful phenotypes do not exist” and: (p.218) “Landscapes are rugged and multipeaked. Adaptive processes typically become trapped on such optima”.

The packing rules of Ritchie and Olff (1999) [16] can be used as a measure of the filling of niche space. They apply to savanna plants and large herbivorous mammals, but not to all the parasite species examined so far. It seems likely that they do not apply to most animal groups. In other words, most species are not densely packed: many niches remain empty (Rohde 2001).[17]

That niche space may not be saturated, is also shown by introduced pest species. Such species lose, almost without exception, all or many of their parasites (Torchin and Kuris 2005). [18] Species that could occupy the vacant niches either do not exist or, if they exist, cannot adapt to these niches.

Diversity of marine benthos, interrupted by some collapses and plateaus, has increased from the Cambrian to the Recent, and there is no evidence that saturation has been reached (Jablonski 1999). [19]

[edit] Consequences of the nonsaturation of niche space

The view that niche space is largely or completely saturated with species is widespread. It is thought that new species are accommodated mainly by subdivision of niches occupied by previously existing species, although an increase in diversity by colonization of large empty living spaces (such as land in the geologic past) or by the formation of new baupläne also occurs. It is also recognized that many populations never completely reach a climax state (i.e., they may come close to an equilibrium but never quite reach it). However, altogether the view prevails that individuals and species are densely packed and that interspecific competition is of paramount significance. According to this view, nonequilibria are generally caused by environmental disturbances.

However, many recent studies (above and Rohde 2005a,b) [1] [20] support the view that niche space is largely unsaturated, i.e. that numerous vacant niches exist. As a consequence, competition between species is not as important as usually assumed. Nonequilibria are caused not only by environmental disturbances, but are widespread because of nonsaturation of niche space. Newly evolved species are absorbed into empty niche space, that is, niches occupied by existing species do not necessarily have to shrink.

[edit] Relative frequency of vacant niches in various groups of animals and plants

Available evidence suggests that vacant niches are more common in some groups than in others. Using SES values (standardized effect sizes) for various groups, which can be used as approximate predictors of the filling of niche space, Gotelli and Rohde (2002)[21] have shown that SES values are high for large and vagile species or for those which occur in large population densities, and that they are low for animal species which occur in small population densities and/or are of small body size and have little vagility. In other words, more vacant niches can be expected for the latter.

[edit] Criticisms of the concept

The concept of vacant niche is not accepted by all. The reason given is that a niche is a property of a species and does therefore not exist if no species is present. In other words, the term is thought to be “illogical”. However, some authors who have contributed most to the formulation of the modern niche concept (Hutchinson, Elton) apparently saw no difficulties in using the term. If a niche is defined as the interrelationship of a species with all the biotic and abiotic factors affecting it, there is no reason not to admit the possibility of additional potential interrelationships. So, it seems logical to refer to vacant niches. (see also ecological niche.)

Furthermore, it seems that authors most critical of the concept "vacant niche" really are critical of the view that niche space is largely empty and can easily absorb additional species. They instead adhere to the view that communities are usually in equilibrium (or at least close to it), resulting in a continual strong competition for resources. This view, indeed, is the basis of Darwinian natural selection. But many recent studies, some empirical , some theoretical, have provided support for the alternate view that nonequilibrium conditions are widespread (see above and the recent review in Rohde 2005b). [1]

In the German literature, an alternate term for vacant niches has found some acceptance. It is that of “freie ökologische Lizens” (free ecological license) (Sudhaus und Rehfeld 1992).[22] It has the disadvantage that it does not convey immediately and easily what is meant, and it indeed does not correspond exactly to the term vacant niche. The usefulness of a term should be assessed on the basis of its pregnancy and easy understandability, and on how fertile it is in promoting future research. The term vacant niche appears to fulfill these requirements.

[edit] Literature

  1. ^ a b c d e K. Rohde: Nonequilibrium Ecology, Cambridge University Press, Cambridge, 2005b, 223 pp. auf http://www.cambridge.org/9780521674553
  2. ^ Hutchinson, G. E. (1957). Concluding remarks. Cold Spring Harbour Symposium on Quantitative Biology 22, 415-427..
  3. ^ Elton, C.S. 1958. The ecology of invasions by animals and plants. Chapman and Hall, London, UK. 181 pp. ).
  4. ^ Rohde, K. (1977). A non-competitive mechanism responsible for restricting niches. Zoologischer Anzeiger 199, 164-172.
  5. ^ Rohde, K. (1979). A critical evaluation of intrinsic and extrinsic factord responsible for restricting niches. American Naturalist 114, 648-671.
  6. ^ Rohde, K. (1980 ). Warum sind ökologische Nischen begrenzt? Zwischenartlicher Antagonismus oder innerartlicher Zusammenhalt?. Naturwissenschaftliche Rundschau, 33, 98-102. ,
  7. ^ Lawton, J.H. (1984). Non-competitive populations, non-convergent communities, and vacant niches: the herbivores of bracken. In: Strong, D.R. Jr., Simberloff, D., Abele, L.G. and Thistle, A.B. eds. Ecological communities: conceptual issues and the evidence. Princeton University Press, Princeton, N.J., pp. 67-101.
  8. ^ Price, P.W. (1984). Alternative paradigms in community ecology. In: Price, P.W., Slobodchikoff, C.N. and Gaud, W.S. eds. (1984). A new ecology. Novel approaches to interactive systems. John Wiley & Sons, New York, Chichester, Brisbane, Toronto, Singapore, pp.353-383.
  9. ^ Compton, S.G., Lawton, J.H. and Rashbrook, V.K. (1989). Regional diversity, local community structure and vacant niches: the herbivorous arthropods of bracken in South Africa. Ecological Entomology 14, 365-373.
  10. ^ Begon, M.J., Harper, L. and Townsend, C.R. (1990). Ecology. Individuals, populations and communities. 2.ed. Blackwell Scientific, Boston.
  11. ^ Cornell, H.V. (1999). Unsaturation and regional influences on species richness in ecological communities: a review of the evidence. Ecoscience 6, 303-315.
  12. ^ Lawton, J.H. (1984). Non-competitive populations, non-convergent communities, and vacant niches: the herbivores of bracken. In: Strong, D.R. Jr., Simberloff, D., Abele, L.G. and Thistle, A.B. eds. Ecological communities: conceptual issues and the evidence. Princeton University Press, Princeton, N.J., pp. 67-101.
  13. ^ Walker, T.D. und Valentine, J.W.(1984). Equilibrium models of evolutionary diversity and the number of empty niches. American Naturalist 124, 887-899.
  14. ^ Kauffman, S.A. (1993). The origins of order. Self-organization and selection in evolution. Oxford University Press, New York Oxford.
  15. ^ Wolfram, S. (2002). A new kind of science. Wolfram Media Inc. Champaign, Il.
  16. ^ Ritchie, M. und Olff, H. (1999). Spatial scaling laws yield a synthetic theory of biodiversity. Nature 400, 557-562.
  17. ^ Rohde, K. (2001). Spatial scaling laws may not apply to most animal species. Oikos 93, 499-503.
  18. ^ Torchin, M.E. and Kuris, A.M. (2005). Introduced parasites. In: Rohde, K. (Ed.) Marine Parasitology. CSIRO Publishing Melbourne und CABI Wallingford, Oxon., pp. 358-366.
  19. ^ D.Jablonski: The future of the fossil record, Science 284, 2114-2116, 1999.
  20. ^ Rohde, K. (2005a) Eine neue Ökologie. Aktuelle Probleme der evolutionären Ökologie. Naturwissenschaftliche Rundschau, 58, 420-426.
  21. ^ Gotelli, N.J. and Rohde, K. (2002). Co-occurrence of ectoparasites of marine fishes: null-model analysis. Ecology Letters 5, 86-94.
  22. ^ Sudhaus,W. und Rehfeld,K. Einführung in die Phylogenetik und Systematik. Gustav Fischer Verlag Jena.

[edit] See also

Retrieved from "http://en.wikipedia.org../../../v/a/c/Vacant_niches.html"