Biological dispersal refers to a species movement away from an existing population or away from the parent organism. Through simply moving from one habitat patch to another, the dispersal of an individual has consequences not only for individual fitness, but also for population dynamics, population genetics, and species distribution. Understanding dispersal and the consequences on an ecosystem level requires understanding on the type of dispersal, the dispersal range of a given species, and the dispersal mechanisms involved.
 Types of dispersal
Dispersal from parent population
In general there are two basic types of dispersal:
- Density independent dispersal
- Organisms have evolved adaptations for dispersal that take advantage of various forms of kinetic energy occurring naturally in the environment. This is referred to as density independent or passive dispersal and operates on many groups of organisms (some invertebrates, fish, insects and sessile organisms such as plants) that depend on animal vectors, wind, gravity or current for dispersal.
- Density dependent dispersal
- Density dependent or active dispersal for many animals largely depends on factors such as local population size, resource competition, habitat quality, and habitat size. Due to population density, dispersal may relieve pressure for resources in an ecosystem, and competition for these resources may be a selection factor for dispersal mechanisms.
Dispersal of organisms is a critical process for understanding both geographic isolation in evolution through gene flow and the broad patterns of current geographic distributions (biogeography).
At some time during its life, an animal moves, or is moved, so that it does not die exactly where it was born. Such movement is called dispersal.
 Dispersal range
"Dispersal range" refers to the distance a species can move from an existing population or the parent organism. An ecosystem depends critically on the ability of individuals and populations to disperse from one habitat patch to another. Therefore, biological dispersal is critical to the stability of ecosystems.
 Environmental constraints
Few species are ever evenly or randomly distributed within or across landscapes. In general, species significantly vary across the landscape in association with environmental features that influence their reproductive success and population persistence. Spatial patterns in environmental features (e.g. resources) permit individuals to escape unfavorable conditions and seek out new locations. This allows the organism to "test" new environments for their suitability, provided they are within animal's geographic range. In addition, the ability of a species to disperse over a gradually changing environment could enable a population to survive extreme conditions. (i.e. climate change).
 Dispersal barriers
A dispersal barrier may mean that the dispersal range of a species is much smaller than the species distribution. An artificial example is habitat fragmentation due to human land use. Natural barriers to dispersal that limit species distribution include mountain ranges and rivers. An example is the separation of the ranges of the two species of chimpanzee by the Congo River.
On the other hand, human activities may also expand the dispersal range of a species by providing new dispersal methods (e.g., ships).
 Dispersal mechanisms
Most (but not all) animals are capable of locomotion and the basic mechanism of dispersal is movement from one place to another. Locomotion allows the organism to "test" new environments for their suitability, provided they are within animal's range. Movements are usually guided by inherited behaviors.
The formation of barriers to dispersal or gene flow between adjacent areas can isolate populations on either side of the emerging divide. The geographic separation and subsequent genetic isolation of portions of an ancestral population can result in speciation. Geodispersal occurs with the erosion of these barriers to dispersal or gene flow, thereby allowing the mixing of previously isolated populations (Lieberman, 2008).
 Plant dispersal mechanisms
are an example of a seed dispersion mechanism which uses a biotic vector, in this case animals
Main article: Seed dispersal
Seed dispersal is the movement or transport of seeds away from the parent plant. Plants have limited mobility and consequently rely upon a variety of dispersal vectors to transport their propagules, including both abiotic and biotic vectors. Seeds can be dispersed away from the parent plant individually or collectively, as well as dispersed in both space and time. The patterns of seed dispersal are determined in large part by the dispersal mechanism and this has important implications for the demographic and genetic structure of plant populations, as well as migration patterns and species interactions. There are five main modes of seed dispersal: gravity, wind, ballistic, water and by animals and the sky.
 Animal dispersal mechanisms
 Non-motile animals
There are numerous animal forms that are non'motile, such as sponges, bryozoans, tunicates, sea anemones, corals, and oysters. In common, they are all either marine or aquatic. It may seem curious that plants have been so successful at stationary life on land, while animals have not, but the answer lies in the food supply. Plants produce their own food from sunlight and carbon dioxide'both generally more abundant on land than in water. Animals fixed in place must rely on the surrounding medium to bring food at least close enough to grab, and this occurs in the three-dimensional water environment, but with much less abundance in the atmosphere.
All of the marine and aquatic invertebrates whose lives are spent fixed to the bottom (more or less; anemones are capable of getting up and moving to a new location if conditions warrant) produce dispersal units. These may be specialized "buds", or motile sexual reproduction products, or even a sort of alteration of generations as in certain cnidaria.
Corals provide a good example of how sedentary species achieve dispersion. Corals reproduce by releasing sperm and eggs directly into the water. These release events are coordinated by lunar phase in certain warm months, such that all corals of one or many species on a given reef will release on the same single or several consecutive nights. The released eggs are fertilized, and the resulting zygote develops quickly into a multicellular planula. This motile stage then attempts to find a suitable substratum for settlement. Most are unsuccessful and die or are fed upon by zooplankton and bottom dwelling predators such as anemones and other corals. However, untold millions are produced, and a few do succeed in locating spots of bare limestone, where they settle and transform by growth into a polyp. All things being favorable, the single polyp grows into a coral head by budding off new polyps to form a colony.
 Motile animals
The majority of all animals are motile. Although motile animals can, in theory, disperse themselves by their spontaneous and independent locomotive powers, a great many species utilize the existing kinetic energies in the environment, resulting in passive movement. Dispersal by water currents is especially associated with the physically small inhabitants of marine waters known as zooplankton. The term plankton comes from the Greek, πî»î�î�î��î¿î�, meaning "wanderer" or "drifter".
 Dispersal by dormant stages
Many animal species, especially freshwater invertebrates, are able to disperse by wind or by transfer with an aid of larger animals (birds, mammals or fishes) as dormant eggs? dormant embrios or, in some cases, dormant adult stages. Tardigrades, some rotifers and some copepods are able to withstand desiccation as adult dormant stages. Many other taxa (Cladocera, Bryozoa, Hydra, Copepoda and so on) can disperse as dormant eggs or embryos. Freshwater sponges usually have special dormant propagules called gemmulae for such a dispersal. Many kinds of dispersal dormant stages are able to withstand not only desiccation and low and high temperature, but also action of digestive enzymes during their transfer through digestive tracts of birds and other animals, high concentration of salts and many kinds of toxicants. Such dormant resistant stages made possible the long-distance dispersal from one water body to another and broad distribution ranges of many freshwater animals.
 See also
- ^ DUNNING, J. B. J., STEWART, D. J., DANIELSON, B. J., NOON, B. R., ROOT, T. L., LAMBERSON, R.H. & STEVENS, E. E. (1995). Spatially explicit population models: current forms and future uses. Ecological Applications
- ^ Hanski, I. & Gilpin, M. E. (eds.) (1997). Metapopulation biology : ecology, genetics and evolution, Academic Press, San Diego.
- ^ HANSKI, I. (1999). Metapopulation Ecology, Oxford University Press, Oxford.
- ^ Maguire Jr., B., 1963. The passive dispersal of small aquatic organisms and their colonization of isolated bodies of water. Ecol. Monogr.
- ^ NATHAN, R. (2001). The challenges of studying dispersal. Trends in Ecology & Evolution.
- ^ JOHST, K. & BRANDL, R. (1997). The effect of dispersal on local population dynamics. Ecological Modelling
- ^ Bowler, D. E. & Benton, T.G. (2005). Causes and consequences of animal dispersal strategies: relating individual behaviour to spatial dynamics. Biol. Rev.
- ^ Irwini, A.J. & Taylor, P.D. (2007). Evolution of Dispersal in a Stepping-Stone Population with Overlapping Generations. Theoretical Population Biology
- ^ Groom MJ, Meffe GK, Carroll CR. 2005. Principles of Conservation Biology. Sunderland (MA): Sinauer Associates, Inc.
- ^ Martin TE. 1998. Are microhabitat preferences of coexisting species under selection and adaptive? Ecology
- ^ Turner MG, Gardner RH, O'Neill. 2001. Landscape Ecology: In theory and practice, pattern and process. New York (NY): Springer Science.
 Further reading
- Ingold, C. T. (1971) Fungal spores: their liberation and dispersal Oxford, Clarendon Press 302 p. ISBN 0198541155
- Lidicker, W. Z. and R. L. Caldwell (1982) Dispersal and migration Stroudsburg, Pa. : Hutchinson Ross Pub. Co 311 p. ISBN 0879334355 (Dispersal of animals)
- Bullock, J. M.; R. E. Kenward, and R. S. Hails (editors) (2002) Dispersal ecology : the 42nd symposium of the British Ecological Society. Oxford, UK : Blackwell Science 458 p. ISBN 0632058765 (Animals and plants)
- Lieberman, B. S. 2008. Emerging syntheses between palaeobiogeography and macroevolutionary theory. Proceedings of the Royal Society of Victoria 120: 51-57.
- Turner MG, Gardner RH, O'Neill. 2001. Landscape Ecology: In theory and practice, pattern and process. New York (NY): Springer Science.
- Groom MJ, Meffe GK, Carroll CR. 2005. Principles of Conservation Biology. Sunderland (MA): Sinauer Associates, Inc. 793 p.
- Hanski, I. (1999). Metapopulation Ecology, Oxford University Press, Oxford.
- Hanski, I. & Gilpin, M. E. (eds.) (1997). Metapopulation biology : ecology, genetics and evolution, Academic Press, San Diego.
- Levin, S.A. 1974. Dispersion and Population Interactions. The American Naturalist. 108:960, p. 207.
- Clobert, J., E. Danchin , A.A. Dhondt , and J.D. Nichols (eds.)(2001) "dispersal", Oxford University Press, Oxford.
- Cousens, R., C. Dytham, R. Law (2008), Dispersal in plants: a population perspective, Oxford University Press, Oxford
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