User:Leafcutter Ant/Competition (biology)
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[edit]Competition is an interaction between organisms or species in which both require a resource that is in limited supply (such as food, water, or territory).[1] Competition lowers the fitness of both organisms involved, since the presence of one of the organisms always reduces the amount of the resource available to the other.[2]
In the study of community ecology, competition within and between members of a species is an important biological interaction. Competition is one of many interacting biotic and abiotic factors that affect community structure, species diversity, and population dynamics (shifts in a population over time).[3]
There are three major mechanisms of competition: interference, exploitation, and apparent competition (in order from most direct to least direct). Interference and exploitation competition can be classed as "real" forms of competition, while apparent competition is not, as organisms do not share a resource, but instead share a predator.[4] Competition among members of the same species is known as intraspecific competition, while competition between individuals of different species is known as interspecific competition.
According to the competitive exclusion principle, species less suited to compete for resources must either adapt or die out, although competitive exclusion is rarely found in natural ecosystems.[3] According to evolutionary theory, competition within and between species for resources is important in natural selection. More recently, however, researchers have suggested that evolutionary biodiversity for vertebrates has been driven not by competition between organisms, but by these animals adapting to colonize empty livable space; this is termed the 'Room to Roam' hypothesis.[5]
Interference competition
[edit]During interference competition, organisms interact directly by fighting for scarce resources. For example, large aphids defend feeding sites on cottonwood leaves by ejecting smaller aphids from better sites. Male-male competition in red deer during rut is an example of interference competition that occurs within a species.
Interference competition occurs directly between individuals via aggression when the individuals interfere with foraging, survival, reproduction of others, or by directly preventing their physical establishment in a portion of the habitat. An example of this can be seen between the ant Novomessor cockerelli and red harvester ants, where the former interferes with the ability of the latter to forage by plugging the entrances to their colonies with small rocks.[6] Male bowerbirds, who create elaborate structures called bowers to attract potential mates, may reduce the fitness of their neighbors directly by stealing decorations from their structures.[7]
In animals, interference competition is a strategy mainly adopted by larger and stronger organisms within a habitat. As such, populations with high interference competition have adult-driven generation cycles.[8] At first, the growth of juveniles is stunted by larger adult competitors. However, once the juveniles reach adulthood, they experience a secondary growth cycle.[8] Plants, on the otherhand, primarily engage in interference competition with their neighbors through allelopathy, or the production of biochemicals.[9]
The strategy of interference competition can be seen as having a clear cost (injury or death) and benefit (obtaining resources that would have gone to other organisms).[10] In order to cope with strong interference competition, other organisms often either do the same or engage in exploitation competition. For example, depending on the season, larger ungulate red deer males are competitively dominant due to interference competition. However, other deer have dealt with this through temporal resource partitioning — foraging for food only when adult males are not present.[11]
Exploitation competition
[edit]Exploitation competition, or scramble competition, occurs indirectly when organisms both use a common limiting resource or shared food item. Instead of fighting or exhibiting aggressive behavior in order to win resources, exploitative competition occurs when resource use by one organism depletes the total amount available for other organism. These organisms might never interact directly, but compete by responding to changes in resource levels. Very obvious examples of this phenomenon include a diurnal species and a nocturnal species that nevertheless share the same resources, or a plant that competes with neighboring plants for light, nutrients, and space for root growth.[12][9]
This form of competition typically rewards those organisms who claim the resource first. As such, exploitation competition is often size-dependent and smaller organisms are favored since smaller organisms typically have higher foraging rates.[8] Since smaller organisms have an advantage when exploitative competition is important in an ecosystem, this mechanism of competition might lead to a juvenile-driven generation cycle: individual juveniles succeed and grow fast, but once they mature they are outcompeted by smaller organisms.[8]
In plants, exploitative competition can occur both above- and below-ground. Aboveground, plants reduce the fitness of their neighbors by vying for sunlight plants consume nitrogen by absorbing it into their roots, making nitrogen unavailable to nearby plants. Plants that produce many roots typically reduce soil nitrogen to very low levels, eventually killing neighboring plants.
Exploitative competition has also been shown to occur both within species (intraspecific) and between different species (interspecific). Furthermore, many competitive interactions between organisms are some combination of exploitative and interference competition, meaning the two mechanisms are far from mutually exclusive. For example, a recent 2019 study found that the native thrip species Frankliniella intonsa was competitively dominant over an invasive thrip species Frankliniella occidentalis because it not only exhibited greater time feeding (exploitative competition) but also greater time guarding its resources (interference competition).[13] Plants may also exhibit both forms of competition, not only scrambling for space for root growth but also directly inhibiting other plants' development through allelopathy.
Apparent competition
[edit]Apparent competition occurs when two otherwise unrelated prey species indirectly compete for survival through a shared predator.[14] This form of competition typicially manifests in new equilibrium abundances of each prey species. For example, suppose there are two species (species A and species B), which are preyed upon by food-limited predator species C. Scientists observe an increase in the abundance of species A and a decline in the abundance of species B. In an apparent competition model, this relationship is found to be mediated through predator C; a population explosion of species A increases the abundance of the predator species C due to a greater total food source. Since there are now more predators, species A and B would be hunted at higher rates than before. Thus, the success of species A was to the detriment to species B — not because they competed for resources, but because their increased numbers had indirect effects on the predator population.
This one-predator/two-prey model has been explored by ecologists as early as 1925, but the term "apparent competition" was first coined by University of Florida ecologist Robert D. Holt in 1977.[14][15] Holt found that field ecologists at the time were erroneously attributing negative interactions among prey species to niche partitioning and competitive exclusion, ignoring the role of food-limited predators.[14]
Apparent Competition and Realized Niche
[edit]Apparent competition can help shape a species' realized niche, or the area the species can actually persist due to interspecific interactions. The effect on realized niche could be incredibly strong, especially when there is an absence of more traditional interference or exploitative competition. A real world example was studied in the late 1960s, when the introduction of snowshoe hares (Lepus americanus) to Newfoundland reduced the habitat range of native arctic hares (Lepus arcticus). While some ecologists hypothesized that this was due to an overlap in niche, other ecologists argued that the more plausible mechanism was that snowshoe hare populations led to an explosion in food-limited lynx populations, a shared predator of both prey species. Since the arctic hare has a relatively weaker defense tactic than the snowshoe hare, they were excluded from woodland areas on the basis of differential predation. However, both apparent competition and exploitation competition might help explain situation to some degree.[14]
Asymmetric Apparent Competition
[edit]Apparent competition can be symmetric or asymmetric.[16] Symmetric apparent competition negatively impacts both species equally (-,-), from which it can be inferred that both species will persist. However, asymmetric apparent competition occurs when one species is affected less than the other. The most extreme scenario of asymmetric apparent competition is when one species is not affected at all by the increase in the predator, which can be seen as a form of amensalism (0, -).[17] Human impacts on endangered prey species have been characterized by conservation scientists as an extreme form of asymmetric apparent competition, often through introducing predator species into ecosystems or resource subsidies. An example of fully asymmetric apparent competition which often occurs near urban centers is subsidies in the form of human garbage or waste. In the early 2000s, the common raven (Corvus corax) population in the Mojave Desert increased due to an influx of human garbage, leading to an indirect negative effect on juvenile desert tortoises (Gopherus agassizii).[18]
Apparent Competition in the Human Microbiome
[edit]Apparent competition has also been viewed in and on the human body. The human immune system can acts as the generalist predator, and a high abundance of a certain bacteria may induce an immune response, damaging all pathogens in the body. Another example of this is of two populations of bacteria that can both support a predatory bacteriophage. In most situations, the one that is most resistant to infection by the shared predator will replace the other.[16]
Apparent competition has also been suggested as an exploitable phenomenon for cancer treatments. Highly specialized viruses that are developed to target malignant cancer cells often go locally extinct prior to eradicating all of the cancer. However, if a virus were developed that targets both healthy and unhealthy host cells to some degree, the large quantity of healthy cells would support the predatory virus for long enough to eliminate all malignant cells.[16]
Size-asymmetric competition
[edit]Main article: Size-asymmetric competition
Competition can be either complete symmetric (all individuals receive the same amount of resources, irrespective of their size), perfectly size symmetric (all individuals exploit the same amount of resource per unit biomass) , or absolutely size-asymmetric (the largest individuals exploit all the available resource).
Among plants, size asymmetry is context-dependent and competition can be both asymmetric and symmetric depending on the most limiting resource. In forest stands, below-ground competition for nutrients and water is size-symmetric, because a tree's root system is typically proportionate to the biomass of the entire tree.[19] Conversely, above-ground competition for light is size-asymmetric — since light has directionality, the forest canopy is dominated entirely by the largest trees. These trees disproportionately exploit most of the resource for their biomass, making the interaction size-asymmetric.[20] Whether above-ground or below-ground resources are more limiting can have major effects on the structure and diversity of ecological communities; in mixed beech stands, for example, size-asymmetric competition for light is a stronger predictor of growth compared with competition for soil resources.[21]
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References
[edit]- ^ Begon, M.; Harper, J. L.; Townsend, C. R. (1996) Ecology: Individuals, populations and communities Blackwell Science.
- ^ "Competition". globalchange.umich.edu. Retrieved 2021-12-08.
- ^ a b "Species Interactions and Competition | Learn Science at Scitable". www.nature.com. Retrieved 2021-12-08.
- ^ "Species Interactions and Competition | Learn Science at Scitable". www.nature.com. Retrieved 2021-12-08.
- ^ Sahney, Sarda; Benton, Michael J.; Ferry, Paul A. (2010-08-23). "Links between global taxonomic diversity, ecological diversity and the expansion of vertebrates on land". Biology Letters. 6 (4): 544–547. doi:10.1098/rsbl.2009.1024. PMC 2936204. PMID 20106856.
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: CS1 maint: PMC format (link) - ^ Barton, Kasey E.; Sanders, Nathan J.; Gordon, Deborah M. (October 2002). "The Effects of Proximity and Colony Age on Interspecific Interference Competition between the Desert Ants Pogonomyrmex barbatus and Aphaenogaster cockerelli". The American Midland Naturalist. 148 (2): 376–382. doi:10.1674/0003-0031(2002)148[0376:TEOPAC]2.0.CO;2. ISSN 0003-0031.
- ^ Borgia, Gerald (1985). "Bower Destruction and Sexual Competition in the Satin Bowerbird (Ptilonorhynchus violaceus)". Behavioral Ecology and Sociobiology. 18 (2): 91–100. ISSN 0340-5443.
- ^ a b c d Le Bourlot, Vincent; Tully, Thomas; Claessen, David (2014-11-01). "Interference versus Exploitative Competition in the Regulation of Size-Structured Populations". The American Naturalist. 184 (5): 609–623. doi:10.1086/678083. ISSN 0003-0147.
- ^ a b Schenk, H. Jochen (July 2006). "Root competition: beyond resource depletion: Root competition: beyond resource depletion". Journal of Ecology. 94 (4): 725–739. doi:10.1111/j.1365-2745.2006.01124.x.
- ^ Case, Ted J.; Gilpin, Michael E. (August 1974). "Interference Competition and Niche Theory". Proceedings of the National Academy of Sciences of the United States of America. 71 (8): 3073–3077. ISSN 0027-8424. PMID 4528606.
- ^ Stone, David B; Martin, James A; Cohen, Bradley S; Prebyl, Thomas J; Killmaster, Charlie; Miller, Karl V (2018-07-06). "Intraspecific temporal resource partitioning at white-tailed deer feeding sites". Current Zoology. 65 (2): 139–146. doi:10.1093/cz/zoy051. ISSN 2396-9814. PMC 6430969. PMID 30936902.
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: CS1 maint: PMC format (link) - ^ Jensen, A. L. (1987-02-01). "Simple models for exploitative and interference competition". Ecological Modelling. 35 (1): 113–121. doi:10.1016/0304-3800(87)90093-7. ISSN 0304-3800.
- ^ Bhuyain, Mohammad Mosharof Hossain; Lim, Un Taek (June 2019). "Interference and Exploitation Competition between Frankliniella occidentalis and F. intonsa (Thysanoptera: Thripidae) in Laboratory Assays". Florida Entomologist. 102 (2): 322–328. doi:10.1653/024.102.0206. ISSN 0015-4040.
- ^ a b c d Holt, Robert D. (1977-10-01). "Predation, apparent competition, and the structure of prey communities". Theoretical Population Biology. 12 (2): 197–229. doi:10.1016/0040-5809(77)90042-9. ISSN 0040-5809.
- ^ Schreiber, Sebastian J.; Křivan, Vlastimil (2020-06-01). "Holt (1977) and apparent competition". Theoretical Population Biology. Fifty years of Theoretical Population Biology. 133: 17–18. doi:10.1016/j.tpb.2019.09.006. ISSN 0040-5809.
- ^ a b c Holt, Robert D.; Bonsall, Michael B. (2017-11-02). "Apparent Competition". Annual Review of Ecology, Evolution, and Systematics. 48 (1): 447–471. doi:10.1146/annurev-ecolsys-110316-022628. ISSN 1543-592X.
- ^ Chaneton, Enrique J.; Bonsall, Michael B. (2000). "Enemy-Mediated Apparent Competition: Empirical Patterns and the Evidence". Oikos. 88 (2): 380–394. ISSN 0030-1299.
- ^ DeCesare, N. J.; Hebblewhite, M.; Robinson, H. S.; Musiani, M. (2010). "Endangered, apparently: the role of apparent competition in endangered species conservation". Animal Conservation. 13 (4): 353–362. doi:10.1111/j.1469-1795.2009.00328.x. ISSN 1469-1795.
- ^ West, P. W.; Ratkowsky, D. A. (2021-10-04). "Problems with models assessing influences of tree size and inter-tree competitive processes on individual tree growth: a cautionary tale". Journal of Forestry Research. doi:10.1007/s11676-021-01395-9. ISSN 1993-0607.
- ^ Pretzsch, Hans; Biber, Peter (February 2010). "Size-symmetric versus size-asymmetric competition and growth partitioning among trees in forest stands along an ecological gradient in central Europe". Canadian Journal of Forest Research. 40 (2): 370–384. doi:10.1139/x09-195. ISSN 0045-5067.
- ^ del Río, Miren; Condés, Sonia; Pretzsch, Hans (August 2014). "Analyzing size-symmetric vs. size-asymmetric and intra- vs. inter-specific competition in beech (Fagus sylvatica L.) mixed stands". Forest Ecology and Management. 325: 90–98. doi:10.1016/j.foreco.2014.03.047.