Competition (biology)

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Great egret and neotropic cormorant competing over territory Bird War 1 (67158617).jpeg
Great egret and neotropic cormorant competing over territory

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]

Contents

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. [3] 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. [4]

Interference competition

Male-male competition in red deer during rut is an example of interference competition within a species. Hirschkampf.jpg
Male-male competition in red deer during rut is an example of interference competition within a species.

During interference competition, also called contest 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 the foraging, survival, and 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. [5] 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. [6]

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. [7] At first, the growth of juveniles is stunted by larger adult competitors. However, once the juveniles reach adulthood, they experience a secondary growth cycle. [7] Plants, on the other hand, primarily engage in interference competition with their neighbors through allelopathy, or the production of biochemicals. [8]

Interference competition can be seen as a strategy that has a clear cost (injury or death) and benefit (obtaining resources that would have gone to other organisms). [9] 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, does and fawns have dealt with this through temporal resource partitioning — foraging for food only when adult males are not present. [10]

Exploitation competition

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 organisms. 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. [11] [8]

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. [7] 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. [7]

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). [12] 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

Apparent competition occurs when two otherwise unrelated prey species indirectly compete for survival through a shared predator. [13] This form of competition typically 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 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 of 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. [13] [14] 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. [13]

Apparent competition and realized niche

Apparent competition can help shape a species' realized niche, or the area or resources the species can actually persist due to interspecific interactions. The effect on realized niches 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 the 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 the situation to some degree. [13] Support for the impact of competition on the breadth of the realized niche with respect to diet is becoming more common in a variety of systems based upon isotopic and spatial data, including both carnivores [15] and small mammals. [16]

Asymmetric apparent competition

Apparent competition can be symmetric or asymmetric. [17] 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, -). [18] 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 ). [19] Asymmetry in apparent competition can also arise as a consequence of resource competition. An empirical example is provided by two small fish species in postglacial lakes in Western Canada, where resource competition between prickly sculpin and threespine stickleback fish leads to a spatial niche shift mainly in threespine stickleback. [20] As a consequence of this shift, predation by a shared trout predator increases for stickleback but decreases for sculpin in lakes where the two species co-occur compared to lakes in which each species occurs on its own together with trout predators. Because sharing predators often comes together with competition for shared food resources, apparent competition and resource competition may often interplay in nature. [21]

Apparent competition in the human microbiome

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. [17]

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 cancer. However, if a virus were developed that targets both healthy and unhealthy host cells to some degree, the large number of healthy cells would support the predatory virus for long enough to eliminate all malignant cells. [17]

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. [22] 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. [23] 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. [24]

Within and between species

Sea anemones compete for the territory in tide pools Clone war of sea anemones 2-17-08-2.jpg
Sea anemones compete for the territory in tide pools

Competition can occur between individuals of the same species, called intraspecific competition, or between different species, called interspecific competition. Studies show that intraspecific competition can regulate population dynamics (changes in population size over time). This occurs because individuals become crowded as the population grows. Since individuals within a population require the same resources, crowding causes resources to become more limited. Some individuals (typically small juveniles) eventually do not acquire enough resources and die or do not reproduce. This reduces population size and slows population growth.[ citation needed ]

Species also interact with other species that require the same resources. Consequently, interspecific competition can alter the sizes of many species populations at the same time. Experiments demonstrate that when species compete for a limited resource, one species eventually drives the populations of other species extinct. These experiments suggest that competing species cannot coexist (they cannot live together in the same area) because the best competitor will exclude all other competing species.[ citation needed ]

Intraspecific

Intraspecific competition occurs when members of the same species compete for the same resources in an ecosystem. [25] A simple example is a stand of equally-spaced plants, which are all of the same age. The higher the density of plants, the more plants will be present per unit ground area, and the stronger the competition will be for resources such as light, water, or nutrients.

Interspecific

Interspecific competition may occur when individuals of two separate species share a limiting resource in the same area. If the resource cannot support both populations, then lowered fecundity, growth, or survival may result in at least one species. Interspecific competition has the potential to alter populations, communities, and the evolution of interacting species. An example among animals could be the case of cheetahs and lions; since both species feed on similar prey, they are negatively impacted by the presence of the other because they will have less food, however, they still persist together, despite the prediction that under competition one will displace the other. In fact, lions sometimes steal prey items killed by cheetahs. Potential competitors can also kill each other, in so-called 'intraguild predation'. For example, in southern California coyotes often kill and eat gray foxes and bobcats, all three carnivores sharing the same stable prey (small mammals). [26]

An example among protozoa involves Paramecium aurelia and Paramecium caudatum. Russian ecologist, Georgy Gause, studied the competition between the two species of Paramecium that occurred as a result of their coexistence. Through his studies, Gause proposed the Competitive exclusion principle, observing the competition that occurred when their different ecological niches overlapped. [27]

Competition has been observed between individuals, populations, and species, but there is little evidence that competition has been the driving force in the evolution of large groups. For example, mammals lived beside reptiles for many millions of years of time but were unable to gain a competitive edge until dinosaurs were devastated by the Cretaceous–Paleogene extinction event. [4]

Evolutionary strategies

In evolutionary contexts, competition is related to the concept of r/K selection theory, which relates to the selection of traits which promote success in particular environments. The theory originates from work on island biogeography by the ecologists Robert MacArthur and E. O. Wilson. [28]

In r/K selection theory, selective pressures are hypothesized to drive evolution in one of two stereotyped directions: r- or K-selection. [29] These terms, r, and K, are derived from standard ecological algebra, as illustrated in the simple Verhulst equation of population dynamics: [30]

where r is the growth rate of the population (N), and K is the carrying capacity of its local environmental setting. Typically, r-selected species exploit empty niches, and produce many offspring, each of whom has a relatively low probability of surviving to adulthood. In contrast, K-selected species are strong competitors in crowded niches, and invest more heavily in much fewer offspring, each with a relatively high probability of surviving to adulthood. [30]

Competitive exclusion principle

1: a smaller (yellow) species of bird forages across whole tree. 2: a larger (red) species competes for resources. 3: red dominates in middle for the more abundant resources. Yellow adapts to a new niches, avoiding competition. Competitive-20Exclusion-20Principle.svg
1: a smaller (yellow) species of bird forages across whole tree.
2: a larger (red) species competes for resources.
3: red dominates in middle for the more abundant resources. Yellow adapts to a new niches, avoiding competition.

To explain how species coexist, in 1934 Georgii Gause proposed the competitive exclusion principle which is also called the Gause principle: species cannot coexist if they have the same ecological niche. The word "niche" refers to a species' requirements for survival and reproduction. These requirements include both resources (like food) and proper habitat conditions (like temperature or pH). Gause reasoned that if two species had identical niches (required identical resources and habitats) they would attempt to live in exactly the same area and would compete for exactly the same resources. If this happened, the species that was the best competitor would always exclude its competitors from that area. Therefore, species must at least have slightly different niches in order to coexist. [31] [32]

Character displacement

Medium ground finch (Geospiza fortis) on Santa Cruz Island in the Galapagos Geospiza fortis.jpg
Medium ground finch ( Geospiza fortis ) on Santa Cruz Island in the Galapagos

Competition can cause species to evolve differences in traits. This occurs because the individuals of a species with traits similar to competing species always experience strong interspecific competition. These individuals have less reproduction and survival than individuals with traits that differ from their competitors. Consequently, they will not contribute many offspring to future generations. For example, Darwin's finches can be found alone or together on the Galapagos Islands. Both species populations actually have more individuals with intermediate-sized beaks when they live on islands without the other species present. However, when both species are present on the same island, competition is intense between individuals that have intermediate-sized beaks of both species because they all require intermediate-sized seeds. Consequently, individuals with small and large beaks have greater survival and reproduction on these islands than individuals with intermediate-sized beaks. Different finch species can coexist if they have traits—for instance, beak size—that allow them to specialize in particular resources. When Geospiza fortis and Geospiza fuliginosa are present on the same island, G. fuliginosa tends to evolve a small beak and G. fortis a large beak. The observation that competing species' traits are more different when they live in the same area than when competing species live in different areas is called character displacement. For the two finch species, beak size was displaced: Beaks became smaller in one species and larger in the other species. Studies of character displacement are important because they provide evidence that competition is important in determining ecological and evolutionary patterns in nature. [33]

See also

Related Research Articles

<span class="mw-page-title-main">Theoretical ecology</span>

Theoretical ecology is the scientific discipline devoted to the study of ecological systems using theoretical methods such as simple conceptual models, mathematical models, computational simulations, and advanced data analysis. Effective models improve understanding of the natural world by revealing how the dynamics of species populations are often based on fundamental biological conditions and processes. Further, the field aims to unify a diverse range of empirical observations by assuming that common, mechanistic processes generate observable phenomena across species and ecological environments. Based on biologically realistic assumptions, theoretical ecologists are able to uncover novel, non-intuitive insights about natural processes. Theoretical results are often verified by empirical and observational studies, revealing the power of theoretical methods in both predicting and understanding the noisy, diverse biological world.

<span class="mw-page-title-main">Ecological niche</span> Fit of a species living under specific environmental conditions

In ecology, a niche is the match of a species to a specific environmental condition. It describes how an organism or population responds to the distribution of resources and competitors and how it in turn alters those same factors. "The type and number of variables comprising the dimensions of an environmental niche vary from one species to another [and] the relative importance of particular environmental variables for a species may vary according to the geographic and biotic contexts".

<span class="mw-page-title-main">Biological interaction</span> Effect that organisms have on other organisms

In ecology, a biological interaction is the effect that a pair of organisms living together in a community have on each other. They can be either of the same species, or of different species. These effects may be short-term, or long-term, both often strongly influence the adaptation and evolution of the species involved. Biological interactions range from mutualism, beneficial to both partners, to competition, harmful to both partners. Interactions can be direct when physical contact is established or indirect, through intermediaries such as shared resources, territories, ecological services, metabolic waste, toxins or growth inhibitors. This type of relationship can be shown by net effect based on individual effects on both organisms arising out of relationship.

This glossary of ecology is a list of definitions of terms and concepts in ecology and related fields. For more specific definitions from other glossaries related to ecology, see Glossary of biology, Glossary of evolutionary biology, and Glossary of environmental science.

<span class="mw-page-title-main">Competitive exclusion principle</span> Ecology proposition

In ecology, the competitive exclusion principle, sometimes referred to as Gause's law, is a proposition that two species which compete for the same limited resource cannot coexist at constant population values. When one species has even the slightest advantage over another, the one with the advantage will dominate in the long term. This leads either to the extinction of the weaker competitor or to an evolutionary or behavioral shift toward a different ecological niche. The principle has been paraphrased in the maxim "complete competitors cannot coexist".

<span class="mw-page-title-main">Population ecology</span> Study of the dynamics of species populations and how these populations interact with the environment

Population ecology is a sub-field of ecology that deals with the dynamics of species populations and how these populations interact with the environment, such as birth and death rates, and by immigration and emigration.

<span class="mw-page-title-main">Character displacement</span>

Character displacement is the phenomenon where differences among similar species whose distributions overlap geographically are accentuated in regions where the species co-occur, but are minimized or lost where the species' distributions do not overlap. This pattern results from evolutionary change driven by biological competition among species for a limited resource. The rationale for character displacement stems from the competitive exclusion principle, also called Gause's Law, which contends that to coexist in a stable environment two competing species must differ in their respective ecological niche; without differentiation, one species will eliminate or exclude the other through competition.

<span class="mw-page-title-main">Intraspecific competition</span> Species members compete for resources

Intraspecific competition is an interaction in population ecology, whereby members of the same species compete for limited resources. This leads to a reduction in fitness for both individuals, but the more fit individual survives and is able to reproduce. By contrast, interspecific competition occurs when members of different species compete for a shared resource. Members of the same species have rather similar requirements for resources, whereas different species have a smaller contested resource overlap, resulting in intraspecific competition generally being a stronger force than interspecific competition.

<span class="mw-page-title-main">Interspecific competition</span> Form of competition

Interspecific competition, in ecology, is a form of competition in which individuals of different species compete for the same resources in an ecosystem. This can be contrasted with mutualism, a type of symbiosis. Competition between members of the same species is called intraspecific competition.

<span class="mw-page-title-main">Community (ecology)</span> Associated populations of species in a given area

In ecology, a community is a group or association of populations of two or more different species occupying the same geographical area at the same time, also known as a biocoenosis, biotic community, biological community, ecological community, or life assemblage. The term community has a variety of uses. In its simplest form it refers to groups of organisms in a specific place or time, for example, "the fish community of Lake Ontario before industrialization".

An ecological cascade effect is a series of secondary extinctions that are triggered by the primary extinction of a key species in an ecosystem. Secondary extinctions are likely to occur when the threatened species are: dependent on a few specific food sources, mutualistic, or forced to coexist with an invasive species that is introduced to the ecosystem. Species introductions to a foreign ecosystem can often devastate entire communities, and even entire ecosystems. These exotic species monopolize the ecosystem's resources, and since they have no natural predators to decrease their growth, they are able to increase indefinitely. Olsen et al. showed that exotic species have caused lake and estuary ecosystems to go through cascade effects due to loss of algae, crayfish, mollusks, fish, amphibians, and birds. However, the principal cause of cascade effects is the loss of top predators as the key species. As a result of this loss, a dramatic increase of prey species occurs. The prey is then able to overexploit its own food resources, until the population numbers decrease in abundance, which can lead to extinction. When the prey's food resources disappear, they starve and may go extinct as well. If the prey species is herbivorous, then their initial release and exploitation of the plants may result in a loss of plant biodiversity in the area. If other organisms in the ecosystem also depend upon these plants as food resources, then these species may go extinct as well. An example of the cascade effect caused by the loss of a top predator is apparent in tropical forests. When hunters cause local extinctions of top predators, the predators' prey's population numbers increase, causing an overexploitation of a food resource and a cascade effect of species loss. Recent studies have been performed on approaches to mitigate extinction cascades in food-web networks.

A guild is any group of species that exploit the same resources, or that exploit different resources in related ways. It is not necessary that the species within a guild occupy the same, or even similar, ecological niches.

The storage effect is a coexistence mechanism proposed in the ecological theory of species coexistence, which tries to explain how such a wide variety of similar species are able to coexist within the same ecological community or guild. The storage effect was originally proposed in the 1980s to explain coexistence in diverse communities of coral reef fish, however it has since been generalized to cover a variety of ecological communities. The theory proposes one way for multiple species to coexist: in a changing environment, no species can be the best under all conditions. Instead, each species must have a unique response to varying environmental conditions, and a way of buffering against the effects of bad years. The storage effect gets its name because each population "stores" the gains in good years or microhabitats (patches) to help it survive population losses in bad years or patches. One strength of this theory is that, unlike most coexistence mechanisms, the storage effect can be measured and quantified, with units of per-capita growth rate.

Island ecology is the study of island organisms and their interactions with each other and the environment. Islands account for nearly 1/6 of earth’s total land area, yet the ecology of island ecosystems is vastly different from that of mainland communities. Their isolation and high availability of empty niches lead to increased speciation. As a result, island ecosystems comprise 30% of the world’s biodiversity hotspots, 50% of marine tropical diversity, and some of the most unusual and rare species. Many species still remain unknown.

<span class="mw-page-title-main">Universal adaptive strategy theory</span> Theoretical ecology

Universal adaptive strategy theory (UAST) is an evolutionary theory developed by J. Philip Grime in collaboration with Simon Pierce describing the general limits to ecology and evolution based on the trade-off that organisms face when the resources they gain from the environment are allocated between either growth, maintenance or regeneration – known as the universal three-way trade-off.

<span class="mw-page-title-main">Intraguild predation</span> Killing and sometimes eating of potential competitors

Intraguild predation, or IGP, is the killing and sometimes eating of a potential competitor of a different species. This interaction represents a combination of predation and competition, because both species rely on the same prey resources and also benefit from preying upon one another. Intraguild predation is common in nature and can be asymmetrical, in which one species feeds upon the other, or symmetrical, in which both species prey upon each other. Because the dominant intraguild predator gains the dual benefits of feeding and eliminating a potential competitor, IGP interactions can have considerable effects on the structure of ecological communities.

<span class="mw-page-title-main">Coexistence theory</span> Framework explaining how competitor traits can maintain species diversity

Coexistence theory is a framework to understand how competitor traits can maintain species diversity and stave-off competitive exclusion even among similar species living in ecologically similar environments. Coexistence theory explains the stable coexistence of species as an interaction between two opposing forces: fitness differences between species, which should drive the best-adapted species to exclude others within a particular ecological niche, and stabilizing mechanisms, which maintains diversity via niche differentiation. For many species to be stabilized in a community, population growth must be negative density-dependent, i.e. all participating species have a tendency to increase in density as their populations decline. In such communities, any species that becomes rare will experience positive growth, pushing its population to recover and making local extinction unlikely. As the population of one species declines, individuals of that species tend to compete predominantly with individuals of other species. Thus, the tendency of a population to recover as it declines in density reflects reduced intraspecific competition (within-species) relative to interspecific competition (between-species), the signature of niche differentiation.

The R* rule is a hypothesis in community ecology that attempts to predict which species will become dominant as the result of competition for resources. The hypothesis was formulated by American ecologist David Tilman. It predicts that if multiple species are competing for a single limiting resource, then whichever species can survive at the lowest equilibrium resource level can outcompete all other species. If two species are competing for two resources, then coexistence is only possible if each species has a lower R* on one of the resources. For example, two phytoplankton species may be able to coexist if one is more limited by nitrogen, and the other is more limited by phosphorus.

Size-asymmetric competition refers to situations in which larger individuals exploit disproportionately greater amounts of resources when competing with smaller individuals. This type of competition is common among plants but also exists among animals. Size-asymmetric competition usually results from large individuals monopolizing the resource by "pre-emption"—i.e., exploiting the resource before smaller individuals are able to obtain it. Size-asymmetric competition has major effects on population structure and diversity within ecological communities.

<span class="mw-page-title-main">Ontogenetic niche shift</span> Ecological phenomenon

Ontogenetic niche shift is an ecological phenomenon where an organism changes its diet or habitat during its ontogeny (development). During the ontogenetic niche shifting an ecological niche of an individual changes its breadth and position. The best known representatives of taxa that exhibit some kind of the ontogenetic niche shift are fish, insects and amphibians. A niche shift is thought to be determined genetically, while also being irreversible. Important aspect of the ONS is the fact, that individuals of different stages of a population utilize different kind of resources and habitats. The term was introduced in a 1984 paper by biologists Earl E. Werner and James F. Gilliam.

References

  1. ↑ Begon, M.; Harper, J. L.; Townsend, C. R. (1996) Ecology: Individuals, populations and communities Blackwell Science.
  2. ↑ "Competition". globalchange.umich.edu. Retrieved 2021-12-08.
  3. 1 2 3 "Species Interactions and Competition | Learn Science at Scitable". www.nature.com. Retrieved 2021-12-08.
  4. 1 2 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.
  5. ↑ Barton, Kasey E.; Sanders, Nathan J.; Gordon, Deborah M. (2002-10-01). "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. S2CID   7668877.
  6. ↑ Borgia, Gerald (1985). "Bower Destruction and Sexual Competition in the Satin Bowerbird (Ptilonorhynchus violaceus)". Behavioral Ecology and Sociobiology. 18 (2): 91–100. doi:10.1007/BF00299037. ISSN   0340-5443. JSTOR   4599867. S2CID   36871646.
  7. 1 2 3 4 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. PMID   25325745. S2CID   206002300.
  8. 1 2 Schenk, H. Jochen (2006-03-24). "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 . S2CID   86320966.
  9. ↑ 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. Bibcode:1974PNAS...71.3073C. doi: 10.1073/pnas.71.8.3073 . ISSN   0027-8424. PMC   388623 . PMID   4528606.
  10. ↑ 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.
  11. ↑ 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. hdl: 2027.42/26823 . ISSN   0304-3800.
  12. ↑ Bhuyain, Mohammad Mosharof Hossain; Lim, Un Taek (2019-06-14). "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. S2CID   196662034.
  13. 1 2 3 4 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. PMID   929457.
  14. ↑ 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. PMID   31711965. S2CID   207952477.
  15. ↑ Fowler, N.L.; Petroelje, T.R.; Kautz, T.M.; Svoboda, N.J.; Duquette, J.F.; Kellner, K.F.; Beyer, D.E.; Belant, J.J. (2022). "Variable effects of wolves on niche breadth and density of intraguild competitors". Ecology and Evolution. 12. doi:10.1002/ece3.8542. PMC   8829107 .
  16. ↑ Allen, A.G.; Roehrs, Z.P.; Seville, R.S.; Lanier, H.C. (2022). "Competitive release during fire succession influences ecological turnover in a small mammal community". Ecology. 103 (8): 1–12. doi:10.1002/ecy.3733. PMC   9891167 . PMID   35430726.
  17. 1 2 3 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.
  18. ↑ Chaneton, Enrique J.; Bonsall, Michael B. (2000). "Enemy-Mediated Apparent Competition: Empirical Patterns and the Evidence". Oikos. 88 (2): 380–394. doi:10.1034/j.1600-0706.2000.880217.x. ISSN   0030-1299. JSTOR   3547034.
  19. ↑ 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. S2CID   83416826.
  20. ↑ Roesti, M., Groh, J.S., Blain, S.A., Huss, M., Rassias, P. & Bolnick, D.I. et al. (2023) Species divergence under competition and shared predation. Ecology Letters, 26, 111–123. Available from: https://doi.org/10.1111/ele.14138
  21. ↑ Roesti, M., Groh, J.S., Blain, S.A., Huss, M., Rassias, P. & Bolnick, D.I. et al. (2023) Species divergence under competition and shared predation. Ecology Letters, 26, 111–123. Available from: https://doi.org/10.1111/ele.14138
  22. ↑ 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. 33 (2): 565–577. doi: 10.1007/s11676-021-01395-9 . ISSN   1993-0607. S2CID   244202914.
  23. ↑ Pretzsch, Hans; Biber, Peter (2010-02-15). "Size-symmetric versus the 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.
  24. ↑ del Río, Miren; Condés, Sonia; Pretzsch, Hans (2014-08-01). "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.
  25. ↑ Townsend, Colin R.; Begon, Michael (2008). Essentials of Ecology. pp. 103–105. ISBN   978-1-4051-5658-5.
  26. ↑ .Fedriani, J. M., T. K. Fuller, R. M. Sauvajot and E. C. York. 2000. Competition and intraguild predation among three sympatric carnivores. Oecologia, 125:258-270.
  27. ↑ Gause, G.F. (1934). The struggle for existence. Baltimore, MD: Williams & Wilkins.
  28. ↑ MacArthur, R. and Wilson, E. O. (1967). The Theory of Island Biogeography, Princeton University Press (2001 reprint), ISBN   0-691-08836-5.
  29. ↑ Pianka, E. R. (1970). On r and K selection. American Naturalist '104' , 592-597.
  30. 1 2 Verhulst, P. F. (1838). Notice sur la loi que la population pursuit dans son accroissement. Corresp. Math. Phys. '10' , 113-121.
  31. ↑ Hardin, Garrett (1960). "The competitive exclusion principle" (PDF). Science. 131 (3409): 1292–1297. Bibcode:1960Sci...131.1292H. doi:10.1126/science.131.3409.1292. PMID   14399717. Archived from the original (PDF) on 2017-11-17. Retrieved 2017-01-10.
  32. ↑ Pocheville, Arnaud (2015). "The Ecological Niche: History and Recent Controversies". In Heams, Thomas; Huneman, Philippe; Lecointre, Guillaume; et al. (eds.). Handbook of Evolutionary Thinking in the Sciences. Dordrecht: Springer. pp. 547–586. ISBN   978-94-017-9014-7.
  33. ↑ Brown, W. L., and E. O. Wilson. 1956. "Character displacement". Systematic Zoology 5:49–65.
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