Chapter 54 - Community Ecology
Interactions with members of other species in the community are some of the most important relationships in an organism's life.
Competition, predation, herbivory, parasitism, mutualism, and commensalism are examples of interspecific interactions. In this part, we will identify and describe each of these interactions, categorizing them based on whether they have a positive (+) or negative (-) influence on the survival and reproduction of the two species involved.
Predation, for example, is a +/- interaction that benefits the predator population while harming the prey population. Mutualism is a +/+ relationship since both species rely on one other for life and reproduction.
Most ecological research has traditionally focused on interactions that have a negative impact on at least one species, such as competition and predation. Positive contacts, on the other hand, are common and have a significant impact on community structure, as we will see.
Competition is a -/- interaction that happens when members of various species compete for a resource, limiting each species' survival and reproduction. Weeds in a garden fight for soil nutrients and water with garden plants. Lynx and foxes compete for food such as snowshoe hares in Alaska and Canada's northern woods.
Most ecological research has traditionally focused on interactions that have a negative impact on at least one species, such as competition and predation. Positive contacts, on the other hand, are common and have a significant impact on community structure, as we will see.
Competition is a -/- interaction that happens when members of various species compete for a resource, limiting each species' survival and reproduction. Weeds in a garden fight for soil nutrients and water with garden plants. Lynx and foxes compete for food such as snowshoe hares in Alaska and Canada's northern woods.
The term Character displacement refers to a byproduct of the previous rivalry.
Geospiza fuliginosa and Geospiza fortis allopatric populations on Los Hermanos and Daphne Islands exhibit comparable beak morphology (top two graphs) and probably consume similarly sized seeds.
However, in Floreana and San Cristóbal, where the two species are sympatric, G. fuliginosa has a shallower, smaller beak and G. fortis has a deeper, bigger beak (bottom graph), adaptations that promote eating different-sized seeds.
Commensalism refers to a relationship between species that benefits one but neither damages nor helps the other (+/0). Commensalisms, like mutualism, are widespread in nature.
Many wildflower species, for example, that thrive in low light levels are exclusively found in shady, forest floor settings.
Such shade-tolerant "specialists" are completely reliant on the trees that loom above them—the trees supply their dark environment.
These wildflowers, however, have little effect on the survival or reproduction of the trees. As a result, these species are engaged in a +/0 interaction in which the wildflowers benefit while the trees are unaffected.
Interactions in the community are categorized based on whether they benefit, hurt, or have an influence on the species concerned. Interspecific interactions have an impact on survival as well as the reproduction of the species that participate in them.
As demonstrated, These interactions in the table may be classified into three major categories. Competition, exploitation, and good relations are the three categories.
Competitive exclusion states that two species vying for the same resource cannot live in the same location indefinitely.
The differentiation of ecological niches that allow species to live in a community is referred to as resource partitioning. Biological communities are distinguished by their diversity and trophic structure.
The number of species in a community (its species richness) and their relative abundance both influence species diversity. More diversified ecosystems usually generate more biomass, have less year-to-year fluctuation in growth, and are more resistant to alien species invasion.
The trophic structure is an important aspect of community dynamics. From producers to apex predators, food chains connect the trophic levels. Food webs are formed by branching food chains and intricate trophic interactions.
Dominant species are the most numerous in a community. Keystone species are often less common species.
Keystone species are often low-abundance species that have a disproportionate impact on community structure.
The impacts of ecosystem engineers on the physical environment have an impact on community organizations. The bottom-up paradigm suggests a one-way effect from lower to higher trophic levels, with nutrients and other abiotic variables determining community structure largely.
According to the top-down paradigm, each trophic level is controlled by the trophic level above it, with the consequence that predators control herbivores, which regulate primary producers. Disturbance has an impact on species diversity and composition.
A growing body of data shows that disruption and a lack of
Increasing evidence shows that turbulence and lack of balance are the norm for most groups, rather than stability and equilibrium. The intermediate disturbance hypothesis proposes that moderate degrees of disturbance can promote more species variety than low or high levels of disturbance.
The series of community and ecosystem changes following a disturbance is referred to as ecological succession. Primary succession happens when there is no soil when succession begins; secondary succession occurs where soil persists after a disturbance.
Generally, species richness decreases along a latitudinal gradient from the tropics to the poles. Climate has an impact on the diversity gradient via energy (heat and light) and water. Tropical ecosystems' higher age may also contribute to their increased species diversity.
The species-area curve formalizes the notion that species richness is directly proportional to a community's geographic extent.
The richness of species on islands is determined by the size of the island and its distance from the mainland. According to the island equilibrium model, species richness on an ecological island approaches an equilibrium in which fresh immigrations are balanced by extinctions.
Pathogens change the structure of communities both locally and internationally.
Pathogens have an important influence on the structure of terrestrial and marine ecosystems, according to recent research.
Zoonotic pathogens are infections that spread from animals to people and are responsible for the majority of developing human illnesses.
Community ecology provides a framework for identifying important species interactions associated with such diseases, as well as for tracking and controlling their spread.
Interactions with members of other species in the community are some of the most important relationships in an organism's life.
Competition, predation, herbivory, parasitism, mutualism, and commensalism are examples of interspecific interactions. In this part, we will identify and describe each of these interactions, categorizing them based on whether they have a positive (+) or negative (-) influence on the survival and reproduction of the two species involved.
Predation, for example, is a +/- interaction that benefits the predator population while harming the prey population. Mutualism is a +/+ relationship since both species rely on one other for life and reproduction.
Most ecological research has traditionally focused on interactions that have a negative impact on at least one species, such as competition and predation. Positive contacts, on the other hand, are common and have a significant impact on community structure, as we will see.
Competition is a -/- interaction that happens when members of various species compete for a resource, limiting each species' survival and reproduction. Weeds in a garden fight for soil nutrients and water with garden plants. Lynx and foxes compete for food such as snowshoe hares in Alaska and Canada's northern woods.
Most ecological research has traditionally focused on interactions that have a negative impact on at least one species, such as competition and predation. Positive contacts, on the other hand, are common and have a significant impact on community structure, as we will see.
Competition is a -/- interaction that happens when members of various species compete for a resource, limiting each species' survival and reproduction. Weeds in a garden fight for soil nutrients and water with garden plants. Lynx and foxes compete for food such as snowshoe hares in Alaska and Canada's northern woods.
The term Character displacement refers to a byproduct of the previous rivalry.
Geospiza fuliginosa and Geospiza fortis allopatric populations on Los Hermanos and Daphne Islands exhibit comparable beak morphology (top two graphs) and probably consume similarly sized seeds.
However, in Floreana and San Cristóbal, where the two species are sympatric, G. fuliginosa has a shallower, smaller beak and G. fortis has a deeper, bigger beak (bottom graph), adaptations that promote eating different-sized seeds.
Commensalism refers to a relationship between species that benefits one but neither damages nor helps the other (+/0). Commensalisms, like mutualism, are widespread in nature.
Many wildflower species, for example, that thrive in low light levels are exclusively found in shady, forest floor settings.
Such shade-tolerant "specialists" are completely reliant on the trees that loom above them—the trees supply their dark environment.
These wildflowers, however, have little effect on the survival or reproduction of the trees. As a result, these species are engaged in a +/0 interaction in which the wildflowers benefit while the trees are unaffected.
Interactions in the community are categorized based on whether they benefit, hurt, or have an influence on the species concerned. Interspecific interactions have an impact on survival as well as the reproduction of the species that participate in them.
As demonstrated, These interactions in the table may be classified into three major categories. Competition, exploitation, and good relations are the three categories.
Competitive exclusion states that two species vying for the same resource cannot live in the same location indefinitely.
The differentiation of ecological niches that allow species to live in a community is referred to as resource partitioning. Biological communities are distinguished by their diversity and trophic structure.
The number of species in a community (its species richness) and their relative abundance both influence species diversity. More diversified ecosystems usually generate more biomass, have less year-to-year fluctuation in growth, and are more resistant to alien species invasion.
The trophic structure is an important aspect of community dynamics. From producers to apex predators, food chains connect the trophic levels. Food webs are formed by branching food chains and intricate trophic interactions.
Dominant species are the most numerous in a community. Keystone species are often less common species.
Keystone species are often low-abundance species that have a disproportionate impact on community structure.
The impacts of ecosystem engineers on the physical environment have an impact on community organizations. The bottom-up paradigm suggests a one-way effect from lower to higher trophic levels, with nutrients and other abiotic variables determining community structure largely.
According to the top-down paradigm, each trophic level is controlled by the trophic level above it, with the consequence that predators control herbivores, which regulate primary producers. Disturbance has an impact on species diversity and composition.
A growing body of data shows that disruption and a lack of
Increasing evidence shows that turbulence and lack of balance are the norm for most groups, rather than stability and equilibrium. The intermediate disturbance hypothesis proposes that moderate degrees of disturbance can promote more species variety than low or high levels of disturbance.
The series of community and ecosystem changes following a disturbance is referred to as ecological succession. Primary succession happens when there is no soil when succession begins; secondary succession occurs where soil persists after a disturbance.
Generally, species richness decreases along a latitudinal gradient from the tropics to the poles. Climate has an impact on the diversity gradient via energy (heat and light) and water. Tropical ecosystems' higher age may also contribute to their increased species diversity.
The species-area curve formalizes the notion that species richness is directly proportional to a community's geographic extent.
The richness of species on islands is determined by the size of the island and its distance from the mainland. According to the island equilibrium model, species richness on an ecological island approaches an equilibrium in which fresh immigrations are balanced by extinctions.
Pathogens change the structure of communities both locally and internationally.
Pathogens have an important influence on the structure of terrestrial and marine ecosystems, according to recent research.
Zoonotic pathogens are infections that spread from animals to people and are responsible for the majority of developing human illnesses.
Community ecology provides a framework for identifying important species interactions associated with such diseases, as well as for tracking and controlling their spread.