Community Ecology: How Species Interact and Coexist
What Is a Community
An ecological community is the assemblage of all species populations living and interacting in a particular area at a particular time. Communities can be defined at many scales, from the microbial community living on a single leaf surface to the entire assemblage of species in a tropical forest. What distinguishes a community from a random collection of species is that the species interact, and these interactions influence which species are present, how abundant they are, and how the community changes over time.
Community ecologists study several key properties. Species richness is the number of different species present. Species diversity incorporates both richness and the relative abundance of each species, with communities where individuals are evenly distributed among species considered more diverse than those dominated by one or two species. Community structure refers to the physical and biological organization of the community, including the vertical layering of vegetation, the distribution of body sizes among animals, and the network of feeding relationships.
Competition and the Niche
Competition occurs when two or more species require the same limited resource. Resources can include food, water, space, light, nesting sites, or any other factor that organisms need to survive and reproduce. Interspecific competition, competition between different species, is one of the most important forces shaping community structure. It can reduce the growth rate, reproduction, or survival of one or both competing species and, in extreme cases, can lead to the local extinction of one species through a process called competitive exclusion.
The concept of the ecological niche is central to understanding competition. A species niche is the full range of environmental conditions and resources it uses, including its habitat, diet, activity patterns, and relationships with other species. The fundamental niche is the full range of conditions under which a species could survive and reproduce in the absence of competitors. The realized niche is the subset of the fundamental niche that a species actually occupies when competitors are present. Competition typically restricts species to a narrower realized niche than their fundamental niche would allow.
Niche partitioning occurs when competing species evolve to use different portions of a shared resource, reducing the intensity of competition and allowing coexistence. Darwin finches on the Galapagos Islands provide a classic example: closely related species have evolved different beak sizes and shapes that allow them to specialize on different food types, reducing direct competition. Character displacement, the evolutionary divergence of competing species in sympatry, is a key mechanism producing niche partitioning and is considered strong evidence that competition shapes community structure over evolutionary time.
Predation and Its Community Effects
Predation, broadly defined to include herbivory and parasitism as well as true predation, is a major force structuring communities. Predators can control prey populations, a phenomenon called top-down regulation. When predators are removed, prey populations can explode and overexploit their own food resources, leading to cascading effects throughout the community. Keystone predators maintain community diversity by preventing competitive exclusion among prey species.
Prey species have evolved an enormous array of defenses against predators, including camouflage, warning coloration, mimicry, chemical toxins, spines, armor, speed, group vigilance, and alarm calls. Predators in turn have evolved counter-adaptations, creating evolutionary arms races that drive specialization and diversification. These coevolutionary dynamics, playing out across millions of years, have produced much of the behavioral and morphological diversity seen in modern communities.
Herbivory, the consumption of plant tissue by animals, profoundly influences plant community composition and structure. Heavy grazing can shift grasslands from tall-grass to short-grass species, alter the competitive balance between trees and grasses, and change nutrient cycling rates. Plants have evolved chemical defenses, including alkaloids, tannins, and terpenoids, that deter herbivores, and many plants tolerate herbivory by storing reserves in roots or by growing rapidly to replace lost tissue.
Mutualism and Facilitation
Not all species interactions are antagonistic. Mutualism, in which both species benefit, is ubiquitous in nature and plays a crucial role in community organization. Plant-pollinator mutualisms maintain the reproduction of approximately 87 percent of flowering plant species. Mycorrhizal associations between fungi and plant roots occur in over 90 percent of plant families and can increase plant nutrient uptake by orders of magnitude. Coral-zooxanthellae mutualisms form the structural foundation of reef ecosystems that support roughly 25 percent of all marine species.
Facilitation occurs when one species makes conditions more favorable for another without necessarily receiving a direct benefit. Nurse plants in deserts provide shade and moisture that allow seedlings of other species to establish. Nitrogen-fixing plants enrich the soil, benefiting neighboring species. Foundation species, organisms that create habitat for many others, include reef-building corals, kelp forest canopy species, mangrove trees, and oyster reef builders. The loss of foundation species can cause the collapse of entire communities that depend on the habitat they create.
Community Assembly and Succession
How do communities come together? Community assembly is the process by which species from a regional species pool colonize a local habitat and form a functioning community. This process is influenced by dispersal ability (which species can reach the site), environmental filtering (which species can tolerate local conditions), and biotic interactions (which species can coexist). The order in which species arrive can affect the final community composition, a phenomenon called priority effects.
The debate over whether communities are tightly integrated units or loose assemblages of independently distributed species has a long history in ecology. Frederick Clements argued that communities are like superorganisms with predictable developmental trajectories, while Henry Gleason argued that species respond individually to environmental gradients and assemble into communities by coincidence. Modern ecology supports an intermediate view: species do respond individually to environmental conditions, but biotic interactions strongly modify the outcome, creating communities with nonrandom structure that are nonetheless less predictable and more variable than Clements envisioned.
Disturbance and Diversity
Disturbances, events that kill or remove organisms and free up resources, play a fundamental role in maintaining community diversity. The intermediate disturbance hypothesis, proposed by Joseph Connell in 1978, suggests that species diversity is highest at intermediate levels of disturbance. At low disturbance levels, competitive exclusion reduces diversity as dominant species monopolize resources. At high disturbance levels, only the most resilient species survive. At intermediate levels, disturbance prevents competitive exclusion while still allowing many species to persist, maximizing diversity.
Natural disturbances include fires, storms, floods, droughts, disease outbreaks, and volcanic eruptions. Many ecosystems are adapted to particular disturbance regimes, and suppressing natural disturbances can paradoxically reduce biodiversity and ecosystem health. Fire suppression in fire-adapted forests, for example, leads to dense understory growth, competitive exclusion of fire-dependent species, and eventually catastrophic fires that are far more destructive than the frequent, low-intensity fires the ecosystem evolved with. Understanding disturbance regimes and their role in maintaining diversity is essential for effective ecosystem management.
Species Diversity Patterns
One of the most striking patterns in community ecology is the latitudinal diversity gradient: species richness increases from the poles toward the equator in virtually all taxonomic groups. Tropical forests, coral reefs, and tropical oceans support far more species than their temperate or polar counterparts. Multiple hypotheses explain this pattern, including greater energy availability in the tropics, longer evolutionary time without glacial extinctions, larger tropical area, and more intense biotic interactions driving finer niche partitioning. No single explanation is sufficient, and the pattern likely results from the interaction of multiple factors operating at different scales.
At local scales, species diversity is influenced by productivity, habitat heterogeneity, area, isolation, and the history of disturbance and colonization. The species-area relationship, one of the oldest and most robust patterns in ecology, describes how species richness increases with habitat area. This relationship has critical implications for conservation, as habitat loss inevitably leads to species loss, often with a time delay known as extinction debt, where species committed to extinction persist temporarily after their habitat has been reduced below a viable threshold.
Metacommunity theory extends community ecology to regional scales by considering how dispersal between local communities influences species composition and diversity. The framework recognizes that local communities are not isolated but are connected by the movement of organisms across landscapes. In high-dispersal metacommunities, species composition across patches is similar because immigrants constantly arrive from neighboring communities. In low-dispersal metacommunities, local patches develop distinct compositions based on their specific environmental conditions and the historical sequence of colonization. Understanding these dynamics is increasingly important as habitat fragmentation alters the connectivity between communities worldwide.
Community ecology reveals how competition, predation, mutualism, and facilitation interact to determine which species coexist, how abundant they are, and how communities change over time.