Ecology Terms Starting With C
Ecology Glossary: C
Carbon Cycle
/ KAR-bon SY-kul / · Latin carbonum (carbon) + Greek kyklos (circle)
Carbon Cycle is the continuous movement of carbon atoms through the atmosphere, living organisms, oceans, soils, and rocks via biological, chemical, and geological processes.
Photosynthesis removes carbon dioxide from the atmosphere and fixes it into glucose and cellulose, storing carbon in plant biomass for years to centuries. Cellular respiration by plants, animals, and microorganisms releases approximately half of the carbon fixed by photosynthesis back to the atmosphere within days to months. Decomposition of dead organic matter by fungi and bacteria returns carbon from soil and sediments to the atmosphere over weeks to years, completing the short-term biological loop.
The ocean absorbs about 30 percent of atmospheric carbon dioxide through physical dissolution and biological uptake by phytoplankton, whose remains sink to the deep sea and can sequester carbon for centuries in a process called the biological pump.
Peatlands cover only about 3 percent of Earth's land surface but store roughly 550 billion metric tons of carbon, more than all the world's forests combined, because waterlogged, low-oxygen conditions slow decomposition to a near halt.
The carbon cycle is balanced. Human fossil fuel burning now releases approximately 37 billion metric tons of carbon dioxide annually, a flux that exceeds the combined capacity of terrestrial and oceanic carbon sinks, causing atmospheric carbon dioxide to rise each year.
Mangrove forests along tropical coastlines fix carbon dioxide through photosynthesis and bury organic matter in waterlogged sediments at rates of 6 to 8 metric tons of carbon per hectare per year, roughly three to five times the sequestration rate of most terrestrial forests. When mangroves are cleared for aquaculture, that stored carbon oxidizes and returns to the atmosphere within years.
Carbon Footprint
/ KAR-bon FOOT-print / · Latin carbonum (carbon) + Old English fot + prente (impression)
Carbon Footprint is the total quantity of greenhouse gases released directly or indirectly by a person, product, activity, or organization, expressed as an equivalent mass of carbon dioxide.
Calculating a carbon footprint requires accounting for both direct emissions, such as burning gasoline in a car, and indirect emissions embedded in the production of food, goods, and electricity. The average American generates roughly 16 metric tons of carbon dioxide equivalent per year, more than twice the global average of about 7 metric tons. Food choices contribute substantially to this total: producing one kilogram of beef generates approximately 27 kilograms of carbon dioxide equivalent, while producing one kilogram of lentils generates less than 1 kilogram.
Reducing emissions from electricity generation, transportation, and diet are the three categories with the largest potential to lower individual and national carbon footprints.
Shipping accounts for roughly 2.5 percent of global greenhouse gas emissions, meaning that a single large container vessel crossing the Pacific can emit more carbon dioxide on one voyage than thousands of passenger cars emit in a year.
Greenhouse Gases →Carbon footprint measures only emissions from driving or flying. Food production, home heating and cooling, purchased goods, and waste disposal each contribute to a total that often exceeds transportation emissions for many households.
Beef production in Brazil generates a carbon footprint of roughly 50 to 80 kilograms of carbon dioxide equivalent per kilogram of beef when land-use change from deforestation is included. Shifting the same land to soy production for direct human consumption reduces the per-kilogram greenhouse gas output by more than 90 percent.
Carrying Capacity
/ KAIR-ee-ing kuh-PAS-ih-tee / · Latin carricare (to load) + capacitas (holding power)
Carrying capacity is the maximum population size that an environment can sustain indefinitely given the available supply of food, water, space, and other limiting resources.
Carrying capacity is set by whichever resource is least abundant, whether food, fresh water, nesting sites, or dissolved oxygen in aquatic environments. When a population exceeds carrying capacity, birth rates decline and death rates increase through starvation, disease, or reduced reproductive success, pushing numbers back down. Carrying capacity fluctuates seasonally and across years as rainfall, temperature, predator abundance, and disease prevalence change.
A grassland in the American West, for example, can support roughly 50 elk per square kilometer in wet years but only 20 in drought years because vegetation productivity drops sharply when precipitation falls below seasonal averages.
Reindeer (Rangifer tarandus) introduced to St. Matthew Island in Alaska in 1944 grew from 29 animals to approximately 6,000 by 1963, then crashed to fewer than 50 after overgrazing destroyed the lichen that formed their primary winter food source, a textbook case of population overshoot and collapse.
Populations stop growing smoothly at carrying capacity. Real populations frequently overshoot, then crash or oscillate around the carrying capacity as resource depletion and recovery lag behind population change.
A pond can support only a limited number of largemouth bass (Micropterus salmoides) before food and oxygen become insufficient to sustain further growth. Stocking a pond beyond its carrying capacity typically reduces average fish size and increases mortality rather than producing a larger total harvest.
Climax Community
/ KLY-maks kuh-MYOO-nih-tee / · Greek klimax (ladder, climax) + Latin communitas
Climax Community is a relatively stable, late-successional assemblage of species that develops over a long period following disturbance and persists as long as environmental conditions remain consistent.
A climax community represents a late-successional state where dominant species change slowly and species diversity reaches relatively high levels, typically 100 to 300 years after disturbance in temperate forests. The classic example of an oak-hickory or beech-maple forest in eastern North America consists of shade-tolerant species that replace early colonizers such as pioneer grasses and fast-growing aspens (Populus tremuloides). Modern ecological understanding recognizes that climax communities are not truly permanent endpoints but dynamic assemblages maintained by recurring disturbances such as windstorms, insect outbreaks, and fires.
Climate change, invasive species, and chronic human management actively prevent many communities from reaching stable endpoints, leading most ecologists today to prefer the term “late-successional state” over the older climax concept.
The concept of the climax community was developed by Frederic Clements in the early twentieth century, who argued that every region converges on a single predictable endpoint. Henry Gleason challenged this view in 1926, arguing that communities are individualistic assemblages shaped by chance and local conditions, a perspective that now dominates ecological theory.
Climax communities exist in a permanent stable state. Recurring disturbances such as windstorms, fires, and insect outbreaks constantly reshape these communities, and no terrestrial community remains unchanged over centuries.
An old-growth beech-maple forest in the Great Lakes region of North America can persist for centuries with relatively stable canopy composition, but a single severe ice storm or outbreak of beech bark disease can open large gaps and reset patches of the forest to an earlier successional stage. Gap sizes as small as 0.1 hectares are enough to shift local light conditions and allow early-successional species to re-establish.
Commensalism
/ koh-MEN-sah-liz-um / · Latin com, together; mensa, table; -ism
Commensalism is a biological interaction between two species in which one species gains a measurable benefit while the other experiences no detectable positive or negative effect.
In a commensal relationship, one organism gains food, shelter, protection, or transportation from another, while the host shows no measurable gain or loss. Barnacles (order Sessilia) growing on the skin of humpback whales (Megaptera novaeangliae) travel to food-rich polar feeding grounds at no apparent cost to the whale, gaining access to prey-dense waters they could not reach independently. Cattle egrets (Bubulcus ibis) follow herds of large grazing mammals and catch insects flushed from the vegetation by the animals’ feet, increasing their foraging success by up to 50 percent compared with birds foraging alone, while the cattle experience no documented benefit or harm.
Distinguishing true commensalism from subtle mutualism or parasitism requires careful measurement, because small effects on the host are easy to overlook.
Remora fish (family Echeneidae) attach to sharks using a modified dorsal fin that forms a suction disc, feeding on scraps from the shark's meals. Studies tracking shark swimming costs have found no measurable increase in drag attributable to attached remoras, supporting a commensal rather than parasitic classification.
Commensalism means both species benefit from the interaction. When both species gain, the relationship is mutualism; commensalism specifically describes cases where only one species gains a measurable advantage and the other experiences no detectable effect.
Epiphytic orchids in tropical rainforests grow on the branches of large trees, using the elevated position to access sunlight without competing for rooted soil space. Some epiphyte-laden trees in the Amazon basin support more than 30 orchid species simultaneously, yet show no measurable reduction in growth or survival compared with epiphyte-free individuals of the same species.
Competition
/ kom-peh-TIH-shun / · Latin competere (to strive together)
Competition is an ecological interaction in which two or more organisms seek the same limited resource, reducing the availability of that resource for each competitor.
Competition intensifies when organisms depend on a limiting resource in short supply, such as nitrogen in soil, sunlight in dense vegetation, or breeding territory in crowded conditions. Competitive exclusion can occur when one species consistently outcompetes another for the same resource, eventually eliminating the weaker competitor from that location, a principle demonstrated experimentally by G.F. Gause in 1934 using two Paramecium species in laboratory cultures.
Plants compete for light by growing taller or producing broader leaves, while animals compete through aggressive encounters, territoriality, or monopolization of food patches. Competitive outcomes shift with environmental conditions, so a species that dominates in one habitat may lose to a different competitor when temperature, moisture, or nutrient levels change.
Interference competition can be chemical as well as physical: black walnut trees (Juglans nigra) release a compound called juglone from their roots and decomposing leaves that suppresses the germination and growth of many neighboring plant species within a radius of up to 15 to 18 meters.
Competition always involves direct fighting or aggressive encounters. Plants compete for light, water, and nutrients through growth form and root architecture, with no physical contact between competitors.
Common reed (Phragmites australis) invades North American wetlands and outcompetes native cattails (Typha spp.) by growing 1 to 4 meters tall at densities of 50 to 200 stems per square meter, shading out competitors and releasing allelopathic compounds that suppress germination of neighboring species. Removal experiments at Chesapeake Bay marshes showed that eliminating Phragmites for three consecutive years allowed native sedge and cattail cover to recover from below 5 percent to above 60 percent, demonstrating that competitive exclusion was reversible when the dominant was controlled. Phragmites achieves this dominance partly through clonal spread via rhizomes extending up to 10 meters per year, allowing a single genetic individual to occupy patches exceeding a hectare.
Competitive Exclusion
/ kom-PET-ih-tiv eks-KLOO-zhun / · Latin competere, to strive; excludere, to shut out
Competitive exclusion is the ecological principle stating that two species competing for identical limiting resources in the same habitat cannot coexist indefinitely, because the superior competitor will eventually eliminate or displace the other.
The principle was formalized by Georgy Gause in the 1930s through laboratory experiments with two Paramecium species grown together on the same bacterial food source. When resources were identical and the environment was uniform, one species consistently drove the other to local extinction within weeks. The outcome depends on which species grows faster, tolerates resource scarcity better, or reproduces more efficiently under the given conditions.
In nature, complete competitive exclusion is less common than niche differentiation, where competing species shift their resource use enough to reduce direct overlap and permit coexistence.
Gause's Paramecium experiments used species so similar that modern genetic analysis places them in the same species complex, making his original interpretation of "two species" more complicated than textbooks typically present.
Competitive exclusion predicts that ecologically identical species cannot share a habitat. Two species with even slight differences in resource use can coexist by partitioning their niches.
The red squirrel (Sciurus vulgaris) was largely displaced from most of England after the gray squirrel (Sciurus carolinensis) was introduced in the 1870s. Gray squirrels outcompete red squirrels for food and also carry a poxvirus that kills red squirrels, and red squirrel populations declined by more than 95 percent across most of their former English range within a century.
Consumer
/ kun-SYOO-mer / · Latin consumere (to use up)
Consumer consumer is an organism that obtains energy by eating other organisms or their remains rather than producing its own food through photosynthesis or chemosynthesis.
Primary consumers obtain energy directly from producers by eating plants, algae, or photosynthetic microorganisms. Secondary consumers obtain energy by eating primary consumers, capturing only about 10 percent of the energy stored in their prey because the rest is lost as heat during metabolism. Detritivores, including earthworms, millipedes, and dung beetles, consume dead organic matter and feces, recycling nutrients back to soil and water.
Parasites and parasitoids consume energy from living hosts without killing them immediately, representing a distinct strategy of energy acquisition that does not fit neatly into simple herbivore-carnivore categories.
Consumers at higher trophic levels require much larger total areas of ecosystem to support them because energy transfer between trophic levels is inefficient.
Consumers are only animals. Some protists, fungi-like organisms, and parasitic plants also consume other organisms and qualify as consumers in food webs.
How To Become A Parasitologist? →A monarch caterpillar (Danaus plexippus) feeding on milkweed leaves is a primary consumer, obtaining energy directly from plant tissue. A black-headed grosbeak (Pheucticus melanocephalus) that eats the caterpillar is a secondary consumer, and it captures roughly 10 percent of the energy the caterpillar stored from the milkweed.
What Do Birds Eat? →Cooperation
/ koh-op-er-AY-shun / · Latin cooperari, to work together
Cooperation is an interaction in which two or more organisms behave in ways that provide a net benefit to at least one participant, even when the cooperating individual incurs some cost.
African wild dogs (Lycaon pictus) regurgitate food for pack members that were too ill or injured to join a hunt, a behavior that persists even among unrelated individuals within the pack. Cleaner wrasses (Labroides dimidiatus) remove parasites and dead tissue from larger reef fish that could easily consume them, benefiting both parties. Cooperation among relatives is partly explained by kin selection, where helping a sibling or offspring propagates shared genes even if the helper does not reproduce directly.
Among unrelated individuals, reciprocal altruism can sustain cooperation when animals interact repeatedly and cheaters are recognized and excluded from future exchanges.
Vampire bats (Desmodus rotundus) practice reciprocal food sharing: a bat that received a blood meal from a roost-mate on a previous night is significantly more likely to donate a meal to that same individual on a future night, even when the two are not closely related.
Cooperation is always selfless. Cooperative behavior typically benefits the helper directly through immediate reward, future reciprocation, or the propagation of shared genes in relatives.
Meerkats (Suricata suricatta) take turns standing as sentinels on elevated perches while other group members forage with their heads down. A single sentinel shift lasts roughly one hour, and the sentinel gives distinct alarm calls for aerial versus ground predators, allowing foragers to choose the appropriate escape response.
Coral Bleaching
/ KOR-ul BLEE-ching / · Latin corallium (coral) + Old English blaecan
Coral bleaching is the process by which thermally or chemically stressed reef-building corals expel their symbiotic photosynthetic algae, causing the coral tissue to turn white and depriving the animal of its primary energy source.
Coral bleaching occurs when heat stress, pollution, or other disturbances cause corals to expel their symbiotic zooxanthellae, which normally provide 70 to 90 percent of the coral’s energy through photosynthesis. Temperature increases of just 1 to 2 degrees Celsius above the seasonal maximum can trigger bleaching within weeks, as occurred during the 2016 global coral bleaching event that damaged the Great Barrier Reef across an area larger than Belgium. Bleached corals can recover if conditions improve within a few weeks, but prolonged stress lasting months leads to coral starvation and death.
Repeated bleaching events prevent full recovery and cause permanent habitat loss for the thousands of species that depend on reef structure.
Certain coral populations in the Persian Gulf routinely survive water temperatures above 35 degrees Celsius, temperatures that would bleach most Indo-Pacific corals within days, suggesting that heat tolerance can evolve under sustained thermal pressure.
Bleached coral is always dead. Bleached coral is severely stressed and can recover full zooxanthellae populations if water temperatures return to normal within a few weeks.
During the 2016 marine heat wave, staghorn corals (Acropora cervicornis) across the northern Great Barrier Reef bleached at rates exceeding 90 percent on some reefs. Surveys conducted afterward found that corals exposed to temperatures 1 degree Celsius above the long-term maximum for eight or more weeks had mortality rates near 50 percent, while those exposed for shorter periods showed partial recovery.
