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For other uses, see Ecosystem (disambiguation). "Biosystem" redirects here. For the journal, see BioSystems.

Coral reefs are a highly productive marine ecosystem.
Left: Coral reef ecosystems are highly productive marine systems.[1] Right: Temperate rainforest, a terrestrial ecosystem.
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An ecosystem (or ecological system) is a system formed by organisms in interaction with their environment.[2]: 458  The biotic and abiotic components are linked together through nutrient cycles and energy flows.

Ecosystems are controlled by external and internal factors. External factors such as climate, parent material which forms the soil and topography, control the overall structure of an ecosystem but are not themselves influenced by the ecosystem. Internal factors are controlled, for example, by decomposition, root competition, shading, disturbance, succession, and the types of species present. While the resource inputs are generally controlled by external processes, the availability of these resources within the ecosystem is controlled by internal factors. Therefore, internal factors not only control ecosystem processes but are also controlled by them.

Ecosystems are dynamic entities—they are subject to periodic disturbances and are always in the process of recovering from some past disturbance. The tendency of an ecosystem to remain close to its equilibrium state, despite that disturbance, is termed its resistance. The capacity of a system to absorb disturbance and reorganize while undergoing change so as to retain essentially the same function, structure, identity, and feedbacks is termed its ecological resilience. Ecosystems can be studied through a variety of approaches—theoretical studies, studies monitoring specific ecosystems over long periods of time, those that look at differences between ecosystems to elucidate how they work and direct manipulative experimentation. Biomes are general classes or categories of ecosystems. However, there is no clear distinction between biomes and ecosystems. Ecosystem classifications are specific kinds of ecological classifications that consider all four elements of the definition of ecosystems: a biotic component, an abiotic complex, the interactions between and within them, and the physical space they occupy. Biotic factors of the ecosystem are living things; such as plants, animals, and bacteria, while abiotic are non-living components; such as water, soil and atmosphere.

Plants allow energy to enter the system through photosynthesis, building up plant tissue. Animals play an important role in the movement of matter and energy through the system, by feeding on plants and on one another. They also influence the quantity of plant and microbial biomass present. By breaking down dead organic matter, decomposers release carbon back to the atmosphere and facilitate nutrient cycling by converting nutrients stored in dead biomass back to a form that can be readily used by plants and microbes.

Ecosystems provide a variety of goods and services upon which people depend, and may be part of. Ecosystem goods include the "tangible, material products" of ecosystem processes such as water, food, fuel, construction material, and medicinal plants. Ecosystem services, on the other hand, are generally "improvements in the condition or location of things of value". These include things like the maintenance of hydrological cycles, cleaning air and water, the maintenance of oxygen in the atmosphere, crop pollination and even things like beauty, inspiration and opportunities for research. Many ecosystems become degraded through human impacts, such as soil loss, air and water pollution, habitat fragmentation, water diversion, fire suppression, and introduced species and invasive species. These threats can lead to abrupt transformation of the ecosystem or to gradual disruption of biotic processes and degradation of abiotic conditions of the ecosystem. Once the original ecosystem has lost its defining features, it is considered "collapsed". Ecosystem restoration can contribute to achieving the Sustainable Development Goals.

Definition

An ecosystem (or ecological system) consists of all the organisms and the abiotic pools (or physical environment) with which they interact.[3][4]: 5 [2]: 458  The biotic and abiotic components are linked together through nutrient cycles and energy flows.[5]

"Ecosystem processes" are the transfers of energy and materials from one pool to another.[2]: 458  Ecosystem processes are known to "take place at a wide range of scales". Therefore, the correct scale of study depends on the question asked.[4]: 5 

Origin and development of the term

The term "ecosystem" was first used in 1935 in a publication by British ecologist Arthur Tansley. The term was coined by Arthur Roy Clapham, who came up with the word at Tansley's request.[6] Tansley devised the concept to draw attention to the importance of transfers of materials between organisms and their environment.[4]: 9  He later refined the term, describing it as "The whole system, ... including not only the organism-complex, but also the whole complex of physical factors forming what we call the environment".[3] Tansley regarded ecosystems not simply as natural units, but as "mental isolates".[3] Tansley later defined the spatial extent of ecosystems using the term "ecotope".[7]

G. Evelyn Hutchinson, a limnologist who was a contemporary of Tansley's, combined Charles Elton's ideas about trophic ecology with those of Russian geochemist Vladimir Vernadsky. As a result, he suggested that mineral nutrient availability in a lake limited algal production. This would, in turn, limit the abundance of animals that feed on algae. Raymond Lindeman took these ideas further to suggest that the flow of energy through a lake was the primary driver of the ecosystem. Hutchinson's students, brothers Howard T. Odum and Eugene P. Odum, further developed a "systems approach" to the study of ecosystems. This allowed them to study the flow of energy and material through ecological systems.[4]: 9 

Processes

Rainforest ecosystems are rich in biodiversity. This is the Gambia River in Senegal's Niokolo-Koba National Park.
Flora of Baja California desert, Cataviña region, Mexico

External and internal factors

Ecosystems are controlled by both external and internal factors. External factors, also called state factors, control the overall structure of an ecosystem and the way things work within it, but are not themselves influenced by the ecosystem. On broad geographic scales, climate is the factor that "most strongly determines ecosystem processes and structure".[4]: 14  Climate determines the biome in which the ecosystem is embedded. Rainfall patterns and seasonal temperatures influence photosynthesis and thereby determine the amount of energy available to the ecosystem.[8]: 145 

Parent material determines the nature of the soil in an ecosystem, and influences the supply of mineral nutrients. Topography also controls ecosystem processes by affecting things like microclimate, soil development and the movement of water through a system. For example, ecosystems can be quite different if situated in a small depression on the landscape, versus one present on an adjacent steep hillside.[9]: 39 [10]: 66 

Other external factors that play an important role in ecosystem functioning include time and potential biota, the organisms that are present in a region and could potentially occupy a particular site. Ecosystems in similar environments that are located in different parts of the world can end up doing things very differently simply because they have different pools of species present.[11]: 321  The introduction of non-native species can cause substantial shifts in ecosystem function.[12]

Unlike external factors, internal factors in ecosystems not only control ecosystem processes but are also controlled by them.[4]: 16  While the resource inputs are generally controlled by external processes like climate and parent material, the availability of these resources within the ecosystem is controlled by internal factors like decomposition, root competition or shading.[13] Other factors like disturbance, succession or the types of species present are also internal factors.

Primary production

Global oceanic and terrestrial phototroph abundance, from September 1997 to August 2000. As an estimate of autotroph biomass, it is only a rough indicator of primary production potential and not an actual estimate of it.
Main article: Primary production

Primary production is the production of organic matter from inorganic carbon sources. This mainly occurs through photosynthesis. The energy incorporated through this process supports life on earth, while the carbon makes up much of the organic matter in living and dead biomass, soil carbon and fossil fuels. It also drives the carbon cycle, which influences global climate via the greenhouse effect.

Through the process of photosynthesis, plants capture energy from light and use it to combine carbon dioxide and water to produce carbohydrates and oxygen. The photosynthesis carried out by all the plants in an ecosystem is called the gross primary production (GPP).[8]: 124  About half of the gross GPP is respired by plants in order to provide the energy that supports their growth and maintenance.[14]: 157  The remainder, that portion of GPP that is not used up by respiration, is known as the net primary production (NPP).[14]: 157  Total photosynthesis is limited by a range of environmental factors. These include the amount of light available, the amount of leaf area a plant has to capture light (shading by other plants is a major limitation of photosynthesis), the rate at which carbon dioxide can be supplied to the chloroplasts to support photosynthesis, the availability of water, and the availability of suitable temperatures for carrying out photosynthesis.[8]: 155 

Energy flow

Main article: Energy flow (ecology)
See also: Food web and Trophic level

Energy and carbon enter ecosystems through photosynthesis, are incorporated into living tissue, transferred to other organisms that feed on the living and dead plant matter, and eventually released through respiration.[14]: 157  The carbon and energy incorporated into plant tissues (net primary production) is either consumed by animals while the plant is alive, or it remains uneaten when the plant tissue dies and becomes detritus. In terrestrial ecosystems, the vast majority of the net primary production ends up being broken down by decomposers. The remainder is consumed by animals while still alive and enters the plant-based trophic system. After plants and animals die, the organic matter contained in them enters the detritus-based trophic system.[15]

Ecosystem respiration is the sum of respiration by all living organisms (plants, animals, and decomposers) in the ecosystem.[16] Net ecosystem production is the difference between gross primary production (GPP) and ecosystem respiration.[17] In the absence of disturbance, net ecosystem production is equivalent to the net carbon accumulation in the ecosystem.

Energy can also be released from an ecosystem through disturbances such as wildfire or transferred to other ecosystems (e.g., from a forest to a stream to a lake) by erosion.

In aquatic systems, the proportion of plant biomass that gets consumed by herbivores is much higher than in terrestrial systems.[15] In trophic systems, photosynthetic organisms are the primary producers. The organisms that consume their tissues are called primary consumers or secondary producers—herbivores. Organisms which feed on microbes (bacteria and fungi) are termed microbivores. Animals that feed on primary consumers—carnivores—are secondary consumers. Each of these constitutes a trophic level.[15]

The sequence of consumption—from plant to herbivore, to carnivore—forms a food chain. Real systems are much more complex than this—organisms will generally feed on more than one form of food, and may feed at more than one trophic level. Carnivores may capture some prey that is part of a plant-based trophic system and others that are part of a detritus-based trophic system (a bird that feeds both on herbivorous grasshoppers and earthworms, which consume detritus). Real systems, with all these complexities, form food webs rather than food chains which present a number of common, non random properties in the topology of their network.[18]

Decomposition

See also: Decomposition
Sequence of a decomposing pig carcass over time

The carbon and nutrients in dead organic matter are broken down by a group of processes known as decomposition. This releases nutrients that can then be re-used for plant and microbial production and returns carbon dioxide to the atmosphere (or water) where it can be used for photosynthesis. In the absence of decomposition, the dead organic matter would accumulate in an ecosystem, and nutrients and atmospheric carbon dioxide would be depleted.[19]: 183 

Decomposition processes can be separated into three categories—leaching, fragmentation and chemical alteration of dead material. As water moves through dead organic matter, it dissolves and carries with it the water-soluble components. These are then taken up by organisms in the soil, react with mineral soil, or are transported beyond the confines of the ecosystem (and are considered lost to it).[20]: 271–280  Newly shed leaves and newly dead animals have high concentrations of water-soluble components and include sugars, amino acids and mineral nutrients. Leaching is more important in wet environments and less important in dry ones.[10]: 69–77 

Fragmentation processes break organic material into smaller pieces, exposing new surfaces for colonization by microbes. Freshly shed leaf litter may be inaccessible due to an outer layer of cuticle or bark, and cell contents are protected by a cell wall. Newly dead animals may be covered by an exoskeleton. Fragmentation processes, which break through these protective layers, accelerate the rate of microbial decomposition.[19]: 184  Animals fragment detritus as they hunt for food, as does passage through the gut. Freeze-thaw cycles and cycles of wetting and drying also fragment dead material.[19]: 186 

The chemical alteration of the dead organic matter is primarily achieved through bacterial and fungal action. Fungal hyphae produce enzymes that can break through the tough outer structures surrounding dead plant material. They also produce enzymes that break down lignin, which allows them access to both cell contents and the nitrogen in the lignin. Fungi can transfer carbon and nitrogen through their hyphal networks and thus, unlike bacteria, are not dependent solely on locally available resources.[19]: 186 

Decomposition rates

Decomposition rates vary among ecosystems.[21] The rate of decomposition is governed by three sets of factors—the physical environment (temperature, moisture, and soil properties), the quantity and quality of the dead material available to decomposers, and the nature of the microbial community itself.[19]: 194  Temperature controls the rate of microbial respiration; the higher the temperature, the faster the microbial decomposition occurs. Temperature also affects soil moisture, which affects decomposition. Freeze-thaw cycles also affect decomposition—freezing temperatures kill soil microorganisms, which allows leaching to play a more important role in moving nutrients around. This can be especially important as the soil thaws in the spring, creating a pulse of nutrients that become available.[20]: 280 

Decomposition rates are low under very wet or very dry conditions. Decomposition rates are highest in wet, moist conditions with adequate levels of oxygen. Wet soils tend to become deficient in oxygen (this is especially true in wetlands), which slows microbial growth. In dry soils, decomposition slows as well, but bacteria continue to grow (albeit at a slower rate) even after soils become too dry to support plant growth.[19]: 200 

Dynamics and resilience

Further information: Resistance (ecology) and Ecological resilience

Ecosystems are dynamic entities. They are subject to periodic disturbances and are always in the process of recovering from past disturbances.[22]: 347  When a perturbation occurs, an ecosystem responds by moving away from its initial state. The tendency of an ecosystem to remain close to its equilibrium state, despite that disturbance, is termed its resistance. The capacity of a system to absorb disturbance and reorganize while undergoing change so as to retain essentially the same function, structure, identity, and feedbacks is termed its ecological resilience.[23][24] Resilience thinking also includes humanity as an integral part of the biosphere where we are dependent on ecosystem services for our survival and must build and maintain their natural capacities to withstand shocks and disturbances.[25] Time plays a central role over a wide range, for example, in the slow development of soil from bare rock and the faster recovery of a community from disturbance.[14]: 67 

Disturbance also plays an important role in ecological processes. F. Stuart Chapin and coauthors define disturbance as "a relatively discrete event in time that removes plant biomass".[22]: 346  This can range from herbivore outbreaks, treefalls, fires, hurricanes, floods, glacial advances, to volcanic eruptions. Such disturbances can cause large changes in plant, animal and microbe populations, as well as soil organic matter content. Disturbance is followed by succession, a "directional change in ecosystem structure and functioning resulting from biotically driven changes in resource supply."[2]: 470 

The frequency and severity of disturbance determine the way it affects ecosystem function. A major disturbance like a volcanic eruption or glacial advance and retreat leave behind soils that lack plants, animals or organic matter. Ecosystems that experience such disturbances undergo primary succession. A less severe disturbance like forest fires, hurricanes or cultivation result in secondary succession and a faster recovery.[22]: 348  More severe and more frequent disturbance result in longer recovery times.

From one year to another, ecosystems experience variation in their biotic and abiotic environments. A drought, a colder than usual winter, and a pest outbreak all are short-term variability in environmental conditions. Animal populations vary from year to year, building up during resource-rich periods and crashing as they overshoot their food supply. Longer-term changes also shape ecosystem processes. For example, the forests of eastern North America still show legacies of cultivation which ceased in 1850 when large areas were reverted to forests.[22]: 340  Another example is the methane production in eastern Siberian lakes that is controlled by organic matter which accumulated during the Pleistocene.[26]

A freshwater lake in Gran Canaria, an island of the Canary Islands. Clear boundaries make lakes convenient to study using an ecosystem approach.

Nutrient cycling

See also: Nutrient cycle, Biogeochemical cycle, and Nitrogen cycle
Biological nitrogen cycling

Ecosystems continually exchange energy and carbon with the wider environment. Mineral nutrients, on the other hand, are mostly cycled back and forth between plants, animals, microbes and the soil. Most nitrogen enters ecosystems through biological nitrogen fixation, is deposited through precipitation, dust, gases or is applied as fertilizer.[20]: 266  Most terrestrial ecosystems are nitrogen-limited in the short term making nitrogen cycling an important control on ecosystem production.[20]: 289  Over the long term, phosphorus availability can also be critical.[27]

Macronutrients which are required by all plants in large quantities include the primary nutrients (which are most limiting as they are used in largest amounts): Nitrogen, phosphorus, potassium.[28]: 231  Secondary major nutrients (less often limiting) include: Calcium, magnesium, sulfur. Micronutrients required by all plants in small quantities include boron, chloride, copper, iron, manganese, molybdenum, zinc. Finally, there are also beneficial nutrients which may be required by certain plants or by plants under specific environmental conditions: aluminum, cobalt, iodine, nickel, selenium, silicon, sodium, vanadium.[28]: 231 

Until modern times, nitrogen fixation was the major source of nitrogen for ecosystems. Nitrogen-fixing bacteria either live symbiotically with plants or live freely in the soil. The energetic cost is high for plants that support nitrogen-fixing symbionts—as much as 25% of gross primary production when measured in controlled conditions. Many members of the legume plant family support nitrogen-fixing symbionts. Some cyanobacteria are also capable of nitrogen fixation. These are phototrophs, which carry out photosynthesis. Like other nitrogen-fixing bacteria, they can either be free-living or have symbiotic relationships with plants.[22]: 360  Other sources of nitrogen include acid deposition produced through the combustion of fossil fuels, ammonia gas which evaporates from agricultural fields which have had fertilizers applied to them, and dust.[20]: 270  Anthropogenic nitrogen inputs account for about 80% of all nitrogen fluxes in ecosystems.[20]: 270 

When plant tissues are shed or are eaten, the nitrogen in those tissues becomes available to animals and microbes. Microbial decomposition releases nitrogen compounds from dead organic matter in the soil, where plants, fungi, and bacteria compete for it. Some soil bacteria use organic nitrogen-containing compounds as a source of carbon, and release ammonium ions into the soil. This process is known as nitrogen mineralization. Others convert ammonium to nitrite and nitrate ions, a process known as nitrification. Nitric oxide and nitrous oxide are also produced during nitrification.[20]: 277  Under nitrogen-rich and oxygen-poor conditions, nitrates and nitrites are converted to nitrogen gas, a process known as denitrification.[20]: 281 

Mycorrhizal fungi which are symbiotic with plant roots, use carbohydrates supplied by the plants and in return transfer phosphorus and nitrogen compounds back to the plant roots.[29][30] This is an important pathway of organic nitrogen transfer from dead organic matter to plants. This mechanism may contribute to more than 70 Tg of annually assimilated plant nitrogen, thereby playing a critical role in global nutrient cycling and ecosystem function.[30]

Phosphorus enters ecosystems through weathering. As ecosystems age this supply diminishes, making phosphorus-limitation more common in older landscapes (especially in the tropics).[20]: 287–290  Calcium and sulfur are also produced by weathering, but acid deposition is an important source of sulfur in many ecosystems. Although magnesium and manganese are produced by weathering, exchanges between soil organic matter and living cells account for a significant portion of ecosystem fluxes. Potassium is primarily cycled between living cells and soil organic matter.[20]: 291 

Function and biodiversity

Main article: Biodiversity
See also: Ecosystem diversity
Loch Lomond in Scotland forms a relatively isolated ecosystem. The fish community of this lake has remained stable over a long period until a number of introductions in the 1970s restructured its food web.[31]
Spiny forest at Ifaty, Madagascar, featuring various Adansonia (baobab) species, Alluaudia procera (Madagascar ocotillo) and other vegetation

Biodiversity plays an important role in ecosystem functioning.[32]: 449–453  Ecosystem processes are driven by the species in an ecosystem, the nature of the individual species, and the relative abundance of organisms among these species. Ecosystem processes are the net effect of the actions of individual organisms as they interact with their environment. Ecological theory suggests that in order to coexist, species must have some level of limiting similarity—they must be different from one another in some fundamental way, otherwise, one species would competitively exclude the other.[33] Despite this, the cumulative effect of additional species in an ecosystem is not linear: additional species may enhance nitrogen retention, for example. However, beyond some level of species richness,[11]: 331  additional species may have little additive effect unless they differ substantially from species already present.[11]: 324  This is the case for example for exotic species.[11]: 321 

The addition (or loss) of species that are ecologically similar to those already present in an ecosystem tends to only have a small effect on ecosystem function. Ecologically distinct species, on the other hand, have a much larger effect. Similarly, dominant species have a large effect on ecosystem function, while rare species tend to have a small effect. Keystone species tend to have an effect on ecosystem function that is disproportionate to their abundance in an ecosystem.[11]: 324 

An ecosystem engineer is any organism that creates, significantly modifies, maintains or destroys a habitat.[34]

Study approaches

Ecosystem ecology

Main article: Ecosystem ecology
See also: Ecosystem model
A hydrothermal vent is an ecosystem on the ocean floor. (The scale bar is 1 m.)

Ecosystem ecology is the "study of the interactions between organisms and their environment as an integrated system".[2]: 458  The size of ecosystems can range up to ten orders of magnitude, from the surface layers of rocks to the surface of the planet.[4]: 6 

The Hubbard Brook Ecosystem Study started in 1963 to study the White Mountains in New Hampshire. It was the first successful attempt to study an entire watershed as an ecosystem. The study used stream chemistry as a means of monitoring ecosystem properties, and developed a detailed biogeochemical model of the ecosystem.[35] Long-term research at the site led to the discovery of acid rain in North America in 1972. Researchers documented the depletion of soil cations (especially calcium) over the next several decades.[36]

Ecosystems can be studied through a variety of approaches—theoretical studies, studies monitoring specific ecosystems over long periods of time, those that look at differences between ecosystems to elucidate how they work and direct manipulative experimentation.[37] Studies can be carried out at a variety of scales, ranging from whole-ecosystem studies to studying microcosms or mesocosms (simplified representations of ecosystems).[38] American ecologist Stephen R. Carpenter has argued that microcosm experiments can be "irrelevant and diversionary" if they are not carried out in conjunction with field studies done at the ecosystem scale. In such cases, microcosm experiments may fail to accurately predict ecosystem-level dynamics.[39]

Classifications

Further information: Ecosystem classification and Biogeoclimatic ecosystem classification

Biomes are general classes or categories of ecosystems.[4]: 14  However, there is no clear distinction between biomes and ecosystems.[40] Biomes are always defined at a very general level. Ecosystems can be described at levels that range from very general (in which case the names are sometimes the same as those of biomes) to very specific, such as "wet coastal needle-leafed forests".

Biomes vary due to global variations in climate. Biomes are often defined by their structure: at a general level, for example, tropical forests, temperate grasslands, and arctic tundra.[4]: 14  There can be any degree of subcategories among ecosystem types that comprise a biome, e.g., needle-leafed boreal forests or wet tropical forests. Although ecosystems are most commonly categorized by their structure and geography, there are also other ways to categorize and classify ecosystems such as by their level of human impact (see anthropogenic biome), or by their integration with social processes or technological processes or their novelty (e.g. novel ecosystem). Each of these taxonomies of ecosystems tends to emphasize different structural or functional properties.[41] None of these is the "best" classification.

Ecosystem classifications are specific kinds of ecological classifications that consider all four elements of the definition of ecosystems: a biotic component, an abiotic complex, the interactions between and within them, and the physical space they occupy.[41] Different approaches to ecological classifications have been developed in terrestrial, freshwater and marine disciplines, and a function-based typology has been proposed to leverage the strengths of these different approaches into a unified system.[42]

Human interactions with ecosystems

Human activities are important in almost all ecosystems. Although humans exist and operate within ecosystems, their cumulative effects are large enough to influence external factors like climate.[4]: 14 

Ecosystem goods and services

The High Peaks Wilderness Area in the 6,000,000-acre (2,400,000 ha) Adirondack Park is an example of a diverse ecosystem.
Main articles: Ecosystem services and Ecological goods and services
See also: Ecosystem valuation and Ecological yield

Ecosystems provide a variety of goods and services upon which people depend.[43] Ecosystem goods include the "tangible, material products" of ecosystem processes such as water, food, fuel, construction material, and medicinal plants.[44][45] They also include less tangible items like tourism and recreation, and genes from wild plants and animals that can be used to improve domestic species.[43]

Ecosystem services, on the other hand, are generally "improvements in the condition or location of things of value".[45] These include things like the maintenance of hydrological cycles, cleaning air and water, the maintenance of oxygen in the atmosphere, crop pollination and even things like beauty, inspiration and opportunities for research.[43] While material from the ecosystem had traditionally been recognized as being the basis for things of economic value, ecosystem services tend to be taken for granted.[45]

The Millennium Ecosystem Assessment is an international synthesis by over 1000 of the world's leading biological scientists that analyzes the state of the Earth's ecosystems and provides summaries and guidelines for decision-makers. The report identified four major categories of ecosystem services: provisioning, regulating, cultural and supporting services.[46] It concludes that human activity is having a significant and escalating impact on the biodiversity of the world ecosystems, reducing both their resilience and biocapacity. The report refers to natural systems as humanity's "life-support system", providing essential ecosystem services. The assessment measures 24 ecosystem services and concludes that only four have shown improvement over the last 50 years, 15 are in serious decline, and five are in a precarious condition.[46]: 6–19 

The Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES) is an intergovernmental organization established to improve the interface between science and policy on issues of biodiversity and ecosystem services.[47][48] It is intended to serve a similar role to the Intergovernmental Panel on Climate Change.[49]

Ecosystem services are limited and also threatened by human activities.[50] To help inform decision-makers, many ecosystem services are being assigned economic values, often based on the cost of replacement with anthropogenic alternatives. The ongoing challenge of prescribing economic value to nature, for example through biodiversity banking, is prompting transdisciplinary shifts in how we recognize and manage the environment, social responsibility, business opportunities, and our future as a species.[50]

Degradation and decline

See also: Ecosystem collapse, Biodiversity loss, and Effects of climate change on biomes

As human population and per capita consumption grow, so do the resource demands imposed on ecosystems and the effects of the human ecological footprint. Natural resources are vulnerable and limited. The environmental impacts of anthropogenic actions are becoming more apparent. Problems for all ecosystems include: environmental pollution, climate change and biodiversity loss. For terrestrial ecosystems further threats include air pollution, soil degradation, and deforestation. For aquatic ecosystems threats also include unsustainable exploitation of marine resources (for example overfishing), marine pollution, microplastics pollution, the effects of climate change on oceans (e.g. warming and acidification), and building on coastal areas.[51]

Many ecosystems become degraded through human impacts, such as soil loss, air and water pollution, habitat fragmentation, water diversion, fire suppression, and introduced species and invasive species.[52]: 437 

These threats can lead to abrupt transformation of the ecosystem or to gradual disruption of biotic processes and degradation of abiotic conditions of the ecosystem. Once the original ecosystem has lost its defining features, it is considered collapsed (see also IUCN Red List of Ecosystems).[53] Ecosystem collapse could be reversible and in this way differs from species extinction.[54] Quantitative assessments of the risk of collapse are used as measures of conservation status and trends.

Management

Main articles: Ecosystem management, Ecosystem-based management, and Ecosystem approach

When natural resource management is applied to whole ecosystems, rather than single species, it is termed ecosystem management.[55] Although definitions of ecosystem management abound, there is a common set of principles which underlie these definitions: A fundamental principle is the long-term sustainability of the production of goods and services by the ecosystem;[52] "intergenerational sustainability [is] a precondition for management, not an afterthought".[43] While ecosystem management can be used as part of a plan for wilderness conservation, it can also be used in intensively managed ecosystems[43] (see, for example, agroecosystem and close to nature forestry).

Restoration and sustainable development

See also: Restoration ecology

Integrated conservation and development projects (ICDPs) aim to address conservation and human livelihood (sustainable development) concerns in developing countries together, rather than separately as was often done in the past.[52]: 445 

See also

Types

The following articles are types of ecosystems for particular types of regions or zones:

Ecosystems grouped by condition

Instances

Main category: Ecosystems by region

Ecosystem instances in specific regions of the world:

References

  1. ^ Hatcher, Bruce Gordon (1990). "Coral reef primary productivity. A hierarchy of pattern and process". Trends in Ecology and Evolution. 5 (5): 149–155. doi:10.1016/0169-5347(90)90221-X. PMID 21232343.
  2. ^ a b c d e Chapin, F. Stuart III (2011). "Glossary". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  3. ^ a b c Tansley, A. G. (1935). "The Use and Abuse of Vegetational Concepts and Terms" (PDF). Ecology. 16 (3): 284–307. Bibcode:1935Ecol...16..284T. doi:10.2307/1930070. JSTOR 1930070. Archived from the original (PDF) on 2016-10-06.
  4. ^ a b c d e f g h i j Chapin, F. Stuart III (2011). "Chapter 1: The Ecosystem Concept". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  5. ^ Odum, Eugene P (1971). Fundamentals of Ecology (third ed.). New York: Saunders. ISBN 978-0-534-42066-6.
  6. ^ Willis, A.J. (1997). "The Ecosystem: An Evolving Concept Viewed Historically". Functional Ecology. 11 (2): 268–271. doi:10.1111/j.1365-2435.1997.00081.x.
  7. ^ Tansley, A.G. (1939). The British Islands and Their Vegetation. Cambridge University Press.
  8. ^ a b c Chapin, F. Stuart III (2011). "Chapter 5: Carbon Inputs to Ecosystems". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  9. ^ Chapin, F. Stuart III (2011). "Chapter 2: Earth's Climate System". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  10. ^ a b Chapin, F. Stuart III (2011). "Chapter 3: Geology, Soils, and Sediments". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  11. ^ a b c d e Chapin, F. Stuart III (2011). "Chapter 11: Species Effects on Ecosystem Processes". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  12. ^ Simberloff, Daniel; Martin, Jean-Louis; Genovesi, Piero; Maris, Virginie; Wardle, David A.; Aronson, James; Courchamp, Franck; Galil, Bella; García-Berthou, Emili (2013). "Impacts of biological invasions: what's what and the way forward". Trends in Ecology & Evolution. 28 (1): 58–66. doi:10.1016/j.tree.2012.07.013. hdl:10261/67376. ISSN 0169-5347. PMID 22889499.
  13. ^ "46.1A: Ecosystem Dynamics". Biology LibreTexts. 2018-07-17. Archived from the original on 2021-08-02. Retrieved 2021-08-02.Open access icon Text was copied from this source, which is available under a Creative Commons Attribution 4.0 International License Archived 2017-10-16 at the Wayback Machine.
  14. ^ a b c d Chapin, F. Stuart III (2011). "Chapter 6: Plant Carbon Budgets". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  15. ^ a b c Chapin, F. Stuart III (2011). "Chapter 10: Trophic Dynamics". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  16. ^ Yvon-Durocher, Gabriel; Caffrey, Jane M.; Cescatti, Alessandro; Dossena, Matteo; Giorgio, Paul del; Gasol, Josep M.; Montoya, José M.; Pumpanen, Jukka; Staehr, Peter A. (2012). "Reconciling the temperature dependence of respiration across timescales and ecosystem types". Nature. 487 (7408): 472–476. Bibcode:2012Natur.487..472Y. doi:10.1038/nature11205. ISSN 0028-0836. PMID 22722862. S2CID 4422427.
  17. ^ Lovett, Gary M.; Cole, Jonathan J.; Pace, Michael L. (2006). "Is Net Ecosystem Production Equal to Ecosystem Carbon Accumulation?". Ecosystems. 9 (1): 152–155. Bibcode:2006Ecosy...9..152L. doi:10.1007/s10021-005-0036-3. ISSN 1435-0629. S2CID 5890190.
  18. ^ Briand, F.; Cohen, J.E. (19 January 1984). "Community food webs have scale-invariant structure". Nature. 307 (5948): 264–267. Bibcode:1984Natur.307..264B. doi:10.1038/307264a0. S2CID 4319708.
  19. ^ a b c d e f Chapin, F. Stuart III (2011). "Chapter 7: Decomposition and Ecosystem Carbon Budgets". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  20. ^ a b c d e f g h i j Chapin, F. Stuart III (2011). "Chapter 9: Nutrient cycling". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  21. ^ Ochoa-Hueso, R; Delgado-Baquerizo, M; King, PTA; Benham, M; Arca, V; Power, SA (February 2019). "Ecosystem type and resource quality are more important than global change drivers in regulating early stages of litter decomposition". Soil Biology and Biochemistry. 129: 144–152. doi:10.1016/j.soilbio.2018.11.009. hdl:10261/336676. S2CID 92606851.
  22. ^ a b c d e Chapin, F. Stuart III (2011). "Chapter 12: Temporal Dynamics". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  23. ^ Chapin, F. Stuart III; Kofinas, Gary P.; Folke, Carl; Chapin, Melissa C., eds. (2009). Principles of ecosystem stewardship: resilience-based natural resource management in a changing world (1st ed.). New York: Springer. ISBN 978-0-387-73033-2. OCLC 432702920.
  24. ^ Walker, Brian; Holling, C. S.; Carpenter, Stephen R.; Kinzig, Ann P. (2004). "Resilience, Adaptability and Transformability in Social-ecological Systems". Ecology and Society. 9 (2): art5. doi:10.5751/ES-00650-090205. hdl:10535/3282. ISSN 1708-3087. Archived from the original on 2019-05-17. Retrieved 2021-07-23.
  25. ^ Simonsen, S.H. "Applying Resilience Thinking" (PDF). Stockholm Resilience Centre. Archived (PDF) from the original on 2017-12-15.
  26. ^ Walter, K. M.; Zimov, S. A.; Chanton, J. P.; Verbyla, D.; Chapin, F. S. (2006). "Methane bubbling from Siberian thaw lakes as a positive feedback to climate warming" (PDF). Nature. 443 (7107): 71–75. Bibcode:2006Natur.443...71W. doi:10.1038/nature05040. ISSN 0028-0836. PMID 16957728. S2CID 4415304. Archived from the original (PDF) on Nov 23, 2011. Retrieved 2021-08-16.
  27. ^ Vitousek, P.; Porder, S. (2010). "Terrestrial phosphorus limitation: mechanisms, implications, and nitrogen–phosphorus interactions". Ecological Applications. 20 (1): 5–15. Bibcode:2010EcoAp..20....5V. doi:10.1890/08-0127.1. PMID 20349827.
  28. ^ a b Chapin, F. Stuart III (2011). "Chapter 8: Plant Nutrient Use". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  29. ^ Bolan, N.S. (1991). "A critical review on the role of mycorrhizal fungi in the uptake of phosphorus by plants". Plant and Soil. 134 (2): 189–207. Bibcode:1991PlSoi.134..189B. doi:10.1007/BF00012037. S2CID 44215263.
  30. ^ a b Hestrin, R.; Hammer, E.C.; Mueller, C.W. (2019). "Synergies between mycorrhizal fungi and soil microbial communities increase plant nitrogen acquisition". Commun Biol. 2: 233. doi:10.1038/s42003-019-0481-8. PMC 6588552. PMID 31263777.
  31. ^ Adams, C.E. (1994). "The fish community of Loch Lomond, Scotland: its history and rapidly changing status". Hydrobiologia. 290 (1–3): 91–102. doi:10.1007/BF00008956. S2CID 6894397.
  32. ^ Schulze, Ernst-Detlef; Erwin Beck; Klaus Müller-Hohenstein (2005). Plant Ecology. Berlin: Springer. ISBN 978-3-540-20833-4.
  33. ^ Schoener, Thomas W. (2009). "Ecological Niche". In Simon A. Levin (ed.). The Princeton Guide to Ecology. Princeton: Princeton University Press. pp. 2–13. ISBN 978-0-691-12839-9.
  34. ^ Jones, Clive G.; Lawton, John H.; Shachak, Moshe (1994). "Organisms as Ecosystem Engineers". Oikos. 69 (3): 373–386. Bibcode:1994Oikos..69..373J. doi:10.2307/3545850. ISSN 0030-1299. JSTOR 3545850.
  35. ^ Lindenmayer, David B.; Gene E. Likens (2010). "The Problematic, the Effective and the Ugly – Some Case Studies". Effective Ecological Monitoring. Collingwood, Australia: CSIRO Publishing. pp. 87–145. ISBN 978-1-84971-145-6.
  36. ^ Likens, Gene E. (2004). "Some perspectives on long-term biogeochemical research from the Hubbard Brook Ecosystem Study" (PDF). Ecology. 85 (9): 2355–2362. Bibcode:2004Ecol...85.2355L. doi:10.1890/03-0243. JSTOR 3450233. Archived from the original (PDF) on 2013-05-01.
  37. ^ Carpenter, Stephen R.; Jonathan J. Cole; Timothy E. Essington; James R. Hodgson; Jeffrey N. Houser; James F. Kitchell; Michael L. Pace (1998). "Evaluating Alternative Explanations in Ecosystem Experiments". Ecosystems. 1 (4): 335–344. Bibcode:1998Ecosy...1..335C. doi:10.1007/s100219900025. S2CID 33559404.
  38. ^ Schindler, David W. (1998). "Replication versus Realism: The Need for Ecosystem-Scale Experiments". Ecosystems. 1 (4): 323–334. doi:10.1007/s100219900026. JSTOR 3658915. S2CID 45418039.
  39. ^ Carpenter, Stephen R. (1996). "Microcosm Experiments have Limited Relevance for Community and Ecosystem Ecology". Ecology. 77 (3): 677–680. Bibcode:1996Ecol...77..677C. doi:10.2307/2265490. JSTOR 2265490.
  40. ^ "Differences Between the Grassland & the Tundra". Sciencing. Archived from the original on 2021-07-16. Retrieved 2021-07-16.
  41. ^ a b Keith, D.A.; Ferrer-Paris, J.R.; Nicholson, E.; Kingsford, R.T., eds. (2020). The IUCN Global Ecosystem Typology 2.0: Descriptive profiles for biomes and ecosystem functional groups. Gland, Switzerland: IUCN. doi:10.2305/IUCN.CH.2020.13.en. ISBN 978-2-8317-2077-7. S2CID 241360441.
  42. ^ Keith, David A.; Ferrer-Paris, José R.; Nicholson, Emily; Bishop, Melanie J.; Polidoro, Beth A.; Ramirez-Llodra, Eva; Tozer, Mark G.; Nel, Jeanne L.; Mac Nally, Ralph; Gregr, Edward J.; Watermeyer, Kate E.; Essl, Franz; Faber-Langendoen, Don; Franklin, Janet; Lehmann, Caroline E. R.; Etter, Andrés; Roux, Dirk J.; Stark, Jonathan S.; Rowland, Jessica A.; Brummitt, Neil A.; Fernandez-Arcaya, Ulla C.; Suthers, Iain M.; Wiser, Susan K.; Donohue, Ian; Jackson, Leland J.; Pennington, R. Toby; Iliffe, Thomas M.; Gerovasileiou, Vasilis; Giller, Paul; Robson, Belinda J.; Pettorelli, Nathalie; Andrade, Angela; Lindgaard, Arild; Tahvanainen, Teemu; Terauds, Aleks; Chadwick, Michael A.; Murray, Nicholas J.; Moat, Justin; Pliscoff, Patricio; Zager, Irene; Kingsford, Richard T. (12 October 2022). "A function-based typology for Earth's ecosystems". Nature. 610 (7932): 513–518. Bibcode:2022Natur.610..513K. doi:10.1038/s41586-022-05318-4. PMC 9581774. PMID 36224387.
  43. ^ a b c d e Christensen, Norman L.; Bartuska, Ann M.; Brown, James H.; Carpenter, Stephen; D'Antonio, Carla; Francis, Robert; Franklin, Jerry F.; MacMahon, James A.; Noss, Reed F.; Parsons, David J.; Peterson, Charles H.; Turner, Monica G.; Woodmansee, Robert G. (1996). "The Report of the Ecological Society of America Committee on the Scientific Basis for Ecosystem Management". Ecological Applications. 6 (3): 665–691. Bibcode:1996EcoAp...6..665C. CiteSeerX 10.1.1.404.4909. doi:10.2307/2269460. JSTOR 2269460. S2CID 53461068.
  44. ^ "Ecosystem Goods and Services" (PDF). Archived (PDF) from the original on 2009-11-10.
  45. ^ a b c Brown, Thomas C.; John C. Bergstrom; John B. Loomis (2007). "Defining, valuing and providing ecosystem goods and services" (PDF). Natural Resources Journal. 47 (2): 329–376. Archived from the original (PDF) on 2013-05-25.
  46. ^ a b "Millennium Ecosystem Assessment". 2005. Archived from the original on 2011-05-24. Retrieved 10 November 2021.
  47. ^ "IPBES". Archived from the original on 27 June 2019. Retrieved 28 June 2019.
  48. ^ Díaz, Sandra; Demissew, Sebsebe; Carabias, Julia; Joly, Carlos; Lonsdale, Mark; Ash, Neville; Larigauderie, Anne; Adhikari, Jay Ram; Arico, Salvatore; Báldi, András; Bartuska, Ann (2015). "The IPBES Conceptual Framework — connecting nature and people". Current Opinion in Environmental Sustainability. 14: 1–16. Bibcode:2015COES...14....1D. doi:10.1016/j.cosust.2014.11.002. hdl:11336/56765. S2CID 14000233.
  49. ^ "Biodiversity crisis is worse than climate change, experts say". ScienceDaily. January 20, 2012. Archived from the original on December 29, 2021. Retrieved September 11, 2019.
  50. ^ a b Ceccato, Pietro; Fernandes, Katia; Ruiz, Daniel; Allis, Erica (17 June 2014). "Climate and environmental monitoring for decision making". Earth Perspectives. 1 (1): 16. Bibcode:2014EarP....1...16C. doi:10.1186/2194-6434-1-16. S2CID 46200068.
  51. ^ Alexander, David E. (1 May 1999). Encyclopedia of Environmental Science. Springer. ISBN 978-0-412-74050-3.
  52. ^ a b c Chapin, F. Stuart III (2011). "Chapter 15: Managing and Sustaining Ecosystems". Principles of terrestrial ecosystem ecology. P. A. Matson, Peter Morrison Vitousek, Melissa C. Chapin (2nd ed.). New York: Springer. ISBN 978-1-4419-9504-9. OCLC 755081405.
  53. ^ Keith, DA; Rodríguez, J.P.; Rodríguez-Clark, K.M.; Aapala, K.; Alonso, A.; Asmussen, M.; Bachman, S.; Bassett, A.; Barrow, E.G.; Benson, J.S.; Bishop, M.J.; Bonifacio, R.; Brooks, T.M.; Burgman, M.A.; Comer, P.; Comín, F.A.; Essl, F.; Faber-Langendoen, D.; Fairweather, P.G.; Holdaway, R.J.; Jennings, M.; Kingsford, R.T.; Lester, R.E.; Mac Nally, R.; McCarthy, M.A.; Moat, J.; Nicholson, E.; Oliveira-Miranda, M.A.; Pisanu, P.; Poulin, B.; Riecken, U.; Spalding, M.D.; Zambrano-Martínez, S. (2013). "Scientific Foundations for an IUCN Red List of Ecosystems". PLOS ONE. 8 (5): e62111. Bibcode:2013PLoSO...862111K. doi:10.1371/journal.pone.0062111. PMC 3648534. PMID 23667454.
  54. ^ Boitani, Luigi; Mace, Georgina M.; Rondinini, Carlo (2014). "Challenging the Scientific Foundations for an IUCN Red List of Ecosystems" (PDF). Conservation Letters. 8 (2): 125–131. doi:10.1111/conl.12111. hdl:11573/624610. S2CID 62790495. Archived (PDF) from the original on 2018-07-22. Retrieved 2021-01-06.Open access icon
  55. ^ Grumbine, R. Edward (1994). "What is ecosystem management?" (PDF). Conservation Biology. 8 (1): 27–38. Bibcode:1994ConBi...8...27G. doi:10.1046/j.1523-1739.1994.08010027.x. Archived from the original (PDF) on 2013-05-02.
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