Wikipedia

Ecosystem service

(Redirected from Ecological services)

Ecosystem services are the various benefits that humans derive from healthy ecosystems. These ecosystems, when functioning well, offer such things as provision of food, natural pollination of crops, clean air and water, decomposition of wastes, or flood control. Ecosystem services are grouped into four broad categories of services. There are provisioning services, such as the production of food and water. Regulating services, such as the control of climate and disease. Supporting services, such as nutrient cycles and oxygen production. And finally there are cultural services, such as spiritual and recreational benefits.[1] Evaluations of ecosystem services may include assigning an economic value to them.

An example of an ecosystem service is pollination, here by a honey bee on avocado crop.

For example, estuarine and coastal ecosystems are marine ecosystems that perform the four categories of ecosystem services in several ways. Firstly, their provisioning services include marine resources and genetic resources. Secondly, their supporting services include nutrient cycling and primary production. Thirdly, their regulating services include carbon sequestration (which helps with climate change mitigation) and flood control. Lastly, their cultural services include recreation and tourism.

The Millennium Ecosystem Assessment (MA) in the early 2000s has made this concept better known.[2]

Definition

edit

Ecosystem services or eco-services are defined as the goods and services provided by ecosystems to humans.[3] Per the 2006 Millennium Ecosystem Assessment (MA), ecosystem services are "the benefits people obtain from ecosystems". The MA also delineated the four categories of ecosystem services into provisioning, regulating, supporting, and cultural.[2]

By 2010, there had evolved various working definitions and descriptions of ecosystem services in the literature.[4] To prevent double-counting in ecosystem services audits, for instance, The Economics of Ecosystems and Biodiversity (TEEB) replaced "Supporting Services" in the MA with "Habitat Services" and "ecosystem functions", defined as "a subset of the interactions between ecosystem structure and processes that underpin the capacity of an ecosystem to provide goods and services".[5]

While Gretchen Daily's original definition distinguished between ecosystem goods and ecosystem services, Robert Costanza and colleagues' later work and that of the Millennium Ecosystem Assessment lumped all of these together as ecosystem services.[6][7]

Categories

edit
 
Four categories of ecosystem services

Four different types of ecosystem services have been distinguished by the scientific body: regulating services, provisioning services, cultural services and supporting services. An ecosystem does not necessarily offer all four types of services simultaneously; but given the intricate nature of any ecosystem, it is usually assumed that humans benefit from a combination of these services. The services offered by diverse types of ecosystems (forests, seas, coral reefs, mangroves, etc.) differ in nature and in consequence. In fact, some services directly affect the livelihood of neighboring human populations (such as fresh water, food or aesthetic value, etc.) while other services affect general environmental conditions by which humans are indirectly impacted (such as climate change, erosion regulation or natural hazard regulation, etc.).[8]

The Millennium Ecosystem Assessment report 2005 defined ecosystem services as benefits people obtain from ecosystems and distinguishes four categories of ecosystem services, where the so-called supporting services are regarded as the basis for the services of the other three categories.[9]

Provisioning services

edit

Provisioning services consist of all "the products obtained from ecosystems". The following services are also known as ecosystem goods:[10]

  • food (including seafood and game), crops, wild foods, and spices
  • raw materials (including lumber, skins, fuelwood, organic matter, fodder, and fertilizer)
  • genetic resources (including crop improvement genes, and health care)
  • biogenic minerals
  • medicinal resources (including pharmaceuticals, chemical models, and test and assay organisms)
  • energy (hydropower, biomass fuels)
  • ornamental resources (including fashion, handicrafts, jewelry, pets, worship, decoration, and souvenirs like furs, feathers, ivory, orchids, butterflies, aquarium fish, shells, etc.)
 
Social forestry in Andhra Pradesh, India, providing fuel, soil protection, shade, and even well-being to travelers.

Forests and forest management produce a large type and variety of timber products, including roundwood, sawnwood, panels, and engineered wood, e.g., cross-laminated timber, as well as pulp and paper.[11] Besides the production of timber, forestry activities may also result in products that undergo little processing, such as fire wood, charcoal, wood chips and roundwood used in an unprocessed form.[12] Global production and trade of all major wood-based products recorded their highest ever values in 2018.[13] Production, imports and exports of roundwood, sawnwood, wood-based panels, wood pulp, wood charcoal and pellets reached[14] their maximum quantities since 1947 when FAO started reporting global forest product statistics.[13] In 2018, growth in production of the main wood-based product groups ranged from 1 percent (woodbased panels) to 5 percent (industrial roundwood).[13] The fastest growth occurred in the Asia-Pacific, Northern American and European regions, likely due to positive economic growth in these areas.[13] Over 40% of the territory in the European Union is covered by forests. This region has grown via afforestation by roughly 0.4% year in recent decades. In the European Union, just 60% of the yearly forest growth is harvested.[15][16][17]

Forests also provide non-wood forest products, including fodder, aromatic and medicinal plants, and wild foods. Worldwide, around 1 billion people depend to some extent on wild foods such as wild meat, edible insects, edible plant products, mushrooms and fish, which often contain high levels of key micronutrients.[14] The value of forest foods as a nutritional resource is not limited to low- and middle-income countries; more than 100 million people in the European Union (EU) regularly consume wild food.[14] Some 2.4 billion people – in both urban and rural settings – use wood-based energy for cooking.[14]

Regulating services

edit
 
Upland bog in Wales, forming the official source of the River Severn. Healthy bogs sequester carbon, hold back water thereby reducing flood risk, and supply cleaned water better than degraded habitats do.

Regulating services are the "benefits obtained from the regulation of ecosystem processes".[18] These include:

Water purification

edit

An example for water purification as an ecosystem service is as follows: In New York City, where the quality of drinking water had fallen below standards required by the U.S. Environmental Protection Agency (EPA), authorities opted to restore the polluted Catskill Watershed that had previously provided the city with the ecosystem service of water purification. Once the input of sewage and pesticides to the watershed area was reduced, natural abiotic processes such as soil absorption and filtration of chemicals, together with biotic recycling via root systems and soil microorganisms, water quality improved to levels that met government standards. The cost of this investment in natural capital was estimated at $1–1.5 billion, which contrasted dramatically with the estimated $6–8 billion cost of constructing a water filtration plant plus the $300 million annual running costs.[20]

Pollination

edit

Pollination of crops by bees is required for 15–30% of U.S. food production; most large-scale farmers import non-native honey bees to provide this service. A 2005 study[21] reported that in California's agricultural region, it was found that wild bees alone could provide partial or complete pollination services or enhance the services provided by honey bees through behavioral interactions. However, intensified agricultural practices can quickly erode pollination services through the loss of species. The remaining species are unable to compensate this. The results of this study also indicate that the proportion of chaparral and oak-woodland habitat available for wild bees within 1–2 km of a farm can stabilize and enhance the provision of pollination services. The presence of such ecosystem elements functions almost like an insurance policy for farmers.

Buffer zones

edit
Main article: Coastal management

Coastal and estuarine ecosystems act as buffer zones against natural hazards and environmental disturbances, such as floods, cyclones, tidal surges and storms. The role they play is to "[absorb] a portion of the impact and thus [lessen] its effect on the land".[22] Wetlands (which include saltwater swamps, salt marshes, ...) and the vegetation it supports – trees, root mats, etc. – retain large amounts of water (surface water, snowmelt, rain, groundwater) and then slowly releases them back, decreasing the likeliness of floods.[23] Mangrove forests protect coastal shorelines from tidal erosion or erosion by currents; a process that was studied after the 1999 cyclone that hit India. Villages that were surrounded with mangrove forests encountered less damages than other villages that were not protected by mangroves.[24]

Supporting services

edit

Supporting services are the services that allow for the other ecosystem services to be present. They have indirect impacts on humans that last over a long period of time. Several services can be considered as being both supporting services and regulating/cultural/provisioning services.[25]

Supporting services include for example nutrient cycling, primary production, soil formation, habitat provision. These services make it possible for the ecosystems to continue providing services such as food supply, flood regulation, and water purification.

Nutrient cycling

edit
 
Detritivores like this dung beetle help to turn animal wastes into organic material that can be reused by primary producers.

Nutrient cycling is the movement of nutrients through an ecosystem by biotic and abiotic processes.[26] The ocean is a vast storage pool for these nutrients, such as carbon, nitrogen and phosphorus. The nutrients are absorbed by the basic organisms of the marine food web and are thus transferred from one organism to the other and from one ecosystem to the other. Nutrients are recycled through the life cycle of organisms as they die and decompose, releasing the nutrients into the neighboring environment. "The service of nutrient cycling eventually impacts all other ecosystem services as all living things require a constant supply of nutrients to survive".[22]

Primary production

edit

Primary production refers to the production of organic matter, i.e., chemically bound energy, through processes such as photosynthesis and chemosynthesis. The organic matter produced by primary producers forms the basis of all food webs. Further, it generates oxygen (O2), a molecule necessary to sustain animals and humans.[27][28][29][30] On average, a human consumes about 550 liter of oxygen per day, whereas plants produce 1,5 liter of oxygen per 10 grams of growth.[31]

Cultural services

edit

Cultural services relate to the non-material world, as they benefit the benefit recreational, aesthetic, cognitive and spiritual activities, which are not easily quantifiable in monetary terms.[32] They include:

  • cultural (including use of nature as motif in books, film, painting, folklore, national symbols, advertising, etc.)
  • spiritual and historical (including use of nature for religious or heritage value or natural)
  • recreational experiences (including ecotourism, outdoor sports, and recreation)
  • science and education (including use of natural systems for school excursions, and scientific discovery)
  • therapeutic (including eco-therapy, social forestry and animal assisted therapy)

As of 2012, there was a discussion as to how the concept of cultural ecosystem services could be operationalized, how landscape aesthetics, cultural heritage, outdoor recreation, and spiritual significance to define can fit into the ecosystem services approach.[33] who vote for models that explicitly link ecological structures and functions with cultural values and benefits. Likewise, there has been a fundamental critique of the concept of cultural ecosystem services that builds on three arguments:[34]

  1. Pivotal cultural values attaching to the natural/cultivated environment rely on an area's unique character that cannot be addressed by methods that use universal scientific parameters to determine ecological structures and functions.
  2. If a natural/cultivated environment has symbolic meanings and cultural values the object of these values are not ecosystems but shaped phenomena like mountains, lakes, forests, and, mainly, symbolic landscapes.[35]
  3. Cultural values do result not from properties produced by ecosystems but are the product of a specific way of seeing within the given cultural framework of symbolic experience.[36]

The Common International Classification of Ecosystem Services (CICES) is a classification scheme developed to accounting systems (like National counts etc.), in order to avoid double-counting of Supporting Services with others Provisioning and Regulating Services.[37]

Recreation and tourism

edit

Sea sports are very popular among coastal populations: surfing, snorkeling, whale watching, kayaking, recreational fishing ... a lot of tourists also travel to resorts close to the sea or rivers or lakes to be able to experience these activities, and relax near the water.[38] The United Nations Sustainable Development Goal 14 also has targets aimed at enhancing the use of ecosystem services for sustainable tourism especially in Small Island Developing States.[39]

Estuarine and coastal ecosystem services

edit

Estuarine and marine coastal ecosystems are both marine ecosystems. Together, these ecosystems perform the four categories of ecosystem services in a variety of ways: The provisioning services include forest products, marine products, fresh water, raw materials, biochemical and genetic resources. Regulating services include carbon sequestration (contributing to climate change mitigation) as well as waste treatment and disease regulation and buffer zones. Supporting services of coastal ecosystems include nutrient cycling, biologically mediated habitats and primary production. Cultural services of coastal ecosystems include inspirational aspects, recreation and tourism, science and education.

Coasts and their adjacent areas on and offshore are an important part of a local ecosystem. The mixture of fresh water and salt water (brackish water) in estuaries provides many nutrients for marine life. Salt marshes, mangroves and beaches also support a diversity of plants, animals and insects crucial to the food chain. The high level of biodiversity creates a high level of biological activity, which has attracted human activity for thousands of years. Coasts also create essential material for organisms to live by, including estuaries, wetland, seagrass, coral reefs, and mangroves. Coasts provide habitats for migratory birds, sea turtles, marine mammals, and coral reefs.[40]

Economics

edit
Further information: Environmental economics, Ecological economics, Economic analysis of climate change, and The Economics of Ecosystems and Biodiversity
 
Sustainable urban drainage pond near housing in Scotland. The filtering and cleaning of surface and waste water by natural vegetation is a form of ecosystem service.

There are questions regarding the environmental and economic values of ecosystem services.[41] Some people may be unaware of the environment in general and humanity's interrelatedness with the natural environment, which may cause misconceptions. Although environmental awareness is rapidly improving in our contemporary world, ecosystem capital and its flow are still poorly understood, threats continue to impose, and we suffer from the so-called 'tragedy of the commons'.[42] Many efforts to inform decision-makers of current versus future costs and benefits now involve organizing and translating scientific knowledge to economics, which articulate the consequences of our choices in comparable units of impact on human well-being.[7] An especially challenging aspect of this process is that interpreting ecological information collected from one spatial-temporal scale does not necessarily mean it can be applied at another; understanding the dynamics of ecological processes relative to ecosystem services is essential in aiding economic decisions.[43] Weighting factors such as a service's irreplaceability or bundled services can also allocate economic value such that goal attainment becomes more efficient.

The economic valuation of ecosystem services also involves social communication and information, areas that remain particularly challenging and are the focus of many researchers.[44] In general, the idea is that although individuals make decisions for any variety of reasons, trends reveal the aggregated preferences of a society, from which the economic value of services can be inferred and assigned. The six major methods for valuing ecosystem services in monetary terms are:[45]

  • Avoided cost: Services allow society to avoid costs that would have been incurred in the absence of those services (e.g. waste treatment by wetland habitats avoids health costs)
  • Replacement cost: Services could be replaced with human-made systems (e.g. restoration of the Catskill Watershed cost less than the construction of a water purification plant)
  • Factor income: Services provide for the enhancement of incomes (e.g. improved water quality increases the commercial take of a fishery and improves the income of fishers)
  • Travel cost: Service demand may require travel, whose costs can reflect the implied value of the service (e.g. value of ecotourism experience is at least what a visitor is willing to pay to get there)
  • Hedonic pricing: Service demand may be reflected in the prices people will pay for associated goods (e.g. coastal housing prices exceed that of inland homes)
  • Contingent valuation: Service demand may be elicited by posing hypothetical scenarios that involve some valuation of alternatives (e.g. visitors willing to pay for increased access to national parks)

A peer-reviewed study published in 1997 estimated the value of the world's ecosystem services and natural capital to be between US$16 and $54 trillion per year, with an average of US$33 trillion per year.[46] However, Salles (2011) indicated 'The total value of biodiversity is infinite, so having debate about what is the total value of nature is actually pointless because we can't live without it'.[47]

As of 2012, many companies were not fully aware of the extent of their dependence and impact on ecosystems and the possible ramifications. Likewise, environmental management systems and environmental due diligence tools are more suited to handle "traditional" issues of pollution and natural resource consumption. Most focus on environmental impacts, not dependence. Several tools and methodologies can help the private sector value and assess ecosystem services, including Our Ecosystem,[48] the 2008 Corporate Ecosystem Services Review,[49] the Artificial Intelligence for Environment & Sustainability (ARIES) project from 2007,[50] the Natural Value Initiative (2012)[51] and InVEST (Integrated Valuation of Ecosystem Services & Tradeoffs, 2012)[52]

To provide an example of a cost comparison: The land of the United States Department of Defense is said to provide substantial ecosystem services to local communities, including benefits to carbon storage, resiliency to climate, and endangered species habitat.[53][54] As of 2020, the Eglin Air Force Base is said to provide about $110 million in ecosystem services per year, $40 million more than if no base was present.[53]

Payments

edit
This section is an excerpt from Payment for ecosystem services.[edit]
 
Payments for Ecosystem Services (PES)
Payments for ecosystem services (PES), also known as payments for environmental services (or benefits), are incentives offered to farmers or landowners in exchange for managing their land to provide some sort of ecological service. They have been defined as "a transparent system for the additional provision of environmental services through conditional payments to voluntary providers".[55] These programmes promote the conservation of natural resources in the marketplace.

Management and policy

edit
 
Ecosystem services in urban and rural areas

Although monetary pricing continues with respect to the valuation of ecosystem services, the challenges in policy implementation and management are significant and considerable. The administration of common pool resources has been a subject of extensive academic pursuit.[56][57][58][59][60] From defining the problems to finding solutions that can be applied in practical and sustainable ways, there is much to overcome. Considering options must balance present and future human needs, and decision-makers must frequently work from valid but incomplete information. Existing legal policies are often considered insufficient since they typically pertain to human health-based standards that are mismatched with necessary means to protect ecosystem health and services. In 2000, to improve the information available, the implementation of an Ecosystem Services Framework has been suggested (ESF[61]), which integrates the biophysical and socio-economic dimensions of protecting the environment and is designed to guide institutions through multidisciplinary information and jargon, helping to direct strategic choices.

As of 2005 Local to regional collective management efforts were considered appropriate for services like crop pollination or resources like water.[21][56] Another approach that has become increasingly popular during the 1990s is the marketing of ecosystem services protection. Payment and trading of services is an emerging worldwide small-scale solution where one can acquire credits for activities such as sponsoring the protection of carbon sequestration sources or the restoration of ecosystem service providers. In some cases, banks for handling such credits have been established and conservation companies have even gone public on stock exchanges, defining an evermore parallel link with economic endeavors and opportunities for tying into social perceptions.[7] However, crucial for implementation are clearly defined land rights, which are often lacking in many developing countries.[62] In particular, many forest-rich developing countries suffering deforestation experience conflict between different forest stakeholders.[62] In addition, concerns for such global transactions include inconsistent compensation for services or resources sacrificed elsewhere and misconceived warrants for irresponsible use. As of 2001, another approach focused on protecting ecosystem service biodiversity hotspots. Recognition that the conservation of many ecosystem services aligns with more traditional conservation goals (i.e. biodiversity) has led to the suggested merging of objectives for maximizing their mutual success. This may be particularly strategic when employing networks that permit the flow of services across landscapes, and might also facilitate securing the financial means to protect services through a diversification of investors.[63][64]

For example, as of 2013, there had been interest in the valuation of ecosystem services provided by shellfish production and restoration.[65] A keystone species, low in the food chain, bivalve shellfish such as oysters support a complex community of species by performing a number of functions essential to the diverse array of species that surround them. There is also increasing recognition that some shellfish species may impact or control many ecological processes; so much so that they are included on the list of "ecosystem engineers"—organisms that physically, biologically or chemically modify the environment around them in ways that influence the health of other organisms.[66] Many of the ecological functions and processes performed or affected by shellfish contribute to human well-being by providing a stream of valuable ecosystem services over time by filtering out particulate materials and potentially mitigating water quality issues by controlling excess nutrients in the water. As of 2018, the concept of ecosystem services had not been properly implemented into international and regional legislation yet.[67]

Notwithstanding, the United Nations Sustainable Development Goal 15 has a target to ensure the conservation, restoration, and sustainable use of ecosystem services.[68]

An estimated $125 trillion to $140 trillion is added to the economy each year by all ecosystem services.[69][70][71] However, many of these services are at risk due to climate and other anthropogenic impacts. Climate-driven shifts in biome ranges is expected to cause a 9% decline in ecosystem services on average at global scale by 2100[72]

Ecosystem-based adaptation (EbA)

edit
This section is an excerpt from Ecosystem-based adaptation.[edit]

Ecosystem-based adaptation (EBA or EbA) encompasses a broad set of approaches to adapt to climate change. They all involve the management of ecosystems and their services to reduce the vulnerability of human communities to the impacts of climate change. The Convention on Biological Diversity (CBD) defines EBA as "the use of biodiversity and ecosystem services as part of an overall adaptation strategy to help people to adapt to the adverse effects of climate change".[73][74]

EbA involves the conservation, sustainable management and restoration of ecosystems, such as forests, grasslands, wetlands, mangroves or coral reefs to reduce the harmful impacts of climate hazards including shifting patterns or levels of rainfall, changes in maximum and minimum temperatures, stronger storms, and increasingly variable climatic conditions. EbA measures can be implemented on their own or in combination with engineered approaches (such as the construction of water reservoirs or dykes), hybrid measures (such as artificial reefs) and approaches that strengthen the capacities of individuals and institutions to address climate risks (such as the introduction of early warning systems).

Land use change decisions

edit

Ecosystem services decisions require making complex choices at the intersection of ecology, technology, society, and the economy. The process of making ecosystem services decisions must consider the interaction of many types of information, honor all stakeholder viewpoints, including regulatory agencies, proposal proponents, decision makers, residents, NGOs, and measure the impacts on all four parts of the intersection. These decisions are usually spatial, always multi-objective, and based on uncertain data, models, and estimates. Often it is the combination of the best science combined with the stakeholder values, estimates and opinions that drive the process.[75]

One analytical study modeled the stakeholders as agents to support water resource management decisions in the Middle Rio Grande basin of New Mexico. This study focused on modeling the stakeholder inputs across a spatial decision, but ignored uncertainty.[76] Another study used Monte Carlo methods to exercise econometric models of landowner decisions in a study of the effects of land-use change. Here the stakeholder inputs were modeled as random effects to reflect the uncertainty.[77] A third study used a Bayesian decision support system to both model the uncertainty in the scientific information Bayes Nets and to assist collecting and fusing the input from stakeholders. This study was about siting wave energy devices off the Oregon Coast, but presents a general method for managing uncertain spatial science and stakeholder information in a decision making environment.[78] Remote sensing data and analyses can be used to assess the health and extent of land cover classes that provide ecosystem services, which aids in planning, management, monitoring of stakeholders' actions, and communication between stakeholders.[79]

In Baltic countries scientists, nature conservationists and local authorities are implementing integrated planning approach for grassland ecosystems.[80] They are developing an integrated planning tool based on GIS (geographic information system) technology and put online that will help for planners to choose the best grassland management solution for concrete grassland. It will look holistically at the processes in the countryside and help to find best grassland management solutions by taking into account both natural and socioeconomic factors of the particular site.[81]

History

edit

While the notion of human dependence on Earth's ecosystems reaches to the start of Homo sapiens' existence, the term 'natural capital' was first coined by E. F. Schumacher in 1973 in his book Small is Beautiful.[82] Recognition of how ecosystems could provide complex services to humankind date back to at least Plato (c. 400 BC) who understood that deforestation could lead to soil erosion and the drying of springs.[83][84] Modern ideas of ecosystem services probably began when Marsh challenged in 1864 the idea that Earth's natural resources are unbounded by pointing out changes in soil fertility in the Mediterranean.[85][page needed] It was not until the late 1940s that three key authors—Henry Fairfield Osborn, Jr,[86] William Vogt,[87] and Aldo Leopold[88]—promoted recognition of human dependence on the environment.

In 1956, Paul Sears drew attention to the critical role of the ecosystem in processing wastes and recycling nutrients.[89] In 1970, Paul Ehrlich and Rosa Weigert called attention to "ecological systems" in their environmental science textbook[90] and "the most subtle and dangerous threat to man's existence ... the potential destruction, by man's own activities, of those ecological systems upon which the very existence of the human species depends".

The term environmental services was introduced in a 1970 report of the Study of Critical Environmental Problems,[91] which listed services including insect pollination, fisheries, climate regulation and flood control. In following years, variations of the term were used, but eventually 'ecosystem services' became the standard in scientific literature.[92]

The ecosystem services concept has continued to expand and includes socio-economic and conservation objectives.[83]

See also

edit

References

edit
  1. ^ Millennium Ecosystem Assessment (2005). Ecosystems and human well-being : synthesis (PDF). Washington, DC: Island Press. ISBN 1-59726-040-1. Retrieved 7 August 2014.
  2. ^ a b Millennium Ecosystem Assessment (2005). Ecosystems and human well-being : synthesis (PDF). Washington, DC: Island Press. ISBN 1-59726-040-1. Retrieved 7 August 2014.
  3. ^ Austin, Troy (2009). "Estimating Ecosystem Services in Southern Ontario" (PDF). {{cite journal}}: Cite journal requires |journal= (help)
  4. ^ Ojea, Elena; Chiabai, Aline; Martin-Ortega, Julia (September 2010). Classifying Ecosystem Services for Economic Valuation: The case of forest water services (PDF). BIOCON Conference. hdl:10810/14215.
  5. ^ The Ecological and Economic Foundation Archived 3 December 2013 at the Wayback Machine, chapter 1, p.19, TEEB, 2010
  6. ^ 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 25 May 2013.
  7. ^ a b c Daily, Gretchen C.; Söderqvist, Tore; Aniyar, Sara; Arrow, Kenneth; Dasgupta, Partha; Ehrlich, Paul R.; Folke, Carl; Jansson, AnnMari; Jansson, Bengt-Owe; Kautsky, Nils; Levin, Simon; Lubchenco, Jane; Mäler, Karl-Göran; Simpson, David; Starrett, David; Tilman, David; Walker, Brian (21 July 2000). "The Value of Nature and the Nature of Value". Science. 289 (5478): 395–396. doi:10.1126/science.289.5478.395. PMID 10939949. S2CID 27639803.
  8. ^ Barbier, Edward B.; Hacker, Sally D.; Kennedy, Chris; Koch, Evamaria W.; Stier, Adrian C.; Silliman, Brian R. (May 2011). "The value of estuarine and coastal ecosystem services". Ecological Monographs. 81 (2): 169–193. Bibcode:2011EcoM...81..169B. doi:10.1890/10-1510.1. hdl:20.500.11919/920. S2CID 86155063.
  9. ^ "Tunza Eco-generation Eco-generation".
  10. ^ Walter V. Reid, H. A. (2005). Ecosystems and Human Well-Being - A Report of the Millennium Ecosystem Assessment. Washington DC: Millennium Ecosystem Assessment Board. Retrieved from http://www.millenniumassessment.org/documents/document.356.aspx.pdf
  11. ^ Global Forest Resources Assessment 2020 – Main report. Rome: FAO. 2020. doi:10.4060/ca9825en. ISBN 978-92-5-132974-0. S2CID 241774391.
  12. ^ Global Forest Resources Assessment 2020 – Key findings. FAO. 2020. doi:10.4060/ca8753en. ISBN 978-92-5-132581-0. S2CID 130116768.
  13. ^ a b c d Global forest products facts and figures 2018. FAO. 2019.
  14. ^ a b c d The State of the World's Forests 2020. Forests, biodiversity and people – In brief. Rome: FAO & UNEP. 2020. doi:10.4060/ca8985en. ISBN 978-92-5-132707-4. S2CID 241416114.
  15. ^ "What is an ecosystem service?". European Investment Bank. Retrieved 19 July 2023.
  16. ^ "The European Union and forests | Fact Sheets on the European Union | European Parliament". www.europarl.europa.eu. 31 March 2023. Retrieved 19 July 2023.
  17. ^ "Over 40% of the EU covered with forests". ec.europa.eu. Retrieved 19 July 2023.
  18. ^ "Millennium Ecosystem Assessment". www.millenniumassessment.org. Archived from the original on 24 February 2018. Retrieved 28 April 2018.
  19. ^ Basic Biology (2016). "Wetlands".
  20. ^ Chichilnisky, Graciela; Heal, Geoffrey (February 1998). "Economic returns from the biosphere". Nature. 391 (6668): 629–630. Bibcode:1998Natur.391..629C. doi:10.1038/35481. S2CID 4322093.
  21. ^ a b Kremen, Claire (May 2005). "Managing ecosystem services: what do we need to know about their ecology?: Ecology of ecosystem services". Ecology Letters. 8 (5): 468–479. doi:10.1111/j.1461-0248.2005.00751.x. PMID 21352450.
  22. ^ a b Molnar, Michelle; Clarke-Murray, Cathryn; Whitworth, John; Tam, Jordan (2009). "Marine and Coastal Ecosystem Services" (PDF). Archived from the original (PDF) on 3 March 2016. Retrieved 1 December 2014.
  23. ^ Campos C., Adolfo; Hernández, María E.; Moreno-Casasola, Patricia; Cejudo Espinosa, Eduardo; Robledo R., Alezandra; Infante Mata, Dulce (December 2011). "Soil water retention and carbon pools in tropical forested wetlands and marshes of the Gulf of Mexico". Hydrological Sciences Journal. 56 (8): 1388–1406. Bibcode:2011HydSJ..56.1388C. doi:10.1080/02626667.2011.629786. S2CID 85551159.
  24. ^ Badola, Ruchi; Hussain, S. A. (March 2005). "Valuing ecosystem functions: an empirical study on the storm protection function of Bhitarkanika mangrove ecosystem, India". Environmental Conservation. 32 (1): 85–92. Bibcode:2005EnvCo..32...85B. doi:10.1017/S0376892905001967. S2CID 54753792.
  25. ^ "Ecosystem Services". National Wildlife Federation. Retrieved 19 July 2021.
  26. ^ "Nutrient Cycles: Recycling in Ecosystems, The Carbon and Nitrogen Cycles – ScienceAid". ScienceAid. Retrieved 16 May 2018.
  27. ^ "ISBN1118506243 – Google zoeken". Retrieved 28 April 2018.
  28. ^ "Ecosystem Services". msu.edu. Archived from the original on 28 December 2017. Retrieved 28 April 2018.
  29. ^ "Oxygen and Human Requirements". www.geography.hunter.cuny.edu. Archived from the original on 22 October 2017. Retrieved 28 April 2018.
  30. ^ "BBC – GCSE Bitesize: Inhaled and exhaled air". bbc.co.uk. Archived from the original on 26 October 2017. Retrieved 28 April 2018.
  31. ^ New Scientist, June 2019[full citation needed]
  32. ^ "Cultural services". Food and Agriculture Organization of the United Nations. Retrieved 19 July 2021.
  33. ^ Daniel, T. C.; Muhar, A.; Arnberger, A.; Aznar, O.; Boyd, J. W.; Chan, K. M. A.; Costanza, R.; Elmqvist, T.; Flint, C. G.; Gobster, P. H.; Gret-Regamey, A.; Lave, R.; Muhar, S.; Penker, M.; Ribe, R. G.; Schauppenlehner, T.; Sikor, T.; Soloviy, I.; Spierenburg, M.; Taczanowska, K.; Tam, J.; von der Dunk, A. (5 June 2012). "Contributions of cultural services to the ecosystem services agenda". Proceedings of the National Academy of Sciences. 109 (23): 8812–8819. Bibcode:2012PNAS..109.8812D. doi:10.1073/pnas.1114773109. PMC 3384142. PMID 22615401.
  34. ^ Kirchhoff, Thomas (13 November 2012). "Pivotal cultural values of nature cannot be integrated into the ecosystem services framework". Proceedings of the National Academy of Sciences. 109 (46): E3146. Bibcode:2012PNAS..109E3146K. doi:10.1073/pnas.1212409109. PMC 3503173. PMID 23012476.
  35. ^ Cf. Cosgrove, D.E. 1984: Social Formation and Symbolic Landscape, London; Schama, S. 1995: Landscape and memory. New York; Kirchhoff, T./Trepl, L./Vicenzotti, V. 2012:What is landscape ecology? An analysis and evaluation of six different conceptions. Landscape Research iFirst.
  36. ^ Cf. Cosgrove, D.E. 1984: Social Formation and Symbolic Landscape, London; Schama, S. 1995: Landscape and memory. New York; Backhaus, G./Murungi, J. (eds.): Symbolic Landscapes. Dordrecht 2009.
  37. ^ https://cices.eu/[full citation needed]
  38. ^ Westcott, Morgan; Wendy Anderson, Eds (4 June 2021). "5.2 Recreation and Adventure Tourism in BC". {{cite journal}}: Cite journal requires |journal= (help)
  39. ^ "Goal 14 targets". UNDP. Archived from the original on 30 September 2020. Retrieved 24 September 2020.
  40. ^ US EPA, ORD (2 November 2017). "Coastal Waters". US EPA. Retrieved 4 May 2020.
  41. ^ Raudsepp-Hearne, Ciara; Peterson, Garry D.; Tengö, Maria; Bennett, Elena M.; Holland, Tim; Benessaiah, Karina; MacDonald, Graham K.; Pfeifer, Laura (September 2010). "Untangling the Environmentalist's Paradox: Why Is Human Well-being Increasing as Ecosystem Services Degrade?". BioScience. 60 (8): 576–589. doi:10.1525/bio.2010.60.8.4. S2CID 27270296.
  42. ^ Hardin, Garrett (13 December 1968). "The Tragedy of the Commons: The population problem has no technical solution; it requires a fundamental extension in morality". Science. 162 (3859): 1243–1248. Bibcode:1968Sci...162.1243H. doi:10.1126/science.162.3859.1243. PMID 17756331.
  43. ^ DeFries, Ruth S.; Foley, Jonathan A.; Asner, Gregory P. (June 2004). "Land-use choices: balancing human needs and ecosystem function". Frontiers in Ecology and the Environment. 2 (5): 249–257. doi:10.1890/1540-9295(2004)002[0249:LCBHNA]2.0.CO;2.
  44. ^ Górriz-Mifsud, Elena; Varela, Elsa; Piqué, Míriam; Prokofieva, Irina (February 2016). "Demand and supply of ecosystem services in a Mediterranean forest: Computing payment boundaries". Ecosystem Services. 17: 53–63. Bibcode:2016EcoSv..17...53G. doi:10.1016/j.ecoser.2015.11.006.
  45. ^ Farber, Stephen C.; Costanza, Robert; Wilson, Matthew A. (June 2002). "Economic and ecological concepts for valuing ecosystem services". Ecological Economics. 41 (3): 375–392. Bibcode:2002EcoEc..41..375F. doi:10.1016/S0921-8009(02)00088-5.
  46. ^ Costanza, Robert; d'Arge, Ralph; de Groot, Rudolf; Farber, Stephen; Grasso, Monica; Hannon, Bruce; Limburg, Karin; Naeem, Shahid; O'Neill, Robert V.; Paruelo, Jose; Raskin, Robert G.; Sutton, Paul; van den Belt, Marjan (May 1997). "The value of the world's ecosystem services and natural capital" (PDF). Nature. 387 (6630): 253–260. Bibcode:1997Natur.387..253C. doi:10.1038/387253a0. S2CID 672256. Archived from the original (PDF) on 22 September 2017. Retrieved 26 October 2021.
  47. ^ Salles, Jean-Michel (May 2011). "Valuing biodiversity and ecosystem services: Why put economic values on Nature?". Comptes Rendus Biologies. 334 (5–6): 469–482. doi:10.1016/j.crvi.2011.03.008. PMID 21640956.
  48. ^ "Our Ecosystem – Mapping & Data Sharing Software". Ecometrica. Archived from the original on 17 June 2013. Retrieved 9 July 2012.
  49. ^ Hanson, C, J Ranganathan, C Iceland, and J Finisdore. (2008) The Corporate Ecosystem Services Review (Version 1.0). World Resources Institute. "Ecosystem Services Review | World Resources Institute". Archived from the original on 1 April 2009. Retrieved 17 March 2009.
  50. ^ "ARIES :: ARtificial Intelligence for Environment & Sustainability". aries.integratedmodelling.org/. Archived from the original on 7 June 2012. Retrieved 9 July 2012.
  51. ^ "Welcome". Natural Value Initiative. Archived from the original on 16 May 2016. Retrieved 9 July 2012.
  52. ^ "Home". Natural Capital Project. Archived from the original on 28 June 2012. Retrieved 9 July 2012.
  53. ^ a b James Kagan, Mark Borsuk (18 September 2019). "Assessing Ecosystem Service Benefits from Military Installations". Nicholas Institute, Duke University. Retrieved 19 May 2020.
  54. ^ "RC18-1605 Project Overview. Value and Resiliency of Ecosystem Services on Department of Defense (DoD) Lands". www.serdp-estcp.org Pacific Northwest National Laboratory. 19 May 2020. Retrieved 19 May 2020.
  55. ^ Tacconi, L (2012). "Redefining payments for environmental services". Ecological Economics. 73 (1): 29–36. doi:10.1016/j.ecolecon.2011.09.028.
  56. ^ a b Ostrom, Elinor (1990). Governing the Commons: The Evolution of Institutions for Collective Action. Cambridge University Press. ISBN 978-0-521-40599-7.[page needed]
  57. ^ Dietz, Thomas; Ostrom, Elinor; Stern, Paul C. (12 December 2003). "The Struggle to Govern the Commons". Science. 302 (5652): 1907–1912. Bibcode:2003Sci...302.1907D. doi:10.1126/science.1091015. PMID 14671286. S2CID 2373413.
  58. ^ Pretty, Jules (12 December 2003). "Social Capital and the Collective Management of Resources". Science. 302 (5652): 1912–1914. Bibcode:2003Sci...302.1912P. doi:10.1126/science.1090847. hdl:10919/65915. PMID 14671287. S2CID 25070261.
  59. ^ Heikkila, Tanya (2004). "Institutional boundaries and common-pool resource management: A comparative analysis of water management programs in California". Journal of Policy Analysis and Management. 23 (1): 97–117. doi:10.1002/pam.10181.
  60. ^ Gibson, Clark C.; Williams, John T.; Ostrom, Elinor (February 2005). "Local Enforcement and Better Forests". World Development. 33 (2): 273–284. doi:10.1016/j.worlddev.2004.07.013. S2CID 13025667.
  61. ^ Daily, Gretchen C. (December 2000). "Management objectives for the protection of ecosystem services". Environmental Science & Policy. 3 (6): 333–339. Bibcode:2000ESPol...3..333D. CiteSeerX 10.1.1.463.824. doi:10.1016/S1462-9011(00)00102-7.
  62. ^ a b Jessica Brown and Neil Bird 2010. Costa Rica sustainable resource management: Successfully tackling tropical deforestation Archived 14 May 2011 at the Wayback Machine. London: Overseas Development Institute
  63. ^ Balvanera, Patricia; Daily, Gretchen C.; Ehrlich, Paul R.; Ricketts, Taylor H.; Bailey, Sallie-Anne; Kark, Salit; Kremen, Claire; Pereira, Henrique (16 March 2001). "Conserving Biodiversity and Ecosystem Services". Science. 291 (5511): 2047. doi:10.1126/science.291.5511.2047. PMID 11256386. S2CID 20296413.
  64. ^ Chan, Kai M. A.; Shaw, M. Rebecca; Cameron, David R.; Underwood, Emma C.; Daily, Gretchen C. (31 October 2006). "Conservation Planning for Ecosystem Services". PLOS Biology. 4 (11): e379. doi:10.1371/journal.pbio.0040379. PMC 1629036. PMID 17076586.
  65. ^ Northern Economics Inc. "Valuation of Ecosystem Services from Shellfish Restoration, Enhancement and Management: A Review of the Literature" (PDF). Prepared for Pacific Shellfish Institute. Archived (PDF) from the original on 3 December 2013.
  66. ^ Jones; Lawton, and Shachak (1994). "Organisms as Ecosystem Engineers". Oikos. 69 (3): 373–386. Bibcode:1994Oikos..69..373J. doi:10.2307/3545850. JSTOR 3545850.
  67. ^ Kistenkas, Frederik H.; Bouwma, Irene M. (February 2018). "Barriers for the ecosystem services concept in European water and nature conservation law". Ecosystem Services. 29: 223–227. Bibcode:2018EcoSv..29..223K. doi:10.1016/j.ecoser.2017.02.013.
  68. ^ "Goal 15 targets". UNDP. Archived from the original on 4 September 2017. Retrieved 24 September 2020.
  69. ^ US EPA, OAR (18 October 2022). "Climate Change Impacts on Ecosystems". www.epa.gov. Retrieved 19 July 2023.
  70. ^ "What is an ecosystem service?". European Investment Bank. Retrieved 19 July 2023.
  71. ^ "How much is nature worth? $125 trillion, according to this report". World Economic Forum. 30 October 2018. Retrieved 19 July 2023.
  72. ^ Bastien-Olvera, B. A.; Conte, M. N.; Dong, X.; Briceno, T.; Batker, D.; Emmerling, J.; Tavoni, M.; Granella, F.; Moore, F. C. (18 December 2023). "Unequal climate impacts on global values of natural capital". Nature. 625 (7996): 722–727. doi:10.1038/s41586-023-06769-z. ISSN 1476-4687. PMC 10808060. PMID 38110573.
  73. ^ CBD (2009). Connecting Biodiversity and Climate Change Mitigation and Adaptation: Report of the Second Ad Hoc Technical Expert Group on Biodiversity and Climate Change. Montreal, Technical Series No. 41, 126 pages.
  74. ^ "ebaflagship.org" (PDF). Archived from the original (PDF) on 11 February 2015. Retrieved 11 May 2015.
  75. ^ Gorriz-Misfud, Elena; Secco, L; Pisani, E (2016). "Exploring the interlinkages between governance and social capital: A dynamic model for forestry". Forest Policy and Economics. 65: 25–36. doi:10.1016/j.forpol.2016.01.006.
  76. ^ Siirola, John; Tidwell, Vincent; Benz, Zachary; Stansbury, Melanie; Richards, Elizabeth; Turnley, Jessica; Warrender, Christina; Morrow, James (1 February 2012). "Decision insight into stakeholder conflict for ERN". doi:10.2172/1035334. {{cite journal}}: Cite journal requires |journal= (help)
  77. ^ Lewis, David; Alig, Ralph (2009). "Empirical methods for modeling landscape change, ecosystem services, and biodiversity". Western Economics Forum. 8 (1): 29–39.
  78. ^ Ullman D. G.; K. Halsey; C. Goldfinger (2013). "Managing Eco-System Services Decisions" (PDF). Archived (PDF) from the original on 6 June 2013.
  79. ^ Quoc Vo, Tuan; Kuenzer, C.; Oppelt, N. (August 2015). "How remote sensing supports mangrove ecosystem service valuation: A case study in Ca Mau province, Vietnam". Ecosystem Services. 14: 67–75. Bibcode:2015EcoSv..14...67Q. doi:10.1016/j.ecoser.2015.04.007.
  80. ^ "About the project | LIFE Viva Grass".
  81. ^ "Sustainable grassland management efforts in the Baltics: interview with Žymantas Morkvėnas – GO-GRASS". www.go-grass.eu. 8 September 2020. Retrieved 1 August 2021.
  82. ^ Schumacher, E. F. (1973). Small is Beautiful: A Study of Economics As If People Mattered.
  83. ^ a b Daily, G. C. 1997. Nature's Services: Societal Dependence on Natural Ecosystems. Island Press, Washington. 392pp.
  84. ^ Hughes, J. Donald; Thirgood, J. V. (1 April 1982). "Deforestation, Erosion, and Forest Management in Ancient Greece and Rome". Journal of Forest History. 26 (2): 60–75. doi:10.2307/4004530. ISSN 0094-5080. JSTOR 4004530. S2CID 130391537.
  85. ^ Marsh, G. P. 1864 (1965). Man and Nature. Charles Scribner's Sons, New York. 472pp.
  86. ^ Osborn, F. 1948. Our Plundered Planet. Little, Brown and Company: Boston. 217pp.
  87. ^ Vogt, W. 1948. Road to Survival. William Sloan: New York. 335pp.
  88. ^ Leopold, A. 1949. A Sand County Almanac and Sketches from Here and There. Oxford University Press, New York. 226pp.
  89. ^ Sears, P. B. 1956. "The processes of environmental change by man." In: W. L. Thomas, editor. Man's Role in Changing the Face of the Earth (Volume 2). University of Chicago Press, Chicago. 1193pp.
  90. ^ Ehrlich, P. R., and A. Ehrlich. 1970. Population, Resources, Environment: Issues in Human Ecology. W. H. Freeman, San Francisco. 383pp. – see p.157
  91. ^ Study of Critical Environmental Problems (SCEP). 1970. Man's Impact on the Global Environment. MIT Press, Cambridge. 319pp.
  92. ^ Ehrlich, P. R., and A. Ehrlich. 1981. Extinction: The Causes and Consequences of the Disappearance of Species. Random House, New York. 305pp.

Sources

edit

  This article incorporates text from a free content work. Licensed under CC BY-SA 3.0 IGO (license statement/permission). Text taken from The State of the World’s Forests 2020. Forests, biodiversity and people – In brief​, FAO & UNEP, FAO & UNEP.

  This article incorporates text from a free content work. Licensed under CC BY-SA 3.0 IGO (license statement/permission). Text taken from Global Forest Resources Assessment 2020 – Key findings​, FAO, FAO.

edit


Retrieved from "https://en.wiki.x.io/w/index.php?title=Ecosystem_service&oldid=1241337623"