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Freshwater ecosystem

Freshwater ecosystems are a subset of Earth's aquatic ecosystems. They include lakes, ponds, rivers, streams, springs, bogs, and wetlands.[1] They can be contrasted with marine ecosystems, which have a larger salt content. Freshwater habitats can be classified by different factors, including temperature, light penetration, nutrients, and vegetation. There are three basic types of freshwater ecosystems: Lentic (slow moving water, including pools, ponds, and lakes), lotic (faster moving water, for example streams and rivers) and wetlands (areas where the soil is saturated or inundated for at least part of the time).[2][1] Freshwater ecosystems contain 41% of the world's known fish species.[3]

Freshwater ecosystem

Freshwater ecosystems have undergone substantial transformations over time, which has impacted various characteristics of the ecosystems.[4] Original attempts to understand and monitor freshwater ecosystems were spurred on by threats to human health (for example cholera outbreaks due to sewage contamination).[5] Early monitoring focused on chemical indicators, then bacteria, and finally algae, fungi and protozoa. A new type of monitoring involves quantifying differing groups of organisms (macroinvertebrates, macrophytes and fish) and measuring the stream conditions associated with them.[6]

Threats to freshwater biodiversity include overexploitation, water pollution, flow modification, destruction or degradation of habitat, and invasion by exotic species.[7] Climate change is putting further pressure on these ecosystems because water temperatures have already increased by about 1 °C, and there have been significant declines in ice coverage which have caused subsequent ecosystem stresses.[8]

Types

There are three basic types of freshwater ecosystems: Lentic (slow moving water, including pools, ponds, and lakes), lotic (faster moving water, for example streams and rivers) and wetlands (areas where the soil is saturated or inundated for at least part of the time). Limnology (and its branch freshwater biology) is a study about freshwater ecosystems.[1]

Lentic ecosystems

 
The three primary zones of a lake

A lake ecosystem or lacustrine ecosystem includes biotic (living) plants, animals and micro-organisms, as well as abiotic (non-living) physical and chemical interactions.[9] Lake ecosystems are a prime example of lentic ecosystems (lentic refers to stationary or relatively still freshwater, from the Latin lentus, which means "sluggish"), which include ponds, lakes and wetlands, and much of this article applies to lentic ecosystems in general. Lentic ecosystems can be compared with lotic ecosystems, which involve flowing terrestrial waters such as rivers and streams. Together, these two ecosystems are examples of freshwater ecosystems.

Lentic systems are diverse, ranging from a small, temporary rainwater pool a few inches deep to Lake Baikal, which has a maximum depth of 1642 m.[10] The general distinction between pools/ponds and lakes is vague, but Brown[9] states that ponds and pools have their entire bottom surfaces exposed to light, while lakes do not. In addition, some lakes become seasonally stratified. Ponds and pools have two regions: the pelagic open water zone, and the benthic zone, which comprises the bottom and shore regions. Since lakes have deep bottom regions not exposed to light, these systems have an additional zone, the profundal.[11] These three areas can have very different abiotic conditions and, hence, host species that are specifically adapted to live there.[9]

Lotic ecosystems

 
This stream operating together with its environment can be thought of as forming a river ecosystem.

River ecosystems are flowing waters that drain the landscape, and include the biotic (living) interactions amongst plants, animals and micro-organisms, as well as abiotic (nonliving) physical and chemical interactions of its many parts.[12][13] River ecosystems are part of larger watershed networks or catchments, where smaller headwater streams drain into mid-size streams, which progressively drain into larger river networks. The major zones in river ecosystems are determined by the river bed's gradient or by the velocity of the current. Faster moving turbulent water typically contains greater concentrations of dissolved oxygen, which supports greater biodiversity than the slow-moving water of pools. These distinctions form the basis for the division of rivers into upland and lowland rivers.

The food base of streams within riparian forests is mostly derived from the trees, but wider streams and those that lack a canopy derive the majority of their food base from algae. Anadromous fish are also an important source of nutrients. Environmental threats to rivers include loss of water, dams, chemical pollution and introduced species.[14] A dam produces negative effects that continue down the watershed. The most important negative effects are the reduction of spring flooding, which damages wetlands, and the retention of sediment, which leads to the loss of deltaic wetlands.[15]

River ecosystems are prime examples of lotic ecosystems. Lotic refers to flowing water, from the Latin lotus, meaning washed. Lotic waters range from springs only a few centimeters wide to major rivers kilometers in width.[16] Much of this article applies to lotic ecosystems in general, including related lotic systems such as streams and springs. Lotic ecosystems can be contrasted with lentic ecosystems, which involve relatively still terrestrial waters such as lakes, ponds, and wetlands. Together, these two ecosystems form the more general study area of freshwater or aquatic ecology.

Wetlands

Wetlands, or simply a wetland, is a distinct ecosystem that is flooded or saturated by water, either permanently (for years or decades) or seasonally (for weeks or months). Flooding results in oxygen-free (anoxic) processes prevailing, especially in the soils.[17] The primary factor that distinguishes wetlands from terrestrial land forms or water bodies is the characteristic vegetation of aquatic plants, adapted to the unique anoxic hydric soils.[18] Wetlands are considered among the most biologically diverse of all ecosystems, serving as home to a wide range of plant and animal species. Methods for assessing wetland functions, wetland ecological health, and general wetland condition have been developed for many regions of the world. These methods have contributed to wetland conservation partly by raising public awareness of the functions some wetlands provide.[19]

Wetlands occur naturally on every continent.[20] The water in wetlands is either freshwater, brackish or saltwater.[18] The main wetland types are classified based on the dominant plants and/or the source of the water. For example, marshes are wetlands dominated by emergent vegetation such as reeds, cattails and sedges; swamps are ones dominated by woody vegetation such as trees and shrubs (although reed swamps in Europe are dominated by reeds, not trees). Examples of wetlands classified by their sources of water include tidal wetlands (oceanic tides), estuaries (mixed tidal and river waters), floodplains (excess water from overflowed rivers or lakes), springs, seeps and fens (groundwater discharge out onto the surface), and bogs and vernal ponds (rainfall or meltwater).[17][21] Some wetlands have multiple types of plants and are fed by multiple sources of water, making them difficult to classify. The world's largest wetlands include the Amazon River basin, the West Siberian Plain,[22] the Pantanal in South America,[23] and the Sundarbans in the Ganges-Brahmaputra delta.[24]

Wetlands contribute a number of functions that benefit people. These are called ecosystem services and include water purification, groundwater replenishment, stabilization of shorelines and storm protection, water storage and flood control, processing of carbon (carbon fixation, decomposition and sequestration), other nutrients and pollutants, and support of plants and animals.[25] Wetlands are reservoirs of biodiversity and provide wetland products. According to the UN Millennium Ecosystem Assessment, wetlands are more affected by environmental degradation than any other ecosystem on Earth.[26] Wetlands can be important sources and sinks of carbon, depending on the specific wetland, and thus will play an important role in climate change and need to be considered in attempts to mitigate climate change. However, some wetlands are a significant source of methane emissions and some are also emitters of nitrous oxide.[27][28] Constructed wetlands are designed and built to treat municipal and industrial wastewater as well as to divert stormwater runoff. Constructed wetlands may also play a role in water-sensitive urban design.

Threats

Biodiversity

Five broad threats to freshwater biodiversity include overexploitation, water pollution, flow modification, destruction or degradation of habitat, and invasion by exotic species.[7] Recent extinction trends can be attributed largely to sedimentation, stream fragmentation, chemical and organic pollutants, dams, and invasive species.[29] Common chemical stresses on freshwater ecosystem health include acidification, eutrophication and copper and pesticide contamination.[30]

Freshwater biodiversity faces many threats.[31] The World Wide Fund for Nature's Living Planet Index noted an 83% decline in the populations of freshwater vertebrates between 1970 and 2014.[32] These declines continue to outpace contemporaneous declines in marine or terrestrial systems. The causes of these declines are related to:[33][31]

  1. A rapidly changing climate
  2. Online wildlife trade and invasive species
  3. Infectious disease
  4. Toxic algae blooms
  5. Hydropower damming and fragmenting of half the world's rivers
  6. Emerging contaminants, such as hormones
  7. Engineered nanomaterials
  8. Microplastic pollution
  9. Light and noise interference
  10. Saltier coastal freshwaters due to sea level rise
  11. Calcium concentrations falling below the needs of some freshwater organisms
  12. The additive—and possibly synergistic—effects of these threats

Extinction of freshwater fauna

Over 123 freshwater fauna species have gone extinct in North America since 1900. Of North American freshwater species, an estimated 48.5% of mussels, 22.8% of gastropods, 32.7% of crayfishes, 25.9% of amphibians, and 21.2% of fish are either endangered or threatened.[29] Extinction rates of many species may increase severely into the next century because of invasive species, loss of keystone species, and species which are already functionally extinct (e.g., species which are not reproducing).[29] Even using conservative estimates, freshwater fish extinction rates in North America are 877 times higher than background extinction rates (1 in 3,000,000 years).[34] Projected extinction rates for freshwater animals are around five times greater than for land animals, and are comparable to the rates for rainforest communities.[29] Given the dire state of freshwater biodiversity, a team of scientists and practitioners from around the globe recently drafted an Emergency Action plan to try and restore freshwater biodiversity.[35]

Current freshwater biomonitoring techniques focus primarily on community structure, but some programs measure functional indicators like biochemical (or biological) oxygen demand, sediment oxygen demand, and dissolved oxygen.[6] Macroinvertebrate community structure is commonly monitored because of the diverse taxonomy, ease of collection, sensitivity to a range of stressors, and overall value to the ecosystem.[36] Additionally, algal community structure (often using diatoms) is measured in biomonitoring programs. Algae are also taxonomically diverse, easily collected, sensitive to a range of stressors, and overall valuable to the ecosystem.[37] Algae grow very quickly and communities may represent fast changes in environmental conditions.[37]

In addition to community structure, responses to freshwater stressors are investigated by experimental studies that measure organism behavioural changes, altered rates of growth, reproduction or mortality.[6] Experimental results on single species under controlled conditions may not always reflect natural conditions and multi-species communities.[6]

The use of reference sites is common when defining the idealized "health" of a freshwater ecosystem. Reference sites can be selected spatially by choosing sites with minimal impacts from human disturbance and influence.[6] However, reference conditions may also be established temporally by using preserved indicators such as diatom valves, macrophyte pollen, insect chitin and fish scales can be used to determine conditions prior to large scale human disturbance.[6] These temporal reference conditions are often easier to reconstruct in standing water than moving water because stable sediments can better preserve biological indicator materials.

Climate change

The effects of climate change greatly complicate and frequently exacerbate the impacts of other stressors that threaten many fish,[38] invertebrates,[39] phytoplankton,[40] and other organisms. Climate change is increasing the average temperature of water bodies, and worsening other issues such as changes in substrate composition, oxygen concentration, and other system changes that have ripple effects on the biology of the system.[8] Water temperatures have already increased by around 1 °C, and significant declines in ice coverage have caused subsequent ecosystem stresses.[8]

See also

References

  1. ^ a b c G., Wetzel, Robert (2001). Limnology : lake and river ecosystems (3rd ed.). San Diego: Academic Press. ISBN 978-0127447605. OCLC 46393244.
  2. ^ Vaccari, David A. (8 November 2005). Environmental Biology for Engineers and Scientists. Wiley-Interscience. ISBN 0-471-74178-7.
  3. ^ Daily, Gretchen C. (1 February 1997). Nature's Services. Island Press. ISBN 1-55963-476-6.
  4. ^ Carpenter, Stephen R.; Stanley, Emily H.; Vander Zanden, M. Jake (2011). "State of the World's Freshwater Ecosystems: Physical, Chemical, and Biological Changes". Annual Review of Environment and Resources. 36 (1): 75–99. doi:10.1146/annurev-environ-021810-094524. ISSN 1543-5938.
  5. ^ Rudolfs, Willem; Falk, Lloyd L.; Ragotzkie, R. A. (1950). "Literature Review on the Occurrence and Survival of Enteric, Pathogenic, and Relative Organisms in Soil, Water, Sewage, and Sludges, and on Vegetation: I. Bacterial and Virus Diseases". Sewage and Industrial Wastes. 22 (10): 1261–1281. JSTOR 25031419.
  6. ^ a b c d e f Friberg, Nikolai; Bonada, Núria; Bradley, David C.; Dunbar, Michael J.; Edwards, Francois K.; Grey, Jonathan; Hayes, Richard B.; Hildrew, Alan G.; Lamouroux, Nicolas (2011), "Biomonitoring of Human Impacts in Freshwater Ecosystems", Advances in Ecological Research, Elsevier, pp. 1–68, doi:10.1016/b978-0-12-374794-5.00001-8, ISBN 9780123747945
  7. ^ a b Dudgeon, David; Arthington, Angela H.; Gessner, Mark O.; Kawabata, Zen-Ichiro; Knowler, Duncan J.; Lévêque, Christian; Naiman, Robert J.; Prieur-Richard, Anne-Hélène; Soto, Doris (2005-12-12). "Freshwater biodiversity: importance, threats, status and conservation challenges". Biological Reviews. 81 (2): 163–82. CiteSeerX 10.1.1.568.4047. doi:10.1017/s1464793105006950. ISSN 1464-7931. PMID 16336747. S2CID 15921269.
  8. ^ a b c Parmesan, Camille; Morecroft, Mike; Trisurat, Yongyut; et al. "Chapter 2: Terrestrial and Freshwater Ecosystems and their Services" (PDF). Climate Change 2022: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change. Intergovernmental Panel on Climate Change.
  9. ^ a b c Brown, A. L. (1987). Freshwater Ecology. Heinimann Educational Books, London. p. 163. ISBN 0435606220.
  10. ^ Brönmark, C.; L. A. Hansson (2005). The Biology of Lakes and Ponds. Oxford University Press, Oxford. p. 285. ISBN 0198516134.
  11. ^ Kalff, J. (2002). Limnology. Prentice Hall, Upper Saddle, NJ. p. 592. ISBN 0130337757.
  12. ^ Angelier, E. 2003. Ecology of Streams and Rivers. Science Publishers, Inc., Enfield. Pp. 215.
  13. ^ ”Biology Concepts & Connections Sixth Edition”, Campbell, Neil A. (2009), page 2, 3 and G-9. Retrieved 2010-06-14.
  14. ^ Alexander, David E. (1 May 1999). Encyclopedia of Environmental Science. Springer. ISBN 0-412-74050-8.
  15. ^ Keddy, Paul A. (2010). Wetland Ecology. Principles and Conservation. Cambridge University Press. p. 497. ISBN 978-0-521-51940-3.
  16. ^ Allan, J.D. 1995. Stream Ecology: structure and function of running waters. Chapman and Hall, London. Pp. 388.
  17. ^ a b Keddy, P.A. (2010). Wetland ecology: principles and conservation (2nd ed.). New York: Cambridge University Press. ISBN 978-0521519403. [1] 2013-04-11 at the Wayback Machine
  18. ^ a b "Official page of the Ramsar Convention". Retrieved 2011-09-25.
  19. ^ Dorney, J.; Savage, R.; Adamus, P.; Tiner, R., eds. (2018). Wetland and Stream Rapid Assessments: Development, Validation, and Application. London; San Diego, CA: Academic Press. ISBN 978-0-12-805091-0. OCLC 1017607532.
  20. ^ Davidson, N.C. (2014). "How much wetland has the world lost? Long-term and recent trends in global wetland area". Marine and Freshwater Research. 65 (10): 934–941. doi:10.1071/MF14173. S2CID 85617334.
  21. ^ "US EPA". 2015-09-18. Retrieved 2011-09-25.
  22. ^ Fraser, L.; Keddy, P.A., eds. (2005). The World's Largest Wetlands: Their Ecology and Conservation. Cambridge, UK: Cambridge University Press. ISBN 978-0521834049.
  23. ^ "WWF Pantanal Programme". Retrieved 2011-09-25.
  24. ^ Giri, C.; Pengra, B.; Zhu, Z.; Singh, A.; Tieszen, L.L. (2007). "Monitoring mangrove forest dynamics of the Sundarbans in Bangladesh and India using multi-temporal satellite data from 1973 to 2000". Estuarine, Coastal and Shelf Science. 73 (1–2): 91–100. Bibcode:2007ECSS...73...91G. doi:10.1016/j.ecss.2006.12.019.
  25. ^ "Wetlands". USDA- Natural Resource Conservation Center.
  26. ^ Davidson, N.C.; D'Cruz, R. & Finlayson, C.M. (2005). Ecosystems and Human Well-being: Wetlands and Water Synthesis: a report of the Millennium Ecosystem Assessment (PDF). Washington, DC: World Resources Institute. ISBN 978-1-56973-597-8.
  27. ^ Bange, Hermann W. (2006). "Nitrous oxide and methane in European coastal waters". Estuarine, Coastal and Shelf Science. 70 (3): 361–374. Bibcode:2006ECSS...70..361B. doi:10.1016/j.ecss.2006.05.042.
  28. ^ Thompson, A. J.; Giannopoulos, G.; Pretty, J.; Baggs, E. M.; Richardson, D. J. (2012). "Biological sources and sinks of nitrous oxide and strategies to mitigate emissions". Philosophical Transactions of the Royal Society B. 367 (1593): 1157–1168. doi:10.1098/rstb.2011.0415. PMC 3306631. PMID 22451101.
  29. ^ a b c d Ricciardi, Anthony; Rasmussen, Joseph B. (1999-10-23). "Extinction Rates of North American Freshwater Fauna". Conservation Biology. 13 (5): 1220–1222. doi:10.1046/j.1523-1739.1999.98380.x. ISSN 0888-8892. S2CID 85338348.
  30. ^ Xu, F (September 2001). "Lake Ecosystem Health Assessment: Indicators and Methods". Water Research. 35 (13): 3157–3167. doi:10.1016/s0043-1354(01)00040-9. ISSN 0043-1354. PMID 11487113.
  31. ^ a b Reid, AJ; et al. (2019). "Emerging threats and persistent conservation challenges for freshwater biodiversity". Biological Reviews. 94 (3): 849–873. doi:10.1111/brv.12480. PMID 30467930.
  32. ^ "Living Planet Report 2018 | WWF". wwf.panda.org. Retrieved 2019-04-09.
  33. ^ Reid, Andrea Jane; Cooke, Steven J. "Freshwater wildlife face an uncertain future". The Conversation. Retrieved 2019-04-09.
  34. ^ Burkhead, Noel M. (September 2012). "Extinction Rates in North American Freshwater Fishes, 1900–2010". BioScience. 62 (9): 798–808. doi:10.1525/bio.2012.62.9.5. ISSN 1525-3244.
  35. ^ Tickner, David; Opperman, Jeffrey J; Abell, Robin; Acreman, Mike; Arthington, Angela H; Bunn, Stuart E; Cooke, Steven J; Dalton, James; Darwall, Will; Edwards, Gavin; Harrison, Ian (2020-04-01). "Bending the Curve of Global Freshwater Biodiversity Loss: An Emergency Recovery Plan". BioScience. 70 (4): 330–342. doi:10.1093/biosci/biaa002. ISSN 0006-3568. PMC 7138689. PMID 32284631.
  36. ^ Johnson, R. K.; Wiederholm, T.; Rosenberg, D. M. (1993). Freshwater biomonitoring and benthic macroinvertebrates, 40-158. pp. 40–158.
  37. ^ a b Stevenson, R. Jan; Smol, John P. (2003), "Use of Algae in Environmental Assessments", Freshwater Algae of North America, Elsevier, pp. 775–804, doi:10.1016/b978-012741550-5/50024-6, ISBN 9780127415505
  38. ^ Arthington, Angela H.; Dulvy, Nicholas K.; Gladstone, William; Winfield, Ian J. (2016). "Fish conservation in freshwater and marine realms: status, threats and management". Aquatic Conservation: Marine and Freshwater Ecosystems. 26 (5): 838–857. doi:10.1002/aqc.2712. ISSN 1099-0755.
  39. ^ Prather, Chelse M.; Pelini, Shannon L.; Laws, Angela; Rivest, Emily; Woltz, Megan; Bloch, Christopher P.; Del Toro, Israel; Ho, Chuan-Kai; Kominoski, John; Newbold, T. A. Scott; Parsons, Sheena; Joern, A. (2012). "Invertebrates, ecosystem services and climate change: Invertebrates, ecosystems and climate change". Biological Reviews. 88 (2): 327–348. doi:10.1111/brv.12002. PMID 23217156. S2CID 23578609.
  40. ^ Winder, Monika; Sommer, Ulrich (2012). "Phytoplankton response to a changing climate". Hydrobiologia. 698 (1): 5–16. doi:10.1007/s10750-012-1149-2. ISSN 0018-8158. S2CID 16907349.



freshwater, ecosystem, subset, earth, aquatic, ecosystems, they, include, lakes, ponds, rivers, streams, springs, bogs, wetlands, they, contrasted, with, marine, ecosystems, which, have, larger, salt, content, freshwater, habitats, classified, different, facto. Freshwater ecosystems are a subset of Earth s aquatic ecosystems They include lakes ponds rivers streams springs bogs and wetlands 1 They can be contrasted with marine ecosystems which have a larger salt content Freshwater habitats can be classified by different factors including temperature light penetration nutrients and vegetation There are three basic types of freshwater ecosystems Lentic slow moving water including pools ponds and lakes lotic faster moving water for example streams and rivers and wetlands areas where the soil is saturated or inundated for at least part of the time 2 1 Freshwater ecosystems contain 41 of the world s known fish species 3 Freshwater ecosystem Freshwater ecosystems have undergone substantial transformations over time which has impacted various characteristics of the ecosystems 4 Original attempts to understand and monitor freshwater ecosystems were spurred on by threats to human health for example cholera outbreaks due to sewage contamination 5 Early monitoring focused on chemical indicators then bacteria and finally algae fungi and protozoa A new type of monitoring involves quantifying differing groups of organisms macroinvertebrates macrophytes and fish and measuring the stream conditions associated with them 6 Threats to freshwater biodiversity include overexploitation water pollution flow modification destruction or degradation of habitat and invasion by exotic species 7 Climate change is putting further pressure on these ecosystems because water temperatures have already increased by about 1 C and there have been significant declines in ice coverage which have caused subsequent ecosystem stresses 8 Contents 1 Types 1 1 Lentic ecosystems 1 2 Lotic ecosystems 1 3 Wetlands 2 Threats 2 1 Biodiversity 2 2 Extinction of freshwater fauna 2 3 Climate change 3 See also 4 ReferencesTypes EditThere are three basic types of freshwater ecosystems Lentic slow moving water including pools ponds and lakes lotic faster moving water for example streams and rivers and wetlands areas where the soil is saturated or inundated for at least part of the time Limnology and its branch freshwater biology is a study about freshwater ecosystems 1 Lentic ecosystems Edit This section is an excerpt from Lake ecosystem edit The three primary zones of a lake A lake ecosystem or lacustrine ecosystem includes biotic living plants animals and micro organisms as well as abiotic non living physical and chemical interactions 9 Lake ecosystems are a prime example of lentic ecosystems lentic refers to stationary or relatively still freshwater from the Latin lentus which means sluggish which include ponds lakes and wetlands and much of this article applies to lentic ecosystems in general Lentic ecosystems can be compared with lotic ecosystems which involve flowing terrestrial waters such as rivers and streams Together these two ecosystems are examples of freshwater ecosystems Lentic systems are diverse ranging from a small temporary rainwater pool a few inches deep to Lake Baikal which has a maximum depth of 1642 m 10 The general distinction between pools ponds and lakes is vague but Brown 9 states that ponds and pools have their entire bottom surfaces exposed to light while lakes do not In addition some lakes become seasonally stratified Ponds and pools have two regions the pelagic open water zone and the benthic zone which comprises the bottom and shore regions Since lakes have deep bottom regions not exposed to light these systems have an additional zone the profundal 11 These three areas can have very different abiotic conditions and hence host species that are specifically adapted to live there 9 Lotic ecosystems Edit This section is an excerpt from River ecosystem edit This stream operating together with its environment can be thought of as forming a river ecosystem River ecosystems are flowing waters that drain the landscape and include the biotic living interactions amongst plants animals and micro organisms as well as abiotic nonliving physical and chemical interactions of its many parts 12 13 River ecosystems are part of larger watershed networks or catchments where smaller headwater streams drain into mid size streams which progressively drain into larger river networks The major zones in river ecosystems are determined by the river bed s gradient or by the velocity of the current Faster moving turbulent water typically contains greater concentrations of dissolved oxygen which supports greater biodiversity than the slow moving water of pools These distinctions form the basis for the division of rivers into upland and lowland rivers The food base of streams within riparian forests is mostly derived from the trees but wider streams and those that lack a canopy derive the majority of their food base from algae Anadromous fish are also an important source of nutrients Environmental threats to rivers include loss of water dams chemical pollution and introduced species 14 A dam produces negative effects that continue down the watershed The most important negative effects are the reduction of spring flooding which damages wetlands and the retention of sediment which leads to the loss of deltaic wetlands 15 River ecosystems are prime examples of lotic ecosystems Lotic refers to flowing water from the Latin lotus meaning washed Lotic waters range from springs only a few centimeters wide to major rivers kilometers in width 16 Much of this article applies to lotic ecosystems in general including related lotic systems such as streams and springs Lotic ecosystems can be contrasted with lentic ecosystems which involve relatively still terrestrial waters such as lakes ponds and wetlands Together these two ecosystems form the more general study area of freshwater or aquatic ecology Wetlands Edit This section is an excerpt from Wetland edit Wetlands or simply a wetland is a distinct ecosystem that is flooded or saturated by water either permanently for years or decades or seasonally for weeks or months Flooding results in oxygen free anoxic processes prevailing especially in the soils 17 The primary factor that distinguishes wetlands from terrestrial land forms or water bodies is the characteristic vegetation of aquatic plants adapted to the unique anoxic hydric soils 18 Wetlands are considered among the most biologically diverse of all ecosystems serving as home to a wide range of plant and animal species Methods for assessing wetland functions wetland ecological health and general wetland condition have been developed for many regions of the world These methods have contributed to wetland conservation partly by raising public awareness of the functions some wetlands provide 19 Wetlands occur naturally on every continent 20 The water in wetlands is either freshwater brackish or saltwater 18 The main wetland types are classified based on the dominant plants and or the source of the water For example marshes are wetlands dominated by emergent vegetation such as reeds cattails and sedges swamps are ones dominated by woody vegetation such as trees and shrubs although reed swamps in Europe are dominated by reeds not trees Examples of wetlands classified by their sources of water include tidal wetlands oceanic tides estuaries mixed tidal and river waters floodplains excess water from overflowed rivers or lakes springs seeps and fens groundwater discharge out onto the surface and bogs and vernal ponds rainfall or meltwater 17 21 Some wetlands have multiple types of plants and are fed by multiple sources of water making them difficult to classify The world s largest wetlands include the Amazon River basin the West Siberian Plain 22 the Pantanal in South America 23 and the Sundarbans in the Ganges Brahmaputra delta 24 Wetlands contribute a number of functions that benefit people These are called ecosystem services and include water purification groundwater replenishment stabilization of shorelines and storm protection water storage and flood control processing of carbon carbon fixation decomposition and sequestration other nutrients and pollutants and support of plants and animals 25 Wetlands are reservoirs of biodiversity and provide wetland products According to the UN Millennium Ecosystem Assessment wetlands are more affected by environmental degradation than any other ecosystem on Earth 26 Wetlands can be important sources and sinks of carbon depending on the specific wetland and thus will play an important role in climate change and need to be considered in attempts to mitigate climate change However some wetlands are a significant source of methane emissions and some are also emitters of nitrous oxide 27 28 Constructed wetlands are designed and built to treat municipal and industrial wastewater as well as to divert stormwater runoff Constructed wetlands may also play a role in water sensitive urban design Threats EditFurther information Lake ecosystem Human impacts River ecosystem Human impacts and Ecosystem Human interactions with ecosystems Biodiversity Edit Five broad threats to freshwater biodiversity include overexploitation water pollution flow modification destruction or degradation of habitat and invasion by exotic species 7 Recent extinction trends can be attributed largely to sedimentation stream fragmentation chemical and organic pollutants dams and invasive species 29 Common chemical stresses on freshwater ecosystem health include acidification eutrophication and copper and pesticide contamination 30 Freshwater biodiversity faces many threats 31 The World Wide Fund for Nature s Living Planet Index noted an 83 decline in the populations of freshwater vertebrates between 1970 and 2014 32 These declines continue to outpace contemporaneous declines in marine or terrestrial systems The causes of these declines are related to 33 31 A rapidly changing climate Online wildlife trade and invasive species Infectious disease Toxic algae blooms Hydropower damming and fragmenting of half the world s rivers Emerging contaminants such as hormones Engineered nanomaterials Microplastic pollution Light and noise interference Saltier coastal freshwaters due to sea level rise Calcium concentrations falling below the needs of some freshwater organisms The additive and possibly synergistic effects of these threatsExtinction of freshwater fauna Edit Over 123 freshwater fauna species have gone extinct in North America since 1900 Of North American freshwater species an estimated 48 5 of mussels 22 8 of gastropods 32 7 of crayfishes 25 9 of amphibians and 21 2 of fish are either endangered or threatened 29 Extinction rates of many species may increase severely into the next century because of invasive species loss of keystone species and species which are already functionally extinct e g species which are not reproducing 29 Even using conservative estimates freshwater fish extinction rates in North America are 877 times higher than background extinction rates 1 in 3 000 000 years 34 Projected extinction rates for freshwater animals are around five times greater than for land animals and are comparable to the rates for rainforest communities 29 Given the dire state of freshwater biodiversity a team of scientists and practitioners from around the globe recently drafted an Emergency Action plan to try and restore freshwater biodiversity 35 Current freshwater biomonitoring techniques focus primarily on community structure but some programs measure functional indicators like biochemical or biological oxygen demand sediment oxygen demand and dissolved oxygen 6 Macroinvertebrate community structure is commonly monitored because of the diverse taxonomy ease of collection sensitivity to a range of stressors and overall value to the ecosystem 36 Additionally algal community structure often using diatoms is measured in biomonitoring programs Algae are also taxonomically diverse easily collected sensitive to a range of stressors and overall valuable to the ecosystem 37 Algae grow very quickly and communities may represent fast changes in environmental conditions 37 In addition to community structure responses to freshwater stressors are investigated by experimental studies that measure organism behavioural changes altered rates of growth reproduction or mortality 6 Experimental results on single species under controlled conditions may not always reflect natural conditions and multi species communities 6 The use of reference sites is common when defining the idealized health of a freshwater ecosystem Reference sites can be selected spatially by choosing sites with minimal impacts from human disturbance and influence 6 However reference conditions may also be established temporally by using preserved indicators such as diatom valves macrophyte pollen insect chitin and fish scales can be used to determine conditions prior to large scale human disturbance 6 These temporal reference conditions are often easier to reconstruct in standing water than moving water because stable sediments can better preserve biological indicator materials Climate change Edit See also Effects of climate change on the water cycle Impacts on freshwater ecosystems The effects of climate change greatly complicate and frequently exacerbate the impacts of other stressors that threaten many fish 38 invertebrates 39 phytoplankton 40 and other organisms Climate change is increasing the average temperature of water bodies and worsening other issues such as changes in substrate composition oxygen concentration and other system changes that have ripple effects on the biology of the system 8 Water temperatures have already increased by around 1 C and significant declines in ice coverage have caused subsequent ecosystem stresses 8 See also Edit Ecology portal Water portalEcology FreshwaterReferences Edit a b c G Wetzel Robert 2001 Limnology lake and river ecosystems 3rd ed San Diego Academic Press ISBN 978 0127447605 OCLC 46393244 Vaccari David A 8 November 2005 Environmental Biology for Engineers and Scientists Wiley Interscience ISBN 0 471 74178 7 Daily Gretchen C 1 February 1997 Nature s Services Island Press ISBN 1 55963 476 6 Carpenter Stephen R Stanley Emily H Vander Zanden M Jake 2011 State of the World s Freshwater Ecosystems Physical Chemical and Biological Changes Annual Review of Environment and Resources 36 1 75 99 doi 10 1146 annurev environ 021810 094524 ISSN 1543 5938 Rudolfs Willem Falk Lloyd L Ragotzkie R A 1950 Literature Review on the Occurrence and Survival of Enteric Pathogenic and Relative Organisms in Soil Water Sewage and Sludges and on Vegetation I Bacterial and Virus Diseases Sewage and Industrial Wastes 22 10 1261 1281 JSTOR 25031419 a b c d e f Friberg Nikolai Bonada Nuria Bradley David C Dunbar Michael J Edwards Francois K Grey Jonathan Hayes Richard B Hildrew Alan G Lamouroux Nicolas 2011 Biomonitoring of Human Impacts in Freshwater Ecosystems Advances in Ecological Research Elsevier pp 1 68 doi 10 1016 b978 0 12 374794 5 00001 8 ISBN 9780123747945 a b Dudgeon David Arthington Angela H Gessner Mark O Kawabata Zen Ichiro Knowler Duncan J Leveque Christian Naiman Robert J Prieur Richard Anne Helene Soto Doris 2005 12 12 Freshwater biodiversity importance threats status and conservation challenges Biological Reviews 81 2 163 82 CiteSeerX 10 1 1 568 4047 doi 10 1017 s1464793105006950 ISSN 1464 7931 PMID 16336747 S2CID 15921269 a b c Parmesan Camille Morecroft Mike Trisurat Yongyut et al Chapter 2 Terrestrial and Freshwater Ecosystems and their Services PDF Climate Change 2022 Impacts Adaptation and Vulnerability Contribution of Working Group II to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change Intergovernmental Panel on Climate Change a b c Brown A L 1987 Freshwater Ecology Heinimann Educational Books London p 163 ISBN 0435606220 Bronmark C L A Hansson 2005 The Biology of Lakes and Ponds Oxford University Press Oxford p 285 ISBN 0198516134 Kalff J 2002 Limnology Prentice Hall Upper Saddle NJ p 592 ISBN 0130337757 Angelier E 2003 Ecology of Streams and Rivers Science Publishers Inc Enfield Pp 215 Biology Concepts amp Connections Sixth Edition Campbell Neil A 2009 page 2 3 and G 9 Retrieved 2010 06 14 Alexander David E 1 May 1999 Encyclopedia of Environmental Science Springer ISBN 0 412 74050 8 Keddy Paul A 2010 Wetland Ecology Principles and Conservation Cambridge University Press p 497 ISBN 978 0 521 51940 3 Allan J D 1995 Stream Ecology structure and function of running waters Chapman and Hall London Pp 388 a b Keddy P A 2010 Wetland ecology principles and conservation 2nd ed New York Cambridge University Press ISBN 978 0521519403 1 Archived 2013 04 11 at the Wayback Machine a b Official page of the Ramsar Convention Retrieved 2011 09 25 Dorney J Savage R Adamus P Tiner R eds 2018 Wetland and Stream Rapid Assessments Development Validation and Application London San Diego CA Academic Press ISBN 978 0 12 805091 0 OCLC 1017607532 Davidson N C 2014 How much wetland has the world lost Long term and recent trends in global wetland area Marine and Freshwater Research 65 10 934 941 doi 10 1071 MF14173 S2CID 85617334 US EPA 2015 09 18 Retrieved 2011 09 25 Fraser L Keddy P A eds 2005 The World s Largest Wetlands Their Ecology and Conservation Cambridge UK Cambridge University Press ISBN 978 0521834049 WWF Pantanal Programme Retrieved 2011 09 25 Giri C Pengra B Zhu Z Singh A Tieszen L L 2007 Monitoring mangrove forest dynamics of the Sundarbans in Bangladesh and India using multi temporal satellite data from 1973 to 2000 Estuarine Coastal and Shelf Science 73 1 2 91 100 Bibcode 2007ECSS 73 91G doi 10 1016 j ecss 2006 12 019 Wetlands USDA Natural Resource Conservation Center Davidson N C D Cruz R amp Finlayson C M 2005 Ecosystems and Human Well being Wetlands and Water Synthesis a report of the Millennium Ecosystem Assessment PDF Washington DC World Resources Institute ISBN 978 1 56973 597 8 Bange Hermann W 2006 Nitrous oxide and methane in European coastal waters Estuarine Coastal and Shelf Science 70 3 361 374 Bibcode 2006ECSS 70 361B doi 10 1016 j ecss 2006 05 042 Thompson A J Giannopoulos G Pretty J Baggs E M Richardson D J 2012 Biological sources and sinks of nitrous oxide and strategies to mitigate emissions Philosophical Transactions of the Royal Society B 367 1593 1157 1168 doi 10 1098 rstb 2011 0415 PMC 3306631 PMID 22451101 a b c d Ricciardi Anthony Rasmussen Joseph B 1999 10 23 Extinction Rates of North American Freshwater Fauna Conservation Biology 13 5 1220 1222 doi 10 1046 j 1523 1739 1999 98380 x ISSN 0888 8892 S2CID 85338348 Xu F September 2001 Lake Ecosystem Health Assessment Indicators and Methods Water Research 35 13 3157 3167 doi 10 1016 s0043 1354 01 00040 9 ISSN 0043 1354 PMID 11487113 a b Reid AJ et al 2019 Emerging threats and persistent conservation challenges for freshwater biodiversity Biological Reviews 94 3 849 873 doi 10 1111 brv 12480 PMID 30467930 Living Planet Report 2018 WWF wwf panda org Retrieved 2019 04 09 Reid Andrea Jane Cooke Steven J Freshwater wildlife face an uncertain future The Conversation Retrieved 2019 04 09 Burkhead Noel M September 2012 Extinction Rates in North American Freshwater Fishes 1900 2010 BioScience 62 9 798 808 doi 10 1525 bio 2012 62 9 5 ISSN 1525 3244 Tickner David Opperman Jeffrey J Abell Robin Acreman Mike Arthington Angela H Bunn Stuart E Cooke Steven J Dalton James Darwall Will Edwards Gavin Harrison Ian 2020 04 01 Bending the Curve of Global Freshwater Biodiversity Loss An Emergency Recovery Plan BioScience 70 4 330 342 doi 10 1093 biosci biaa002 ISSN 0006 3568 PMC 7138689 PMID 32284631 Johnson R K Wiederholm T Rosenberg D M 1993 Freshwater biomonitoring and benthic macroinvertebrates 40 158 pp 40 158 a b Stevenson R Jan Smol John P 2003 Use of Algae in Environmental Assessments Freshwater Algae of North America Elsevier pp 775 804 doi 10 1016 b978 012741550 5 50024 6 ISBN 9780127415505 Arthington Angela H Dulvy Nicholas K Gladstone William Winfield Ian J 2016 Fish conservation in freshwater and marine realms status threats and management Aquatic Conservation Marine and Freshwater Ecosystems 26 5 838 857 doi 10 1002 aqc 2712 ISSN 1099 0755 Prather Chelse M Pelini Shannon L Laws Angela Rivest Emily Woltz Megan Bloch Christopher P Del Toro Israel Ho Chuan Kai Kominoski John Newbold T A Scott Parsons Sheena Joern A 2012 Invertebrates ecosystem services and climate change Invertebrates ecosystems and climate change Biological Reviews 88 2 327 348 doi 10 1111 brv 12002 PMID 23217156 S2CID 23578609 Winder Monika Sommer Ulrich 2012 Phytoplankton response to a changing climate Hydrobiologia 698 1 5 16 doi 10 1007 s10750 012 1149 2 ISSN 0018 8158 S2CID 16907349 Wikimedia Commons has media related to Freshwater ecosystems Retrieved from https en wikipedia org w index php title Freshwater ecosystem amp oldid 1148602748, wikipedia, wiki, book, books, library,

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