An estuary is a partially enclosed coastal body of brackish water with one or more rivers or streams flowing into it, and with a free connection to the open sea.[1] Estuaries form a transition zone between river environments and maritime environments and are an example of an ecotone. Estuaries are subject both to marine influences such as tides, waves, and the influx of saline water, and to fluvial influences such as flows of freshwater and sediment. The mixing of seawater and freshwater provides high levels of nutrients both in the water column and in sediment, making estuaries among the most productive natural habitats in the world.[2]

Most existing estuaries formed during the Holocene epoch with the flooding of river-eroded or glacially scoured valleys when the sea level began to rise about 10,000–12,000 years ago.[3] Estuaries are typically classified according to their geomorphological features or to water-circulation patterns. They can have many different names, such as bays, harbors, lagoons, inlets, or sounds, although some of these water bodies do not strictly meet the above definition of an estuary and could be fully saline.

Many estuaries suffer degeneration from a variety of factors including soil erosion, deforestation, overgrazing, overfishing and the filling of wetlands. Eutrophication may lead to excessive nutrients from sewage and animal wastes; pollutants including heavy metals, polychlorinated biphenyls, radionuclides and hydrocarbons from sewage inputs; and diking or damming for flood control or water diversion.[3][4]

Definition

A general video on Natura 2000 estuaries in Wales; 2015
River Exe estuary
River Exe estuary
Estuary mouth located in Darwin, Northern Territory, Australia
Estuary mouth located in Darwin, Northern Territory, Australia
A crowded estuary mouth in Paravur near the city of Kollam, India
A crowded estuary mouth in Paravur near the city of Kollam, India
Estuary mouth
Estuary mouth
Estuary mouth of the Yachats River in Yachats, Oregon
Estuary mouth of the Yachats River in Yachats, Oregon
Amazon estuary
Amazon estuary

The word "estuary" is derived from the Latin word aestuarium meaning tidal inlet of the sea, which in itself is derived from the term aestus, meaning tide. There have been many definitions proposed to describe an estuary. The most widely accepted definition is: "a semi-enclosed coastal body of water, which has a free connection with the open sea, and within which seawater is measurably diluted with freshwater derived from land drainage".[1] However, this definition excludes a number of coastal water bodies such as coastal lagoons and brackish seas.

A more comprehensive definition of an estuary is "a semi-enclosed body of water connected to the sea as far as the tidal limit or the salt intrusion limit and receiving freshwater runoff; however the freshwater inflow may not be perennial, the connection to the sea may be closed for part of the year and tidal influence may be negligible".[3] This broad definition also includes fjords, lagoons, river mouths, and tidal creeks. An estuary is a dynamic ecosystem having a connection to the open sea through which the sea water enters with the rhythm of the tides. The effects of tides on estuaries can show nonlinear effects on the movement of water which can have important impacts on the ecosystem and waterflow. The seawater entering the estuary is diluted by the fresh water flowing from rivers and streams. The pattern of dilution varies between different estuaries and depends on the volume of freshwater, the tidal range, and the extent of evaporation of the water in the estuary.[2]

Classification based on geomorphology

Drowned river valleys

Main article: Ria

Drowned river valleys are also known as coastal plain estuaries. In places where the sea level is rising relative to the land, sea water progressively penetrates into river valleys and the topography of the estuary remains similar to that of a river valley. This is the most common type of estuary in temperate climates. Well-studied estuaries include the Severn Estuary in the United Kingdom and the Ems Dollard along the Dutch-German border.

The width-to-depth ratio of these estuaries is typically large, appearing wedge-shaped (in cross-section) in the inner part and broadening and deepening seaward. Water depths rarely exceed 30 m (100 ft). Examples of this type of estuary in the U.S. are the Hudson River, Chesapeake Bay, and Delaware Bay along the Mid-Atlantic coast, and Galveston Bay and Tampa Bay along the Gulf Coast.[5]

Lagoon-type or bar-built

See also: Mouth bar

Bar-built estuaries are found in a place where the deposition of sediment has kept pace with rising sea levels so that the estuaries are shallow and separated from the sea by sand spits or barrier islands. They are relatively common in tropical and subtropical locations.

These estuaries are semi-isolated from ocean waters by barrier beaches (barrier islands and barrier spits). Formation of barrier beaches partially encloses the estuary, with only narrow inlets allowing contact with the ocean waters. Bar-built estuaries typically develop on gently sloping plains located along tectonically stable edges of continents and marginal sea coasts. They are extensive along the Atlantic and Gulf coasts of the U.S. in areas with active coastal deposition of sediments and where tidal ranges are less than 4 m (13 ft). The barrier beaches that enclose bar-built estuaries have been developed in several ways:

Fjord-type

Fjords were formed where Pleistocene glaciers deepened and widened existing river valleys so that they become U-shaped in cross-sections. At their mouths there are typically rocks, bars or sills of glacial deposits, which have the effects of modifying the estuarine circulation.

Fjord-type estuaries are formed in deeply eroded valleys formed by glaciers. These U-shaped estuaries typically have steep sides, rock bottoms, and underwater sills contoured by glacial movement. The estuary is shallowest at its mouth, where terminal glacial moraines or rock bars form sills that restrict water flow. In the upper reaches of the estuary, the depth can exceed 300 m (1,000 ft). The width-to-depth ratio is generally small. In estuaries with very shallow sills, tidal oscillations only affect the water down to the depth of the sill, and the waters deeper than that may remain stagnant for a very long time, so there is only an occasional exchange of the deep water of the estuary with the ocean. If the sill depth is deep, water circulation is less restricted, and there is a slow but steady exchange of water between the estuary and the ocean. Fjord-type estuaries can be found along the coasts of Alaska, the Puget Sound region of western Washington state, British Columbia, eastern Canada, Greenland, Iceland, New Zealand, and Norway.

Tectonically produced

These estuaries are formed by subsidence or land cut off from the ocean by land movement associated with faulting, volcanoes, and landslides. Inundation from eustatic sea-level rise during the Holocene Epoch has also contributed to the formation of these estuaries. are only a small number of tectonically produced estuaries; one example is the San Francisco Bay, which was formed by the crustal movements of the San Andreas fault system causing the inundation of the lower reaches of the Sacramento and San Joaquin rivers.[6]

Classification based on water circulation

See also: Estuarine water circulation

Salt wedge

"Salt wedge" redirects here. Not to be confused with Salt wedging (geology).

See also: Saltwater intrusion

In this type of estuary, river output greatly exceeds marine input and tidal effects have minor importance. Freshwater floats on top of the seawater in a layer that gradually thins as it moves seaward. The denser seawater moves landward along the bottom of the estuary, forming a wedge-shaped layer that is thinner as it approaches land. As a velocity difference develops between the two layers, shear forces generate internal waves at the interface, mixing the seawater upward with the freshwater. An example of a salt wedge estuary is the Mississippi River.[6]

Partially mixed

As tidal forcing increases, river output becomes less than the marine input. Here, current induced turbulence causes mixing of the whole water column such that salinity varies more longitudinally rather than vertically, leading to a moderately stratified condition. Examples include the Chesapeake Bay and Narragansett Bay.[6]

Well-mixed

Tidal mixing forces exceed river output, resulting in a well-mixed water column and the disappearance of the vertical salinity gradient. The freshwater-seawater boundary is eliminated due to the intense turbulent mixing and eddy effects. The lower reaches of Delaware Bay and the Raritan River in New Jersey are examples of vertically homogeneous estuaries.[6]

Inverse

Inverse estuaries occur in dry climates where evaporation greatly exceeds the inflow of freshwater. A salinity maximum zone is formed, and both riverine and oceanic water flow close to the surface towards this zone.[7] This water is pushed downward and spreads along the bottom in both the seaward and landward direction.[3] An example of an inverse estuary is Spencer Gulf, South Australia.[8]

Intermittent

Estuary type varies dramatically depending on freshwater input, and is capable of changing from a wholly marine embayment to any of the other estuary types.[9][10]

Physiochemical variation

The most important variable characteristics of estuary water are the concentration of dissolved oxygen, salinity and sediment load. There is extreme spatial variability in salinity, with a range of near-zero at the tidal limit of tributary rivers to 3.4% at the estuary mouth. At any one point, the salinity will vary considerably over time and seasons, making it a harsh environment for organisms. Sediment often settles in intertidal mudflats which are extremely difficult to colonize. No points of attachment exist for algae, so vegetation based habitat is not established.[clarification needed] Sediment can also clog feeding and respiratory structures of species, and special adaptations exist within mudflat species to cope with this problem. Lastly, dissolved oxygen variation can cause problems for life forms. Nutrient-rich sediment from man-made sources can promote primary production life cycles, perhaps leading to eventual decay removing the dissolved oxygen from the water; thus hypoxic or anoxic zones can develop.[11]

Implications of eutrophication on estuaries

Further information: Eutrophication § Coastal waters

Effects of eutrophication on biogeochemical cycles

Processes that nitrogen undergo in estuarine systems.
Processes that nitrogen undergo in estuarine systems.

Nitrogen is often the lead cause of eutrophication in estuaries in temperate zones.[12] During a eutrophication event, biogeochemical feedback decreases the amount of available silica.[13] These feedbacks also increase the supply of nitrogen and phosphorus, creating conditions where harmful algal blooms can persist. Given the now off-balance nitrogen cycle, estuaries can be driven to phosphorus limitation instead of nitrogen limitation. Estuaries can be severely impacted by an unbalanced phosphorus cycle, as phosphorus interacts with nitrogen and silica availability.

With an abundance of nutrients in the ecosystem, plants and algae overgrow and eventually decompose, which produce a significant amount of carbon dioxide.[14] While releasing CO2 into the water and atmosphere, these organisms are also intaking all or nearly all of the available oxygen creating a hypoxic environment and unbalanced oxygen cycle.[15] The excess carbon in the form of CO2 can lead to low pH levels and ocean acidification, which is more harmful for vulnerable coastal regions like estuaries.

Effects of eutrophication on estuarine plants

A salt marsh with wood storks wading.
A salt marsh with wood storks wading.

Eutrophication has been seen to negatively impact many plant communities in estuarine ecosystems.[16] Salt marshes are a type of ecosystem in some estuaries that have been negatively impacted by eutrophication.[16] Cordgrass vegetation dominates the salt marsh landscape.[17] Excess nutrients allow the plants to grow at greater rates in above ground biomass, however less energy is allocated to the roots since nutrients is abundant.[16][18] This leads to a lower biomass in the vegetation below ground which destabilizes the banks of the marsh causing increased rates of erosion.[16] A similar phenomenon occurs in mangrove swamps, which are another potential ecosystem in estuaries.[18][19] An increase in nitrogen causes an increase in shoot growth and a decrease in root growth.[18] Weaker root systems cause a mangrove tree to be less resilient in seasons of drought, which can lead to the death of the mangrove.[18] This shift in above ground and below ground biomass caused by eutrophication could hindered plant success in these ecosystems.[16][18]

Effects of eutrophication on estuarine animals

Example of a whitefish
Example of a whitefish

Across all biomes, eutrophication often results in plant death but the impacts do not end there. Plant death alters the entire food web structure which can result in the death of animals within the afflicted biome. Estuaries are hotspots for biodiversity, containing a majority of commercial fish catch, making the impacts of eutrophication that much greater within estuaries.[20] Some specific estuarine animals feel the effects of eutrophication more strongly than others. One example is the whitefish species from the European Alps.[21] Eutrophication reduced the oxygen levels in their habitats so greatly that whitefish eggs could not survive, causing local extinctions.[21] However, some animals, such as carnivorous fish, tend to do well in nutrient poor environments and can benefit from eutrophication.[22] This can be seen in populations of bass or pikes.[22]

Effects of eutrophication on human activities

Commercial fishing boat
Commercial fishing boat

Eutrophication can affect many marine habitats which can lead to economic consequences. The commercial fishing industry relies upon estuaries for approximately 68 percent of their catch by value because of the great biodiversity of this ecosystem.[23] During an algal bloom, fishermen have noticed a significant increase in the quantity of fish.[24] A sudden increase in primary productivity causes spikes in fish populations which leads to more oxygen being utilized.[24] It is the continued deoxygenation of the water that then causes a decline in fish populations. These effects can begin in estuaries and have a wide effect on the surrounding water bodies.  In turn, this can decrease fishing industry sales in one area and across the country.[25] Production in 2016 from recreational and commercial fishing contributes billions of dollars to the United States’ gross domestic product (GDP).[23] A decrease in production within this industry can affect any of the 1.7 million people the fishing industry employs yearly across the United States.

Implications for marine life

Estuaries are incredibly dynamic systems, where temperature, salinity, turbidity, depth and flow all change daily in response to the tides. This dynamism makes estuaries highly productive habitats, but also make it difficult for many species to survive year-round. As a result, estuaries large and small experience strong seasonal variation in their fish communities.[26] In winter, the fish community is dominated by hardy marine residents, and in summer a variety of marine and anadromous fishes move into and out of estuaries, capitalizing on their high productivity.[27] Estuaries provide a critical habitat to a variety of species that rely on estuaries for life-cycle completion. Pacific Herring (Clupea pallasii) are known to lay their eggs in estuaries and bays, surfperch give birth in estuaries, juvenile flatfish and rockfish migrate to estuaries to rear, and anadromous salmonids and lampreys use estuaries as migration corridors.[28] Also, migratory bird populations, such as the black-tailed godwit,[29] rely on estuaries.

Two of the main challenges of estuarine life are the variability in salinity and sedimentation. Many species of fish and invertebrates have various methods to control or conform to the shifts in salt concentrations and are termed osmoconformers and osmoregulators. Many animals also burrow to avoid predation and to live in a more stable sedimental environment. However, large numbers of bacteria are found within the sediment which has a very high oxygen demand. This reduces the levels of oxygen within the sediment often resulting in partially anoxic conditions, which can be further exacerbated by limited water flow.

Phytoplankton are key primary producers in estuaries. They move with the water bodies and can be flushed in and out with the tides. Their productivity is largely dependent upon the turbidity of the water. The main phytoplankton present are diatoms and dinoflagellates which are abundant in the sediment.

It is important to remember that a primary source of food for many organisms on estuaries, including bacteria, is detritus from the settlement of the sedimentation.

Human impact

Further information: Ecosystem service § Estuarine and coastal ecosystem services, and Marine ecosystem § Threats

Of the thirty-two largest cities in the world in the early 1990s, twenty-two were located on estuaries.[30]

As ecosystems, estuaries are under threat from human activities such as pollution and overfishing. They are also threatened by sewage, coastal settlement, land clearance and much more. Estuaries are affected by events far upstream, and concentrate materials such as pollutants and sediments.[31] Land run-off and industrial, agricultural, and domestic waste enter rivers and are discharged into estuaries. Contaminants can be introduced which do not disintegrate rapidly in the marine environment, such as plastics, pesticides, furans, dioxins, phenols and heavy metals.

Such toxins can accumulate in the tissues of many species of aquatic life in a process called bioaccumulation. They also accumulate in benthic environments, such as estuaries and bay muds: a geological record of human activities of the last century. The elemental composition of biofilm reflect areas of the estuary impacted by human activities, and over time may shift the basic composition of the ecosystem, and the reversible or irreversible changes in the abiotic and biotic parts of the systems from the bottom up.[32]

For example, Chinese and Russian industrial pollution, such as phenols and heavy metals, has devastated fish stocks in the Amur River and damaged its estuary soil.[33]

Estuaries tend to be naturally eutrophic because land runoff discharges nutrients into estuaries. With human activities, land run-off also now includes the many chemicals used as fertilizers in agriculture as well as waste from livestock and humans. Excess oxygen-depleting chemicals in the water can lead to hypoxia and the creation of dead zones.[34] This can result in reductions in water quality, fish, and other animal populations. Overfishing also occurs. Chesapeake Bay once had a flourishing oyster population that has been almost wiped out by overfishing. Oysters filter these pollutants, and either eat them or shape them into small packets that are deposited on the bottom where they are harmless. Historically the oysters filtered the estuary's entire water volume of excess nutrients every three or four days. Today that process takes almost a year,[35] and sediment, nutrients, and algae can cause problems in local waters.

Examples

Africa[edit]

Asia[edit]

Europe[edit]

North America[edit]

Oceania[edit]

South America[edit]

See also

References

  1. ^ a b Pritchard, D. W. (1967). "What is an estuary: physical viewpoint". In Lauf, G. H. (ed.). Estuaries. A.A.A.S. Publ. Vol. 83. Washington, DC. pp. 3–5. hdl:1969.3/24383.
  2. ^ a b McLusky, D. S.; Elliott, M. (2004). The Estuarine Ecosystem: Ecology, Threats and Management. New York: Oxford University Press. ISBN 978-0-19-852508-0.
  3. ^ a b c d Wolanski, E. (2007). Estuarine Ecohydrology. Amsterdam: Elsevier. ISBN 978-0-444-53066-0.
  4. ^ Silva, Sergio; Lowry, Maran; Macaya-Solis, Consuelo; Byatt, Barry; Lucas, Martyn C. (2017). "Can navigation locks be used to help migratory fishes with poor swimming performance pass tidal barrages? A test with lampreys". Ecological Engineering. 102: 291–302. doi:10.1016/j.ecoleng.2017.02.027.
  5. ^ Kunneke, J. T.; Palik, T. F. (1984). "Tampa Bay environmental atlas" (PDF). U.S. Fish Wildl. Serv. Biol. Rep. 85 (15): 3. Retrieved January 12, 2010.
  6. ^ a b c d Kennish, M. J. (1986). Ecology of Estuaries. Volume I: Physical and Chemical Aspects. Boca Raton, FL: CRC Press. ISBN 978-0-8493-5892-0.
  7. ^ Wolanski, E. (1986). "An evaporation-driven salinity maximum zone in Australian tropical estuaries". Estuarine, Coastal and Shelf Science. 22 (4): 415–424. Bibcode:1986ECSS...22..415W. doi:10.1016/0272-7714(86)90065-X.
  8. ^ a b Gostin, V. & Hall, S.M. (2014): Spencer Gulf: Geological setting and evolution. In: Natural History of Spencer Gulf. Royal Society of South Australia Inc. p. 21. ISBN 9780959662764
  9. ^ Tomczak, M. (2000). "Oceanography Notes Ch. 12: Estuaries". Archived from the original on 7 December 2006. Retrieved 30 November 2006.
  10. ^ Day, J. H. (1981). Estuarine Ecology. Rotterdam: A. A. Balkema. ISBN 978-90-6191-205-7.
  11. ^ Kaiser; et al. (2005). Marine Ecology. Processes, Systems and Impacts. New York: Oxford University Press. ISBN 978-0199249756.
  12. ^ Howarth, Robert W.; Marino, Roxanne (2006). "Nitrogen as the limiting nutrient for eutrophication in coastal marine ecosystems: Evolving views over three decades". Limnology and Oceanography. 51 (1part2): 364–376. Bibcode:2006LimOc..51..364H. doi:10.4319/lo.2006.51.1_part_2.0364. ISSN 0024-3590. S2CID 18144068.
  13. ^ Howarth, Robert; Chan, Francis; Conley, Daniel J; Garnier, Josette; Doney, Scott C; Marino, Roxanne; Billen, Gilles (2011). "Coupled biogeochemical cycles: eutrophication and hypoxia in temperate estuaries and coastal marine ecosystems". Frontiers in Ecology and the Environment. 9 (1): 18–26. doi:10.1890/100008. hdl:1813/60819. ISSN 1540-9295.
  14. ^ Morales-Williams, Ana M.; Wanamaker, Alan D.; Williams, Clayton J.; Downing, John A. (2021). "Eutrophication Drives Extreme Seasonal CO2 Flux in Lake Ecosystems". Ecosystems. 24 (2): 434–450. doi:10.1007/s10021-020-00527-2. ISSN 1432-9840. S2CID 220856626.
  15. ^ Selman, Mindy; Sugg, Zachary; Greenhalgh, Suzie (2008). Eutrophication and Hypoxia in Coastal Areas. ISBN 978-1-56973-681-4.
  16. ^ a b c d e Deegan, Linda A.; Johnson, David Samuel; Warren, R. Scott; Peterson, Bruce J.; Fleeger, John W.; Fagherazzi, Sergio; Wollheim, Wilfred M. (2012). "Coastal eutrophication as a driver of salt marsh loss". Nature. 490 (7420): 388–392. Bibcode:2012Natur.490..388D. doi:10.1038/nature11533. ISSN 0028-0836. PMID 23075989. S2CID 4414196.
  17. ^ Donnelly, Jeffrey P.; Bertness, Mark D. (2001). "Rapid shoreward encroachment of salt marsh cordgrass in response to accelerated sea-level rise". Proceedings of the National Academy of Sciences. 98 (25): 14218–14223. Bibcode:2001PNAS...9814218D. doi:10.1073/pnas.251209298. ISSN 0027-8424. PMC 64662. PMID 11724926.
  18. ^ a b c d e Lovelock, Catherine E.; Ball, Marilyn C.; Martin, Katherine C.; C. Feller, Ilka (2009). "Nutrient Enrichment Increases Mortality of Mangroves". PLOS ONE. 4 (5): e5600. Bibcode:2009PLoSO...4.5600L. doi:10.1371/journal.pone.0005600. ISSN 1932-6203. PMC 2679148. PMID 19440554.
  19. ^ Guest, Michaela A.; Connolly, Rod M. (2005). "Fine-scale movement and assimilation of carbon in saltmarsh and mangrove habitat by resident animals". Aquatic Ecology. 38 (4): 599–609. doi:10.1007/s10452-005-0442-9. ISSN 1386-2588. S2CID 20771999.
  20. ^ Waltham, Nathan J.; McCann, Jack; Power, Trent; Moore, Matt; Buelow, Christina (2020). "Patterns of fish use in urban estuaries: Engineering maintenance schedules to protect broader seascape habitat". Estuarine, Coastal and Shelf Science. 238: 106729. Bibcode:2020ECSS..23806729W. doi:10.1016/j.ecss.2020.106729. ISSN 0272-7714. S2CID 216460098.
  21. ^ a b Vonlanthen, P., Bittner, D., Hudson A.G., et al. (2012). Eutrophication causes speciation reversal in whitefish adaptive radiations. Nature. 482, 337-362. DOI: 10.1038/nature0824.
  22. ^ a b Jeppesen, Erik; Peder Jensen, Jens; Søndergaard, Martin; Lauridsen, Torben; Junge Pedersen, Leif; Jensen, Lars (1997), "Top-down control in freshwater lakes: the role of nutrient state, submerged macrophytes and water depth", Shallow Lakes ’95, Dordrecht: Springer Netherlands, pp. 151–164, doi:10.1007/978-94-011-5648-6_17, ISBN 978-94-010-6382-1, retrieved 2022-04-20
  23. ^ a b Lellis-Dibble, K.A. (2008). "Estuarine Fish and Shellfish Species in US commercial and Recreational Fisheries: Economic Value as an Incentive to Protect and Restore Estuarine Habitat". National Oceanic and Atmospheric Administration.
  24. ^ a b Gao, Yang; Lee, Jeong-Yeol (2012-12-30). "Compensatory Responses of Nile Tilapia Oreochromis niloticus under Different Feed-Deprivation Regimes". Fisheries and Aquatic Sciences. 15 (4): 305–311. doi:10.5657/fas.2012.0305. ISSN 2234-1749.
  25. ^ Fay, Gavin; DePiper, Geret; Steinback, Scott; Gamble, Robert J.; Link, Jason S. (2019). "Economic and Ecosystem Effects of Fishing on the Northeast US Shelf". Frontiers in Marine Science. 6. doi:10.3389/fmars.2019.00133. ISSN 2296-7745.
  26. ^ Osborn, Katherine (December 2017). Seasonal fish and invertebrate communities in three northern California estuaries (M.S. thesis). Humboldt State University.
  27. ^ Allen, Larry G. (1982). "Seasonal abundance, composition and productivity of the littoral fish assemblage in Upper Newport Bay, California" (PDF). Fishery Bulletin. 80 (4): 769–790.
  28. ^ Gillanders, BM; Able, KW; Brown, JA; Eggleston, DB; Sheridan, PF (2003). "Evidence of connectivity between juvenile and adult habitats for mobile marine fauna: An important component of nurseries". Marine Ecology Progress Series. 247: 281–295. Bibcode:2003MEPS..247..281G. doi:10.3354/meps247281. JSTOR 24866466.
  29. ^ Gill, Jennifer A.; Norris, Ken; Potts, Peter M.; Gunnarsson, Tómas Grétar; Atkinson, Philip W.; Sutherland, William J. (2001). "The buffer effect and large-scale population regulation in migratory birds". Nature. 412 (6845): 436–438. Bibcode:2001Natur.412..436G. doi:10.1038/35086568. PMID 11473317. S2CID 4308197.
  30. ^ Ross, D. A. (1995). Introduction to Oceanography. New York: Harper Collins College Publishers. ISBN 978-0-673-46938-0.
  31. ^ Branch, George (1999). "Estuarine vulnerability and ecological impacts". Trends in Ecology & Evolution. 14 (12): 499. doi:10.1016/S0169-5347(99)01732-2.
  32. ^ García-Alonso, J.; Lercari, D.; Araujo, B.F.; Almeida, M.G.; Rezende, C.E. (2017). "Total and extractable elemental composition of the intertidal estuarine biofilm of the Río de la Plata: Disentangling natural and anthropogenic influences". Estuarine, Coastal and Shelf Science. 187: 53–61. Bibcode:2017ECSS..187...53G. doi:10.1016/j.ecss.2016.12.018.
  33. ^ "Indigenous Peoples of the Russian North, Siberia and Far East: Nivkh" Archived 2009-08-07 at the Wayback Machine by Arctic Network for the Support of the Indigenous Peoples of the Russian Arctic
  34. ^ Gerlach, Sebastian A. (1981). Marine Pollution: Diagnosis and Therapy. Berlin: Springer. ISBN 978-0387109404.
  35. ^ "Oyster Reefs: Ecological importance". US National Oceanic and Atmospheric Administration. Archived from the original on October 3, 2008. Retrieved 2008-01-16.
  36. ^ "สัณฐานชายฝั่ง - ระบบฐานข้อมูลทรัพยากรทางทะเลและชายฝั่ง กรมทรัพยากรทางทะเลและชายฝั่ง". km.dmcr.go.th.
  37. ^ "พื้นที่ชุ่มน้ำในประเทศไทย". wetland.onep.go.th.
  38. ^ "Dawei(Tavoy)". myanmarholiday.com. Archived from the original on 2020-07-31. Retrieved 2019-06-14.
  39. ^ Noman, Md. Abu; Mamunur, Rashid; Islam, M. Shahanul; Hossain, M. Belal (2018). "Spatial and seasonal distribution of Intertidal Macrobenthos with their biomass and functional feeding guilds in the Naf River estuary, Bangladesh". Journal of Oceanology and Limnology. 37 (3): 1010–1023. Bibcode:2019JOL....37.1010N. doi:10.1007/s00343-019-8063-7. S2CID 92734488.
  40. ^ Jakobsen, F.; Azam, M.H.; Mahboob-Ul-Kabir, M. (2002). "Residual Flow in the Meghna Estuary on the Coastline of Bangladesh". Estuarine, Coastal and Shelf Science. 55 (4): 587–597. Bibcode:2002ECSS...55..587J. doi:10.1006/ecss.2001.0929.
  41. ^ "The Amazon River Estuary". etai's web.