A lowland area, such as a marsh or swamp, that is saturated with moisture, especially when regarded as the natural habitat of wildlife: a program to preserve our state's wetlands.
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A lowland area, such as a marsh or swamp, that is saturated with moisture, especially when regarded as the natural habitat of wildlife: a program to preserve our state's wetlands.
Any land which is intermittently or periodically waterlogged. This includes salt marshes, tidal estuaries, marshes, and bogs. Wetlands are rapidly disappearing habitats; the Everglades National Park, Florida, is a complex of coastal mangroves, tropical saw-grass marshes, and forest on the slightly raised areas, but flood-control measures to the north, and the ever-increasing number of visitors cause intense pressure on the ecosystem. Other wetlands are increasingly being reclaimed for agriculture, industry, or housing.
In the United States a constructed wetland can involve engineering of hydrology and soils, and is intentionally created from non-wetland sites for the sole purpose of wastewater or storm water treatment, but literature from elsewhere may not distinguish between these terms. The concept of a designer wetland emphasizes the life history strategy of species as the major factor in developing vegetation on a restoration site. It favours engineering and replanting strategies directed at producing a wetland type, with no fixed endpoint. Wetland mitigation is the replacing of wetland areas destroyed or impacted by proposed land disturbances with artificially created wetland areas.
In physical geography, a wetland is an environment "at the interface between truly
terrestrial ecosystems and aquatic systems making them inherently different from each other yet highly dependent on both" (Mitsch
& Gosselink, 1986). In essence, wetlands are ecotones. Wetlands often host considerable
biodiversity and endemism. In many locations such as the
United Kingdom and
The United States Army Corps of Engineers and the United States Environmental Protection Agency jointly define wetlands as: Those areas that are inundated or saturated by surface or ground water at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life in saturated soil conditions. Wetlands generally include swamps, marshes, bogs, and similar areas. [1]
Wetlands are found under a wide range of hydrological conditions, but at least some of the time water saturates the soil. The result is a hydric soil, one characterized by an absence of free oxygen some or all of the time, and therefore called a "reducing environment."
Plants (called hydrophytes or just wetland plants) specifically adapted to the reducing conditions presented by such soils can survive in wetlands, whereas species intolerant of the absence of soil oxygen (called "upland" plants) cannot survive. Adaptations to low soil oxygen characterize many wetland species.
There are many types of vegetation in wetlands. There are plants such as Cattails, bulrushes, Sedges, Arrowhead, Water Lilies, Blue Flag, and Floaters like common duckweed. Pondweed is also another type of plant that grows in wetlands, but it is not easily seen. Peatland can be dominated by red maple, silver maple, and Elm trees. Some types of trees in peatland can exhibit lower trunks and roots that have adapted to the wet surroundings by forming buttresses, enlarged root bases to better support the trees in the mucky soil. Trees can also form knees, raised roots that allow for gas exchange. Swamps can also have white Cedar, Tamarack, and White Pine. Below the canopy, there are often limited amounts of shrubs such as speckled Alder, Winterberry, and Sweet Gale.
Mangroves are a species of plant which typically thrive in coastal wetlands (called marine or estuarine environments). They are a special tree taxon that can survive in salty wetland water. Mangroves also provide the base for the wetland food chain. They are the producers in the wetland environment. Because mangroves add sulfur to the wetlands, it makes the water more acidic, therefor allowing decomposed matter in the water to biodegrade faster than it normally would, which in turn, provides more food for the organisms in the wetland ecosystem.
Generally, the hydrology of a wetland is such that the area is permanently or periodically inundated or saturated at the soil surface for a period of time during the growing season. The presence (or absence) of water is not necessarily a good method for identifying wetlands because the amount of water generally fluctuates depending on such things as rainfall patterns, snow melt, dry seasons, and longer droughts. The three water sources that contribute to wetlands are:
Location determines which of these sources will be contributing water to a [wetland].
Below are terms used for various types of wetlands:
The U.S. Fish and Wildlife Service's National Wetlands Inventory (NWI) produces and provides information on the characteristics, extent, and status of U.S. wetlands and deepwater habitats and other wildlife habitats. The NWI also produces periodic reports on the status and trends of wetlands in the conterminous U.S. The NWI website includes a Wetlands Mapper in which users can view, download, or print maps of digital wetlands information.
The Hydrogeomorphic (HGM) Approach is a system developed by the US Army Corps of Engineers to classify all wetlands based on three factors that influence how they function: position in the landscape (geomorphic setting), water source (hydrology), and the flow and fluctuation of the water once in the wetland (hydrodynamics). There are seven classes (types) of wetlands in this system:
This approach also intends to develop subclasses of wetlands to account for specific conditions of various regions.
In contrast to wetlands in other biomes (usually permanent and fresh water), wetlands in
drylands are more diverse in their composition, depending on the local climate and other particularities of the surroundings.
They can be fresh or saline, permanent, seasonal or temporary, filling intermittently or regularly.
Wetlands in drylands can be attributed all values and uses of wetlands found in other biomes. However, given the stark contrast
to their dry surroundings, many of these values are enhanced. This applies to the water balance where gradual release and storage
of rainwater by wetlands amid drylands is crucial due to the unpredictability and incalculability of rain. During dry seasons,
wetlands in drylands are also pivotal as refugia for wildlife, livestock and people. Moreover, biodiversity levels are higher than in wetlands in other major biomes, in particular because of the
accessibility of water amid an otherwise very dry environment.
Hydrologic functions include long term and short term water storage, subsurface water storage, energy dissipation, and moderation of groundwater flow or discharge.
By absorbing the force of strong winds and tides, wetlands protect terrestrial areas adjoining them from storms, floods, and tidal damage.
Nutrient cycling, retention of particulates, removal of imported elements and compounds, and the import and export of organic carbon are all biogeochemical functions of wetlands. Wetlands remove nutrients from surface and ground water by filtering and by converting nutrients to unavailable forms. Denitrification is arguably the most important of these reactions because humans have increased nitrate worldwide by applying fertilizers. Increased nitrate availability can cause eutrophication, but denitrification converts biologically available nitrogen back into nitrogen gas, which is biologically unavailable except to nitrogen fixing bacteria. Denitrification can be detected in many soils, but denitrification is fastest in wetlands soils (for an example, see Ullah and Faulkner 2006).
Intertidal wetlands provide an excellent example of invasion, modification and succession. The invasion and succession process is establishment of seagrasses. These help stabilize sediment and increase sediment capture rates. The trapped sediment gradually develops into mud flats. Mud flat organisms become established encouraging other life forms changing the organic composition of the soil.
Wetland provide a safe and lush environment for many different species of fish, birds, and insects. It includes the mallard duck, the Sickleback fish, mangroves, and water moccasins.
Like animals, their are number of plant communites that will only survive in the unique environmental conditions of a wetland. In the continental U.S. wetlands account for only 5 percent of the total land area but over 30 percent of the nation's vascular flora occur in wetlands.
Mangroves establish themselves in the shallower water upslope from the mudflats. Mangroves further stabilize sediment and over time increase the soil level. This results in less tidal movement and the development of salt marshes. (succession) The salty nature of the soil means it can only be tolerated by special types of grasses e.g. saltbush, rush and sedge. There is also changing species diversity in each succession.
While many of the functions above are directly or indirectly beneficial to humans and society, wetlands are specifically valuable to people as places for recreational and educational activities such as hunting, fishing, camping, and wildlife observation.
In intertidal wetlands the majority of natural stress comes from salinity and tidal movements. The intertidal wetlands must be able to survive extreme conditions of mainly salt water at high tide, fresh water at low tide and times of flood and brackish water at other times. The saline water is a very difficult condition for plants to survive in. The grey mangrove accomplishes this by excluding salt in the root system, salt glands in the leaf, and waxy leaves to minimize water loss. However it is vulnerable to changes in salinity levels.
Changes to tidal movements through increased run-off or altered drainage can cause the roots of mangroves to be inundated for longer than normal periods affecting their pneumatophones. It can also be pushed past its threshold level if water quality is changed. Thus even healthy ecosystems are vulnerable to change.
Some species such as oysters and molluscs have been used as indicator species, with any decline in their numbers indicating the ecosystem is under stress. A change in nutrient levels may also affect primary productivity and thus bring about change.
Wetlands are often filled in to be used by humans for everything from agriculture to parking lots, in part because the economic value of wetlands has only been recognized recently: the shrimp and fish that breed in salt water marshes are generally harvested in deeper water, for example.
Humans can maximize the area of healthy, functioning intertidal wetlands by minimising their impacts and by developing management strategies that protect, and where possible rehabilitate those ecosystems at risk.
Historically, humans have made large-scale efforts to drain wetlands for development or to flood them for use as recreational lakes. Since the 1970s, more focus has been put on preserving wetlands for their natural function—sometimes also at great expense. One example is the project by the U.S. Army Corps of Engineers to control flooding and enhance development by taming the Everglades, a project which has now been reversed to restore much of the wetlands as a natural habitat and method of flood control.
The creation of the treaty known as the Ramsar Convention (1971), or more properly “The Convention on Wetlands of International Importance, especially as Waterfowl Habitat”, demonstrates the global concern regarding wetland loss and degradation. The primary purposes of the treaty are to list wetlands of international importance and to promote their wise use, with the ultimate goal of preserving the world’s wetlands.
In the United States, some wetlands are regulated by the federal government under the Clean Water Act. Determining the boundary between regulated wetlands and non-regulated lands therefore can be contentious. In reality, there is no natural boundary between the classes that humans define on these gradients (wetland/upland), and this issue is highlighted by the U.S. Fish and Wildlife Service’s definition from Classification of Wetlands and Deepwater Habitats of the United States, which defines wetlands as “lands transitional between terrestrial and aquatic systems.” Regulations to protect water quality and highway safety require that we create arbitrary boundaries within those gradients, but these boundaries are scientifically definable, and consist of areas where three criterion of the presence of hydric soils, the presence of wetland vegetation, and the presence of appropriate hydrology. Such regulations must be predictable, reproducible, and enforced. Otherwise, we will sacrifice clean water for development in the case of wetlands regulation (or vice versa), or sacrifice safe travel for quick travel (or vice versa) in the case of speed limits. Determining which wetlands are regulated under section 404 of the clean water act or section 10 of the rivers and harbors act is termed “jurisdictional determination.” Determining the boundary of wetland, whether jurisdictional under sections 404 or 10, or not jurisdictional but still meeting the technical definition of a wetland, that is having the soils, vegetation and hydrology criterion met is called a "wetland delineation," and generally is performed by college graduates with natural science or biology degrees working for engineering firms or environmental consulting firms who are familiar with the 1987 U.S. Army Corps of Engineers Wetland delineation manual. Defining a boundary depends upon soil and vegetation characteristics; it is easier to do where the slope of the land is steeper. Deciding if a wetland is a regulated wetland depends on classifying the water in it as “water of the United States” or not. Classifying water as “of the U.S.” or “not of the U.S.” for purposes of enforcing the Clean Water Act suggests a natural boundary that probably does not exist in nature, and one that was not created regarding air for purposes of enforcing the Clean Air Act.
Wetlands are the focus of the US National Wetlands Coalition, which in turn has become the focus of some controversy over "false fronts," a form of political camouflage.
Wetlands Delineation Manual by Environmental Laboratory U.S. Army Corps of Engineers Waterways Experiment Station 3909 Halls Ferry Road Vicksburg, MS 39180-6199
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Dansk (Danish)
n. - marsk, vådområde
Nederlands (Dutch)
land dat voor een deel van het jaar onder water staat
Français (French)
n. - terres marécageuses
Deutsch (German)
n. - Feuchtgebiet
Ελληνική (Greek)
n. - υδροβιότοπος
Português (Portuguese)
n. - pântano (m)
Русский (Russian)
сильно увлажненная земля
Español (Spanish)
n. - pantano
Svenska (Swedish)
n. - våtmark
中文(简体) (Chinese (Simplified))
潮湿的土壤, 沼泽地
中文(繁體) (Chinese (Traditional))
n. - 潮濕的土壤, 沼澤地
العربيه (Arabic)
(الاسم) منطقه ذات رطوبه عاليه
עברית (Hebrew)
n. - ביצה, אדמה רוויית לחות
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