Wetlands

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Wetlands

Swamps

Marshes

Shallow open water

Wetland ecology

Losses of wetlands

Resources

Wetlands are low-lying ecosystems that are permanently or periodically saturated with water at or close to the surface. The vegetation of wetlands is adapted to survival under flooded conditions. The most common types of wetlands are swamps, marshes, shallow open waters, and mires (which contains peat-accumulating fens and bogs).

Wetlands provide important habitat for a wide variety of plants and animals. However, wetlands are rapidly disappearing because they are being drained and in-filled for agricultural, urbanization, and industrial purposes. Wetlands are also being degraded by the influx of excessive nutrients; the resulting explosive growth of microorganisms depletes the oxygen from the water (eutrophication). Wetlands are also being degraded by pollution associated with inputs of toxic chemicals and organic materials. Losses of wetlands and the biodiversity that they support are an extremely important aspect of the environmental crisis.

Swamps

swamps are forested or shrub-dominated wetlands, usually associated with low-lying, periodically or permanently flooded areas around streams and rivers. Water flows through swamps, although the movement can sometimes be imperceptible. In southeastern North America swamp forests can be extensive, and are typically dominated by tree species such as bald cypress (Taxodium distichum ), water tupelo (Nyssa sylvatica ), swamp tupelo (N. sylvatica ), and eastern white cedar (Chamaecyparis thyoides ). More northern swamps are usually dominated by red maple (Acer rubrum ), silver maple (Acer saccharinum ), American elm (Ulmus americana ), and green or swamp ash (Fraxinus pennsylvanica ). Freshwater tropical swamps can support much-more diverse species of angiosperm trees, while tropical mangrove swamps support only a few tree species that are tolerant of the brackish water.

Swamps provide habitat for numerous species of animals, many of which have a specific requirement for this type of habitat. For example, swamps of bald cypress in southeastern North America provide habitat for the pileated woodpecker (Dryocopus pileatus ), red-shouldered hawk (Buteo lineatus ), prothonotary warbler (Protonotaria citrea ), Carolina wren (Thryothorus ludovicianus ), and many other small birds. These swamps also provide nesting habitat for wood duck (Aix sponsa ) and for colonies of wading birds such as herons and egrets (e.g., great blue heron, Ardea herodias, and common egret, Casmerodius albus ) and wood stork (Mycteria americana ). Cypress swamps also support mammals, including swamp rabbit (Sylvilagus aquaticus ), white-tailed deer (Odocoileus virginianus ), and panther (Felis concolor ), along with many species of amphibians and reptiles, including the American alligator (Alligator mississippiensis ).

Marshes

a marsh is a wetland in which the vegetation is dominated by tall grass-like plants. Typical plants of North American marshes include cattails (e.g., Typha latifolia ), reeds (e.g., Phragmites communis ), bulrushes (e.g., Scirpus validus ), and saw-grass (Cladium jamaicense ).

Because they are rather productive, marshes can support relatively large populations of certain mammals, such as muskrat (Ondatra zibethicus ). Birds can also be abundant in marshes. This is true of large, extensive marshes, and also of relatively small marshes around lakes and ponds. For example, small ponds are common in the prairies of North America, where they are called potholes. The marshy borders of potholes have historically provided important breeding habitat for most of the continents surface-feeding ducks. Unfortunately, most potholes have been drained or filled to provide land for agriculture. This ecological conversion has increased the importance of the remaining potholes as habitat for declining populations of ducks, other animals, and native plants. Further losses of this habitat type are vigorously resisted by the conservation community, even though agricultural interests continue to encourage the drainage of these important wetlands.

Farther to the north, extensive salt marshes and freshwater fringing marshes provide important breeding habitat for geese, especially snow goose (Chen caerulescens ) and Canada goose (Branta canadensis ).

Shallow open water

Shallow, open-water wetlands are known locally by names such as ponds, sloughs, and potholes. These are small bodies of surface water, less than about 7 feet (2 meters) in depth that often contain floating-leaved vegetation. These wetlands and their fringing marshes can support relatively large populations of waterfowl, amphibians, and other animals.

Wetland ecology

Wetlands are dynamic ecosystems, transitional between terrestrial and aquatic habitats. Over time, most wetlands gradually fill in because of the ongoing deposition of sediment and peat. Consequently, wetlands are most numerous in places where geological forces such as glaciation periodically create conditions that are favorable to their formation.

The ecological conditions of wetlands are dominated by the influences of permanent or temporary waterlogging (the saturation of soil with water). The availability of water to sustain plant growth is not a problem in wetlands. However, waterlogged soil or sediment are usually lacking in oxygen, a factor that inhibits respiration by plant roots. To cope with this stressful environmental condition, some plants have evolved specific adaptations to supply oxygen to their roots. For example, cattails and bulrushes have spongy, air-filled stem and root tissues (aerenchyma), which helps in the transport of oxygen to underwater tissues. Some trees, such as bald cypress and black mangrove, have specialized woody structures called pneumatophores that extend from roots into the air, and have extensive intercellular spaces that are useful in supplying oxygen to below-water tissues.

The anaerobic (oxygen-free) nature of wetland substrates also causes other chemical changes that can pose important problems for plants, by affecting their nutrition and exposing roots to toxic chemicals. For example, access to certain nutrients can be difficult under anaerobic conditions. This is because the nutrients may not be present in a chemical form that is easy for roots to take up, or because roots cannot sustain the oxygen-demanding respiratory demands required for the active uptake of nutrient ions. Anaerobic conditions also encourage the solubilization of certain potentially toxic metals, such as manganese. In addition, anaerobic metabolism within root tissues can lead to excessive accumulations of alcohols, possibly causing toxicity. In general, wetland plants are well-adapted to these conditions, although they may nevertheless be physiologically stressed if these factors are severe enough.

Wetland hydrology is highly variable. Some wetlands are permanently flooded, while others are only waterlogged some of the time, usually seasonally. These dynamics greatly influence the types of plants that can occur in particular wetlands, and on the communities that they develop. Tolerance of permanent or frequent flooding, as occurs, for example, in salt marshes, mangroves, and some swamps, requires highly adapted species of plants. In comparison, wetlands that are only occasionally flooded are, in some respects, a more ephemeral transitional between truly aquatic and terrestrial environments. In these situations, plants must only be tolerant of the stresses of sporadic events of flooding, while growing relatively freely when the water recedes and the soil is drier.

Another highly influential environmental factor in wetlands is the supply of plant nutrients. In general, wetlands that are well supplied with phosphorus (in the form of phosphate), and to a lesser degree nitrogen (as nitrate or ammonium), sustain relatively high rates of plant productivity, and consequently large populations of animals. This is commonly the case for marshes, which are among the most productive natural ecosystems on Earth. In contrast, wetlands with restricted supplies of nutrients, such as ombrotrophic bogs, sustain only small productivities of plants and animals.

Losses of wetlands

All wetlands have great intrinsic value as natural ecosystems, and they all support species of plants and animals that occur nowhere else. Consequently, wetlands have great value in terms of biodiversity.

Sometimes, the biodiversity-related importance of particular types of wetlands is a matter of their relative abundance, in the regional context. For example, although bogs and fens can be extremely abundant in boreal and sub-arctic regions of northern North America, these types of wetlands are uncommon farther south. In these southern regions, the few bogs and fens that occur have great conservation value as scarce and unusual ecosystems, and because most of their species of plants and arthropods are regionally or locally rare. Any proposals to convert these wetlands into agricultural or urbanized lands are usually controversial, because these conversions would cause an irretrievable loss of natural values.

Wetlands also provide essential habitat for species of birds and mammals that are hunted, and this gives them economic value. Waterfowl such as ducks and geese occur primarily in marshes and swamps. During the past century the populations of some of these hunted waterfowl were greatly decreased, as a combined effect of overhunting and loss of natural habitats. Consequently, there are now substantial efforts to regulate hunting, and to preserve or enhance the marshes and swamps that are required as habitat by these birds. Some species of waterfowl are responding well to these conservation measures, and their populations are increasing.

Wetlands are also important because they offer other ecological goods and services, in addition to those previously described. For example, wetlands maintain some control over hydrology, helping to prevent extremes of water flow. This service moderates the risks of flooding caused by heavy rain or the spring flush of snowmelt in northern regions. It also helps to extend supplies of water for drinking or irrigation longer into the drier seasons of the year. Wetlands also provide important services by cleansing the water that flows through them of pollutants, including nutrients and toxic chemicals, such as metals and certain pesticides. Furthermore, wetlands are useful in protecting shorelines from erosion, controlling sedimentation, and providing essential habitat for fish, birds, and other wildlife. Wetlands have good aesthetics, and this also contributes to their value as an ecological resource.

Unfortunately, wetlands are being rapidly lost in most of the world. The most important causes of the destruction of wetlands are drainage and in-filling to provide dry land for agriculture, urbanization, and industrialization. Wetlands are also sometimes used as convenient places for the disposal of mine tailings, municipal solid wastes, and sewage. In some cases, wetlands are degraded or lost because economically useful products can be mined from them, especially peat from bogs, and wood from forested swamps. Wetlands are also degraded if they are subjected to large inputs of nutrients through the runoff of agricultural fertilizers or by sewage dumping. These nutrient inputs can cause eutrophication, with a consequent loss of the original ecological values of the wetland.

All of these disturbances, stresses, and ecological conversions result in net losses of wetlands. The ecological consequences include endangerment of natural wetland ecosystems, endangerment of their species of plants and animals, and the loss of many important services that wetlands can provide. The loss of wetlands is an important environmental issue, which can only be resolved by protection of those wetlands that still survive, and in some areas where the losses have been especially severe, by the active restoration of wetlands.

The protection and conservation of wetlands is an important activity of many governments and private organizations. In the United States and Canada, wetlands are among the highest-priority natural habitats for protection by governments at all levels (national, state or provincial, and local). In addition, non-governmental organizations such as the World Wildlife Fund, The Nature Conservancy, the Nature Conservancy of Canada, and Ducks Unlimited have made the conservation and protection of wetlands a high priority in their activities. Internationally, the Convention on Wetlands of International Importance, Especially as Waterfowl Habitat (also known as the Ramsar Convention, after the city in Iran where it was

KEY TERMS

Alkalinity The amount of alkali in a solution. In fresh water, alkalinity is mainly associated with bicarbonates, carbonates, and hydroxides, and it is generally measured by titration with acid to a fixed end point.

Anaerobic Environments in which oxygen is not present, or only present in a very small concentration.

Eutrophication An aquatic ecosystem process by which increased productivity results from an increase in the rate of nutrient input. Excessive eutrophication and its symptoms are regarded as a type of ecological degradation.

Hydrology The study of the distribution, movement, and physical-chemical properties of water in Earths atmosphere, surface, and near-surface crust.

Minerotrophic This refers to wetlands that receive much of their nutrient supply as substances dissolved in water draining from a part of the water-shed that is higher in altitude.

Ombrotrophic This refers to wetlands with no input of nutrients from ground water or surface water, so that all of the nutrient supply arrives from the atmosphere with precipitation and dust.

Watershed The expanse of terrain from which water flows into a wetland, waterbody, or stream.

negotiated) is an intergovernmental treaty that provides a framework for worldwide cooperation in the conservation of wetlands.

Resources

BOOKS

Dugan, Patrick. Guide to Wetlands. Tonawanda: Firefly Books, 2005.

Tiner, Ralph W. In Search of Swampland: A Wetland Sourcebook And Field Guide. Newark: Rutgers University Press, 2005.

van der Valk, Arnold G. The Biology of Freshwater Wetlands. Oxford: Oxfrod University Press, 2006.

Bill Freedman