US Fish and Wildlife Service 1979 Wetland Classification: a Review Lewis M

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US Fish and Wildlife Service 1979 Wetland Classification: a Review Lewis M University of Rhode Island DigitalCommons@URI Natural Resources Science Faculty Publications Natural Resources Science 1995 US Fish and Wildlife Service 1979 wetland classification: A review Lewis M. Cowardin Francis C. Golet University of Rhode Island, [email protected] Follow this and additional works at: https://digitalcommons.uri.edu/nrs_facpubs Terms of Use All rights reserved under copyright. Citation/Publisher Attribution Cowardin, L.M. & Golet, F.C. Vegetatio (1995) 118: 139. https://doi.org/10.1007/BF00045196 Available at: http://dx.doi.org/10.1007/BF00045196 This Article is brought to you for free and open access by the Natural Resources Science at DigitalCommons@URI. It has been accepted for inclusion in Natural Resources Science Faculty Publications by an authorized administrator of DigitalCommons@URI. For more information, please contact [email protected]. Vegetatio 118: 139-152, 1995. 139 (~) 1995 Kluwer Academic ['ublishers. Printed in Belgium. US Fish and Wildlife Service 1979 wetland classification: A review* Lewis M. Cowardin I & Francis C. Golet 2 1us Fish and Wildlife Service, Northern Prairie Wildlife Research Center, Jamestown, ND 58401, USA; 2Department of Natural Resources Science, University of Rhode Island, Kingston, R102881, USA Key words: Classification, Definition, United States, Wetland Abstract In 1979 the US Fish and Wildlife Service published and adopted a classification of wetlands and deepwater habitats of the United States. The system was designed for use in a national inventory of wetlands. It was intended to be ecologically based, to furnish the mapping units needed for the inventory, and to provide national consistency in terminology and definition. We review the performance of the classification after 13 years of use. The definition of wetland is based on national lists of hydric soils and plants that occur in wetlands. Our experience suggests that wetland classifications must facilitate mapping and inventory because these data gathering functions are essential to management and preservation of the wetland resource, but the definitions and taxa must have ecological basis. The most serious problem faced in construction of the classification was lack of data for many of the diverse wetland types. Review of the performance of the classification suggests that, for the most part, it was successful in accomplishing its objectives, but that problem areas should be corrected and modification could strengthen its utility. The classification, at least in concept, could be applied outside the United States. Experience gained in use of the classification can furnish guidance as to pitfalls to be avoided in the wetland classification process. Introduction The USFWS has a long history of involvement in wetland classification and inventory. Conservation and Development of US Classification management of migratory waterfowl are a responsibil- The wetland classification in use today by the US ity of the USFWS based on migratory bird treaties Fish and Wildlife Service (USFWS) was developed with Canada and Mexico. Thus, conservation of wet- between 1975 and 1979 (Cowardin etal. 1979). It orig- land habitats is one of the agency's primary objectives. inated from a need by the USFWS to inventory the wet- The USFWS conducted the first quantitative national land resources of the United States. The stated purpos- inventory of wetlands in the mid-1950s; the results es of the classification were to: (1) describe ecological were summarized in US Fish and Wildlife Service units that have certain homogeneous natural attributes; Circular 39 (Shaw & Fredine 1956). That inventory (2) arrange those units in a system that would aid deci- was based on a classification, developed by Martin sions about resource management; (3) furnish units et al. (1953), which included 20 classes of wetlands. for inventory and mapping; and (4) provide uniformi- After close scrutiny, the authors found that the Martin ty in concepts and terminology throughout the United et al. classification was inconsistently applied among States. The history and development of the classifica- regions. The reason was primarily lack of detail in def- tion is closely related to the development of the Nation- initions. By the mid-1970s, when the current inventory al Wetland Inventory (NWI). This paper describes and was being planned, there had been an explosion of pub- evaluates the classification. The inventory is described lic and professional interest in wetlands that transcend- by Wilen and Bates (this volume). ed the habitat function for migratory birds. Numer- ous excellent regional classifications (e.g., Stewart & * The uS Government's right to retain a non-exclusive, royalty Kantrud 1971, Golet & Larson 1974; Jeglum et al. free licence in and to any copyright is acknowledged. 140 1974; Odum et al. 1974; Zoltai et al. 1975; Millar Overview of the classification 1976) also had been developed since the Martin et al. classification. Definition of wetland and deepwater habitat In January of 1975, the USFWS convened a small Under the USFWS classification (Cowardin et al. number of interested individuals from various agen- 1979:3), wetlands are defined as follows: cies and regions to formulate the skeleton of a new Wetlands are lands transitional between terrestrial classification that could serve as the basis for a new and aquatic systems where the water table is usu- national wetlands inventory. Three important points ally at or near the surface or the land is covered were agreed upon: (1) none of the existing classifi- by shallow water. For the purposes of this clas- cations met the requirement for national uniformity, sification wetlands must have one or more of the (2) regional classifications would not suffice because of following three attributes: (I) at least periodical- the confusion resulting at regional boundaries, and (3) a ly, the land supports predominantly hydrophytes; new classification should be hierarchical in structure. (2) the substrate is predominantly undrained hydric Following that meeting, Cowardin and Carter (1975) soil; and (3) the substrate is nonsoil and is saturat- prepared a tentative classification that was presented ed with water or covered by shallow water at some at a July 1975 national workshop, where 150 federal time during the growing season of each year. and state wetland management personnel were invit- ed to comment on the proposed classification (Sather In support of this definition, the USFWS has prepared 1976). Input from that workshop resulted in major a list of plants known to occur in U.S. wetlands. The modifications of the Cowardin and Carter paper and first draft, released in 1977, contained 4235 species; the led to the preparation of a revision, Interim Classifi- latest version includes more than 7000 species (Reed cation of Wetlands and Aquatic Habitats of the United 1988). Each of the species in this list is placed into States (Cowardin et al. 1976). The revised system was one of four categories according to its frequency of tested using both high- and low-altitude aerial pho- occurrence in wetlands: Obligate Wetland, Faculta- tographs and field-checks at 21 sites scattered across tive Wetland, Facultative, or Facultative Upland (see the country. The NWI staff worked with the authors Table 1 for definitions). of the 1976 classification to resolve practical prob- Also to supplement the USFWS wetland definition, lems encountered during testing. At the same time, the the US Soil Conservation Service has developed a defi- authors tested the evolving classification at numerous nition of hydric soil, taxonomic and hydrologic criteria locations throughout the United States. The final ver- for identifying hydric soils, and a list of the hydric soils sion was published in 1979 (Cowardin et al. 1979); it of the United States. The first draft, Hydric Soils of the was reprinted in 1985 and 1992. The classification has United Sates, was published in 1982 (Soil Conserva- been used by the NWI for 13 years. It has also been tion Service 1982) and subsequent editions (Soil Con- widely used by other federal and state regulatory and servation Service 1985, 1987, 1991) were released. In resource management agencies, as well as by wetland the latest edition (Soil Conservation Service 1991:1), researchers. hydric soil is defined as follows: A hydric soil is a soil that is saturated, flooded, or Objectives of paper ponded long enough during the growing season to This paper has four objectives: (1) to acquaint the read- develop anaerobic conditions in the upper part. er with the structure of the USFWS classification sys- tem, (2) to explain the rationale for the approach to The aim of the NWI was to map not only those areas classification, (3) to review successes as well as prob- traditionally regarded as wetlands, but also those deep- lems encountered during its use, and (4) to evaluate er waters which frequently are associated with wet- the potential for use of the system on an international lands. For that reason, Cowardin et al. (1979) made scale. a clear distinction between wetlands and 'deepwa- ter habitats'. The latter were defined as permanently flooded lands lying below the deepwater boundary of wetlands. In nontidal areas, the boundary between wet- land and deepwater habitat was placed at a depth of 2 m below low water- the maximum depth to which rooted, emergent plants normally grow (Welch 1952; Zhadin 141 Table 1. Wetland indicator categories for plants that occur in US wetlands (fromReed 1988). Category
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