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State designated Wetlands as compiled by NYS Department of Environmental Conservation. This coverage provides a definitive inventory of state designated Wetlands (greater than 12.4 acres) in Westchester County. Coverage is based on official New York State Freshwater Wetlands Maps as described in Article 24-0301 of the Environmental Conservation Law. Coverages are not, however, a legal substitute for the official maps. For more information go to the NYSDEC website, http://www.dec.state.ny.us.
Hydric Soils derived from soils database (WCSOIL) from the 2013 Westchester County Soil Survey, U.S. Department of Agriculture, Soil Conservation Service. Data was updated September 2015 from U.S. Department of Agriculture, Natural ResourcesConservation Service.
Percent Map symbol and Component of map Landform Hydric Hydric map unit name unit rating criteria --------------------------------------------------------------------------------------------------------------------------------------------------------
Ce: Carlisle muck Carlisle 70 Marshes, Swamps Yes 1, 3 Ff: Fluvaquents-Udifluvents Fluvaquents 35 Flood plains Yes 2B3, 3, 4 complex, frequently flooded Fr: Fredon silt loam Fredon 80 Depressions Yes 2B3 Ip: Ipswich mucky peat Ipswich 80 Tidal marshes Yes 1, 3, 4 LcA: Leicester loam, 0 to 3 percent Leicester 70 Depressions Yes 2B3 slopes, stony Pa: Palms muck Palms 75 Marshes, Swamps Yes 1, 3 Pc: Palms and Carlisle soils, Palms 40 Marshes, Swamps Yes 1, 3 Carlisle 35 Depressions Yes 1, 3 Ra: Raynham silt loam Raynham 75 Depressions Yes 2B3 RdA: Ridgebury loam, 0 to 3 percent Ridgebury 75 Depressions Yes 2B3 Sh: Sun loam Sun 80 Depressions Yes 2B3, 3 Sm: Sun loam, extremely stony Sun 75 Depressions Yes 2B3, 3 This table lists the map unit components that are rated as hydric soils in the survey area. This list can help in planning land uses; however, onsite investigation is recommended to determine the hydric soils on a specific site (National Research Council, 1995; Hurt and others, 2002). The three essential characteristics of wetlands are hydrophytic vegetation, hydric soils, and wetland hydrology (Cowardin and others, 1979; U.S. Army Corps of Engineers, 1987; National Research Council, 1995; Tiner, 1985). Criteria for all of the characteristics must be met for areas to be identified as wetlands. Undrained hydric soils that have natural vegetation should support a dominant population of ecological wetland plant species. Hydric soils that have been converted to other uses should be capable of being restored to wetlands. Hydric soils are defined by the National Technical Committee for Hydric Soils (NTCHS) as soils that formed under conditions of saturation, flooding, or ponding long enough during the growing season to develop anaerobic conditions in the upper part (Federal Register, 1994). These soils, under natural conditions, are either saturated or inundated long enough during the growing season to support the growth and reproduction of hydrophytic vegetation. The NTCHS definition identifies general soil properties that are associated with wetness. In order to determine whether a specific soil is a hydric soil or nonhydric soil, however, more specific information, such as information about the depth and duration of the water table, is needed. Thus, criteria that identify those estimated soil properties unique to hydric soils have been established (Federal Register, 2002). These criteria are used to identify map unit components that normally are associated with wetlands. The criteria used are selected estimated soil properties that are described in "Soil Taxonomy" (Soil Survey Staff, 1999) and "Keys to Soil Taxonomy" (Soil Survey Staff, 2003) and in the "Soil Survey Manual" (Soil Survey Division Staff, 1993). If soils are wet enough for a long enough period of time to be considered hydric, they should exhibit certain properties that can be easily observed in the field. These visible properties are indicators of hydric soils. The indicators used to make onsite determinations of hydric soils are specified in "Field Indicators of Hydric Soils in the United States" (Hurt and others, 2002). Hydric soils are identified by examining and describing the soil to a depth of about 20 inches. This depth may be greater if determination of an appropriate indicator so requires. It is always recommended that soils be excavated and described to the depth necessary for an understanding of the redoximorphic processes. Then, using the completed soil descriptions, soil scientists can compare the soil features required by each indicator and specify which indicators have been matched with the conditions observed in the soil. The soil can be identified as a hydric soil if at least one of the approved indicators is present. Map units that are dominantly made up of hydric soils may have small areas, or inclusions, of nonhydric soils in the higher positions on the landform, and map units dominantly made up of nonhydric soils may have inclusions of hydric soils in the lower positions on the landform. The criteria for hydric soils are represented by codes in the table (for example, 2B3). Definitions for the codes are as follows: 1. All Histels except for Folistels, and Histosols except for Folists. 2. Soils in Aquic suborders, great groups, or subgroups, Albolls suborder, Historthels great group, Histoturbels great group, Pachic subgroups, or Cumulic subgroups that: A. are somewhat poorly drained and have a water table at the surface (0.0 feet) during the growing season, or B. are poorly drained or very poorly drained and have either: 1) a water table at the surface (0.0 feet) during the growing season if textures are coarse sand, sand, or fine sand in all layers within a depth of 20 inches, or 2) a water table at a depth of 0.5 foot or less during the growing season if permeability is equal to or greater than 6.0 in/hr in all layers within a depth of 20 inches, or 3) a water table at a depth of 1.0 foot or less during the growing season if permeability is less than 6.0 in/hr in any layer within a depth of 20 inches. 3. Soils that are frequently ponded for long or very long duration during the growing season. 4. Soils that are frequently flooded for long or very long duration during the growing season. References: Cowardin, L.M., V. Carter, F.C. Golet, and E.T. LaRoe. 1979. Classification of wetlands and deep-water habitats of the United States. U.S. Fish and Wildlife Service FWS/OBS-79/31. Federal Register. September 18, 2002. Hydric soils of the United States. Federal Register. July 13, 1994. Changes in hydric soils of the United States. Hurt, G.W., P.M. Whited, and R.F. Pringle, editors. Version 5.0, 2002. Field indicators of hydric soils in the United States. National Research Council. 1995. Wetlands: Characteristics and boundaries. Soil Survey Division Staff. 1993. Soil survey manual. Soil Conservation Service. U.S. Department of Agriculture Handbook 18.
Data was last processed in April 2020. This layer represents 2019 tax parcel polygons in Westchester County. It was assembled from the collection of tax parcel assessment information of 25 different municipal jurisdictions. Assessment data is from ORPTS 2019 assessment. City names and zip code values were assigned by spatially joining with HERE Postal Code Boundaries (Feb 2020).NOTE: Overlaps and gaps do exist between municipalities due to the fact that each municipal assessment jurisdiction maintains their own data.