SDE Feature Class
Tags
Putnam County, biota, Indian River County, Lake County, St. Johns River Water Management District, Alachua County, Baker County, Vegetation, Flagler County, Polk County, St. Johns County, Orange County, Brevard County, Seminole County, Bradford County, Florida, Counties, Volusia County, wetlands, Duval County, wetland, Nassau County, Marion County, Clay County, Osceola County, Okeechobee County
This wetlands dataset is only for general reference, it should not be used for legal purposes or detailed analysis. These wetlands maps only indicate areas of wetlands vegetation, primarily those in a natural state. They do not delineate hydric soils, by any definition. Developed wetlands areas are usually not included. Wetlands are mapped at a scale greater than 1:24,000, and may not be used accurately for presentation or analysis at larger scales. Local determinations always require field inspection. It is recommended that the SJRWMD Wetlands maps be used in conjunction with other sources, particularly the National Wetlands Inventory, Soil Survey Reports, and Land Use / Land Cover maps. Due to the nature of land cover mapping, there are significant differences among these sources.
This dataset contains SJRWMD wetland and vegetation inventory information. The District's Wetlands Mapping Project began in 1984 and completed approximately 70% of the District's area (150 USGS 7.5' quads). Most of the remaining quads were mapped under contract by Greenhorne and O'Mara, Inc. The mapping by Greenhorne and O'Mara was completed in 2002. The area mapped by the contractor is equivalent to approximately 60 USGS 7.5' quads. It included the following five sub-project areas: 1. Ocala National Forest, Central Orange County, and North-central Polk County 2. Baker County and western Nassau, Duval, and Clay counties 3. Central St. Johns, Flagler, and Volusia counties 4. Eastern Osceola County 5. Cape Canaveral
There are no credits for this item.
The St. Johns River Water Management District prepares and uses information for its own purposes and this information may not be suitable for other purposes. This information is provided "as is". Further documentation of this data can be obtained by contacting: St. Johns River Water Management District, Division of Integrated Application Systems, Post Office Box 1429, Palatka, Florida, 32178-1429, (386) 329-4500.
Extent
West | -82.476808 | East | -80.299350 |
North | 30.833582 | South | 27.457403 |
source material
The St. Johns River Water Management District prepares and uses information for its own purposes and this information may not be suitable for other purposes. This information is provided "as is". Further documentation of this data can be obtained by contacting: St. Johns River Water Management District, Division of Integrated Application Systems, Post Office Box 1429, Palatka, Florida, 32178-1429, (386) 329-4500.
The St. Johns River Water Management District prepares and uses information for its own purposes and this information may not be suitable for other purposes. This information is provided "as is". Further documentation of this data can be obtained by contacting: St. Johns River Water Management District, Division of Integrated Application Systems, Post Office Box 1429, Palatka, Florida, 32178-1429, (386) 329-4500.
There is no charge for downloading data from the DISTRICT web site at http://www.sjrwmd.com. Data can be orded on CD-ROM as instructed on the web site.
Internal feature number.
ESRI
2 Character Wetland Vegetation Code
Feature geometry.
ESRI
This dataset contains SJRWMD wetland and vegetation inventory information. The District's Wetlands Mapping Project began in 1984 and completed approximately 70% of the District's area (150 USGS 7.5' quads). Most of the remaining quads were mapped under contract by Greenhorne and O'Mara, Inc. The mapping by Greenhorne and O'Mara was completed in 2002. The area mapped by the contractor is equivalent to approximately 60 USGS 7.5' quads. It included the following five sub-project areas: 1. Ocala National Forest, Central Orange County, and North-central Polk County 2. Baker County and western Nassau, Duval, and Clay counties 3. Central St. Johns, Flagler, and Volusia counties 4. Eastern Osceola County 5. Cape Canaveral
This wetlands dataset is only for general reference, it should not be used for legal purposes or detailed analysis.
These wetlands maps only indicate areas of wetlands vegetation, primarily those in a natural state. They do not delineate hydric soils, by any definition. Developed wetlands areas are usually not included. Wetlands are mapped at a scale greater than 1:24,000, and may not be used accurately for presentation or analysis at larger scales. Local determinations always require field inspection.
It is recommended that the SJRWMD Wetlands maps be used in conjunction with other sources, particularly the National Wetlands Inventory, Soil Survey Reports, and Land Use / Land Cover maps. Due to the nature of land cover mapping, there are significant differences among these sources.
source material
None
The St. Johns River Water Management District prepares and uses information for its own purposes and this information may not be suitable for other purposes. This information is provided "as is". Further documentation of this data can be obtained by contacting: St. Johns River Water Management District, Division of Integrated Application Systems, Post Office Box 1429, Palatka, Florida, 32178-1429, (386) 329-4500.
Classification is based on species recognition by interpreters, resulting in high thematic accuracy. In the absence of a statistical test, accuracy is estimated at greater than 90% for dominant vegetation types. Accuracy is greater for classes such as water and cypress, and can be less for certain mixed classes that intergrade. For example, Hardwood Swamp can be confused with Hydric Hammock in transitional areas. Accuracy varies for different locations, dates, and interpreters.
Drained wetlands are mapped as uplands if wetlands vegetation is not present, or if land is farmed or developed. Managed forests in hydric areas may be mapped as Forested Depression - Pine or as uplands.
Classification system was modified slightly after the first county, Seminole, was completed. Coding method varies somewhat between interpreters, such as in the use of modifiers or secondary codes. Consistency is enhanced by the small number of interpreters and team approach.
No edit masks present;
Coverages exist in double precision;
Fuzzy tolerances will be 0.0001;
Arc and polygon topology present;
All coverages shall be coordinated edgematched to adjacent coverages;
Identically coded polygons shall not be adjacent to each other within a coverage;
No superfluous pseudo nodes or tics;
No duplicate features;
No sliver polygons, label errors, dangles, or intersection errors shall exist;
No coding is done outside District boundaries. In some quads one or more counties were not mapped. Unmapped areas are coded EX for external. The non-wetlands matrix is coded as U, for upland. Uplands areas may include hydric soils or drained wetlands.
The maps are accurate only for the date of photography used. Many vegetation types undergo rapid change, such as floating vegetation or cleared areas. Many are changed by land use factors. Wetlands maps represent a baseline inventory, and are not edited to reflect changes.
Positional: Georeferencing specifications for this project require an overall RMS (root mean square) error of 30 feet or less, for visible control points. The spec for maximum error for any control point is 50 feet, which is slightly exceeded in some cases. Regardless of specifications, the actual linework may have larger displacement error in some locations where position control was very limited. All control point coordinates were derived from USGS 1:24k quads. The main source of positional error, in general, is from due to the difficulty of delineating wetland boundaries in transitional areas.
Thematic accuracy:
Correct differentiation of wetlands from uplands: 95%
Correct differentiation of saline wetlands from freshwater or transitional wetlands: 95%
Correct differentiation of forested, shrub, herbaceous, or other growth forms: 90%
Correct differentiation of specific types within classes: 80%
Positional Accuracy:
The horizontal error of clearly identifiable features shall not exceed an average of 10 meters or a maximum of 15 meters for any 7.5' quadrangle area, with error measured as horizontal discrepancy between wetlands map coordinates and the locations of features obtained from 1995 Digital Orthoquads.
Wetlands polygons were photointerpreted by district staff from 1:24,000 color infrared photography. The photography dates for each county are:
11/90 Alachua
01/86 Brevard
01/86 Clay
05/84 Duval
11/90 Flagler
04/89 Indian River
02/87 Lake
01/86 Marion
04/89 Nassau
03/88 Orange
11/90 Putnam
03/84 Seminole
01/88 St. Johns
03/88 Volusia
Polygon boundaries and positional control points were delineated on mylar sheets using a zoom stereoscope. The linework and points were digitized and then georeferenced using a SJRWMD fortran program called Space 4, which performs perspective transformation using both ground control and tie points.
Ancillary data used to interpret wetland polygons includes National Wetlands Inventory (NWI) maps, Soil Surveys, USGS 7.5 topo maps, and other sources of Photography archived at the District. Extensive field checking was done on many of the quads.
An index map at /sjr/es2/wetlands/metadata/wetveg_index/windex.cmp shows the completion status of the quads. The coverage windex, same location, includes attributes for the completion status of each quad or sub-quad areas.
Fiducial marks of the photographs were precisely transferred to mylar overlays. Also at this time, reference control points were located on the USGS Digital Ortho Quadrangles and the corresponding points were located on the mylar overlays.
Features were interpreted stereoscopically and polygon boundaries were drawn on mylar overlays.
Vegetation classification: Vegetation was classified according to the District classification system.
Quality Control of Interpretation and Classification
Edgematching: Delineated features on each overlay wereedge matched steroscopically to features interpreted on all adjacent frames and quadarangles
Creation of digital ArcInfo Wetland coverages - The linework mylars were scanned, vectorized and converted to ArcInfo coverages.
Ground truth verification
QualityAssurance of Completed ArcInfo coverages.
ArcInfo coverages were loaded in SDE
Metadata imported.
OBJECT ID 258619 was erroneously coded as HS when it is actually upland. The change was made.
OID 112999 in Brevard County (a large polygon) was erroneously coded as WP (wet prairie) - was fixed to be U (upland)
Metadata imported.
A unique classification system was developed for this project, with terms that are commonly used in this part of Florida. It provides classification at several levels (land form, community, species) into a single character string. The levels coded for each polygon are not consistent - most codes indicate plant community, but for some polygons species type and/or landform are included. This provides useful information, but it may make automated analysis difficult. For shading purposes, only the first two characters of the code are used.
Added symbology (*,ampersandgt;,ampersandlt; /, -) indicate degree of inclusion, over/under story, and sub levels. A number of modifiers, infrequently used, mainly indicate management status.
FRESHWATER WETLANDS
Cypress (CY) - Forested wetlands dominated by Bald cypress or Pond cypress (Taxodium distichum or T. ascendens) that are flooded annually for periods of long duration - typically 4 to 8 months in any given year. Includes Cypress dome, stand, and lakeshore variants.
Hardwood Swamp (HS) - Forested wetlands dominated by one or more deciduous hardwood species that typically include Black gum, Red maple, Water ash, Water elm, and Willows. Cypress is often a significant compo-nent of this type. Subject to annual, seasonal periods of prolonged flooding.
Bay Head (BH) - Forested wetlands dominated by one or more species of broadleaved, evergreen, or Bay trees (Gordonia lasianthus, Persea palustris, or Magnolia virginica). Dahoon holly (Ilex cassine) may occasionally be dominant. Soils are usually organic and nearly constantly saturated as well as being at least occasionally flooded. Some sites may have canopies that are dominated by Pines, but Bays and other indicators will be prevalent in the sub canopy and under story.
Bay Gall (BG) - Forested wetlands typically dominated by one or more species of evergreen, or Bay trees, and, less commonly, by Dahoon holly, deciduous hardwoods, or Pine. Located at the bases of sandy slopes and maintained by down slope seepage. Soils are organic and are nearly constantly saturated but infrequently flooded.
Hydric Hammock (HH) - Forested systems dominated by a mixture of broadleaved, evergreen, and deciduous tree species. Cabbage palmetto (CP) may be dominant in some variants of this type. Seldom inundated, but have saturated soils during much of the year.
Bottomland Hardwoods (BL) - Deciduous forest communities lying in the floodplains of rivers and streams that are subject to the rapid rise and fall of floodwaters. Sometimes they may be relatively well drained, or, at most, saturated by lateral seepage. The associated soils are alluvial.
Forested Flatwoods Depressions (FD) - Typically these are Pond cypress, Pine, deciduous hardwood, Bay, or Cabbage palm dominated communities occupying shallow depressions in mesic flatwoods sites. The under story vegetation consists of hydrophytic shrubs, grasses, and herbs. Saw palmetto, Gallberry and other typical mesic flatwoods species are generally absent. In the absence of fires, or as a result of forest management practices, under story or associated species (such as Loblolly bay) may dominate these sites. Soils are usually sandy and are subject to brief (1 - 2 months) seasonal inundation or prolonged soil saturation.
Shrub Swamp (SS) - Dominated by Willows, Buttonbush, or similar appearing vegetation. The hydrology is similar to that of Cypress, hardwood swamp, or shallow marsh communities.
Shrub Bog (SB) - Dominated by shrubby vegetation occupying typical Bay head sites. Often developing in Bay heads that have been destroyed by fire or some other disturbance. The hydrology is similar to that of Bay head communities.
Shrub Gall (SG) - Wetlands dominated by shrubby vegetation occupying typical Bay gall sites and having similar hydrology and soils.
Transitional Shrub (TS) - Dominated by transitional shrubby vegetation occurring at the upland margins of wetland communites or on clear cut hydric sites. Can also develop on wet prairie sites that have been protected from fire. Wax myrtle (Myrica cerifera) and Baccharis halimnifolia are typical species.
Deep Marsh (DM) - Deepwater wetlands dominated by a mixture of Water lilies and deep water emergent species. Semi-permanently to perma-nently flooded.
Lakeshore Emergents (DM-LS) - Emergent vegetation growing along lakeshores and usually semi-permanently flooded. Panicum hemitomon and species of Scirpus are most common.
Water Lilies (DM-N) - Floating leaved species in the genera Nymphaea, Nuphar, Nelumbo, Brasenia and Nymphoides. Usually semi-permanently to permanently flooded.
Shallow Marsh (SM) - Herbaceous or graminoid communities dominated by species such as Sawgrass, Maidencane, Cattails, Pickerel weed, Arrowhead, or other grasses and broad leaved herbs. Occurs most often on organic soils that are subject to lengthy seasonal inundation. Subject to occasional fire.
Wet Prairie (WP) - Communities of grasses, sedges, rushes, and herbs typically dominated by Sand cordgrass, Maidencane, or a mixture of species. Usually occurs on mineral soils that are inundated for a relatively short duration each year, but with prolonged soil saturation. Subject to frequent fire.
Floating Marshes (FF) - Communities of free-floating plants (such as Water hyacinth, Water lettuce, or Lemna) or floating mats of rhizomatous species (such as Alligator weed or various grasses and sedges).
Freshwater Flats and Barren Areas (BA) - Sandy or muddy sites subject to occasional or regular inundation with less than 33% vegetation cover during the growing season.
SALINE WETLANDS
Mangrove Forest (MF) - Forested saline wetlands dominated by one or more mangrove tree species (Rhizophora mangle, Avicennia germinans, or Laguncularia racemosa) growing on sites where they are capable of achieving tree stature. These communities may be further classified by dominant species or forest physiognomy.
Shrub Mangrove (MS) - Sites dominated by one or more Mangrove tree species growing on sites where they are prevented by natural processes, (including climate, nutrients, and wave action), from achieving tree size. These communities may be further classified according to dominant tree species or by stand physiognomy.
Spartina alterniflora Marsh (SA) - Herbaceous saline wetlands dominated by smooth Cordgrass, often in nearly pure stands. Typically occupies a zone between open water or tidal flat communities and a salt flat or Black needlerush zone.
Juncus roemerianus Marsh (JR) - Herbaceous saline wetlands dominated by Black needlerush, often in nearly pure stands. Typically occupies a zone between the lower smooth Cordgrass zone and the high meadow community type.
Salt Flats (SF) - Communities developing on sandy, hypersaline soils upland from the Spartina or Juncus zone and characterized by concentric bands of vegetation developing in response to a salinity gradient. Consists of salt barrens (SF-B) and vegetated flats (SF-V).
Borrichia frutescens (BO) - Saline wetlands dominated by Sea ox-eye. These are most abundant in marshes with high salinity, low tidal amplitude, and higher elevations. They are found adjacent to high meadow communities.
High Meadow (HM) - High irregularly flooded herbaceous communities transitional between uplands and salt flats or Juncus roemerianus marshes and typically dominated by Spartina bakeri, S. patens, Borrichia frutescens, or other facultative species.
Tidal Flats (TF) - Non-vegetated, shallow-water habitats situated between the low and high tide limits. Substrate soft to semi soft sand or mud. Found where sediments accumulate and usually bordered landward by Spartina alterniflora marshes and seaward by tidal channels or subtidal seagrass beds.
Shoreline and Beach (BE) - Non-vegetated sites occupying slopes exposed to periodic inundation, and wave action. Typically bordering open water areas and transitional to upland coastal dunes and scrub communities.
TRANSITIONAL WETLANDS
Intermediate Marsh (IM) - Herbaceous wetlands of low or fluctuating salinity in which neither estuarine nor freshwater species attain full dominance. Subject to significant freshwater inflows, as well as, daily tides and saltwater influence.
OTHER
UPLANDS (U) - Used for all areas that are not delineated as wetlands vegetation. May include drained areas, developed or farmed lands, and Pine plantations on hydric soils. Hydrology may be xeric, mesic, or hydric.
Water (W) - Unvegetated or sparsely vegetated sites subject to prolonged or semi-permanent flooding. Includes lakes, streams, ponds and other water bodies.
Submerged Aquatic Beds (AB) - Communities of aquatic plants rooted in the sediments of shallow water bodies and having the majority of their photosynthetic tissues below the water surface. Generally permanently flooded.
Additional Codes
CP - Cabbage Palm, PI - Pines
Modifiers
X excavated
A artificial
I impounded
PI partially impounded
D drained
PD partially drained
C clearcut
CO old clearcut
Y regenerative young growth, secondary succession
S saline or salt influenced
B burned
HY occupying heavy clay soils
Conventions
XY Component X is only slightly more dominant than Y
X ampersand gt;Y Component X is dominant; Y is subdominant
X*Y A small percent of Y occurs in X
X/Y X is the overstory; Y is the understory
X-Y Community X contains component species typically associated with Y
The St. Johns River Water Management District prepares and uses information for its own purposes and this information may not be suitable for other purposes. This information is provided "as is". Further documentation of this data can be obtained by contacting: St. Johns River Water Management District, Division of Integrated Application Systems, Post Office Box 1429, Palatka, Florida, 32178-1429, (386) 329-4500.
There is no charge for downloading data from the DISTRICT web site at http://www.sjrwmd.com. Data can be orded on CD-ROM as instructed on the web site.