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This vegetation map was created using the U.S. National Vegetation Classification (USNVC), with alliance as base map units. Plot data were used to determine classification and assisted in establishing reference 'signatures' for mapping. Color infrared aerial photography from 1999 and sets of true color aerial photography from 2005-2009 (1:3000 scale) were used for mapping. Polygons were drawn on-screen (heads-up digitizing). Classification resulted in 20 map classes, including 10 ecological systems.
These data can be used in multiple applications, but were created to assist in tracking the location and extent of natural communities on the coast of Georgia. Conservation managers and biologists may use these data to assist in making management decisions as well as prioritizing lands for conservation. Ultimately, these data will help local governments in planning and making land use decisions.
GENERAL DISCLAIMER
1. These data and maps are intended for use by private land managers, public agencies, nongovernmental organizations and others involved in land use decision-making and land conservation planning efforts. This map is not to be used to identify jurisdictional boundaries of wetlands or other habitats for regulatory purposes or to define critical habitat for listed species. 2. Due to the limited number of coastal Georgia examples in the U.S. National Vegetation Classification System (USNVC), the assignment of natural community names is subject to change as more regional information is gathered. 3. An accuracy assessment of this product indicated an overall accuracy level of 80% at the time of publication. Please keep in mind that natural community boundaries change over time. The Wildlife Resources Division makes no warranty as to the accuracy or completeness of the map and data or their utility for any specific purpose.
CONSERVATION STATUS DISCLAIMER
G-ranks or global scale conservation status have been included for each community type for which it applies. This information has no legal or jurisdictional weight in the State of Georgia and none is implied by the inclusion of this information. In addition, a margin of error is inherent in the use of imagery to delineate distinct community types; thus, detailed on-the-ground inspection of any particular site, may result in revision of the community boundaries or classification established through image analysis. The G-rank designations are assigned and developed by NatureServe, not the State of Georgia nor directly by state biologists. NatureServe is a nonprofit conservation organization that works with a network of natural heritage programs to maintain information about rare and endangered species, threatened ecosystems as well as develops and maintains the standardized U.S. National Vegetation Classification (USNVC) system that was used as the naming convention for this map. NatureServe works with biological inventories or conservation data centers in all 50 states, Canada, Latin America and the Caribbean. The scientific information about species and ecosystems developed by NatureServe is used by all sectors of society: conservation groups, government agencies, corporations, academia, and the public to make informed decisions about managing our natural resources. Determining which communities are thriving and which are rare or declining is crucial for targeting conservation towards elements of biodiversity in greatest need. NatureServe and its member programs and collaborators use a suite of factors to assess conservation status. For more information about these factors go to: http://www.natureserve.org/explorer/ranking.htm. These assessments lead to the designation of a conservation status rank. For ecological communities they provide an estimate of the risk of elimination. Conservation status ranks for communities in North America are currently under development. The conservation status is assigned only to the communities labeled at the association level of the USNVC and is designated by a number from 1 to 5, preceded by a letter reflecting the appropriate geographic scale of the assessment (G = Global), N = National, and S = Subnational). The numbers have the following meaning: 1. Critically imperiled - At very high risk of elimination due to extreme rarity, very steep declines, or other factors.
2. Imperiled - At high risk of elimination due to very restricted range, very few populations, steep declines, or other factors.
3. Vulnerable - At moderate risk of elimination due to a restricted range, relatively few populations, recent and widespread declines, or other factors.
4. Apparently secure - Uncommon but not rare; some cause for long-term concern due to declines or other factors.
5. Secure - Common; widespread and abundant.
For example, G1 would indicate that an ecosystem is critically imperiled across its entire range (i.e., globally). In this sense the community as a whole is regarded as being at very high risk of elimination. A rank of G3 would indicate the community is vulnerable and at moderate risk of elimination. Other variants and qualifiers are used to add information or indicate any range of uncertainty. ? - provisional community not yet in the USNVC system.
NA - Not applicable - this landcover category is not labeled at the association level or is not a vegetated landcover. GU - Unrankable--Currently unrankable due to lack of information or due to substantially conflicting information about status or trends. GNR - Unranked-Global rank not yet assessed. GNA - Not Applicable-A conservation status rank is not applicable because the species is not a suitable target for conservation activities.
Since the assignment of conservation status is under development many G-ranks are assigned a range (i.e., G1G2). To simplify, NatureServe has also provided an average of these ranges (i.e., G1G2 = G1). Both values are presented in the attribute tables of this dataset. For updated rankings, search for the community at http://www.natureserve.org/explorer/servlet/NatureServe?init=Ecol.
The value of a particular community type is complicated and nuanced. Depending on what is being managed for (i.e., individual species of concern or particular ecological function), the viability of a community could be a factor of patch size, connectivity to other similar or complementary community types, or distance from adverse land uses. The global ranking system does not take into account values attributed to a particular community at the state level. In 2005 the state of Georgia developed a Comprehensive Wildlife Conservation Strategy. This document highlights high priority habitats in the five ecoregions of the state. We have cross-walked the USNVC name to these high priority habitat names in the attribute table under "SWAP_COMM". For more information about Georiga's Comprehensive Wildlife Conservation Strategy go to: http://www1.gadnr.org/cwcs/Documents/strategy.html. In addition, state and federal laws have provided jurisdiction to the state for particular habitats that might not be particularly rare in the global conservation ranking system but provide crucial ecological services that warrant protection. For example, the associations found with in the "Southern Atlantic Coastal Plain Salt and Brackish Tidal Marsh" are mostly G4 and G5 communities. In 1970 the state of Georgia enacted Coastal Marshlands Protection Act due to fears of phosphate mining operation and other industrial activities. These areas act as a nursery to many commercially important fish, shellfish and crustaceans as well as protect the mainland from storm surges and provide pollution filtering. This act gives the state the mandate to review any proposed impacts and can deny or grant a permit for any proposed activity that falls with in the jurisdiction of the act. In addition, excellent examples of a particular community type (i.e., have high "ecological integrity") would also warrant focused efforts at preservation especially those that fall under the list of high priority habitats. The G-ranks included in this dataset provide at best a quick snapshot of a community's rarity. Unlike threatened, rare and endangered species, vegetation communities are not provided any legal protection. Thus, the existence of a particular community on private land will not require any particular action by the landowner. The information provided in this dataset is provided as a service to the public. The state of Georgia nor any private entity cannot use the data provided herein to pursue any legal action.
Georgia Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section
January 2011
2009 vegetation/landcover map of Brantley County, Georgia
Brantley_County_Landcover_2_3_2011
vector digital data
withheld
ground condition
2009
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31.375858
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REQUIRED: Reference to a formally registered thesaurus or a similar authoritative source of theme keywords.
Ecological System, Georgia coast, 2009, vegetation map
Georgia coast
2009
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Georgia Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section.
Matt Elliott
Georgia Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section
Program manager
770-918-6411
Matt.Elliott@dnr.state.ga.us
mailing and physical address
2065 US Hwy278 East
Social Circle
Georgia
30025-4743
United States
en
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local time
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Social Circle
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30025-4743
2065 US Hwy278 East
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770-918-6411
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Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section
20110411
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Natureserve ecological system code
CES203.384
This ecological system occupies large, seasonally inundated basins with peaty substrates. These basins are nonriverine and do not receive overbank flooding. Examples are generally forested; the vegetation is characterized by Taxodium distichum, Nyssa biflora, evergreen "bay" shrubs, and/or mixed hardwoods. Emergent Pinus elliottii may also be present. Some characteristic shrubs include Cliftonia monophylla, Cyrilla racemiflora, Lyonia lucida, and Smilax laurifolia.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
CES203.252
This ecological system encompasses seepage-fed wetlands in dissected landscapes. Examples are usually associated with ravines or along headwater streams. Vegetation consists of open to closed forests of acid-tolerant wetland hardwoods or pine. Generally there is a dense shrub layer.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
CES203.247
Occurs in floodplains of small streams that carry little mineral sediment. A variety of tree species may be present; wetter examples are often strongly dominated by Taxodium distichum and Nyssa biflora. Other examples have mixtures of these species with Quercus spp. and other bottomland hardwoods tolerant of blackwater conditions. Species richness ranges from low to moderate, but is lower than in comparable brownwater systems. Flooding is an important ecological factor in this system and may be the most important factor separating it from adjacent systems.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
CES203.536
Examples of this system and component community associations share the common features of wet, seasonally saturated, mineral soils and historic exposure to frequent low-intensity fire. The vegetation is naturally dominated by Pinus palustris or, on wetter sites, Pinus elliottii or less commonly Pinus serotina. In natural condition (frequent fires, including a growing-season component) there tends to be a dense ground cover of herbs and low shrubs; grasses can dominate, but there is often a large diversity of other herbs and shrubs.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
CES203.281
This system of upland Pinus palustris-dominated vegetation was once perhaps the most extensive system in the Outer Coastal Plain within its range. Examples and associations share the common feature of upland (non-wetland) moisture regimes and natural exposure to frequent fire. They occur on a variety of well- to excessively drained soils, and on the higher parts of upland-wetland mosaics. Most associations have an understory of scrub oaks. The herb layer is generally well-developed and dominated by grasses.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
CES203.494
Thick stands of Quercus virginiana and/or Quercus geminata are diagnostic of this system. Examples often occupy locally distinct microhabitats that differ from the surrounding landscape, such as shallow depressions or slight topographic highs in a predominantly longleaf pine-dominated landscape. Under more frequent fire regimes, these sites would likely be occupied by longleaf pine.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
CES203.262
This ecological system consists of wetlands in small basins formed in unconsolidated sediments. Vegetation usually ranges from open water or floating-leaved aquatics in the center of the deepest basins, to emergent marsh zones in semipermanent water, to drawdown zones with diverse small graminoid and forb vegetation, to dense shrub or woodland edges. A smaller number of basins may have emergent trees throughout their extent.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
CES203.497
The vegetation consists of an assemblage of xeric communities that also occur in other xeric habitats in the Coastal Plain. These include Pinus palustris - Quercus laevis communities and a scrub community akin to Inland Florida Scrub.This system is distinguished from more typical xeric sandhills of the Coastal Plain by its occurrence on the deep sands of river dunes. In addition this environment is naturally topographically isolated and consequently has a lower fire-return interval than other upland systems of which Pinus palustris is a component.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
CES203.476
This forested system of the southern East Gulf and Atlantic coastal plains occurs on steep slopes, bluffs, or sheltered ravines where fire is naturally rare, generally within the natural range of Pinus glabra. Stands are mesic, and vegetation typically includes species such as Fagus grandifolia, Magnolia grandiflora, Illicium floridanum, and other species rarely encountered outside this system in the region.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
CES203.241
Oak-dominated forests of somewhat fire-sheltered dry to dry-mesic sites. Sites where this system occurs are somewhat protected from most natural fires by some combination of steeper topography, isolation from the spread of fire, and limited flammability of the vegetation. If fires were more frequent, more fire-tolerant southern pines, especially Pinus palustris, would likely replace the vegetation.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
NA
NA
0
0
NS_ECO_NAM
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Natureserve ecological system name
Atlantic Coastal Plain Blackwater Stream Floodplain Forest
Occurs in floodplains of small streams that carry little mineral sediment. A variety of tree species may be present; wetter examples are often strongly dominated by Taxodium distichum and Nyssa biflora. Other examples have mixtures of these species with Quercus spp. and other bottomland hardwoods tolerant of blackwater conditions. Species richness ranges from low to moderate, but is lower than in comparable brownwater systems. Flooding is an important ecological factor in this system and may be the most important factor separating it from adjacent systems.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Atlantic Coastal Plain Dry and Dry-Mesic Oak Forest
Oak-dominated forests of somewhat fire-sheltered dry to dry-mesic sites. Sites where this system occurs are somewhat protected from most natural fires by some combination of steeper topography, isolation from the spread of fire, and limited flammability of the vegetation. If fires were more frequent, more fire-tolerant southern pines, especially Pinus palustris, would likely replace the vegetation.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Atlantic Coastal Plain Streamhead Seepage Swamp, Pocosin and Baygall
This ecological system encompasses seepage-fed wetlands in dissected landscapes. Examples are usually associated with ravines or along headwater streams. Vegetation consists of open to closed forests of acid-tolerant wetland hardwoods or pine. Generally there is a dense shrub layer.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Atlantic Coastal Plain Upland Longleaf Pine Woodland
This system of upland Pinus palustris-dominated vegetation was once perhaps the most extensive system in the Outer Coastal Plain within its range. Examples and associations share the common feature of upland (non-wetland) moisture regimes and natural exposure to frequent fire. They occur on a variety of well- to excessively drained soils, and on the higher parts of upland-wetland mosaics. Most associations have an understory of scrub oaks. The herb layer is generally well-developed and dominated by grasses.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Nonalluvial (Blackwater) Rivers and Swamps
River with little mineral sediment, low levels of turbidity and high levels of tannins. Originate within the coastal plain.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Developed
Urban areas with little or no tree canopy.
Early Successional Vegetation
Timber recently harvested and in early stages of regeneration.
Impoundment
Man-made pond or small lake.
Loblolly Pine-Water Oak-Sweetgum Successional Vegetation
Occurs after timber is harvested, agriculture abandoned, etc. and land is left idle. Mid to late succession dominated by loblolly pine, water oak, and sweetgum.
Open Field
Open grassland created by man, often agricultural.
Orchard
Cropland dedicated to trees. Often peaches or pecans.
Pine Plantation
Land dedicated to the monoculture or intensive silviculture of pine trees.
Quarries
Exposed rock and soil from industrial uses, gravel pits, landfills.
Southern Atlantic Coastal Plain Depressional Pondshore
This ecological system consists of wetlands in small basins formed in unconsolidated sediments. Vegetation usually ranges from open water or floating-leaved aquatics in the center of the deepest basins, to emergent marsh zones in semipermanent water, to drawdown zones with diverse small graminoid and forb vegetation, to dense shrub or woodland edges. Many may be more densely forested.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Southern Atlantic Coastal Plain Wet Pine Savanna and Flatwoods
Examples of this system and component community associations share the common features of wet, seasonally saturated, mineral soils and historic exposure to frequent low-intensity fire. The vegetation is naturally dominated by Pinus palustris or, on wetter sites, Pinus elliottii or less commonly Pinus serotina. In natural condition (frequent fires, including a growing-season component) there tends to be a dense ground cover of herbs and low shrubs; grasses can dominate, but there is often a large diversity of other herbs and shrubs.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Southern Atlantic Coastal Plain Xeric River Dune
The vegetation consists of an assemblage of xeric communities that also occur in other xeric habitats in the Coastal Plain. These include Pinus palustris - Quercus laevis communities and a scrub community akin to Inland Florida Scrub.This system is distinguished from more typical xeric sandhills of the Coastal Plain by its occurrence on the deep sands of river dunes. In addition this environment is naturally topographically isolated and consequently has a lower fire-return interval than other upland systems of which Pinus palustris is a component.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Southern Coastal Plain Mesic Slope Forest
This forested system of the southern East Gulf and Atlantic coastal plains occurs on steep slopes, bluffs, or sheltered ravines where fire is naturally rare, generally within the natural range of Pinus glabra. Stands are mesic, and vegetation typically includes species such as Fagus grandifolia, Magnolia grandiflora, Illicium floridanum, and other species rarely encountered outside this system in the region.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Southern Coastal Plain Nonriverine Basin Swamp
This ecological system occupies large, seasonally inundated basins with peaty substrates. These basins are nonriverine and do not receive overbank flooding. Examples are generally forested; the vegetation is characterized by Taxodium distichum, Nyssa biflora, evergreen "bay" shrubs, and/or mixed hardwoods. Emergent Pinus elliottii may also be present. Some characteristic shrubs include Cliftonia monophylla, Cyrilla racemiflora, Lyonia lucida, and Smilax laurifolia.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Southern Coastal Plain Oak Dome and Hammock
Thick stands of Quercus virginiana and/or Quercus geminata are diagnostic of this system. Examples often occupy locally distinct microhabitats that differ from the surrounding landscape, such as shallow depressions or slight topographic highs in a predominantly longleaf pine-dominated landscape.
NatureServe. 2010. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. Available http://www.natureserve.org/explorer. (Accessed: December 17, 2010 ).
Transportation
Roads, railroads, airports, and runways.
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Natureserve association name
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Disturbanc
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Comments about human disturbance.
0
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G_Rank
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50
Global rarity rank value.
0
0
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50
State rarity rank value.
0
0
NOTE_
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254
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0
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Average global rank.
0
0
Verified
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Community verified during preliminary field visits or accuracy assessment.
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0
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254
Georgia State Wildlife Action Plan ecosystem classification.
0
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Values indicate specific land cover types.
Dataset copied. The vegetation communities of Brantley County were delineated using heads up digitizing, creating polygons around the different communities and landforms in ArcEditor (version 9.3, ESRI, Redlands, California) by natural resource biologists with the Georgia Department of Natural Resources, Wildlife Resource Division, Nongame Conservation Section. Digitizing was based on interpretation of digital ortho-imagery from two sources: 1999 eq. CIR imagery (equalized color infrared) (1-meter pixel resolution), and 2005,2007,2009 NAIP (National Agricultural Imagery Program) (1-meter pixel resolution) . Each set of imagery was useful in different ways in aiding in classification and interpretation. In particular, the 1999 eq. CIR imagery which is leaf off and represents species actively photosynthesizing as red and areas that were wet as blue to black, was helpful in separating transportation infrastructure and other man-made features from the surrounding vegetation as well as separating communities with a heavy presence of pine or other evergreen species from communities dominated by deciduous species. In addition, the timing of the 1999 eq. CIR imagery gave a distinct signature of the wetness of the community in the winter months, allowing the separation of wetlands and floodplain forest from the surrounding uplands. By comparing 1999 eq. CIR to the later years imagery it was possible to determine if a community had been cut over in the intervening years and if it should be classified as early successional instead of a natural grassland or shrub community type. The NAIP imagery was taken during the growing season so this gave another signature to the communities with leaf on. In particular, the 2005 imagery was useful in defining the concentration of pines scattered in mixed hardwood communities. The 2007 NAIP imagery was not of the best quality but was useful in making corrections for changes in transportation infrastructure, powerline / pipelines, and increases in areas under development. However, the bulk of interpretation and fine scale delineation was dependent on the 2009 imagery. In addition to the imagery, USGS topographic quad maps, soils data from the Soil Survey Geographic (SSURGO) database and NWI (national wetland inventory) vector data were utilized to further separate communities based on changes in topography, soils and wetland classification. This was particularly useful in discovering communities restricted to slopes, sand hill communities on well drained sandy soils, and properly identifying wetlands based on water regime. The classification of communities was an iterative process where major man-made landscape features were first delineated i.e. transportation, powerline / pipelines, developed land, industrial sites. Following this, vegetated areas were delineated based on perceived differences in the imagery, topography, SSURGO soil, and NWI information.
withheld
20101124
08453300
Matt Elliott
Georgia Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section
Program manager
mailing and physical address
2065 US Hwy278 East
Social Circle
Georgia
30025-4743
United States
770-918-6411
Dataset copied.
20101124
11544300
Dataset copied.
withheld
20110125
15080400
Matt Elliott
Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section
Program Manager
770-918-6411
2065 US Hwy278 East
Social Circle
Georgia
30025-4743
US
ArcGIS Metadata
1.0
Georgia Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section
Feature Class
CRC_Reg13.DBO.Landcover
Georgia Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section
<DIV STYLE="text-align:Left;"><DIV><P><SPAN>This vegetation map was created using the U.S. National Vegetation Classification (USNVC), with alliance as base map units. Plot data were used to determine classification and assisted in establishing reference 'signatures' for mapping. Color infrared aerial photography from 1999 and sets of true color aerial photography from 2005-2009 (1:3000 scale) were used for mapping. Polygons were drawn on-screen (heads-up digitizing). Classification resulted in 20 map classes, including 10 ecological systems.</SPAN></P></DIV></DIV>
These data can be used in multiple applications, but were created to assist in tracking the location and extent of natural communities on the coast of Georgia. Conservation managers and biologists may use these data to assist in making management decisions as well as prioritizing lands for conservation. Ultimately, these data will help local governments in planning and making land use decisions.
Georgia Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section.
Matt Elliott
Georgia Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section
Program manager
770-918-6411
2065 US Hwy278 East
Social Circle
Georgia
30025-4743
US
Matt.Elliott@dnr.state.ga.us
Georgia coast
2009
Ecological System
Georgia coast
2009
vegetation map
2009
Georgia coast
Ecological System
Georgia coast
2009
vegetation map
2021
Enhancing Coastal Resiliency using Green Infrastructure
ground condition
2009-01-01
GENERAL DISCLAIMER 1. These data and maps are intended for use by private land managers, public agencies, nongovernmental organizations and others involved in land use decision-making and land conservation planning efforts. This map is not to be used to identify jurisdictional boundaries of wetlands or other habitats for regulatory purposes or to define critical habitat for listed species. 2. Due to the limited number of coastal Georgia examples in the U.S. National Vegetation Classification System (USNVC), the assignment of natural community names is subject to change as more regional information is gathered. 3. An accuracy assessment of this product indicated an overall accuracy level of 80% at the time of publication. Please keep in mind that natural community boundaries change over time. The Wildlife Resources Division makes no warranty as to the accuracy or completeness of the map and data or their utility for any specific purpose. CONSERVATION STATUS DISCLAIMER G-ranks or global scale conservation status have been included for each community type for which it applies. This information has no legal or jurisdictional weight in the State of Georgia and none is implied by the inclusion of this information. In addition, a margin of error is inherent in the use of imagery to delineate distinct community types; thus, detailed on-the-ground inspection of any particular site, may result in revision of the community boundaries or classification established through image analysis. The G-rank designations are assigned and developed by NatureServe, not the State of Georgia nor directly by state biologists. NatureServe is a nonprofit conservation organization that works with a network of natural heritage programs to maintain information about rare and endangered species, threatened ecosystems as well as develops and maintains the standardized U.S. National Vegetation Classification (USNVC) system that was used as the naming convention for this map. NatureServe works with biological inventories or conservation data centers in all 50 states, Canada, Latin America and the Caribbean. The scientific information about species and ecosystems developed by NatureServe is used by all sectors of society: conservation groups, government agencies, corporations, academia, and the public to make informed decisions about managing our natural resources. Determining which communities are thriving and which are rare or declining is crucial for targeting conservation towards elements of biodiversity in greatest need. NatureServe and its member programs and collaborators use a suite of factors to assess conservation status. For more information about these factors go to: http://www.natureserve.org/explorer/ranking.htm. These assessments lead to the designation of a conservation status rank. For ecological communities they provide an estimate of the risk of elimination. Conservation status ranks for communities in North America are currently under development. The conservation status is assigned only to the communities labeled at the association level of the USNVC and is designated by a number from 1 to 5, preceded by a letter reflecting the appropriate geographic scale of the assessment (G = Global), N = National, and S = Subnational). The numbers have the following meaning: 1. Critically imperiled - At very high risk of elimination due to extreme rarity, very steep declines, or other factors. 2. Imperiled - At high risk of elimination due to very restricted range, very few populations, steep declines, or other factors. 3. Vulnerable - At moderate risk of elimination due to a restricted range, relatively few populations, recent and widespread declines, or other factors. 4. Apparently secure - Uncommon but not rare; some cause for long-term concern due to declines or other factors. 5. Secure - Common; widespread and abundant. For example, G1 would indicate that an ecosystem is critically imperiled across its entire range (i.e., globally). In this sense the community as a whole is regarded as being at very high risk of elimination. A rank of G3 would indicate the community is vulnerable and at moderate risk of elimination. Other variants and qualifiers are used to add information or indicate any range of uncertainty. ? - provisional community not yet in the USNVC system. NA - Not applicable - this landcover category is not labeled at the association level or is not a vegetated landcover. GU - Unrankable--Currently unrankable due to lack of information or due to substantially conflicting information about status or trends. GNR - Unranked-Global rank not yet assessed. GNA - Not Applicable-A conservation status rank is not applicable because the species is not a suitable target for conservation activities. Since the assignment of conservation status is under development many G-ranks are assigned a range (i.e., G1G2). To simplify, NatureServe has also provided an average of these ranges (i.e., G1G2 = G1). Both values are presented in the attribute tables of this dataset. For updated rankings, search for the community at http://www.natureserve.org/explorer/servlet/NatureServe?init=Ecol. The value of a particular community type is complicated and nuanced. Depending on what is being managed for (i.e., individual species of concern or particular ecological function), the viability of a community could be a factor of patch size, connectivity to other similar or complementary community types, or distance from adverse land uses. The global ranking system does not take into account values attributed to a particular community at the state level. In 2005 the state of Georgia developed a Comprehensive Wildlife Conservation Strategy. This document highlights high priority habitats in the five ecoregions of the state. We have cross-walked the USNVC name to these high priority habitat names in the attribute table under "SWAP_COMM". For more information about Georiga's Comprehensive Wildlife Conservation Strategy go to: http://www1.gadnr.org/cwcs/Documents/strategy.html. In addition, state and federal laws have provided jurisdiction to the state for particular habitats that might not be particularly rare in the global conservation ranking system but provide crucial ecological services that warrant protection. For example, the associations found with in the "Southern Atlantic Coastal Plain Salt and Brackish Tidal Marsh" are mostly G4 and G5 communities. In 1970 the state of Georgia enacted Coastal Marshlands Protection Act due to fears of phosphate mining operation and other industrial activities. These areas act as a nursery to many commercially important fish, shellfish and crustaceans as well as protect the mainland from storm surges and provide pollution filtering. This act gives the state the mandate to review any proposed impacts and can deny or grant a permit for any proposed activity that falls with in the jurisdiction of the act. In addition, excellent examples of a particular community type (i.e., have high "ecological integrity") would also warrant focused efforts at preservation especially those that fall under the list of high priority habitats. The G-ranks included in this dataset provide at best a quick snapshot of a community's rarity. Unlike threatened, rare and endangered species, vegetation communities are not provided any legal protection. Thus, the existence of a particular community on private land will not require any particular action by the landowner. The information provided in this dataset is provided as a service to the public. The state of Georgia nor any private entity cannot use the data provided herein to pursue any legal action.
Version 6.2 (Build 9200) ; Esri ArcGIS 10.5.1.7333
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Dataset copied. The vegetation communities of Brantley County were delineated using heads up digitizing, creating polygons around the different communities and landforms in ArcEditor (version 9.3, ESRI, Redlands, California) by natural resource biologists with the Georgia Department of Natural Resources, Wildlife Resource Division, Nongame Conservation Section. Digitizing was based on interpretation of digital ortho-imagery from two sources: 1999 eq. CIR imagery (equalized color infrared) (1-meter pixel resolution), and 2005,2007,2009 NAIP (National Agricultural Imagery Program) (1-meter pixel resolution) . Each set of imagery was useful in different ways in aiding in classification and interpretation. In particular, the 1999 eq. CIR imagery which is leaf off and represents species actively photosynthesizing as red and areas that were wet as blue to black, was helpful in separating transportation infrastructure and other man-made features from the surrounding vegetation as well as separating communities with a heavy presence of pine or other evergreen species from communities dominated by deciduous species. In addition, the timing of the 1999 eq. CIR imagery gave a distinct signature of the wetness of the community in the winter months, allowing the separation of wetlands and floodplain forest from the surrounding uplands. By comparing 1999 eq. CIR to the later years imagery it was possible to determine if a community had been cut over in the intervening years and if it should be classified as early successional instead of a natural grassland or shrub community type. The NAIP imagery was taken during the growing season so this gave another signature to the communities with leaf on. In particular, the 2005 imagery was useful in defining the concentration of pines scattered in mixed hardwood communities. The 2007 NAIP imagery was not of the best quality but was useful in making corrections for changes in transportation infrastructure, powerline / pipelines, and increases in areas under development. However, the bulk of interpretation and fine scale delineation was dependent on the 2009 imagery. In addition to the imagery, USGS topographic quad maps, soils data from the Soil Survey Geographic (SSURGO) database and NWI (national wetland inventory) vector data were utilized to further separate communities based on changes in topography, soils and wetland classification. This was particularly useful in discovering communities restricted to slopes, sand hill communities on well drained sandy soils, and properly identifying wetlands based on water regime. The classification of communities was an iterative process where major man-made landscape features were first delineated i.e. transportation, powerline / pipelines, developed land, industrial sites. Following this, vegetated areas were delineated based on perceived differences in the imagery, topography, SSURGO soil, and NWI information.
Matt Elliott
Georgia Department of Natural Resources, Wildlife Resources Division, Nongame Conservation Section
Program manager
770-918-6411
2065 US Hwy278 East
Social Circle
Georgia
30025-4743
US
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dataset
EPSG
5.3(9.0.0)
177774
20210831