Natural Resources
Conservation Service
Ecological site F123XY001TN
Limestone Uplands
Last updated: 9/06/2018
Accessed: 11/13/2024
General information
Provisional. A provisional ecological site description has undergone quality control and quality assurance review. It contains a working state and transition model and enough information to identify the ecological site.
MLRA notes
Major Land Resource Area (MLRA): 123X–Nashville Basin
123—Nashville Basin
This area is entirely in Tennessee (fig. 123-1). It makes up about 5,625 square miles (14,580 square kilometers). The cities of Nashville, Franklin, Hendersonville, Columbia, Murfreesboro, and Shelbyville are in this area.
Physiography
Most of this area is in the Nashville Basin Section of the Interior Low Plateaus Province of the Interior Plains. A small part of the northeast corner and the western and southern fourth of the area are in the Highland Rim Section of the same province and division. Most of the outer part of the Nashville Basin is deeply dissected and consists of steep slopes between narrow, rolling ridgetops and narrow valleys. The inner part of the basin is dominantly undulating and rolling. In many areas the land surface is deeply pitted by limestone sinks, and outcrops of limestone are almost everywhere. Elevation generally is about 650 feet (200 meters), but it is 1,000 to 1,325 feet (305 to 405 meters) on isolated hills and is as low as 450 feet (135 meters) in some of the more deeply cut stream channels.
Geology
The bedrock geology in this area consists of Ordovician limestone exposed by geologic erosion of the top of the Nashville Dome (a high part of the Cincinnati Arch) throughout this area. Sinkholes are common in the limestone and are either open to the subsurface or are covered by soils and colluvium that have collected in the depressions formed on the land surface above the sinkhole. Younger rocks occur as a rim just outside this area. Surficial deposits include loess on the less eroded landforms and alluvium along the rivers and streams.
Source: United States Department of Agriculture, Natural Resources Conservation Service. 2006. Land Resource Regions and Major Land Resource Areas of the United States, the
Caribbean, and the Pacific Basin. U.S. Department of Agriculture Handbook 296.
LRU notes
N/A
Classification relationships
Scientific Name: Southern Interior Low Plateau Dry-Mesic Oak Forest
Unique Identifier: CES202.898
Ecological site concept
This mixed oak and oak-hickory forest concepts are derived from available NRCS data. Field verification is needed prior to utilizing this information for conservation planning.
NatureServe Ecological Associations found on these soils may include:
Common Name: Interior Southern Red Oak - White Oak Forest, CEGL007244
Common Name: White Oak - Mixed Oak Dry Mesic Alkaline Forest, CEGL002070
Common Name: Shumard Oak - Chinkapin Oak Mesic Limestone Forest
Table 1. Dominant plant species
| Tree |
(1) Quercus falcata |
|---|---|
| Shrub |
(1) Cornus florida |
| Herbaceous |
(1) Sanicula canadensis |
Physiographic features
This ecosite is found on hills, plateaus, and basins in MLRA 123. NASIS list the unique landforms as escarpment, flat, hillside, hillslope, and ridge.
Table 2. Representative physiographic features
| Landforms |
(1)
Hill
(2) Flat (3) Escarpment |
|---|---|
| Flooding frequency | None |
| Ponding frequency | None |
| Elevation | 360 – 1,400 ft |
| Slope | 2 – 40% |
| Water table depth | 13 – 51 in |
| Aspect | Aspect is not a significant factor |
Climatic features
The average annual precipitation in this area is 48 to 57
inches (1,220 to 1,450 millimeters). The maximum
precipitation occurs in midwinter and early in spring, and the minimum occurs in autumn. Rainfall primarily occurs during high-intensity, convective thunderstorms. Some snow occurs in winter, but it does not remain on the ground for long periods.
The average annual temperature is 56 to 60 degrees F (14 to 16 degrees C). The freeze-free period averages 210 days and ranges from 195 to 230 days. The longer freeze-free periods occur in the southern part of the area.
Source: United States Department of Agriculture, Natural Resources Conservation Service. 2006. Land Resource Regions and Major Land Resource Areas of the United States, the Caribbean, and the Pacific Basin. U.S. Department of Agriculture Handbook 296.
Table 3. Representative climatic features
| Frost-free period (average) | 170 days |
|---|---|
| Freeze-free period (average) | 194 days |
| Precipitation total (average) | 55 in |
Figure 1. Monthly precipitation range
Figure 2. Monthly average minimum and maximum temperature
Figure 3. Annual precipitation pattern
Figure 4. Annual average temperature pattern
Climate stations used
-
(1) COLUMBIA 3 WNW [USC00401957], Columbia, TN
-
(2) NASHVILLE INTL AP [USW00013897], Nashville, TN
-
(3) GAINESBORO [USC00403370], Gainesboro, TN
-
(4) FAYETTEVILLE WTP [USC00403074], Fayetteville, TN
Influencing water features
These sites have no influencing water features.
Soil features
Multiple soil series are included in this PES group including Talbott, Stiversville, Sandhill, Mimosa, Maury, Inman, Hampshire, Donerail, Colbert, Braxton, Bradyville, and Ashwood. Included soils vary in depth and multiple ESDs may be developed in the future from this grouping.
Table 4. Representative soil features
| Parent material |
(1)
Residuum
–
limestone
(2) Loess – limestone and shale (3) Alluvium – limestone and sandstone |
|---|---|
| Surface texture |
(1) Channery loam (2) Very gravelly silty clay loam (3) Flaggy clay loam |
| Family particle size |
(1) Loamy |
| Drainage class | Moderately well drained to well drained |
| Permeability class | Slow to moderately rapid |
| Soil depth | 16 – 59 in |
| Surface fragment cover <=3" | 8% |
| Surface fragment cover >3" | 8% |
| Available water capacity (0-40in) |
2 – 7 in |
| Calcium carbonate equivalent (0-40in) |
Not specified |
| Electrical conductivity (0-40in) |
Not specified |
| Sodium adsorption ratio (0-40in) |
Not specified |
| Soil reaction (1:1 water) (0-40in) |
5.3 – 6.5 |
| Subsurface fragment volume <=3" (Depth not specified) |
20% |
| Subsurface fragment volume >3" (Depth not specified) |
30% |
Ecological dynamics
Provisional Ecological Site (PES): F123XY001TN - Limestone Uplands
Major Land Resource Area (MLRA) 123
This PES describes ecological communities likely to be found on soil in the PES soil grouping. Future field work is required to develop detailed and accurate ecological site descriptions (ESDs) that can be used by conservation planners for restoration and planning activities. This PES describes hypotheses based on available data from many different sources and scales and has not been developed using site specific ecological field monitoring. Future ESD development will result in this initial PES group being split into more refined ecological communities.
Soil series currently included in this project are Ashwood, Barfield, Bradyville, Braxton, Colbert, Donerail, Gladdice, Hampshire, Inman, Maury, Mimosa, Noah, Sandhill, Stiversville, and Talbott.
Forest Vegetation as listed in Official Series Descriptions (OSDs):
Ashwood: The native vegetation is forests of hickory, hackberry, elm, black walnut, redbud, black locust, ash, and red cedar.
Barfield: original hardwood trees consisting chiefly of oak, hickory, red cedar, elm, maple, and redbud.
Bradyville: About 5 percent is in woodland consisting chiefly of oaks, hickory, elm, hackberry, and red cedar.
Braxton: The native vegetation was mixed hardwood forest.
Colbert: Forest are mixed hardwoods and pine.
Donerail: Native vegetation was principally hardwood forests of white and red oak, elm, ash, hackberry, black walnut and black locust, with glades of grasses, sedges, and canes.
Gladdice: The native vegetation is forests of hickory, hackberry, elm, black walnut, redbud, black locust, ash, and red cedar.
Hampshire: The native vegetation is forests of oaks, walnut, locust, ash, hickory, beech, elm, and maple.
Inman: The native vegetation is forest of oaks, walnut, locust, ash, hickory, beech, elm, maple, and cedar.
Maury: Native vegetation was dominated by oaks, elm, ash, black walnut, black and honey locust, hackberry, black cherry, and Kentucky coffee tree. Glades of native grasses and canes were reported by early settlers.
Mimosa: Wooded areas are in oak, hickory, black walnut, elm, maple, hackberry, black and honey locust, and redcedar.
Noah: Native vegetation is mixed hardwoods of oak, hickory, elm, yellow-poplar, locust and dogwood.
Sandhill: Most areas are used for growing pasture and hay or are in hardwood forest.
Stiversville: The native vegetation was oak, hickory, elm, hackberry, maple, beech, black walnut, ash, locust, and yellow poplar.
Talbott: Originally hardwoods, chiefly oak, hickory, elm, maple, and redcedar.
Trees listed for PES map units in the USDA-NRCS Tennessee County Soil Surveys include southern red oak, white oak, eastern red cedar, tulip poplar, northern red oak, loblolly pine, shortleaf pine, Virginia pine, black walnut, black cherry, common hackberry, and black locust. Most commonly listed species for these soils were southern red oak, white oak, eastern red cedar and pines.
Only two tree species can be selected for entry into the ESIS database as dominants: however, multiple tree species can be dominant on these sites and it will vary by aspect, soil depth, seed sources, management, disturbance history, fire regime, micro-topography and available water. Trees found on these sites include southern red oak, white oak, black oak, Shumard oak, northern red oak, chinkapin oak, pignut hickory, shagbark hickory, black oak, black cherry, white ash, hophornbeam, American hophornbeam, common serviceberry, blue ash, sugar maple, flowering dogwood, eastern redbuds, tulip poplar, and blackgum.
Ecological Dynamics
This PES describes an oak-hickory forest community on predominately limestone soils in the Nashville Basin area of Tennessee. There will be variations in plant composition on these sites due to soil depth, available water, and aspect. Actual field work is required to develop a full ecological site description (ESD), a field-based state and transition model, and accurate plant community phases to support future conservation planning.
State 1. (Reference)
State 1, Phase 1.1: Plant species dominants: southern red oak (Quercus falcata) – white oak (Quercus alba) / eastern dogwood (Cornus florida) – eastern redbud (Cercis canadensis) /
Canadian blacksnakeroot (Sanicula canadensis) - ticktrefoil (Desmodium spp.)
Most mapunits in this initial PES grouping range from moderately deep to very deep; however, a few mapunits of shallow Barfield soils have been included too. Future ESD develop will result in field monitoring that will provide the needed documentation to split this initial PES group into multiple ESDs.
Protected sites will have a robust and diverse herbaceous layer including many native spring wildflowers such as dwarf larkspur, spring beauty, bloodroot, hepatica, false rue anemone, twinleaf, early rue anemone, violets, and trillium. Common summer understory species may include agrimony, black snakeroot, white snakeroot, Virginia creeper, poison ivy, bedstraw, and avens. Shrubs may include coralberry, blueberries, and in more sheltered areas, northern spicebush.
State 2. Pastureland
State 2, Phase 2.1: Managed Pasture.
Plant species dominants: Schedonorus arundinaceus (tall fescue)
Plant species within pasture phases depend on seeding, management, and concurrent land uses. As with all sites, soil characteristics and management inputs will influence production levels.
Many species of warm-season or cool-season grasses are feasible for these sites. Common forage species include tall fescue, orchard grass, Johnson grass, and timothy.
Management of pasture sites should follow conservation planning standards and protocols which will benefit water quality, forage production, and soil health.
Transitioning this state to a reference condition would likely require extensive and long-term timber stand improvement practices including control of non-native vegetation and management for desired native tree, shrub and understory species.
State 3. Transitional Field
State 3, Phase 3.1: Plant species dominants: Eastern red cedar (Juniperus virginiana) / tall ironweed (Vernonia gigantean)- tall fescue (Schedonorus arundinaceus)
Tree species would be dependent upon several factors including severity and duration of disturbance, adjacent plant communities, available seed sources, post-disturbance management (control of invasive plants, grazing, etc.). A wide range of hardwoods is possible and may include tulip poplar, maples, ashes, locust, black cherry, eastern red cedar, pines, and if seed sources are nearby, oaks and hickories. Common shrubs would be berries, roses, and sumac.
Transitioning this state to a reference condition will require timber stand improvement practices to control non-native vegetation and manage for higher quality oak or hickory species.
State 4. Croplands
Dependent upon seeding and management. Corn and soybeans are common.
Abandonment of cropland would result in weed species taking over the site. Dozens of species are possible depending on the seed sources. Initially annual weeds would predominate followed annual and perennial grasses, shrubs, and finally, pioneer tree species such as pines, eastern red cedar, locusts, maples, ashes, and tulip poplar. Restoration would be required to return this State to a reference community, including oak and hickory regeneration, control of non-native vegetation, and planting of native understory species. Protection from disturbance (grazing) would also be required.
State and transition model
More interactive model formats are also available.
View Interactive Models
More interactive model formats are also available.
View Interactive Models
Click on state and transition labels to scroll to the respective text
State 1 submodel, plant communities
State 2 submodel, plant communities
State 3 submodel, plant communities
State 4 submodel, plant communities
State 1
Forestland (Reference)
This State is a oak-hickory or mixed oak hardwood forest. The Hierarchical Classification Relationship to reference this community is: Scientific Name: Southern Interior Low Plateau Dry-Mesic Oak Forest Unique Identifier: CES202.898
Community 1.1
Oak Hickory Forest
Forest overstory. These sites and mixed oak or oak-hickory forests. NRCS data currently available lists southern red oak (Quercus falcata) and white oak (Quercus alba) as the most prevalent overstory species. Besides oaks and hickories, other hardwoods found on these sites may include ashes, maples, elms, black walnut, black cherry, blackgum, dogwoods, redbuds, and hophornbeams.
Future ESD development will result in this initial PES forest group being split into more defined groups.
Forest understory. eastern dogwood (Cornus florida) – eastern redbud (Cercis canadensis) / Canadian blacksnakeroot (Sanicula canadensis) - ticktrefoil (Desmodium spp.)
State 2
Pastureland (managed)
This state will consist of whatever grass and/or forbs have been seeded and managed for. Most common is fescue or fescue - orchard grass -clover mix. Native or non-native grasses could be grown on these sites.
Community 2.1
Managed Pasture
Reoccurring management inputs including mowing, brush control, weed control and seeding may be occurring. Species managed for may including native and non-native grasses depending on management objectives.
Figure 5. Annual production by plant type (representative values) or group (midpoint values)
Table 5. Annual production by plant type
| Plant type | Low (lb/acre) |
Representative value (lb/acre) |
High (lb/acre) |
|---|---|---|---|
| Grass/Grasslike | – | – | – |
| Total | – | – | – |
State 3
Transitional
This state is a successional vegetation state which without interference will move naturally from a managed pasture scenario to an unmanaged pasture to a shrubland to a mixed woodland. Each of these phases would exhibit differing dominant species - grasses to shrubs to trees. However, timber stand improvement would be needed to achieve a quality oak or oak-hickory reference state community.
Community 3.1
Transitional
Transitional field state is a successional stage. One possible scenario is that a major disturbance (logging, massive storm damage, fire)has occurred to a forestland and moved to this phase. Another alternative is that a managed pasture is no longer being maintained and brush/trees are encroaching on the site. Many of these sites have high wildlife values.
Forest overstory. This successional site will include various trees depending on seed sources. Eastern red cedar will be common on limestone sites along with various hardwoods such as maples, ashes, and oaks.
Forest understory. Grass and forbs will be a mix of many native and introduced species. Common grasses will include tall fescue, orchard grass, Johnson grass, foxtails, bromes, and timothy. Common herbs include both native and weedy species such as tall ironweed, goldenrods, thistles, pigweed, ragweed (common and giant), sour dock, chicory, Queen Anne's lace, etc.
State 4
Cropland
The dominant species in this state will depend upon what is planted and what the landowner management goals are. Corn, soybean, wheat, and tobacco are just some of the crops found on these soils. USDA-NRCS county soil surveys are available to landowner and provide production data for croplands based on soil series.
Community 4.1
Cropland
Species and management will depend on objectives. Commonly grown crops include corn, soybeans, and in some areas, tobacco.
Transition T1A
State 1 to 2
Forest to pastureland
Transition T1B
State 1 to 3
This is a transitional (successional) state. This state could occur due to disturbances which remove the overstory canopy. This state would also occur moving from a managed to unmanaged pasture. Tree species would encroach. Forest state management would be required to achieve a quality mixed oak or oak hickory forest.
Transition T1C
State 1 to 4
Forestland to Cropland
Restoration pathway R2A
State 2 to 1
Restoration of an oak-hickory or mixed-oak forest from a pasture state. Multiple forest conservation practices would be required to successfully restore this reference community. Forest management planning, weed control, plantings, brush management, and even fire management may be warranted.
Conservation practices
| Brush Management | |
|---|---|
| Tree/Shrub Site Preparation | |
| Tree/Shrub Establishment | |
| Upland Wildlife Habitat Management | |
| Invasive Plant Species Control | |
| Forest Management Plan - Written | |
| Forest Management Plan - Applied |
Transition T2A
State 2 to 3
Managed pasture to abandoned pasture. natural successional changes will occur including brush and trees encroaching on the site. Often these sites have high wildlife values.
Transition T2B
State 2 to 4
Pastureland to croplands. Crops seeded will depend on management goals.
Restoration pathway R3A
State 3 to 1
Restoration of a oak-hickory or mixed-oak forest would require multiple conservation practices and long-term management inputs. Practices may include brush and non-native species control and desired tree species plantings. the development of a comprehensive forest management plan would be the initial step toward a successful forestland restoration goal.
Conservation practices
| Brush Management | |
|---|---|
| Tree/Shrub Site Preparation | |
| Tree/Shrub Establishment | |
| Forest Stand Improvement | |
| Forest Management Plan - Written | |
| Forest Management Plan - Applied |
Transition T3A
State 3 to 2
Transitional site to managed pasture. Management activities may include brush removal, weed control, seeding, fertilizer, etc.
Transition T3B
State 3 to 4
Management transition from pasture to cropland. Seeded species will depend upon management objectives.
Restoration pathway R4A
State 4 to 1
Restoration of cropland to a oak-hickory or mixed oak forest would require multiple forest stand improvement activities. A comprehensive forest management plan would be the first step in restoring this high quality environment.
Conservation practices
| Brush Management | |
|---|---|
| Tree/Shrub Establishment | |
| Forest Stand Improvement | |
| Native Plant Community Restoration and Management | |
| Forest Management Plan - Written | |
| Forest Management Plan - Applied |
Transition T4A
State 4 to 2
Cropland can be transitioned to any of the States on this STM model, but the most common is transitioning to a managed pasture state.
Additional community tables
Table 6. Community 1.1 forest overstory composition
| Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | Diameter (in) | Basal area (square ft/acre) |
|---|---|---|---|---|---|---|---|
|
Tree
|
|||||||
| white ash | FRAM2 | Fraxinus americana | Native | – | – | – | – |
| blue ash | FRQU | Fraxinus quadrangulata | Native | – | – | – | – |
| shagbark hickory | CAOV2 | Carya ovata | Native | – | – | – | – |
| pignut hickory | CAGL8 | Carya glabra | Native | – | – | – | – |
| white oak | QUAL | Quercus alba | Native | – | – | – | – |
| southern red oak | QUFA | Quercus falcata | Native | – | – | – | – |
| chinquapin oak | QUMU | Quercus muehlenbergii | Native | – | – | – | – |
| Shumard's oak | QUSH | Quercus shumardii | Native | – | – | – | – |
| black oak | QUVE | Quercus velutina | Native | – | – | – | – |
| northern red oak | QURU | Quercus rubra | Native | – | – | – | – |
Table 7. Community 3.1 forest overstory composition
| Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | Diameter (in) | Basal area (square ft/acre) |
|---|---|---|---|---|---|---|---|
|
Tree
|
|||||||
| honeylocust | GLTR | Gleditsia triacanthos | Native | – | – | – | – |
| eastern redcedar | JUVI | Juniperus virginiana | Native | – | – | – | – |
| tuliptree | LITU | Liriodendron tulipifera | Native | – | – | – | – |
| maple | ACER | Acer | Native | – | – | – | – |
| oak | QUERC | Quercus | Native | – | – | – | – |
Table 8. Community 3.1 forest understory composition
| Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | |
|---|---|---|---|---|---|---|
|
Grass/grass-like (Graminoids)
|
||||||
| tall fescue | SCAR7 | Schedonorus arundinaceus | Introduced | – | – | |
|
Forb/Herb
|
||||||
| giant ironweed | VEGI | Vernonia gigantea | Native | – | – | |
| goldenrod | SOLID | Solidago | Native | – | – | |
| Queen Anne's lace | DACA6 | Daucus carota | Native | – | – | |
|
Shrub/Subshrub
|
||||||
| blackberry | RUBUS | Rubus | Native | – | – | |
| sumac | RHUS | Rhus | Native | – | – | |
| rose | ROSA5 | Rosa | Native | – | – | |
| Amur honeysuckle | LOMA6 | Lonicera maackii | Introduced | – | – | |
Interpretations
Supporting information
Other references
Abrams, M.D. 1992. Fire and the development of oak forests. BioScience, 42: 346–353.
Abrams, M.D. and G.J.Nowacki. 2008. Native Americans as active and passive promoters of mast and fruit trees in the eastern USA. The Holocene 18.7. pp. 1123-1137.
Alexander, H.D. and M.A. Arthur, D.L. Loftis, and S.R. Green. 2008. Survival and growth of upland oak and co-occurring competitor seedlings following single and repeated prescribed fires. Forest Ecology and Management 256: 1021–1030.
Anderson, Michelle D. 2003. Juniperus virginiana. In: Fire Effects Information System, U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, and Fire Sciences Laboratory.
Anderson, R.C. & Brown, L.E. 1983. Comparative effects of fire on trees in a Midwestern savannah and an adjacent forest. Bulletin of the Torrey Botanical Club, 110: 87–90.
Baskin, J.M., C.C. Baskin, and E.W. Chester. 1994. The Big Barrens of Kentucky and Tennessee: Further observations and considerations. Castanea 59:226-254.
Black, B.A., Abrams, M.D. 2001. Influence of Native Americans and surveyor biases on metes and bounds witness tree distribution. Ecology. 82:2574-2586.
Braun, E.L. 1950. Deciduous forests of Eastern North America. Blakinston Co., Pennsylvania. Reprinted in 2001 by Blackburn Press, Caldwell, New Jersey.
Carmean. W.H. 1970. Site quality for eastern hardwoods. The silviculture of oaks and associated species. USDA Forest Service Research paper, Northeast. Forest Exp. Sta., Upper Darby, PA, NE-144: 36-56.
Carmean, W.H. 1971. Soil-site relationships of the upland oaks. Oak Symp. Proc. USDA Forest Service Research Paper. Northeast. Forest Exp. Sta., Upper Darby, PA. p. 23-29.
Carmean, Willard H.; Hahn, Jerold T.; Jacobs, Rodney D. 1989. Site index curves for forest species in the eastern United States. Gen. Tech. Rep. NC-128. St. Paul, MN: U.S. Department of Agriculture, Forest Service, North Central Forest Experiment Station.
Comer, P., D. Faber-Langendoen, R. Evans, S. Gawler, C. Josse, G. Kittel, S. Menard, M. Pyne,
M. Reid, K. Schulz, K. Snow, and J. Teague. 2003. Ecological Systems of the United States: A Working Classification of U.S. Terrestrial Systems. NatureServe, Arlington, Virginia.
Curtis, J. T., 1959. Ecological Systems of the United States: A Working Classification of U.S. Terrestrial Systems. NatureServe, Virginia. .
Denevan, W.M. 1992. The pristine myth: the landscape of the Americas in 1492. Annals of the Association of American Geographers, 82 (3), 369–385.
DeSelm, H. R. 1994. Tennessee barrens. Castanea 59(3):214-225.
Faber-Langendoen, D., editor. 2001. Plant communities of the Midwest: Classification in an ecological context. Association for Biodiversity Information, Arlington, VA. 61 pp. + appendix (705 pp.).
Fenneman, N.M. 1917. Physiographic subdivisions of the United States. Proceedings of the National Academy of Sciences of the United States of America. Vol. 3(1). pp. 17 -22.
Gleason, H.A. and A. Cronquist. Manual of Vascular Plants of Northeastern United States and Adjacent Canada. 2nd edition. The New York Botanical Garden, Bronx.
Griffith, G. E., J. M. Omernik, and S. H. Azevedo. 1998. Ecoregions of Tennessee. (Two-sided color poster with map, descriptive text, summary tables, and photographs). U.S. Geological Survey, Reston, VA. Scale 1:940,000.
Kartesz, J.T., The Biota of North America Program (BONAP). 2011. North American Plant Atlas (http://www.bonap.org/MapSwitchboard.html). Chapel Hill, N.C. [maps generated from Kartesz,
J.T. 2010. Floristic Synthesis of North America, Version 1.0. Biota of North America Program (BONAP). (in press)].
Keever, C. 1978. A study of the mixed mesophytic, western mesophytic, and oak chestnut regions of the eastern deciduous forest including a review of the vegetation and sites recommended as potential natural landmarks. Millersville State College, Pennsylvania.
Kuchler, A.W. 1964. Potential natural vegetation of the conterminous United States. Spec. Publ. 36 New York, NY: American Geographical society.
Land Resource Regions and Major Land Resource Areas of the United States. United States Department of Agriculture Soil Conservation Service Handbook 296. Dec. 1981. 87-88.
Landfire [Landfire National Vegetation Dynamics Database]. 2007a. Landfire National Vegetation Dynamics Models. Landfire Project, USDA Forest Service, U.S. Department of Interior. (January - last update)
Lawless, P. J., Baskin, J. M. and C. C. Baskin. 2006. Xeric Limestone Prairies of Eastern United States: Review and Synthesis. The Botanical Review 73(4): 303–325. The New York Botanical Garden.
Lunt, I.D. & Spooner, P.G. 2005. Using historical ecology to understand patterns of biodiversity in fragmented agricultural landscapes. Journal of Biogeography, 32:1859–1873.
McNab, W.H. and P.E. Avers. 1994. Ecological subregions of the United States. U.S. Forest Service. Prepared in cooperation with Regional Compilers and the ECOMAP Team of the Forest Service.
Miller, J.H., Chambliss, E.B. and Loewenstein, N.J. 2010. A field guide for the Identification of Invasive Plants in Southern Forests. US Forest Service Southern Research Station, General Technical Report SRS-119.
Parker, G.R. 1989. Old-growth forests of the Central Hardwood Region. Nat. Areas J. 9(1): 5-11.
Quarterman, E. and R.L. Powell. 1978. Potential ecological/geological natural landmarks on the Interior Low Plateaus. pp. 7-73. U.S. Department of the Interior, Washington, D.C. Quarterman,
Stritch, L.R. 1990. Landscape-scale restoration of barrens-woodland within the oak-hickory forest mosaic. Restoration & Management Notes 8: 73-77.
Somers, P., L. R. Smith, P. B. Hamel, and E. L. Bridges. 1986. Preliminary analyses of plant communities and seasonal changes in cedar glades of middle Tennessee. ASB Bulletin 33:178-192.
U.S. Department of Agriculture (USDA), Natural Resources Conservation Service.
Soil surveys of Tennessee counties in MLRA 123.
U.S. Department of Agriculture-Forest Service, Agriculture Handbook 654, Silvics of North America.
Zollner, D., M.H. MacRoberts, B.R. MacRoberts, & D. Ladd. 2005. Endemic vascular plants of the Interior Highlands, U.S.A. Sida 21:1781-1791.
Websites:
Cleland, D. T., J. A. Freeouf, J. E. Keys, Jr., G. J. Nowacki, C. A. Carpenter, and W. H. McNab. 2007. Ecological Subregions: Sections and Subsections of the Conterminous United States.
GTR-WO-76C-1. http://fsgeodata.fs.fed.us/other_resources/ecosubregions.html
Ecosystem classification of the United States; Ecological Subregions of the United States.1994. Compiled by W. Henry McNab, Peter E. Avers, et al. Forest Service, U.S. Department of Agriculture [USDA], Washington, DC., USA: http://www.fs.fed.us/land/pubs/ecoregions
Environmental Mapping and Assessment Program (EMAP). 2004. Washington, DC., USA: http://www.epa.gov/docs/emap/
Geospatial Data Gateways: https://gdg.sc.egov.usda.gov/
Landfire: http://www.landfire.gov
NatureServe. NatureServe Explorer: An online encyclopedia of life [web application]. Version 7.1. NatureServe, Arlington, Virginia. http://www.natureserve.org/explorer
Nashville Basin Limestone Glade and Woodland, Ecological System Comprehensive Report
http://http://explorer.natureserve.org/servlet/NatureServe?searchSystemUid=ELEMENT_GLOBAL.2.723170
Official Soil Series Descriptions, USDA-NRCS: https://soilseries.sc.egov.usda.gov/osdname.asp
Silvics of North America, US Forest Service. http://www.na.fs.fed.us/spfo/pubs/silvics_manual/table_of_contents.htm
USDA Plants: http://plants.usda.gov/java/
U.S. Geological Survey (USGS), Center for Biological Informatics (CBI) 2004. U.S. Department of the Interior: http://biology.usgs.gov/cbi
Vascular Plant Image Library: http://botany.csdl.tamu.edu/FLORA/imaxxara.htm
Vegetation Mapping Program, National Vegetation Classification Standard. 2004.
Vegetation Classification Standard, Vegetation Subcommittee, U.S. Geological Survey [USGS; U.S. Department of the Interior], Reston, Virginia, USA. http://www.fgdc.gov/standards/projects/FGDC-standards-projects/vegetation
Vegbank: www.vegbank.org
Web Soil Survey, USDA-NRCS: http://websoilsurvey.nrcs.usda.gov/app/
Woodland Wildflowers of Illinois: http://www.illinoiswildflowers.info/woodland/woodland_index.htm
U.S. Department of Agriculture, Forest Service. 1994. Ecosystem classification of the United States; Ecological Subregions of the United States. Compiled by W. Henry McNab, Peter E. Avers, et al., Washington, DC. http://www.fs.fed.us/land/pubs/ecoregions
U.S. Department of the Interior. 2004. Vegetation Mapping Program, National Vegetation Classification Standard. http://biology.usgs.gov/npsveg
U.S. Geological Survey (USGS), Center for Biological Informatics (CBI) 2004. U.S. Department of the Interior. http://biology.usgs.gov/cbi
Approval
Nels Barrett, 9/06/2018
Rangeland health reference sheet
Interpreting Indicators of Rangeland Health is a qualitative assessment protocol used to determine ecosystem condition based on benchmark characteristics described in the Reference Sheet. A suite of 17 (or more) indicators are typically considered in an assessment. The ecological site(s) representative of an assessment location must be known prior to applying the protocol and must be verified based on soils and climate. Current plant community cannot be used to identify the ecological site.
| Author(s)/participant(s) | |
|---|---|
| Contact for lead author | |
| Date | |
| Approved by | |
| Approval date | |
| Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
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Number and extent of rills:
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Presence of water flow patterns:
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Number and height of erosional pedestals or terracettes:
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Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
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Number of gullies and erosion associated with gullies:
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Extent of wind scoured, blowouts and/or depositional areas:
-
Amount of litter movement (describe size and distance expected to travel):
-
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
-
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
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Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
-
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
-
Functional/Structural Groups (list in order of descending dominance by above-ground annual-production or live foliar cover using symbols: >>, >, = to indicate much greater than, greater than, and equal to):
Dominant:
Sub-dominant:
Other:
Additional:
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Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
-
Average percent litter cover (%) and depth ( in):
-
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
-
Potential invasive (including noxious) species (native and non-native). List species which BOTH characterize degraded states and have the potential to become a dominant or co-dominant species on the ecological site if their future establishment and growth is not actively controlled by management interventions. Species that become dominant for only one to several years (e.g., short-term response to drought or wildfire) are not invasive plants. Note that unlike other indicators, we are describing what is NOT expected in the reference state for the ecological site:
-
Perennial plant reproductive capability:
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The Ecosystem Dynamics Interpretive Tool is an information system framework developed by the USDA-ARS Jornada Experimental Range, USDA Natural Resources Conservation Service, and New Mexico State University.
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