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Conservation Service
Ecological site R135AY140MS
Deep Somewhat Poorly Drained Clay Alkaline Broad Flats
Last updated: 5/29/2025
Accessed: 08/19/2026
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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): 135A–Alabama and Mississippi Blackland Prairie
This MLRA has two narrow (less than 40 miles wide), long, arching bands known as the Blackland Prairie and the Jackson Prairie, which are characterized by clayey, soils with a high shrink-swell potential. Several major drainageways bisect this region on their way to larger tributaries. Very little native prairie vegetation remains due to agriculture and forestry activities.
This area is in eastern Mississippi (57 percent) and central and western Alabama (43 percent). It makes up about 10,165 square miles (26,328 square kilometers). Most of this region is surrounded by the distinctly different MLRA 133C, which has sandy soils and stratified, coastal sediment mineralogy. A very small section of MLRA 135A has a diffuse boundary with MLRA 134 that occurs as a loess cap that gradually thins from west to east. (USDA, NRCS, 2022)LRU notes
This ecological site can be seen in the Blackland Prairie, Jackson Prairie, and the Interior Flatwoods of MLRA 135A. Blackland Prairie: This Physiographic Region is a long Crescent shaped land use area that starts in northeastern Mississippi and ends in central Alabama. The Blackland Prairie soils are formed from mostly calcareous coastal plains. These soils occur on low lying, flat, broad landscapes; they are mostly alkaline, heavy clays, with some weathered acid areas. The Blackand Prairie is Interspersed native prairie and hardwood forests; this area is 90% cultivated.
The Jackson Prairie: This physiographic Region consists of a narrow band of soils that occurs in central Mississippi. These soils are gently sloping and formed from a heavy clay parent material. The Jackson Prairie is mostly acid and weathered. This Region is mostly a mixed conifer forest but does have some local pasture and cultivation.
The Interior Flatwoods: This Physiographic Region consists of a narrow band, of soils which were formed out of an acid gray clay. This band of similar soils is situated directly west of the Blackland Prairie. These acid and clayey soils are flat, low lying, mostly saturated, hardwood forests with some areas in cultivation.Classification relationships
This area is in the East Gulf Coastal Plain section of the Coastal Plain province of the Atlantic Plain. The northern part of the area is a slightly elevated, hilly plain. The separate southwestern part is locally known as the Jackson Prairie portion of the East Gulf Coastal Plain section in Mississippi. (USDA, NRCS, 2022)
National Vegetation Classification System Vegetation Association (NatureServe, 2010):
The reference state for this system is comparable to Schizachyrium scoparium - Sorghastrum nutans - Dalea candida - Liatris squarrosa - (Silphium terebinthinaceum) Black Belt Grassland (CEGL004664). Additionally, the Juniperus virginiana - (Celtis laevigata, Prunus angustifolia, Sideroxylon lycioides) Ruderal Woodland community ( CEGL007747) is also represented heavily in this ecological site.Ecological site concept
These sites are found on flat and gently sloping uplands with deep, somewhat poorly drained, alkaline, clay soils. Historically these sites are a mixture of hardwood stands interspaced by grassy patches. Today, these sites are commonly used for soybeans, corn, hay, cotton, small grains, sorghum, and pasture. In areas that are still wooded common tree species are eastern red cedar, sugarberry, and Osage orange with an understory comprised of forbs and grasses.
Associated sites
R135AY110MS Shallow to Moderately Deep Well Drained Silty Clay to Clay Alkaline Broad Flats
These sites are found in areas with more slope and shallower soil than R135AY140MS
R135AY130MS Deep Moderately Well to Well Drained Clay Alkaline Broad Flats
These sites are higher on the landscape with better drainage than R135AY140MS
F135AY160MS Deep Somewhat Poorly Drained Clay Acid Broad Flats
These sites are on higher, flatter, more weathered sites than R135AY140MS
F135AY230MS Deep Somewhat Poorly Drained To Moderately Well Drained Clay Alkaline Floodplains
These sites are found in the floodplains below R135AY140MS
Similar sites
R135AY110MS Shallow to Moderately Deep Well Drained Silty Clay to Clay Alkaline Broad Flats
These sites are shallower and better drained than R135AY140MS
R135AY130MS Deep Moderately Well to Well Drained Clay Alkaline Broad Flats
These sites are better drained than R135AY140MS
Table 1. Dominant plant species
Tree (1) Prunus angustifolia
(2) Malus angustifoliaShrub (1) Cercis canadensis
(2) Juniperus virginianaHerbaceous (1) Schizachyrium scoparium
(2) Andropogon glomeratusPhysiographic features
Most of this area is underlain by Cretaceous-age clay, marl, soft limestone, or chalk of the Selma Group. The Jackson Prairie part, in southern Mississippi, and parts of the MLRA in southwest Alabama are underlain by Tertiary-age clay, marl, soft limestone, or chalk of the Vicksburg and Jackson Groups. (USDA, NRCS, 2022)
Table 2. Representative physiographic features
Landforms (1) Upland > Flat
(2) Upland > Ridge
(3) Upland > Hillslope
(4) Upland > Toe
Runoff class Medium Flooding frequency None Ponding frequency None Elevation 170 – 500 ft Slope 1 – 3 % Water table depth 12 – 30 in Aspect Aspect is not a significant factor Table 3. Representative physiographic features (actual ranges)
Runoff class Medium Flooding frequency None Ponding frequency None Elevation 100 – 500 ft Slope 0 – 5 % Water table depth 0 – 48 in Climatic features
This ecological site occurs in the thermic temperature regime for MLRA 135A. The thermic soil temperature regime has mean annual soil temperatures of 15 ⁰C or more, but less than 22 ⁰C; and a difference between mean summer and mean winter soil temperatures of greater than 6 ⁰C at 50 cm below the surface.
The average annual precipitation is sampled from areas running the length of MLRA 135A. Rainfall is common throughout the year; with the maximum precipitation occurring in early winter, spring, and midsummer. The lowest rainfall occurs in autumn. The rainfall typically occurs during high intensity, convective thunderstorms in summer, but some heavy rains occur during tropical storms in winter.Table 4 Representative climatic features
Frost-free period (characteristic range) 180-200 days Freeze-free period (characteristic range) 220-240 days Precipitation total (characteristic range) 50-60 in Frost-free period (actual range) 170-210 days Freeze-free period (actual range) 200-240 days Precipitation total (actual range) 50-60 in Frost-free period (average) 190 days Freeze-free period (average) 230 days Precipitation total (average) 60 in Characteristic rangeActual rangeBarLineFigure 1. Monthly precipitation range
Characteristic rangeActual rangeBarLineFigure 2. Monthly minimum temperature range
Characteristic rangeActual rangeBarLineFigure 3. Monthly maximum temperature range
BarLineFigure 4. Monthly average minimum and maximum temperature
Figure 5. Annual precipitation pattern
Figure 6 Annual average temperature pattern
Climate stations used
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(1) CORINTH 7 SW [USC00221962], Corinth, MS
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(2) RIPLEY [USC00227467], Ripley, MS
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(3) BOONEVILLE [USC00220955], Booneville, MS
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(4) TUPELO RGNL AP [USW00093862], Tupelo, MS
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(5) VERONA EXP STN [USC00229173], Tupelo, MS
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(6) FULTON 3 W [USC00223208], Fulton, MS
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(7) HOUSTON [USC00224265], Houston, MS
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(8) ABERDEEN [USC00220021], Amory, MS
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(9) STATE UNIV [USC00228374], Starkville, MS
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(10) COLUMBUS [USC00221880], Columbus, MS
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(11) BROOKSVILLE EXP STN [USC00221111], Brooksville, MS
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(12) MACON 3N [USC00225361], Macon, MS
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(13) LIVINGSTON [USC00014798], Livingston, AL
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(14) MARION JUNCTION 2 NE [USC00015121], Marion Junction, AL
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(15) MONTGOMERY AP [USW00013895], Hope Hull, AL
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(16) MONTGOMERY 6SW [USC00015553], Montgomery, AL
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(17) PELAHATCHIE [USC00226811], Pelahatchie, MS
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(18) FOREST [USC00223107], Forest, MS
">Influencing water features
Due to the topographic position, this site does not have water features or wetlands.
Soil features
Soils associated with this site fall within the thermic temperature regime of MLRA 135A. The thermic soil temperature regime is defined as having a difference in soil temperature of 6 degrees C or more between mean summer (June, July, and August in the Northern Hemisphere) and mean winter (December, January, and February in the Northern Hemisphere) and a mean annual soil temperature of: 15 degrees C (59 degrees F) to 22 degrees C (72 degrees F). Soils in this ecological site are deep somewhat poorly drained alkaline clay. This ecological site is comprised of Brooksville and Faunsdale with the Brooksville series being the modal concept for this site.
Please note that the soils listed in this section of the description may not be all inclusive. There may be additional soils that fit the site’s concepts. Additionally, the soils that provisionally form the concepts of this site may occur elsewhere, either within or outside of the MLRA and may or may not have the same geomorphic characteristics or support similar vegetation. Some soil map units and soil series included in this “provisional” ecological site were used as a “best fit” for a particular soil – landform catena during a specific era of soil mapping, regardless of the origin of parent material or the location of MLRA boundaries. Therefore, the listed soils may not be typical for MLRA 135A or a specific location, and the associated soil map units may warrant further investigation in a joint ecological site inventory – soil survey project. When utilizing this provisional description, the user is encouraged to verify that the area of interest meets the appropriate ecological site concepts by reviewing the soils, landform, vegetation, and physical location. If the site concepts do not match the attributes of the area of interest, please review the Similar or Associated Sites listed in the General Information section of this description to determine if another site may be a better fit for your area of interest.Table 5. Representative soil features
Parent material (1) Marine deposits – chalk
(2) Marine deposits – limestone and dolomite
Surface texture (1) Clay loam
(2) Silty clay
Drainage class Somewhat poorly drained Permeability class Very slow to moderately slow Soil depth 80 – 90 in Surface fragment cover <=3" Not specified Surface fragment cover >3" Not specified Available water capacity
(0-40in)5.4 – 8.2 in Soil reaction (1:1 water)
(0-10in)5.8 – 8.4 Subsurface fragment volume <=3"
(0-60in)0 – 5 % Subsurface fragment volume >3"
(0-60in)Not specified Table 6. Representative soil features (actual values)
Drainage class Somewhat poorly drained to moderately well drained Permeability class Very slow to moderately slow Soil depth 62 – 90 in Surface fragment cover <=3" 0 % Surface fragment cover >3" 0 % Available water capacity
(0-40in)5.4 – 8.3 in Soil reaction (1:1 water)
(0-10in)5.1 – 8.4 Subsurface fragment volume <=3"
(0-60in)0 – 5 % Subsurface fragment volume >3"
(0-60in)0 % Ecological dynamics
This Ecological site has six states: Native Grassland, Wooded Thicket/ Forest, Pasture, Crop land, Aquaculture, and Conservation Area.
Native Grassland is the reference state for this ecological site. Grasslands depend on regular disturbance (fire, mowing, etc.) intervals to stay as grasslands. Today, Native Grasslands are highly encroached upon by non-native species that tend to thrive off of the same disturbances and often outcompete native species.
Wooded thicket/ Forest, the second ecological state, occurs when there is not enough disturbance to maintain a Native Grassland. Trees (especially redcedar) and shrubs are allowed to grow and will eventually outcompete native grass species.
Pasture and Cropland (the third and fourth ecological states) occur as a result of heavy land management changes (clearcutting, herbicide, tilling, grazing, etc.) in order to produce livestock and crops.
Aquaculture, predominantly for catfish production, can occur on flat heavy clay portions of this ecological site.
Conservation areas are sites set aside to try and recapture the historical plant and animal communities of the reference state. These states will never be a perfect replication because of anthropogenic and natural changes to the ecological system.State and transition model
More interactive model formats are also available. View Interactive Models
Click on state and transition labels to scroll to the respective textEcosystem states
States 1, 5, 2 and 6 (additional transitions)
T1-2 - Leave undisturbed T1-3 - Manage for pasture T1-4 - Manage for crops T1-5 - Manage for aquaculture T2-3 - Clear and manage for pasture T2-4 - Manage for crops T2-5 - Manage for aquaculture T2-6 - Manage for native prairie T3-2 - Leave unmanaged T3-4 - Manage for crops T3-5 - Manage for aquaculture T3-6 - Manage for native prairie T4-3 - Manage for grassland or pasture T4-5 - Manage for aquaculture T4-6 - Manage for native prairie T6-2 - Not enough disturbance to maintain the state T6-3 - Manage for pasture T6-4 - Manage for desired crops State 1 submodel, plant communities
State 2 submodel, plant communities
State 3 submodel, plant communities
State 4 submodel, plant communities
State 1
Reference State: Native GrasslandThis ecological state can be broadly defined as any mixed species grassland (potentially with a few trees) on calcareous uplands that have not been modified for pasture, hay production, or cropland. Evidence suggests that this ecological state initially occurred as a result of rotational burning done by the Native American Tribes in the region. Native grasslands were described by many of the early explorers of this region; however, they are seldom, if ever, seen in pristine condition in modern times. Most remnants of the native grasslands occur in small patches between 1-10 acres, and almost all of these remnants now contain non-native and invasive species. Anthropogenic effects, such as changes in land management, introduction of non-native species, and soil erosion, have all led to the degradation and diminishing representation of this ecological state.
Characteristics and indicators. This state is characterized by a mixture of grasses, forbs, sedges, and other herbaceous plants with relatively few trees.
Resilience management. This ecological state requires regular disturbance to be maintained. This disturbance predominantly occurs as burning or mowing. If an area growing as a native grassland is not being managed it will initially transition into a redcedar forest and then a hardwood forest over time.
Community 1.1
Native PrairieThis community is comprised of native grasses, flowers, shrubs, and other native herbaceous plants, with the potential for a few trees spread around the Prairie. This community likely does not exist in the Blackland Prairie anymore as much of the land has been converted for agricultural purposes. Additionally, the areas of prairie that do still exist have an abundance of introduced and invasive species. Returning disturbed areas of this ecological site to near pristine prairie conditions would restore the historic habitat of many native wildlife species including the northern bobwhite (Colinus virginianus), eastern wild turkey (Meleagris gallopovo), white-tailed deer (Odocoileus virginianus), a variety of pollinator species, migratory birds, and many others.
Resilience management. It takes an immense amount of management to maintain a pristine prairie. It would require burning or mowing the area ranging from annually to once every few years to prevent the prairie from turning into a redcedar forest. Additionally, maintaining a pristine prairie would require regular use of selective herbicide or manual removal to minimize invasive species.
Dominant plant species
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eastern redcedar (Juniperus virginiana), tree
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Osage-orange (Maclura pomifera), tree
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big bluestem (Andropogon gerardii), grass
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eastern gamagrass (Tripsacum dactyloides), grass
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winged lythrum (Lythrum alatum), other herbaceous
State 2
Wooded Thicket/ ForestThis ecological state is commonly seen adjacent to cropland and pasture, and it frequently occurs on steeper areas and along property lines, areas that are less likely to be disturbed by agricultural processes. Depending on the plant community, this site can be dominated by eastern redcedar (Juniperus virginiana), white ash (Fraxinus americana), sugarberry (Celtis laevigata), post oak ( Quercus stellata), and Osage orange ( Maclura pomifera ).
Community 2.1
Historical Forest CommunityHistoric documentation indicates that wooded thickets used to be comprised of species such as Chickasaw plum (Prunus angustifolia), hawthorns (Crataegus engelmannii), and crab apple (Malus angustifolia). Furthermore, these records indicate that prior to European settlement there was very little eastern redcedar (Juniperus virginiana) on these sites. This sub-state is virtually never seen today.
Resilience management. In order to achieve this sub-state it would require planting the desired tree species in a cleared location, preventing large scale disturbance to this area to allow these species to grow, and removing red cedar trees from the area.
Dominant plant species
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Engelmann's hawthorn (Crataegus engelmannii), tree
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Chickasaw plum (Prunus angustifolia), tree
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southern crab apple (Malus angustifolia), tree
Community 2.2
Redcedar InvasionThis community occurs when there is not enough disturbance in a grassland community to prevent the growth of redcedar trees. This community is still primarily grasses but has young redcedar trees growing throughout the area.
Resilience management. This community will grow into a redcedar forest if it is left undisturbed. If the area is burned, mowed, or has the trees clear-cut it will revert to a mixed invasive and native grass community.
Dominant plant species
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eastern redcedar (Juniperus virginiana), tree
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Osage-orange (Maclura pomifera), tree
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green ash (Fraxinus pennsylvanica), tree
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sugarberry (Celtis laevigata), tree
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Bermudagrass (Cynodon dactylon), grass
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Johnsongrass (Sorghum halepense), grass
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fescue (Festuca), grass
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sweetclover (Melilotus officinalis), other herbaceous
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sericea lespedeza (Lespedeza cuneata), other herbaceous
Community 2.3
Redcedar ThicketThis community is dominated by eastern redcedar, white ash (Fraxinus americana), and Osage orange (Maclura pomifera). The understory is typically still comprised of grasses and other herbaceous species, but these will not be nearly as prolific in this ecological state as they are in native grassland.
Resilience management. This state will likely be maintained so long as there is no disturbance. There is a possibility, assuming there is no disturbance and soil conditions are adequate, that post oak (<a class="species-link" href="https://plants.usda.gov/core/profile?symbol=QUST" target="_blank" title="Open in plants.usda.gov"><i>Quercus stellata</i></a>) and other hardwoods will take over.
Dominant plant species
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eastern redcedar (Juniperus virginiana), tree
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Osage-orange (Maclura pomifera), tree
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white ash (Fraxinus americana), tree
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sugarberry (Celtis laevigata), tree
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post oak (Quercus stellata), tree
Community 2.4
Hardwood ForestThere is a chance that post oak (Quercus stellata) and other hardwoods will take over on these sites, assuming there is no disturbance for an extended period of time (approximately 25 years) and that soil conditions are on the lower end of the pH for this site.
Resilience management. Leave the site undisturbed.
Dominant plant species
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post oak (Quercus stellata), tree
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eastern redcedar (Juniperus virginiana), tree
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blackjack oak (Quercus marilandica), tree
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southern red oak (Quercus falcata), tree
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black oak (Quercus velutina), tree
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white oak (Quercus alba), tree
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shagbark hickory (Carya ovata), tree
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nutmeg hickory (Carya myristiciformis), tree
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mockernut hickory (Carya tomentosa), tree
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white ash (Fraxinus americana), tree
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winged elm (Ulmus alata), tree
Pathway 2.1.2
Community 2.1 to 2.2This is the natural progression without disturbance.
Pathway 2.2.1
Community 2.2 to 2.1This would require planting desired species, preventing the area from burning, and removing eastern redcedar trees.
Pathway 2.2.3
Community 2.2 to 2.3Over time the redcedar trees will grow and outcompete the grassland species.
Pathway 2.3.1
Community 2.3 to 2.1This would require planting desired species, preventing the area from burning, and removing eastern redcedar trees.
Pathway 2.3.4
Community 2.3 to 2.4This community will only occur on these sites under very specific circumstances. The area will need to remain undisturbed for about twenty five years, with soils on the deeper end for this ecological site concept, and a pH that is on the low end for this ecological site concept
State 3
Pasture/ Non-Native GrasslandPasture is a grassland that occurs as a result of heavy land management changes (clearcutting, herbicide, grazing, planting etc.) in order to produce livestock or hay. Pasture differs from native grassland as the plant species in the pasture are typically selected and planted specifically for forage quality as opposed to allowing livestock to graze on the existing native plant community. Livestock can greatly alter the plant community if proper grazing practices are not followed.
Community 3.1
Mixed GrasslandThis community is characterized by a combination of native grasses and grasses introduced as forage. This community depends upon disturbance, and thus, can be susceptible to invasive species that similarly thrive with regular disturbance.
Dominant plant species
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Bermudagrass (Cynodon dactylon), grass
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Johnsongrass (Sorghum halepense), grass
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fescue (Festuca), grass
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sweetclover (Melilotus officinalis), other herbaceous
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sericea lespedeza (Lespedeza cuneata), other herbaceous
State 4
CroplandCropland occurs as a result of heavy land management changes (clearcutting, herbicide, tilling, etc.) in order to produce crops. Common crops for this ecological site are cotton, soybeans, corn, sorghum, and small grains. There are different management styles used for cropland communities including conventional till, no till, cover crop, double crop, and others. Some of these practices are mutually exclusive, but others can be combined.
Community 4.1
CroplandThis ecological state is used for crop production.
Resilience management. This state takes a substantial amount of management to prevent it from growing to a grassland. If left totally undisturbed it will trend to a redcedar thicket.
State 5
AquacultureAquaculture in this region is predominantly used for the production of catfish. Most producers in this region will excavate ponds at a uniform depth in flat heavy clay areas.
State 6
Conservation AreaConservation areas are sites set aside to try and recapture the historical plant and animal communities of the reference state. These states will never be a perfect replication because of anthropogenic and natural changes to the ecological system. Some of these changes include fire suppression, changes in hydrology (channeling waterways...), extinction of species, introduced species, invasive species, altering landscapes (farming practices and urbanization) and probable changes to the soil microbial communities. These sites are meant to be the best representation possible for these historical communities given the changes that have occurred. For this ecological site, a restoration area would be a native grassland that experiences regular disturbance.
Resilience management. This will require managing for specific native prairie species and incorporating a regular burning or mowing regiment.
Dominant plant species
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little bluestem (Schizachyrium scoparium), grass
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wiry panicgrass (Panicum flexile), grass
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Crawe's sedge (Carex crawei), grass
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bushy bluestem (Andropogon glomeratus), grass
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sideoats grama (Bouteloua curtipendula), grass
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broomsedge bluestem (Andropogon virginicus), grass
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switchgrass (Panicum virgatum), grass
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Indiangrass (Sorghastrum), grass
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big bluestem (Andropogon gerardii), grass
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slimspike threeawn (Aristida longespica), grass
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hairy fimbry (Fimbristylis puberula), grass
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green comet milkweed (Asclepias viridiflora), other herbaceous
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lanceleaf tickseed (Coreopsis lanceolata), other herbaceous
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prairie tea (Croton monanthogynus), other herbaceous
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white prairie clover (Dalea candida), other herbaceous
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prairie fleabane (Erigeron strigosus), other herbaceous
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flowering spurge (Euphorbia corollata), other herbaceous
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lemonyellow false goldenaster (Heterotheca camporum), other herbaceous
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scaly blazing star (Liatris squarrosa), other herbaceous
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grooved flax (Linum sulcatum), other herbaceous
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hoary puccoon (Lithospermum canescens), other herbaceous
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palespike lobelia (Lobelia spicata), other herbaceous
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white four o'clock (Mirabilis albida), other herbaceous
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eastern whiteflower beardtongue (Penstemon tenuiflorus), other herbaceous
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gray goldenrod (Solidago nemoralis), other herbaceous
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late purple aster (Symphyotrichum patens), other herbaceous
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compassplant (Silphium laciniatum), other herbaceous
Transition T1-2
State 1 to 2This is the natural progression for this ecological site. if a grassland is left undisturbed it will first transition to a redcedar thicket before becoming a hardwood forest.
Transition T1-3
State 1 to 3Pasture is a grassland that occurs as a result of heavy land management changes (clearcutting, herbicide, tilling, grazing, planting etc.) in order to produce livestock or hay.
Transition T1-4
State 1 to 4Cropland occur as a result of heavy land management changes (clearcutting, herbicide, tilling, etc.) in order to produce crops.
Transition T1-5
State 1 to 5Dig a pond and manage for aquaculture.
Transition T2-3
State 2 to 3Clear-cut or burn trees and plant it to pasture.
Transition T2-4
State 2 to 4Clear-cut or burn trees and plant desired crops.
Transition T2-5
State 2 to 5Clear trees, dig a pond and manage for aquaculture.
Transition T2-6
State 2 to 6Remove trees and plant a diverse variety of native prairie species. Once this state is established it will require intermittent disturbance to maintain.
Transition T3-2
State 3 to 2This is the natural progression for this ecological site if it is left undisturbed.
Transition T3-4
State 3 to 4Use herbicides or other mechanical methods to get rid of non native grass species and plant desired crops.
Transition T3-5
State 3 to 5Dig a pond and manage for aquaculture.
Transition T3-6
State 3 to 6Clear pasture species and plant a diverse variety of native prairie species. Once this state is established it will require intermittent disturbance to maintain.
Transition T4-3
State 4 to 3Plant to pasture
Transition T4-5
State 4 to 5Dig a pond and manage for aquaculture.
Transition T4-6
State 4 to 6Remove crops and plant a diverse variety of native prairie species. Once this state is established it will require intermittent disturbance to maintain.
Transition T6-2
State 6 to 2This progression occurs when there is not enough disturbance to maintain the restored prairie.
Transition T6-3
State 6 to 3Clear prairie and plant desired forage species.
Transition T6-4
State 6 to 4Clear prairie species and plant desired crops.
Additional community tables
Table 7. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 8. Community 2.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 9. Community 2.2 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 10. Community 2.3 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 11. Community 2.4 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 12. Community 3.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Table 13. Community 4.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Interpretations
Supporting information
Inventory data references
Data collection and analysis of field data will be performed during the Verification Stage of ESD development.
Other references
Barone John A. 2005. The Historical Presence and Distribution of Prairies in the Black Belt of Mississippi and Alabama. Castanea Vol.70 No.3 (2005): 170-183. http://www.bioone.org/doi/full/10.2179/04-25.1
Barone John A. and Jovonn G. Hill. 2007. Herbaceous Flora of Blackland Prairie Remnants in Mississippi and Western Alabama. Castanea Vol.72 No.4 (2007): 226-234. http://www.bioone.org/doi/full/10.2179/06-34.1
Campbell, J.J.N and W.R. Seymour Jr. 2011. A Review of Native Vegetation Types in the Black Belt of Mississippi and Alabama, with Suggested Relationships to the Catenas of Soil Series. Journal of the Mississippi Academy of Sciences Vol. 56 No.2 (2011). http://www.thefreelibrary.com/A+review+of+native+vegetation+types+in+the+Black+Belt+of+Mississippi...-a0266845301
Campbell, J.J.N and W.R. Seymour Jr. 2012. The Flora of Pulliam Prairie, Chickasaw County, Mississippi: a Significant Remnant of Native Vegetation in the Black Belt Region. Journal of the Mississippi Academy of Sciences Vol. 57. https://www.semanticscholar.org/paper/The-Flora-of-Pulliam-Prairie%2CChickasawCounty%2CaCampbelSeymour/3e143794339468a405d660d1b2575e6bff0e4755
Gruchy, John. Restoring Native Grasslands and Bobwhite Quail In The Black Belt Prairie. Mississippi Wildlife, Fisheries, and Parks. https://www.mdwfp.com/media/4199/bbp_restoration_for_onm.pdf
Leidolf, Andreas and Sidney McDaniel. 1998. A Floristic Study of Black Prairie Plant Communities at Sixteen Section Prairie, Oktibbeha County, Mississippi. Castanea 63, no.1 (1998): 51-62. https://www.jstor.org/stable/4034055
McDearman, Will and Malcolm Hodges. Southeast Gulf Coastal Plain Blackland Prairie and Woodland Rapid Assessment Reference Condition Model. US Forest Service. https://www.fs.usda.gov/database/feis/pdfs/PNVGs/Southeast/R9BKBE.pdf
Schotz, Al and Michael Barbour. 2009. Ecological Assessment and Terrestrial Vertebrate Surveys for Black Belt Prairies in Alabama. Auburn University. https://www.outdooralabama.com/sites/default/files/Research/SWG%20Reports/Prairie_SWG_Final_Report.compressed.pdf
U.S. Department of Agriculture, Natural Resources Conservation Service. 2022. Land resource regions and major land resource areas of the United States, the Caribbean, and the Pacific Basin. Agriculture Handbook 296.
U.S. Department of Agriculture, Natural Resources Conservation Service. The PLANTS database. National Plant Data Team, Greensboro, NC. http://plants.usda.gov (accessed 7 August 2023).
Weakley, A.S. 2016. Acer floridanum - Quercus shumardii - Quercus muehlenbergii - (Aesculus glabra, Carya myristiciformis) Forest. NatureServe. https://explorer.natureserve.org/Taxon/ELEMENT_GLOBAL.2.685533/Acer_floridanum_-_Quercus_shumardii_-_Quercus_muehlenbergii_-_(Aesculus_glabra_Carya_myristiciformis)_Forest
Weakly, A.S. and M. Pyne. 2005. Juniperus virginiana - (Celtis laevigata, Prunus angustifolia, Sideroxylon lycioides) Woodland. NatureServe. https://explorer.natureserve.org/Taxon/ELEMENT_GLOBAL.2.688183/Juniperus_virginiana_-_(Celtis_laevigata_Prunus_angustifolia_Sideroxylon_lycioides)_Woodland
Wieland R. and A.Schotz.2003. Schizachyrium scoparium - Sorghastrum nutans - Dalea candida -Liatris squarrosa - (Silphium terebinthinaceum) Black Belt Grassland. NatureServe. https://explorer.natureserve.org/Taxon/ELEMENT_GLOBAL.2.686431/Schizachyrium_scoparium_-_Sorghastrum_nutans_-_Dalea_candida_-_Liatris_squarrosa_-_(Silphium_terebinthinaceum)_Black_Belt_GrasslandContributors
Peyton Fralick
Approval
Charles Stemmans, 5/29/2025
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) Peyton Fralick Contact for lead author Peyton Fralick Peyton.Fralick@usda.gov 662-205-3404 Date 08/19/2026 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:
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Amount of litter movement (describe size and distance expected to travel):
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Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
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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:
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Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
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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):
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Average percent litter cover (%) and depth ( in):
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Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
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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:
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Perennial plant reproductive capability:
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PrintThe 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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