
Natural Resources
Conservation Service
Ecological site PX136X00X200
Mesic Temperature Regime, Basic Upland Flats and Depressions, Expansive Clay, Seasonally Wet and Dry
Last updated: 5/02/2025
Accessed: 05/19/2025
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): 136X–Southern Piedmont
This MLRA is on a large piedmont underlain by metamorphic and igneous bedrock. It stretches from north-central Virginia to east-central Alabama, running parallel to the Appalachian highlands to the northwest and the Atlantic coast to the southeast.
MLRA 136 has only subtle climatic differences with MLRA 148 (Northern Piedmont), with which it shares a common geologic origin. This adjacent MLRA sits to the north. Along the fall line, it shares a boundary with MLRA 133A (Southern Coastal Plain), MLRA 137 (Carolina and Georgia Sand Hills), and 133C (Gulf Coastal Plain). Here, unconsolidated Coastal Plain sediments intersect the much older Piedmont bedrock. Along it's northwestern boundary, it sits adjacent to MLRAs 130B (Southern Blue Ridge), 130A (Northern Blue Ridge), and 128 (Southern Appalachian Ridges and Valleys). These MLRAs are distinguished from the Southern Piedmont by topographic and elevational differences, as well as differences in the age, origin, and degree of metamorphism of the underlying bedrock.
Five states are intersected by the MLRA, including North Carolina (29 percent), Georgia (27 percent), Virginia (20 percent), South Carolina (17 percent), and Alabama (7 percent). The MLRA extent makes up about 63,720 square miles (165,034 square kilometers).
MLRA PHYSIOGRAPHY
The landscape is generally rolling to hilly, with a well-defined drainage pattern. Streams have dissected the original Piedmont plateau, forming narrow ridgetops, somewhat broad interfluves, and short, steep side slopes adjacent to the streams and drainageways. With some exceptions, the valley floors are generally narrow and make up about 10 percent or less of the land area. The associated stream terraces are generally small and of minor extent.
The landscape is moderately dissected overall, with isolated erosional remnants (monadnocks) and other areas of high topographic relief interspersed. Over most of the MLRA, elevation ranges from approximately 325 to 1,315 feet (100 to 400 meters), with elevations generally increasing toward the Appalachian Highlands, in the upper Piedmont, and decreasing toward the Coastal Plain, in the lower Piedmont.
The major rivers that cross this area en route to the ocean include, from north to south, the James, Roanoke, Cape Fear, Savannah, Altamaha, Chattahoochee, and Alabama Rivers. These rivers typically originate within the Piedmont or in the Blue Ridge. They flow east and south across the Coastal Plain and empty into the Atlantic Ocean or the Gulf of America.
MLRA GEOLOGY
Precambrian and Paleozoic metamorphic and igneous rocks underlie almost all of this MLRA. The dominant metamorphic rock types include gneiss, schist, slate, argillite, and phyllite, among others. Dominant igneous rock types include granite and other related felsic crystalline rocks. Mafic intrusive rocks, including gabbro, diabase, amphibolite, and other dark colored rocks, underlie a minority of the upland landscape. These mafic intrusions crop out in the form of dikes and sills, and often weather to produce soils high in base cations.
The Carolina Slate Belt runs lengthwise through the east-central part of the MLRA, in southern Virginia, North Carolina, South Carolina, and the eastern-most part of the Georgia Piedmont. This region is underlain by fine-grained metasedimentary and metavolcanic rock, which generally weathers to produce soils high in silt.
From Virginia to North Carolina, and in a single county in South Carolina, fault-bounded Triassic Basins are scattered amongst the igneous and metamorphic uplands. These basins are underlain by Triassic and Jurassic siltstone, shale, sandstone, and mudstone, which were laid down in response to continental rifting and subsequent erosion during the Mesozoic era.
MLRA SOILS
The dominant soil orders of the MLRA are Ultisols, Inceptisols, and Alfisols. Ultisols and Alfisols are typically found on more stable landforms, such as interfluves, gentle hillslopes, broad ridgetops, and stream terraces, while Inceptisols are typically found on less stable landforms, including flood plains, steep hillslopes, and narrow ridgetops.
Soils of the region predominantly have a thermic temperature regime, a udic moisture regime, and generally have kaolinitic or mixed mineralogy. In the upper Piedmont of Virginia and North Carolina however, soils have a mesic soil temperature regime, as depicted in figure 2. The mesic soil temperature regime portion of the MLRA is oriented from northeast to southwest and occupies approximately 18 percent of the MLRA extent, or 11,729 square miles (30,377 square kilometers).
Broadly speaking, soils of the Southern Piedmont uplands are shallow to very deep, well drained, and loamy or clayey. Soils of the river valleys are generally very deep, well to poorly drained, and loamy. Soils tend to be finer-textured than in Coastal Plain regions.
MLRA CLIMATE
In general, precipitation is evenly distributed throughout the year in this MLRA, with occasional drought-like conditions extending from late summer into autumn. During the growing season, most of the rainfall comes from high-intensity, convective thunderstorms. Significant moisture also comes from the movement of warm and cold fronts across the MLRA from November to April. High amounts of rain can also occur during hurricanes, usually during the months of August through October.
Over most of the MLRA, snowfall is typically light, though overall, the mesic soil temperature regime portion of the MLRA features colder temperatures, more snowfall, and a shorter growing season than in the thermic portion. The cooler climate in this region supports an increase in species with northern or Blue Ridge affinities. Both the mean annual temperature and the length of the freeze-free period increase from north to south and with decreasing elevation from the upper to the lower Piedmont.
MLRA LAND USE AND RESOURCES
Once largely cultivated, much of this region is now planted to loblolly pine or has reverted to successional pine and hardwood forests. The more productive lands support small to medium-size family farms that produce crops and livestock, while the less productive lands have been in forest for some time. Most of the open areas are used for grazing beef cattle, though in years past, dairy cattle were also important to the local economy. The principal crops of the region include corn, soybeans, and small grains. Burley tobacco remains a crop of local importance. Cotton is grown in the thermic soil temperature regime portion of the MLRA.
Several major land cover transformations have occurred in the Southern Piedmont over the past several centuries; from open woodlands sculpted by fire, to farmland, to closed forests and planted pine, past land uses have played an outsized role in shaping present-day soils and vegetation patterns in the region. Land-use intensity peaked with the arrival of the industrial revolution, which gradually increased demand for textiles. Cotton became the dominant crop over much of the region.
In spite of early successes, two centuries of poor management practices accelerated soil erosion, stripping away the fertility and moisture-supplying capacity of soils. In addition to soil losses in the uplands, legacy sediments derived from the eroded land rapidly accumulated in the river valleys below, often leading to changes in hydrology and flooding frequency.
After being stripped of it's loamy topsoil, many areas of the Piedmont had been so badly eroded as to render the land unsuitable or economically impractical for agriculture. The effects of erosion were widespread, with cumulative soil loss estimates ranging from 5 to 10 inches on average. The steeper slopes, which had often been cleared and farmed at the height of the Cotton era, generally suffered greater losses. By the 1930's, crop production was in rapid decline in the Southern Piedmont. The loss of soil productivity due to erosion, losses to the cotton boll weevil, development of synthetic fibers, and the onset of the Great Depression all contributed to rapid abandonment of cropland. By 1960, cropland acres had decreased by more than 50 percent in nearly every county in the Southern Piedmont.
While crop production is still important today on the more productive lands, those of lower productivity, or those that were subject to severe erosion, were often abandoned some time ago. Typically, they have either reverted to forest, or have been converted to other uses. Although the productivity of soils was greatly reduced through erosion, less intensive land uses such as grazing and forestry were still feasible. These land uses gained popularity as patterns of urban migration, low commodity prices, and other factors gradually made crop production less economical on the marginal lands.
In recent years, large-scale adoption of soil conservation practices have led to better outcomes with respect to erosion in much of MLRA, increasing the economic viability and long-term sustainability of Piedmont farms. Despite some success, water erosion remains one of the most important soil resource concerns in the MLRA.
Other major resource concerns include increasing conversion of prime farmland and farmland of statewide importance to urban uses. Throughout the MLRA, metropolitan areas are expanding into lands that have historically been used for timber or agriculture. This change in land use is occurring rapidly in the corridor called the Piedmont Crescent, which extends from Atlanta, Georgia, to Raleigh, North Carolina.
HISTORIC VEGETATION COVER
Over most of the Southern Piedmont uplands, the historic oak-hickory, or oak-hickory-pine forest, once covered large portions of the landscape. It was dominated by upland oaks, such as white oak (Quercus alba), northern red oak (Quercus rubra), and southern red oak (Quercus falcata), with a smaller contribution from hickories (Carya spp.) and pines. The principal pine species are shortleaf pine (Pinus echinata), loblolly pine (Pinus taeda), and to the north and west, Virginia pine (Pinus virginiana). In the southernmost and easternmost portions of the MLRA, the historic montane longleaf pine forest, dominated by longleaf pine (Pinus palustris), shortleaf pine (P. echinata), and dry-site oaks, was found on ridgetops and steep south or west-facing slopes.
According to historic accounts, forests and woodlands of the past were generally more open and park-like, having been exposed to a more frequent fire regime. Piedmont prairies, likely maintained by Native Americans, were also reportedly common across the landscape, as were fire-maintained canebrakes along the streams (Trimble 1974; Daniels 1987; Griffith et al. 2002; Van Lear et al. 2004; Dearman and James 2019; Schomberg et al. 2020; USDA-NRCS 2022).
LRU notes
MLRA 136 is one of the largest MLRAs in the United States. It has a broad north-south and east-west extent and covers a wide range of elevations. The MLRA is partitioned by the mesic-thermic line, which divides the MLRA into mesic and thermic soil temperature regimes (figure 2.). The mesic soil temperature regime was delineated based on estimates of the native range of loblolly pine, which was historically absent in this part of the MLRA. In addition, this region is said to represent the northern and western limits of cotton production, an important crop to the south and east.
ESDs developed for this MLRA were split geographically into mesic and thermic ecological site concepts. Climate variation across the MLRA extent warrants the development of Land Resource Unit (LRU) classifications, to further subdivide the MLRA and support more precise Ecological Site Descriptions.
Classification relationships
APPLICABLE USNVC ASSOCIATIONS
CEGL007403 Quercus phellos / Carex (albolutescens, intumescens, joorii) / Climacium americanum; CEGL004037 Quercus phellos - Quercus (alba, stellata) - Carya carolinae-septentrionalis
APPLICABLE EPA ECOREGIONS
Level III: 45. Piedmont
Level IV: 45e. Northern Inner Piedmont (EPA 2013).
APPLICABLE USFS ECOLOGICAL UNITS
Domain: Humid Temperate
Division: Subtropical
Ecological province: 231. Southeastern Mixed Forest
Ecological sections: 231I.Central Appalachian Piedmont (Cleland et al. 2007).
Based on the USGS physiographic classification system (Fenneman and Johnson 1946), most of MLRA 136 is in the Piedmont Upland section of the Piedmont province, in the Appalachian Highlands division.
Ecological site concept
This ecological site includes seasonally wet and seasonally dry circumneutral soils on upland flats, upland depressions, and at the heads of drainageways. It is geographically restricted to the mesic soil temperature regime portion of the Southern Piedmont, in the northwestern-most part of the MLRA. This ecological site is subject to wetting and drying cycles typical of "hydroxeric" conditions, due primarily to shrink-swell clay minerology and low relief. These sites are saturated or even ponded during the cooler months, but generally dry out by late spring or summer.
Soils on this ecological site are weathered from mafic intrusive rock or strongly basic sedimentary rock of Triassic age. The material can be overlain by a thin mantle of slope alluvium washed from higher areas. Soils are typically moderately deep to deep, poorly drained Alfisols. The subsoil has a high clay content and the clay fraction is dominated by 2:1 clay minerals. Base saturation is greater than or equal to 35 percent in the subsoil.
A transient water table is present within 12 inches of the soil surface during the cooler months. Nevertheless, these wet conditions are temporary and the vegetation generally has a drier character than would be expected. Seasonally drier examples still, in which the water table remains well below the surface, are covered by PX136X00X210, a similar and often associated ecological site.
The reference state supports an open to partially open canopy woodland with a species-rich herbaceous understory. Important canopy species include willow oak (Quercus phellos), post oak (Quercus stellata), and American elm (Ulmus americana). Dominant land uses include pasture and hayland, cropland, wildlife habitat, and other land uses meant to conserve threatened plants and animals. Soils are poorly-suited to most building applications or septic system installations because of seasonal wetness and shrink-swell hazard.
ES CHARACTERISTICS SUMMARY
• Mesic soil temperature regime
• Occurs on Piedmont uplands, on upland flats, upland depressions, and at the heads of drainageways
• Parent materials: mafic intrusive rock or strongly basic Triassic sedimentary rock
• Base saturation: ≥ 35 percent in the subsoil
• Seasonal high water table: perched, 0 - 12 inches from the soil surface
• Soils: moderately deep to deep, poorly drained Alfisols
• The subsoil has a high clay content and a high shrink-swell potential
Associated sites
PX136X00X210 |
Mesic Temperature Regime, Basic Upland Woodland, Expansive Clay, Seasonally Wet and Dry Found in slightly higher and drier landscape positions. Soils have a comparable shrink-swell potential, but the seasonal high water table is deeper (12-40 inches from the soil surface), supporting a relative increase in dry-site species, of which blackjack oak (Quercus marilandica) is most notable. |
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PX136X00X220 |
Mesic Temperature Regime, Basic Upland Forest, Moist Found in higher landscape positions. The seasonal high water table is much deeper (≥ 40 inches from the soil surface, usually deeper). The clay fraction is not dominated by shrink-swell clay minerals, reducing fluctuations in plant available water and allowing moisture-loving plant species to increase in abundance, of which northern red oak (Quercus rubra) is most notable. |
Similar sites
PX136X00X700 |
Basic Upland Flats and Depressions, Expansive Clay, Seasonally Wet and Dry The soil temperature regime is thermic, occurring within the native range of loblolly pine (Pinus taeda). |
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PX136X00X300 |
Mesic Temperature Regime, Acidic Upland Depressions and Heads of Drains, Wet The geomorphic setting is similar, but soils weathered from acidic igneous or metamorphic rock. The subsoil is not dominated by shrink-swell clay minerals and has a base saturation less than 35 percent. Seasonal extremes in plant available water are less pronounced, significantly reducing cover from dry-site species such as post oak (Quercus stellata). These stands are comparatively less diverse. |
PX136X00X210 |
Mesic Temperature Regime, Basic Upland Woodland, Expansive Clay, Seasonally Wet and Dry Soil properties are similar, but the seasonal high water table is deeper (12-40 inches from the soil surface). Cover from dry-site species tends to increase, of which blackjack oak (Quercus marilandica) is most notable. |

Figure 1. EPA level IV ecoregions of the Southern Piedmont (45).

Figure 2. Spatial illustration of soil temperature regimes of the Southern Piedmont.

Figure 3. Spatial extent of this ecological site representing the major areas where this site is important on the landscape.
Table 1. Dominant plant species
Tree |
(1) Quercus phellos |
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Shrub |
(1) Viburnum |
Herbaceous |
(1) Dichanthelium |
Legacy ID
F136XY200VA
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Ecosystem states
T1A | - | Clearcut logging or other large-scale disturbances that cause canopy removal. |
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T1B | - | Selective removals of the most valuable timber specimens, leaving inferior trees behind. |
T1C | - | Mechanical tree/brush/stump/debris removal, seedbed preparation, and planting of perennial grasses and forbs. |
T2A | - | Long-term natural succession. |
T2B | - | Mechanical tree/brush/stump/debris removal, seedbed preparation, and planting of perennial grasses and forbs. |
T3A | - | Clearcut logging or other large-scale disturbances that cause canopy removal. |
T3B | - | Mechanical tree/brush/stump/debris removal, seedbed preparation, applications of fertilizer/lime, weed control, and planting of perennial grasses and forbs. |
T4A | - | Long-term cessation of grazing. |
State 1 submodel, plant communities
1.1A | - | Long-term exclusion of fire. |
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1.2A | - | Prescribed burns and selective removals. |
State 2 submodel, plant communities
2.1A | - | Clearcut logging. |
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2.2A | - | Natural succession. |
2.2B | - | Brush management. |
2.3A | - | Natural succession. |