Print Report

CEGL002391 Quercus stellata - Quercus marilandica / Schizachyrium scoparium Wooded Grassland

Type Concept Sentence: No Data Available


Common (Translated Scientific) Name: Post Oak - Blackjack Oak / Little Bluestem Wooded Grassland

Colloquial Name: Central Post Oak Dry Barrens

Hierarchy Level:  Association

Type Concept: This open post oak barrens community is found in the Interior Highlands region of the central United States. Stands occur on shallow, somewhat excessively drained soil over bedrock (commonly sandstone or sandy/gravelly substrates) or on dry, exposed slopes. Soils are infertile, circumneutral to slightly acidic, and moderately well-drained to rapidly drained. Large boulders and pavements of exposed sandstone may occur. Stunted, xerophytic oaks grow above a sparse layer of grasses less than 1 m tall. Tree canopy species include Quercus marilandica, Quercus stellata, Quercus falcata, Quercus alba, and Quercus velutina. Shrubby areas, often containing Vaccinium arboreum, may be present. The herbaceous layer is composed of Carex pensylvanica, Danthonia spicata, Koeleria macrantha, and Schizachyrium scoparium. Other characteristic species include Clitoria mariana, Liatris squarrosa, and Solidago juncea.

Diagnostic Characteristics: No Data Available

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: This community is found in the Shawnee Hills and widely separated areas along major stream valleys in Illinois. It also occurs in Missouri, Indiana, and Arkansas, and possibly Kentucky, where it is associated with acid oak woodlands. In Indiana, the chert barrens are primarily tracked as ~Quercus stellata - Quercus marilandica / Schizachyrium scoparium - Silphium terebinthinaceum Wooded Grassland (CEGL005134)$$. This community is threatened by lack of fire which has resulted in canopy closure, denser undergrowth, and a loss of ground cover. This "savanna" type is closely allied to ~Quercus stellata - Quercus marilandica - Quercus velutina - Carya texana / Schizachyrium scoparium Woodland (CEGL002149)$$. Together with the woodlands, these communities are often referred to as "barrens" (Hutchison 1994).

Similar NVC Types: No Data Available
note: No Data Available

Physiognomy and Structure: The amount and size of bedrock on the surface dramatically affects the vegetative community. Tree canopy 5-20 m tall, tall shrub 0.5-5 m, and graminoid layer 0-2 m.

Floristics: This community consists of a patchy, open layer of stunted, xerophytic oaks and a patchy layer of grasses less than 1 m tall. The herbaceous layer is composed of Danthonia spicata, Carex pensylvanica, Koeleria macrantha, and Schizachyrium scoparium. Tree canopy species include Quercus marilandica, Quercus stellata, Quercus falcata, Quercus alba, and Quercus velutina. Shrubby areas, often containing Vaccinium arboreum, may be present. Other characteristic species include Clitoria mariana, Liatris squarrosa, and Solidago juncea (TNC 1995a). Exotics which may be invasive include Securigera varia (= Coronilla varia), Elaeagnus umbellata, Populus alba, and Rosa multiflora. The type, size, and percent cover of bedrock within the community has an important effect on species composition. Substrate availability also greatly affects canopy cover, which is extremely variable throughout the range of this natural community. Juniperus virginiana can become a serious invasive within this community, especially if fires are suppressed. Herbaceous diversity can vary considerably with substrate and geographic location.

Dynamics:  Natural disturbances include damage from drought, freeze/thaw, icestorms, lightning, wind, insects, and disease (bacteria, fungi). These open stands, as well as associated woodlands, can be managed by fire to retain their openness. Fires may historically have burned every 5-10 years (Nelson 1985). Summer heat and drought greatly influence vegetative growth and recruitment within this community (Fralish 1988). Periods of freezing and thawing encourage downslope subsidence of soil material and affects substrate availability. These climatic extremes coupled with edaphic characteristics, which include thin, stony, rapidly drained soils and exposed bedrock, favor this open vegetation. Where unnatural fire suppression has occurred, canopy closure may exceed that commonly associated with a sparse woodland. Edaphic factors are largely responsible for successional stability of this community, but natural, low-intensity, infrequent fires may also be important for maintaining this wooded herbaceous community (Fralish et al. 1991, Robertson and Heikens 1994).

Environmental Description:  This community is found on thin, infertile soils which are very rapidly drained and strewn with rock fragments, stones, boulders, and bedrock pavements. Soils are often moderately to highly acidic (pH <6.5) and low in organic matter. Soils are predominantly stony and rocky, developed from windblown loess and weathered sandstone. Southern and western aspects have very high temperatures during the summer as well as frequent periods of freezing and thawing during the winter, which contributes to downslope migration of soil materials and associated rock and organic debris. Droughty conditions prevail throughout most of the year. Soils are subject to erosion, and patches of bare ground are not uncommon. The substrate restricts tree growth and limits herbaceous diversity. In the Cretaceous Hills region of Illinois, the bedrock is sedimentary, formed by the accumulation of minerals, rock debris, and/or organic matter from weathering, erosion, and deposition of rocks present during the Paleozoic Era. Bedrock, which is most frequently sandstone, has a layered appearance due to the accumulation and compression processes. Soil pH is slightly to moderately acidic when underlain or mixed with sandstone, chert, or igneous material (TNC 1995a).

Soils of this open woodland (barrens) are extremely stony and rocky or areas of soils interspersed with many boulders, rock outcrops, and vertical bluffs. Exposed rock is dominant. Conditions vary from site to site and may contain long, narrow sandstone bluffs to oblong areas strewn with boulders and small rock outcrops. Areas with many stones and flags are also common. Intervening soils may be from 10-150 cm thick over bedrock. Surface layers are silt loam or stony silt loam overlying subsurface layers which can be silty clay loam or stony loam. Silty clay occurs where shale is present and crops out on the surface. Soils information was collected from cores and pits and county soils map. Primarily Ultisols with a thermic temperature regime and udic moisture regime. Soils are very stony and rocky, consisting of windblown loess and weathered parent material.

Bedrock is sedimentary, formed by the accumulation of sediments from weathering, erosion, and deposition of rocks present during the Paleozoic Era. These rocks are made of minerals, rock debris, and/or organic matter and have a layered appearance due to accumulation and compression processes. Sandstone is the most frequently encountered bedrock in this forest. Rock color is variable, but most often gray, brown, yellowish, and/or reddish, determined by the type, amount, and color of cementing agents. The degree of hardness is variable but is very hard if cemented by silica. Erosion-resistant sandstone forms ridges in the landscape between pockets of softer rocks. Soil pH is slightly to moderately acidic when underlain or mixed with sandstone, chert, or igneous material.

Environmental variables associated with this open woodland include thin, infertile soils which are very rapidly drained and strewn with rock fragments, stones, boulders, and bedrock pavements. Soils are often moderately to highly acidic (pH <6.5). South to west aspects have high summer heat as well as frequent periods of freezing and thawing, which contribute to downslope migration of soil materials and associated rock and organic debris. The open canopy permits a lot of light to penetrate to the ground layer.

Geographic Range: This open post oak barrens community is found in the Interior Highlands region of the United States, ranging from the Ozark region of Missouri and Arkansas, east to Illinois and Indiana and possibly Kentucky.

Nations: US

States/Provinces:  AR, IL, IN, KY?, MO




Confidence Level: Low - Poorly Documented

Confidence Level Comments: No Data Available

Grank: G2G3

Greasons: No Data Available


Concept Lineage: This community was a Cretaceous Hills only type, but after regional review, is considered to be part of this more broad-ranging post oak dry barrens type.

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: = Quercus stellata - Quercus marilandica / Schizachyrium scoparium Wooded Herbaceous Vegetation (Faber-Langendoen 2001)
= Quercus stellata - Quercus marilandica / Schizachyrium scoparium Wooded Herbaceous Vegetation (TNC 1995a)
? Acid (Chert, Igneous, Sandstone) Savannah (Nelson 1985)
>< Chert Savanna (Nelson 1985)
< Eastern Broadleaf Forests: 100: Oak-Hickory Forest (Quercus-Carya) (Küchler 1964)
< Eastern Broadleaf and Needleleaf Forests: 111: Oak-Hickory-Pine Forest (Quercus-Carya-Pinus) (Küchler 1964)
< IB4c. Western Post Oak - Blackjack Oak Woodland (Allard 1990)
>< Igneous Savanna (Nelson 1985)
< Post Oak - Blackjack Oak: 40 (Eyre 1980)
>< Sandstone Savanna (Nelson 1985)

Concept Author(s): D. Faber-Langendoen (2001)

Author of Description: M. Guetersloh and D. Faber-Langendoen

Acknowledgements: No Data Available

Version Date: 03-24-00

  • Allard, D. J. 1990. Southeastern United States ecological community classification. Interim report, Version 1.2. The Nature Conservancy, Southeast Regional Office, Chapel Hill, NC. 96 pp.
  • Eyre, F. H., editor. 1980. Forest cover types of the United States and Canada. Society of American Foresters, Washington, DC. 148 pp.
  • Faber-Langendoen, D., editor. 2001. Plant communities of the Midwest: Classification in an ecological context. Association for Biodiversity Information, Arlington, VA. 61 pp. plus appendix (705 pp.).
  • Fralish, J. S. 1987. Forest stand basal area and its relationship to individual soil and topographic factors in the Shawnee Hills. Transactions of the Illinois Academy of Science 80(3 and 4):183-194.
  • Fralish, J. S. 1988b. Predicting potential stand composition from site characteristics in the Shawnee Hills Forest of Illinois. The American Midland Naturalist 120(1):79-101.
  • Fralish, J. S., F. B. Crooks, J. L. Chambers, and F. M. Harty. 1991. Comparison of presettlement, second-growth and old-growth forest on six site types in the Illinois Shawnee Hills. The American Midland Naturalist 125:294-309.
  • Heikens, A. L., and P. A. Robertson. 1994. Barrens of the Midwest: A review of the literature. Castanea 59(3):184-194.
  • Homoya, M. A., J. Aldrich, J. Bacone, L. Casebere, and T. Post. 1988. Indiana natural community classification. Indiana Natural Heritage Program, Indianapolis, IN. Unpublished manuscript.
  • Hutchison, M. D. 1994. The barrens of the Midwest: An historical perspective. Castanea 59(3):195-203.
  • Küchler, A. W. 1964. Potential natural vegetation of the conterminous United States. American Geographic Society Special Publication 36. New York, NY. 116 pp.
  • Leahy, Mike. Personal communication. Missouri Natural Heritage Database, Missouri Department of Conservation, Jefferson City.
  • Madany, M. H. 1981. A floristic survey of savannas in Illinois. Pages 177-181 in: R. L. Stuckey and K. J. Reese, editors. The prairie peninsula: In the "shadow" of Transeau. Proceedings of the Sixth North American Prairie Conference. Ohio Biological Survey. Biology Notes, No. 15, Columbus.
  • Midwestern Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Minneapolis, MN.
  • Nelson, P. 2010. The terrestrial natural communities of Missouri. Revised edition. Missouri Natural Areas Committee, Department of Natural Resources and the Department of Conservation, Jefferson City.
  • Nelson, P. W. 1985. The terrestrial natural communities of Missouri. Missouri Natural Areas Committee, Jefferson City. 197 pp. Revised edition, 1987.
  • Robertson, P. A., and A. L. Heikens. 1994. Fire frequency in oak-hickory forests of southern Illinois. Castanea 59(3):286-291.
  • TNC [The Nature Conservancy]. 1995a. A classification and description of plant communities in southern Illinois. Report by the Southern Illinois Field Office, Ullin, IL, and the Midwest Regional Office, Minneapolis, MN.
  • Voigt, J. W., and R. H. Mohlenbrock. 1964. Plant communities of southern Illinois. Southern Illinois University Press, Carbondale. 202 pp.
  • White, J., and M. Madany. 1978. Classification of natural communities in Illinois. Pages 311-405 in: Natural Areas Inventory technical report: Volume I, survey methods and results. Illinois Natural Areas Inventory, Urbana, IL.