Print Report

G017 Quercus stellata - Quercus marilandica Forest & Woodland Group

Type Concept Sentence: This vegetation varies from open woodlands with scattered trees to dense forests with a dense and viney understory, and is found in Oklahoma, ranging north to southeastern Kansas, and south through central Texas to the Inner Coastal Plain. Short, stunted Quercus stellata and/or Quercus marilandica are characteristic and dominant, typically with Carya texana.


Common (Translated Scientific) Name: Post Oak - Blackjack Oak Forest & Woodland Group

Colloquial Name: Cross Timbers & East-Central Texas Plains Oak Forest & Woodland

Hierarchy Level:  Group

Type Concept: This group consists of short, stunted woodlands and forests in eastern, central and western Oklahoma, ranging north to southeastern Kansas, and south through central Texas to the Inner Coastal Plain. The physiognomy of this vegetation varies from open woodlands with scattered trees to dense forests with a dense and viney understory. Canopy height is short (<15 m). This vegetation is located where the forests of the eastern U.S. transition into grasslands of the central U.S. Patches of forests and woodlands are often interspersed with patches of tall- and midgrass prairie. The area consists of irregular plains and rugged scarps with primarily sandy to loamy soils that range from shallow to moderately deep. Rainfall can be moderate, but somewhat erratic, therefore moisture is often limiting during part of the growing season. Short, stunted Quercus stellata and/or Quercus marilandica characterize and dominate this group. Another common canopy tree is Carya texana. Other component species may include Carya cordiformis, Celtis laevigata var. reticulata, Quercus prinoides, Ulmus crassifolia, Ulmus alata, Quercus fusiformis, Quercus incana, and Quercus virginiana within their respective ranges. The understory often contains species typical of the surrounding prairies, in particular Schizachyrium scoparium. Small trees or shrubs such as Sideroxylon lanuginosum, Juniperus spp., Smilax spp., and Rhus spp. may also be present. There is considerable variation in associated species in a broad transition from coastal plain to interior areas, and correspondingly from east to west. Drought, grazing, and fire are the primary natural processes that affect this group. With the disruption of these processes today, many examples of this vegetation trend more toward dense stunted forest than open woodland. Overgrazing and conversion to agriculture, along with fire suppression, have led to the invasion of some areas by problematic brush species such as Juniperus virginiana and Juniperus ashei and Prosopis glandulosa farther south in Texas and Oklahoma. It has also led to decreases in native grass cover allowing for annual grasses and forbs to invade.

Diagnostic Characteristics: Tree canopy strongly dominated by Quercus stellata and/or Quercus marilandica (>90% cover). Other associates may be Carya texana, Carya cordiformis, Celtis laevigata var. reticulata, Quercus prinoides, Ulmus crassifolia, Ulmus alata, Quercus fusiformis, Quercus incana, and Quercus virginiana, but lacking many eastern forest or shrub associates such as Quercus falcata, Quercus alba, Quercus coccinea, Pinus echinata, Vaccinium pallidum, Vaccinium stamineum, and Gaylussacia spp. This group only occurs in Kansas, Oklahoma and Texas.

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: This group is currently circumscribed at the group level, separate from somewhat similar vegetation occurring farther east, that is also characterized by Quercus stellata and Quercus marilandica. It is differentiated from these forests by the lack of other "dry-site" eastern oaks, pines, and shrubs, such as Quercus falcata, Quercus alba, Quercus coccinea, Pinus echinata, Vaccinium pallidum, Vaccinium stamineum, Gaylussacia spp., among others. Even those forests and woodlands in the nearby Ouachita and Ozark mountains, though characterized by post oak and blackjack oak, have a flora more strongly associated with eastern forests. This group represents the western edge of the eastern deciduous forests, and as such is lacking many of the eastern woody species. In addition, it represents a transition of forests to grasslands, and some evidence suggests this group once had a higher grass cover, linking it more closely with the Great Plains grasslands. Many factors are thought to have contributed to this increase in woody cover, primarily the imbalance in two main natural processes that helped maintain this grassland state: fire and grazing. Because this vegetation is allied with the grasslands and was perhaps more so under natural conditions, and because many of the eastern species present in similar vegetation farther east are absent in this vegetation, it is currently circumscribed at the group level. Further investigation and review are necessary to determine if this is appropriate. Three or more alliances are expected to be needed, one north of the range of Ulmus crassifolia and one south, that also brings in some southeastern components such as Ulmus alata, Ilex vomitoria, Callicarpa americana, and Vaccinium arboreum, and then, perhaps one west of the range of these eastern shrubs and where western shrubs such as Mahonia trifoliolata, Condalia hookeri, Colubrina texensis, among others are more prominent. An alliance reflecting a mixture of Quercus stellata and Quercus virginiana may also be warranted in the southern limit of this vegetation.

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

Physiognomy and Structure: Short, stunted Quercus stellata and/or Quercus marilandica characterize and dominate this group. The physiognomy of this vegetation includes scattered trees with high herbaceous cover, open-canopied woodlands, and closed-canopied patches of trees interspersed with grasslands. The expression of this varied physiognomy is thought to be related to environmental conditions such as geology, soils, hydrology, and topography and natural processes such as fire and grazing. The canopy of this vegetation is typically characterized by a low stature (<15 m).

Floristics: This group is usually dominated or codominated by Quercus stellata and/or Quercus marilandica. Other canopy components may include Carya texana, Carya cordiformis, Celtis laevigata var. reticulata, Quercus prinoides, Ulmus crassifolia, Ulmus alata, Quercus fusiformis, Quercus incana, and Quercus virginiana within their respective ranges, but the canopy is typically low in species richness. Where light penetration allows the development of an herbaceous understory or in areas with reduced woody canopy, the ground flora contains species typical of the surrounding prairies, in particular Schizachyrium scoparium, but also including Andropogon gerardii, Bothriochloa laguroides ssp. torreyana, Paspalum plicatulum (to the south), Sorghastrum nutans, and Sporobolus cryptandrus. Species richness is typically higher in the herbaceous ground flora than in the canopy. Woody cover is generally thought to be higher today than historically, and shrubs may attain significant cover in the understory of some examples. Woody understory composition varies geographically and with soil type and may include, within their respective ranges, Sideroxylon lanuginosum, Rhus spp., Smilax spp., Juniperus virginiana, Juniperus ashei, Ilex vomitoria (sometimes with high cover), Callicarpa americana, Vaccinium arboreum, Ilex decidua, Toxicodendron radicans, Prosopis glandulosa, and Symphoricarpos orbiculatus.

Dynamics:  Drought, grazing, and fire are the primary natural processes that affect this group. Overgrazing, fire suppression and conversion to improved pasture or other agricultural uses have led to increased woody cover on most extant occurrences of this group and the invasion of some areas by problematic brush species such as Juniperus virginiana var. virginiana and Prosopis glandulosa within their respective ranges. These factors have also led to decreases in native grass cover allowing for annual grasses and forbs to invade.

Environmental Description:  This vegetation is located where the forests of the eastern U.S. transition into grasslands of the central U.S. Climate: Rainfall can be moderate, generally ranging from 66 to 110 cm (26-43 inches) per year and is somewhat erratic, therefore moisture is often limiting during part of the growing season. Soil/substrate/hydrology: The area consists of irregular plains and rugged scarps with primarily sandy to loamy soils that range from shallow to moderately deep.

Geographic Range: This group forms a north-south band of vegetation on the eastern edge of the Great Plains. It ranges from the southeastern corner of Kansas to the Inner Coastal Plain of Texas.

Nations: US

States/Provinces:  AR, KS, OK, TX




Confidence Level: Moderate

Confidence Level Comments: No Data Available

Grank: GNR

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: > Oak - hickory savanna (Bruner 1931)
>< Oak-Hickory Forest Region, Southern Division, Forest Prairie Transition (Braun 1950) [Conceptually, Braun''s types are vegetation regions, but the forested part of the region corresponds very closely to the group concept described here.]
> Osage Savanna (Blair and Hubbell 1938)

Concept Author(s): E.L. Braun (1950)

Author of Description: J. Teague

Acknowledgements: S. Franklin

Version Date: 04-16-13

  • Barbour, M. G., and W. D. Billings, editors. 1988. North American terrestrial vegetation. Cambridge University Press, New York. 434 pp.
  • Blair, W. F., and T. H. Hubbell. 1938. The biotic districts of Oklahoma. The American Midland Naturalist 20:425-454.
  • Braun, E. L. 1950. Deciduous forests of eastern North America. Hafner Press, New York. 596 pp.
  • Bruner, W. E. 1931. The vegetation of Oklahoma. Ecological Monographs 1:99-188.
  • Dyksterhuis, E. J. 1948. The vegetation of the Western Cross Timbers. Ecological Monographs 18:325-376.
  • Faber-Langendoen, D., J. Drake, S. Gawler, M. Hall, C. Josse, G. Kittel, S. Menard, C. Nordman, M. Pyne, M. Reid, L. Sneddon, K. Schulz, J. Teague, M. Russo, K. Snow, and P. Comer, editors. 2010-2019a. Divisions, Macrogroups and Groups for the Revised U.S. National Vegetation Classification. NatureServe, Arlington, VA. plus appendices. [in preparation]
  • Griffith, G. E., S. A. Bryce, J. M. Omernik, J. A. Comstock, A. C. Rogers, B. Harrison, S. L. Hatch, and D. Bezanson. 2004. Ecoregions of Texas (two-sided color poster with map, descriptive text, summary tables, and photographs). U.S. Geological Survey, Reston, VA. Scale 1:2,500,000.
  • Hoagland, B. 2000. The vegetation of Oklahoma: A classification for landscape mapping and conservation planning. The Southwestern Naturalist 45(4):385-420.
  • MacRoberts, B. R., M. H. MacRoberts, and J. C. Cathey. 2002b. Floristics of xeric sandylands in the Post Oak Savanna region of east Texas. Sida 20(1):373-386.
  • MacRoberts, M. H., B. R. MacRoberts, B. A. Sorrie, and R. E. Evans. 2002a. Endemism in the West Gulf Coastal Plain: Importance of xeric habitats. Sida 20:767-780.
  • MacRoberts, M. H., and B. R. MacRoberts. 2004. The Post Oak Savanna ecoregion: A floristic assessment of its uniqueness. Sida 21(1):399-407.
  • McBride, J. B. 1933. The vegetation and habitat factors of the Carrizo sands. Ecological Monographs 3:247-297.
  • Ricketts, T. H., E. Dinerstein, D. M. Olson, C. J. Loucks, and W. Eichbaum. 1999. Terrestrial ecoregions of North America: A conservation assessment. Island Press, Washington, DC. 485 pp.
  • Singhurst, J. R., J. C. Cathy, D. Prochaska, H. Haucke, G. C. Kroh, and W. C. Holmes. 2004. The vascular flora of Gus Engeling Wildlife Management Area, Anderson County, Texas. Southeastern Naturalist 2(3):347-368.
  • Smeins, F. E., and D. D. Diamond. 1986a. Grasslands and savannahs of east central Texas: Ecology, preservation status and management problems. Pages 381-394 in: D. L. Kulhavy and R. N. Conner, editors. Wilderness and natural areas in the eastern United States: A management challenge. Central Applied Studies, School of Forestry, Stephen F. Austin State University, Nacogdoches, TX.