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CEGL006216 Quercus alba - Carya glabra - Fraxinus americana / Muhlenbergia sobolifera - Elymus hystrix Forest

Type Concept Sentence: No Data Available


Common (Translated Scientific) Name: White Oak - Pignut Hickory - White Ash / Rock Muhly - Eastern Bottlebrush Grass Forest

Colloquial Name: Northern Piedmont Hardpan Basic Oak - Hickory Forest

Hierarchy Level:  Association

Type Concept: Found in the Culpeper Basin and western Piedmont foothills of Virginia and Maryland, this subxeric to submesic oak-hickory forest occurs in association with soils weathered from fine-grained mafic rocks (diabase and metabasalt). These soils often have a plastic, hardpan subsoil or are shallow over bedrock, and some have pronounced shrink-swell properties. Forest canopies can be open to closed, sometimes stunted, with variable combinations of oaks (especially Quercus alba and Quercus rubra), hickories (Carya glabra, Carya ovalis, Carya tomentosa), and Fraxinus americana. Subcanopy tree layers are usually dominated by young hickories and Fraxinus americana. Characteristic species in the shrub and small-tree layers are Cercis canadensis var. canadensis, Juniperus virginiana var. virginiana, Cornus florida, Ulmus rubra, Celtis occidentalis, and Rosa carolina. Less constant, but sometimes locally important, understory species include Ostrya virginiana, Carpinus caroliniana (on more mesic sites), and Chionanthus virginicus. The herb layer of this community is frequently characterized by patch-dominance of the dry-site forest grasses Muhlenbergia sobolifera, Dichanthelium boscii, Elymus hystrix var. hystrix, and Danthonia spicata. Co-occurring among the dominant grasses are a large number of low-cover forbs and graminoids. In 50 Virginia plot samples, this unit has a mean species richness of 82 taxa per 400 m2, one of the highest among all classified upland types in Virginia. This community is distinguished from other Mid-Atlantic region oak-hickory forests by its patch-dominance of forest grasses and its strong association with sub-level topography and soils with an impermeable hardpan or shallow bedrock.

Diagnostic Characteristics: No Data Available

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: This vegetation type has been well-documented by 50 plot samples in Virginia and has emerged strongly in several large regional analyses of plot data (e.g., the 1250-plot analysis for the NCR parks vegetation mapping project). It has also been qualitatively documented in a large diabase sill near Boyds, Montgomery County, Maryland. The type also occurs very locally on metabasalt at low elevations of Catoctin Mountain, Maryland. It is generally distinguished from other mid-Atlantic region oak-hickory forests by its patch-dominance of forest grasses and its strong association with gentle or sub-level topography and soils with an impermeable hardpan or shallow bedrock. This unit is largely confined to Piedmont soils weathered from fine-grained mafic rocks (diabase and metabasalt). Several plots at low elevations of Shenandoah National Park are intermediate between this type and ~Quercus rubra - Quercus montana - Carya ovalis / (Cercis canadensis) / Solidago caesia Forest (CEGL008514)$$ and could be assigned equally well to either type. For the purposes of vegetation mapping in Shenandoah, these plots were assigned to CEGL008514.

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

Physiognomy and Structure: No Data Available

Floristics: Vegetation of this type is an open- to closed-canopy, mixed hardwood forest dominated by oaks, hickories, and white ash. Stands over hardpans or shallow soils over bedrock have a somewhat stunted canopy. Quercus alba, Quercus rubra, Carya glabra, Carya ovalis, Carya tomentosa (= Carya alba), and Fraxinus americana are the leading overstory dominants in variable combinations. In the more western, submontane habitats, Quercus montana (= Quercus prinus) is often codominant. Quercus velutina, Quercus stellata, Quercus montana, Ulmus rubra, and Juglans nigra are occasional overstory associates. Subcanopy tree layers are usually dominated by young hickories and Fraxinus americana. Characteristic species in the shrub and small-tree layers are Cercis canadensis var. canadensis (dominant with up to 850 stems/ha in some areas), Juniperus virginiana var. virginiana, Cornus florida, Ulmus rubra, Celtis occidentalis, and Rosa carolina. Less constant, but sometimes locally important, understory species include Ostrya virginiana, Carpinus caroliniana (on more mesic sites), and Chionanthus virginicus. The herb layer of this community is frequently characterized by patch-dominance of the dry-site forest grasses Muhlenbergia sobolifera, Dichanthelium boscii, Elymus hystrix var. hystrix, and Danthonia spicata. Co-occurring among the dominant grasses are a large number of low-cover forbs and graminoids, among the most characteristic of which are Agrimonia rostellata, Amphicarpaea bracteata, Aristolochia serpentaria, Bromus pubescens, Carex digitalis, Carex hirsutella (= Carex complanata var. hirsuta), Desmodium nudiflorum, Festuca subverticillata, Galium circaezans, Geum virginianum, Houstonia purpurea var. purpurea, Maianthemum racemosum ssp. racemosum, Phryma leptostachya, Polygonatum biflorum, Sanicula canadensis, Scutellaria elliptica, Solidago caesia, Solidago ulmifolia var. ulmifolia, Thalictrum thalictroides, Uvularia perfoliata, and Viola triloba var. triloba (all of these with >50% constancy in 50 plots). Less constant species that are nevertheless locally abundant or characteristic include Antennaria plantaginifolia (2 vars.), Brachyelytrum erectum, Carex albicans var. australis, Carex pensylvanica, Carex planispicata, Clematis ochroleuca, Dichanthelium linearifolium, Galium concinnum, Helianthus divaricatus, Melica mutica, Piptochaetium avenaceum, and Pycnanthemum incanum. Patches of exposed mineral soil around tree bases are frequently occupied by a suite of diminutive annuals including Acalypha virginica, Hedeoma pulegioides, and Paronychia canadensis. Many additional species occur at low cover and/or constancy. In 50 Virginia plot samples, this unit has a mean species richness of 82 taxa per 400 m2, one of the highest among all classified upland types in Virginia. Additionally, a plot of this vegetation containing 125 taxa represents one of the most species-rich upland sample among >3300 plots in the VDNH database (VDNH unpubl. data).

Dynamics:  Historically, this association had a more extensive distribution in northern Virginia, but many stands have been destroyed by development sprawling from the Washington, DC, metropolitan area. Most of the remaining stands have been subject to various anthropogenic disturbances, including cutting, conversion to pine silviculture, and grazing. Excessive deer browse, resulting in reduced tree recruitment and dwarfing of repeatedly grazed herbaceous species, is a serious problem in almost all stands. The rather dry soils occupied by this community keep many exotic plants in check, but the drought-tolerant Lonicera japonica, Poa compressa, and Symphoricarpos orbiculatus (a shrub naturalized from the western U.S.) are problematic invaders. Stands on the most mesic sites are vulnerable to invasion by Microstegium vimineum and Alliaria petiolata. The fungal pathogen Discula destructiva (dogwood anthracnose) is now rampant in virtually all stands of this type and has caused extensive mortality of the former understory codominant Cornus florida.

Environmental Description:  In the main, Piedmont portion of its range, this oak-hickory forest community occurs primarily on soils weathered from Triassic diabase but occasionally on soils weathered from siltstone. Outlying occurrences on western Piedmont foothills and the Blue Ridge are associated with metabasalt of the Catoctin Formation. Large stands occupy low, gentle ridges and rolling to flat uplands (mean slope = 4°) of the Mesozoic Basin. In submontane, foothill settings, stands are usually confined to relatively gentle slope benches with shallow underlying bedrock. Fifty plot-sampled sites in Virginia ranged from subxeric to submesic. Surface substrate of most sites consisted of thin leaf litter, with small patches of bare mineral soil exposed in places. Many plots had at least 1% surface cover of spheroidal diabase or metabasalt boulders or stones, and a few were extremely rocky. Soils collected from plots are very strongly to moderately acidic clay loams with moderately high calcium and magnesium, and very high manganese levels. Most soils occupied by this community have a plastic, hardpan subsoil or are shallow over bedrock, and some have pronounced shrink-swell properties.

Geographic Range: This association is widespread in the northern Virginia Mesozoic (Culpeper) Basin and locally in the extension of that basin in Montgomery County, Maryland. Small patches also occur on western Piedmont foothills and low elevations of the Blue Ridge in Virginia and Maryland. The global range of this community needs further investigation and may include parts of the Frederick Basin in Maryland, local areas around Gettysburg, Pennsylvania, and possibly other Mesozoic basins north to New Jersey or lower New England.

Nations: US

States/Provinces:  MD, PA?, VA




Confidence Level: High

Confidence Level Comments: No Data Available

Grank: G3

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: = Quercus alba - Carya glabra - Fraxinus americana / Cercis canadensis / Muhlenbergia sobolifera - Dichanthelium boscii Forest (Fleming and Weber 2003)
= Quercus alba - Fraxinus americana - Carya (glabra, ovalis) / Cercis canadensis / Muhlenbergia sobolifera - Elymus hystrix Forest (Fleming 2002a)

Concept Author(s): G.P. Fleming (2002a)

Author of Description: G.P. Fleming

Acknowledgements: No Data Available

Version Date: 10-01-06

  • Eastern Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boston, MA.
  • Fleming, G. P. 2001b. Preliminary classification of Piedmont and Inner Coastal Plain vegetation types in Virginia. Natural Heritage Technical Report 02-14, Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond. 29 pp.
  • Fleming, G. P. 2002a. Ecological communities of the Bull Run Mountains, Virginia: Baseline vegetation and floristic data for conservation planning and natural area stewardship. Natural Heritage Technical Report 02-12. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond. 274 pp. plus appendices.
  • Fleming, G. P. 2002b. Preliminary classification of Piedmont & Inner Coastal Plain vegetation types in Virginia. Natural Heritage Technical Report 02-14. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond. 29 pp.
  • Fleming, G. P., K. D. Patterson, and K. Taverna. 2017. The natural communities of Virginia: A classification of ecological community groups and community types. Third approximation. Version 3.0. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond, VA. [http://www.dcr.virginia.gov/natural-heritage/natural-communities/]
  • Fleming, G. P., K. Taverna, and P. P. Coulling. 2007b. Vegetation classification for the National Capitol Region parks, eastern region. Regional (VA-MD-DC) analysis prepared for NatureServe and USGS-NPS Vegetation Mapping Program, March 2007. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond.
  • Fleming, G. P., and J. T. Weber. 2003. Inventory, classification, and map of forested ecological communities at Manassas National Battlefield Park, Virginia. Unpublished report submitted to the National Park Service. Natural Heritage Technical Report 03-07. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond. 101 pp. plus appendix.
  • Fleming, G. P., and K. D. Patterson. 2003. Preliminary vegetation classification for the National Capitol Region parks. Regional (VA-WVA-MD-DC) analysis prepared for NatureServe and USGS-NPS Vegetation Mapping Program, March 2003. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond.
  • Fleming, G. P., and K. D. Patterson. 2004. Natural community inventory of selected areas in the Northern Virginia Culpeper Basin, Fairfax, Loudoun, Prince William, Fauquier, and Culpeper counties. Unpublished report submitted to the Virginia Native Plant Society, Potowmack Chapter. Natural Heritage Technical Report 04-07. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond. 21 pp. plus appendices.
  • Fleming, G. P., and K. Taverna. 2006. Vegetation classification for the National Capitol Region parks, western region. Regional (VA-WVA-MD-DC) analysis prepared for NatureServe and USGS-NPS Vegetation Mapping Program, March 2006. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond.
  • Harrison, J. W. 2011. The natural communities of Maryland: 2011 working list of ecological community groups and community types. Unpublished report. Maryland Department of Natural Resources, Wildlife and Heritage Service, Natural Heritage Program, Annapolis. 33 pp.
  • Harrison, J. W., compiler. 2004. Classification of vegetation communities of Maryland: First iteration. A subset of the International Classification of Ecological Communities: Terrestrial Vegetation of the United States, NatureServe. Maryland Natural Heritage Program, Maryland Department of Natural Resources, Annapolis. 243 pp.