Print Report
CEGL006565 Betula lenta - Quercus montana / Parthenocissus quinquefolia Woodland
Type Concept Sentence: This sweet birch - chestnut oak talus woodland occurs on steep talus slopes composed of quartzite, sandstone, or phyllite, in the Central Appalachians; examples are typically dominated by the tree Betula lenta, with Betula papyrifera, Betula populifolia, or Betula alleghaniensis, as well as Quercus montana and Nyssa sylvatica.
Common (Translated Scientific) Name: Sweet Birch - Chestnut Oak / Virginia Creeper Woodland
Colloquial Name: Sweet Birch - Chestnut Oak Talus Woodland
Hierarchy Level: Association
Type Concept: This talus or rocky slope woodland community occurs in the central Appalachian Mountains and extends west to the Western Allegheny Plateau in Pennsylvania. The substrate is generally quartzite or sandstone talus. Sites are usually steeply sloping, but the type also sometimes occurs on gentler benches and ridge crests. Soils, where present, are shallow, organic, acidic and infertile. The canopy is of variable cover but generally open with gnarled, widely spaced trees. Characteristic trees are birches, primarily Betula lenta but less frequently including Betula papyrifera, Betula populifolia, or Betula alleghaniensis, as well as Nyssa sylvatica. Other tree associates may include Tsuga canadensis, Acer rubrum, Carya glabra, Quercus montana, Quercus alba, Quercus rubra, Quercus velutina, or Quercus coccinea. Typical shrubs include Acer spicatum, Acer pensylvanicum, Amelanchier arborea, Castanea dentata, Kalmia latifolia, Hamamelis virginiana, Menziesia pilosa, Ribes rotundifolium, Vaccinium angustifolium, Vitis spp., Toxicodendron radicans, Smilax rotundifolia, and Parthenocissus quinquefolia. Ferns characterize the herb layer and may include Dryopteris marginalis, Polypodium virginianum, Woodsia obtusa, or Asplenium platyneuron. The forbs Aralia nudicaulis, Heuchera spp., and Scutellaria saxatilis are also well-adapted to the bouldery habitats. Lichens, especially the rock-tripes Lasallia papulosa and Umbilicaria mammulata and the foliose species Flavoparmelia baltimorensis, characterize the nonvascular layer.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: This vegetation type is broadly defined and exhibits considerable geographic and elevational variation. It is also poorly represented by plot data, and additional sampling is needed, particularly of lower elevation and south-slope stands. Even with limited data, potential variants of the type in Virginia were proposed by Fleming and Moorhead (2000). A variant of sheltered north slopes in which Tsuga canadensis is codominant with Betula lenta and/or Quercus spp. has been reported from Virginia by Hupp (1983) and from Pennsylvania by Fike (1999), but may be referable to bouldery variants of ~Tsuga canadensis - Quercus montana - Betula lenta Forest (CEGL006923)$$. Many Virginia populations of the state-rare, northern tree Betula papyrifera var. cordifolia are associated with this community type.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: Physiognomy varies from nearly closed forest to open woodland with widely spaced trees. The canopy is dominated by more-or-less gnarled specimens of Betula lenta and Quercus montana (= Quercus prinus) generally <20 m tall. Betula lenta is usually the sole dominant of less weathered, steeper, more unstable boulderfield habitats, while a greater variety of trees is often codominant with Betula lenta on more weathered and stable habitats. Other overstory associates that may be important on some sites are Quercus rubra, Nyssa sylvatica, Betula populifolia, Betula papyrifera var. cordifolia, Carya glabra, Tsuga canadensis, and Betula alleghaniensis. The presence of well-preserved, fallen boles indicates that Castanea dentata was important on some boulderfields prior to the arrival of chestnut blight (Fleming and Moorhead 2000). Acer rubrum and Nyssa sylvatica are scattered canopy associates and frequent understory species. The typically open shrub layer contains Acer pensylvanicum, Acer spicatum, Amelanchier arborea, Castanea dentata sprouts, Hamamelis virginiana, Ilex montana, Kalmia latifolia, Menziesia pilosa (at the southern end of the range), and Ribes rotundifolium. The ground layer consists almost entirely of low-statured shrubs, particularly Menziesia pilosa and Vaccinium angustifolium, and/or scattered to abundant vines of Parthenocissus quinquefolia, Vitis spp., Toxicodendron radicans, and Smilax rotundifolia. True herbs are very sparse and restricted to mossy pockets or flat boulders; typical species are Dryopteris marginalis, Polypodium appalachianum, Deschampsia flexuosa, and Danthonia spicata. In the southern portion of the range, Heuchera spp. and Scutellaria saxatilis are characteristic herbs. Bryophyte cover ranges up to 65% in some microhabitats. The rock-tripes Lasallia papulosa and Umbilicaria mammulata, and the foliose species Flavoparmelia baltimorensis, are generally the most conspicuous lichens. The combination of surficial boulder cover and nutrient-poor substrate results in a notably low mean species richness (n = 24 taxa per 400 m2) in Virginia and Maryland plot samples of this type.
Dynamics: This boulderfield woodland represents a long-term sere in the geomorphic and vegetational progression from exposed, lichen-dominated block fields to fully forested mountain slopes with well-developed mineral soils. In addition to edaphic stresses, trees of these habitats are subject to frequent damage from wind and ice storms. This community often occurs in patch-mosaics with open, lichen-covered boulderfields that lack vascular plants. Boundaries between the boulderfield woodlands and adjacent forests are often obscure, with composition gradually changing along with substrate conditions and soil depth. This type frequently intergrades with several communities of the Mixed Oak / Heath Forests group, especially ~Quercus montana - Quercus rubra / Hamamelis virginiana Forest (CEGL006057)$$ of somewhat sheltered, often very rocky slopes. In Virginia, this association reaches optimal development on sideslopes of linear sandstone and quartzite strike ridges in the Ridge and Valley, and on the western, metasedimentary flank of the northern Blue Ridge. Landsliding and debris avalanches, which generate and regenerate boulderfield environments, are dominant erosional processes in these landscapes (Hack and Goodlett 1960).
Environmental Description: Sites include the edges of very large, unvegetated (except for lichens), scarcely weathered block fields, as well as a variety of more weathered boulderfields and slopes covered by coarse to fine, bouldery colluvium. Much of the bouldery rubble is weathered from resistant quartzite, sandstone caprock, or phyllite. The elevation range of plot-sampled stands in Virginia is 100 to 1025 m (300-3360 feet). Slope position and aspect are variable, while associated landforms include landslide scarps, slide masses, concave hollow heads, and incised hollow bottoms. Mean cover of exposed boulders at Virginia sampling sites is 72%. In this very rocky environment, soil is limited to local, interstitial, root-rich duff deposits, or to "pads" of moss and underlying, thin, organic / sandy material that have developed on wide, flat boulder surfaces. Interstitial air spaces between boulders may be prevalent for 1.0 m or more below the surface. Soils are largely organic and usually extremely acidic and infertile. There is often some heterogeneity of boulder depth and weathering, as well as of microclimate and soil moisture, within boulderfields. In general, sites are somewhat xeric and show little evidence of subsurface drainage. However, this regime is ameliorated by higher elevations and north aspects, which probably slow evaporation and increase the moisture-holding capacity of the bouldery substrate.
Geographic Range: This community occurs locally throughout the Blue Ridge and Ridge and Valley sections of Pennsylvania, Virginia, West Virginia, and Maryland, extending northeast to the Pennsylvania-New Jersey border and New York.
Nations: US
States/Provinces: MD, NJ, NY, PA, VA, WV
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.685271
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: G4
Greasons: No Data Available
Type | Name | Database Code | Classification Code |
---|---|---|---|
Class | 1 Forest & Woodland Class | C01 | 1 |
Subclass | 1.B Temperate & Boreal Forest & Woodland Subclass | S15 | 1.B |
Formation | 1.B.2 Cool Temperate Forest & Woodland Formation | F008 | 1.B.2 |
Division | 1.B.2.Na Eastern North American Forest & Woodland Division | D008 | 1.B.2.Na |
Macrogroup | 1.B.2.Na.2 Appalachian-Northeastern Oak - Hardwood - Pine Forest & Woodland Macrogroup | M502 | 1.B.2.Na.2 |
Group | 1.B.2.Na.2.c White Oak - Chestnut Oak - Pignut Hickory Forest & Woodland Group | G650 | 1.B.2.Na.2.c |
Alliance | A4466 <i>Quercus rubra - Quercus montana - Betula lenta</i> Talus Woodland | A4466 | 1.B.2.Na.2.c |
Association | CEGL006565 Sweet Birch - Chestnut Oak / Virginia Creeper Woodland | CEGL006565 | 1.B.2.Na.2.c |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: = Betula lenta - Quercus montana - Quercus rubra / Menziesia pilosa / Dryopteris marginalis Forest (Young et al. 2007a)
= Betula lenta - Quercus prinus / Parthenocissus quinquefolia Woodland (Lea 2003)
= Betula lenta - Quercus prinus / Parthenocissus quinquefolia Woodland (Fleming and Taverna 2006)
= Betula lenta - Quercus prinus / Parthenocissus quinquefolia Woodland (Fleming and Patterson 2009a)
> Betula lenta / Parthenocissus quinquefolia Association (Rawinski et al. 1996)
> Betula lenta / Ribes rotundifolium - Menziesia pilosa / Parthenocissus quinquefolia - Polypodium appalachianum Woodland (Fleming and Coulling 2001)
> Quercus rubra - Quercus montana - Betula lenta / Ilex montana / Menziesia pilosa Forest (Fleming and Moorhead 2000)
> Quercus rubra - Quercus montana - Betula lenta / Parthenocissus quinquefolia Forest (Fleming and Moorhead 2000)
> Talus Slope Community (Walz 1996)
= Betula lenta - Quercus prinus / Parthenocissus quinquefolia Woodland (Lea 2003)
= Betula lenta - Quercus prinus / Parthenocissus quinquefolia Woodland (Fleming and Taverna 2006)
= Betula lenta - Quercus prinus / Parthenocissus quinquefolia Woodland (Fleming and Patterson 2009a)
> Betula lenta / Parthenocissus quinquefolia Association (Rawinski et al. 1996)
> Betula lenta / Ribes rotundifolium - Menziesia pilosa / Parthenocissus quinquefolia - Polypodium appalachianum Woodland (Fleming and Coulling 2001)
> Quercus rubra - Quercus montana - Betula lenta / Ilex montana / Menziesia pilosa Forest (Fleming and Moorhead 2000)
> Quercus rubra - Quercus montana - Betula lenta / Parthenocissus quinquefolia Forest (Fleming and Moorhead 2000)
> Talus Slope Community (Walz 1996)
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