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CEGL007543 Liriodendron tulipifera - Betula lenta - Tsuga canadensis / Rhododendron maximum Forest
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Tuliptree - Sweet Birch - Eastern Hemlock / Great Laurel Forest
Colloquial Name: Southern Appalachian Acidic Cove Forest (Typic Type)
Hierarchy Level: Association
Type Concept: This association includes hemlock-hardwood forests and acidic cove forests of lower to intermediate elevations in the Southern Blue Ridge, upper Piedmont, Cumberlands, and adjacent areas, ranging from southwestern Virginia and southern West Virginia, south and west to northwestern Georgia. The concept for this association is intended to be broad and cover both mixed stands of evergreen and deciduous hardwoods as well as stands dominated exclusively by deciduous trees in mesic, acidic environments. These communities occur at low to middle elevations (200-1060 m [650-3500 feet]), generally in coves, gorges or sheltered slopes, over acidic soils. The canopy is usually dominated by Liriodendron tulipifera or Betula lenta mixed with Tsuga canadensis, but substantial portions may be comprised mainly of Tsuga canadensis and the occasional Acer rubrum, while other sites may have little or no Tsuga in the canopy. Other deciduous species more typical of "rich" coves may occur as scattered individuals, including Tilia americana var. heterophylla, Acer saccharum, Fraxinus americana, and Fagus grandifolia. Other canopy/subcanopy species often include Quercus alba, Quercus rubra, Magnolia fraseri, and Pinus strobus. Rhododendron maximum is usually dominant in the shrub stratum, often forming impenetrable thickets. South of Virginia, woody associates may also include Ilex opaca var. opaca, Calycanthus floridus, Halesia tetraptera var. tetraptera, and Leucothoe fontanesiana. Herbaceous cover is sparse but can be diverse and is composed of acid-loving species. Typical herbs include Polystichum acrostichoides, Dryopteris intermedia, Dennstaedtia punctilobula, Goodyera pubescens, Mitchella repens, Thelypteris noveboracensis, Galax urceolata, Viola rotundifolia, and Tiarella cordifolia.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: Deciduous trees more typical of "rich" coves, such as Aesculus flava, Tilia americana var. heterophylla, and Acer saccharum, are present in this forest only as minor components, if at all. Likewise, rich-site herbs, such as Actaea racemosa, Caulophyllum thalictroides, Actaea pachypoda, and Adiantum pedatum, are absent or nearly so. This forest is distinguished from "northern hardwood forests" by the lack of or near absence of Fagus grandifolia, Betula alleghaniensis, Aesculus flava, and the presence of low-elevation species, such as Betula lenta and Liriodendron tulipifera, and generally by a more depauperate herb layer. There is much variability in species composition in the 43 plots classified as this association from the Appalachian Trail region (Fleming and Patterson 2009a), but constancy of the nominal species was quite high (>84%). The most constant species (>64%), in order of descending constancy, are Rhododendron maximum, Tsuga canadensis, Betula lenta, Acer rubrum, Liriodendron tulipifera, Quercus rubra, Mitchella repens, Polystichum acrostichoides, and Hamamelis virginiana. Species richness in 400-m2 plots ranges from 11 to 72 species per plot. This variable richness is probably influenced by somewhat variable soil fertility and the variation in cover/density of evergreen Rhododendron shrub colonies. An interesting example from the Piedmont/Blue Ridge transition of Georgia (Cedar Creek Canyon, Chattahoochee National Forest) has high coverage of Rhododendron minus and other foothills/Piedmont species such as Liquidambar styraciflua and Aesculus sylvatica.
In the 900- to 1060-m (3000-3500 feet) elevational range, the type becomes transitional to ~Betula alleghaniensis - (Tsuga canadensis) / Rhododendron maximum / (Leucothoe fontanesiana) Forest (CEGL007861)$$, which lacks lower-elevation species such as Liriodendron tulipifera and Galax urceolata, and contains many species characteristic of higher elevations and northern latitudes.
Similar vegetation has been observed in coves of the Cumberland Mountains of southwestern Virginia (e.g., Clinch Ranger District: Dark Hollow, Roaring Branch, Pick Breeches and Flannery Ridges,) but comprehensive data are needed to determine whether these stands are part of this forest types or transitional to ~Tsuga canadensis - (Fagus grandifolia, Tilia americana var. heterophylla) / Magnolia tripetala Forest (CEGL008407)$$. The latter unit apparently has an extensive distribution in the Cumberland Plateau of Kentucky and Tennessee, the Southern Ridge and Valley of Tennessee, and the Central Appalachians of West Virginia and southwestern Pennsylvania.
In West Virginia, 45 plots, mostly from New River Gorge National River and Gauley River National Recreation Area, are classified to this association. Outliers at lower elevations on the western flanks of the Allegheny Mountains are also classified here (with less confidence) based on high cover by Rhododendron maximum, which is uncommon in related ~Tsuga canadensis - Fagus grandifolia - Acer saccharum / (Hamamelis virginiana, Kalmia latifolia) Forest (CEGL005043)$$ typical of the Western Allegheny Plateau, and lack of high-elevation associates found in ~Tsuga canadensis - Betula alleghaniensis - Prunus serotina / Rhododendron maximum Forest (CEGL006206)$$ of high elevations in the Allegheny Mountains. West Virginia examples of this association (CEGL007543) include stands with mixed hemlock-deciduous canopies and stands with deciduous canopies, often with hemlock in the lower strata. Fagus grandifolia is not uncommon in WV stands.
In the 900- to 1060-m (3000-3500 feet) elevational range, the type becomes transitional to ~Betula alleghaniensis - (Tsuga canadensis) / Rhododendron maximum / (Leucothoe fontanesiana) Forest (CEGL007861)$$, which lacks lower-elevation species such as Liriodendron tulipifera and Galax urceolata, and contains many species characteristic of higher elevations and northern latitudes.
Similar vegetation has been observed in coves of the Cumberland Mountains of southwestern Virginia (e.g., Clinch Ranger District: Dark Hollow, Roaring Branch, Pick Breeches and Flannery Ridges,) but comprehensive data are needed to determine whether these stands are part of this forest types or transitional to ~Tsuga canadensis - (Fagus grandifolia, Tilia americana var. heterophylla) / Magnolia tripetala Forest (CEGL008407)$$. The latter unit apparently has an extensive distribution in the Cumberland Plateau of Kentucky and Tennessee, the Southern Ridge and Valley of Tennessee, and the Central Appalachians of West Virginia and southwestern Pennsylvania.
In West Virginia, 45 plots, mostly from New River Gorge National River and Gauley River National Recreation Area, are classified to this association. Outliers at lower elevations on the western flanks of the Allegheny Mountains are also classified here (with less confidence) based on high cover by Rhododendron maximum, which is uncommon in related ~Tsuga canadensis - Fagus grandifolia - Acer saccharum / (Hamamelis virginiana, Kalmia latifolia) Forest (CEGL005043)$$ typical of the Western Allegheny Plateau, and lack of high-elevation associates found in ~Tsuga canadensis - Betula alleghaniensis - Prunus serotina / Rhododendron maximum Forest (CEGL006206)$$ of high elevations in the Allegheny Mountains. West Virginia examples of this association (CEGL007543) include stands with mixed hemlock-deciduous canopies and stands with deciduous canopies, often with hemlock in the lower strata. Fagus grandifolia is not uncommon in WV stands.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: This association encompasses hemlock-hardwood forests and acidic cove forests with canopies dominated by mixtures of Tsuga canadensis, Liriodendron tulipifera, Betula lenta, Quercus rubra, and Acer rubrum. The concept for this association is intended to be broad and cover both mixed stands of evergreen and deciduous hardwoods as well as stands dominated exclusively by deciduous trees. Presumably because of past logging, Tsuga canadensis is absent or confined to the understory in some stands, which have mixed canopies of Liriodendron tulipifera, Betula lenta, Acer rubrum, Magnolia acuminata, Quercus rubra, and/or Nyssa sylvatica. Other deciduous species more typical of fertile coves, including Tilia americana var. heterophylla, Acer saccharum, Fraxinus americana, and Fagus grandifolia, may occur as scattered individuals. Minor overstory and understory species include Quercus alba, Quercus montana (= Quercus prinus), Magnolia fraseri, Magnolia tripetala, Oxydendrum arboreum, Prunus serotina, and Pinus strobus. Rhododendron maximum is scattered to dominant in the shrub stratum often forming nearly impenetrable colonies. Kalmia latifolia is also a typical, but less abundant, shrub. In the southern portion of this type''s range, Calycanthus floridus, Halesia tetraptera, and Leucothoe fontanesiana may be common; these are lacking in Virginia and West Virginia occurrences, where Hamamelis virginiana and Acer pensylvanicum may be minor associates. Herbaceous cover is sparse but can be diverse and is composed of acid-loving species. Frequent low-cover species of this layer include Arisaema triphyllum, Chimaphila maculata, Dioscorea quaternata, Dryopteris intermedia, Dryopteris marginalis, Eurybia divaricata (= Aster divaricatus), Galax urceolata, Gaultheria procumbens, Goodyera pubescens, Hexastylis spp., Luzula echinata, Monotropa uniflora, Medeola virginiana, Mitchella repens, Polypodium virginianum, Polystichum acrostichoides, Thelypteris noveboracensis, Tiarella cordifolia, Viola blanda, and Waldsteinia fragarioides. The spectacular sedge Cymophyllus fraserianus is often associated with this forest. Bryophytes identified in West Virginia plots include Leucobryum glaucum, Thuidium delicatulum, Hypnum imponens, Bazzania trilobata, Dicranum scoparium, Dicranum fulvum, Brotherella recurvans, and Polytrichum pallidisetum.
Dynamics: In Virginia, the hemlock component of many stands has been devastated by outbreaks of hemlock woolly adelgid, resulting in extensive damage and mortality to the mature overstory trees.
Environmental Description: This association is typically found at lower to intermediate elevations (200-1060 m [650-3500 feet]) in the Southern Appalachians and adjacent foothills as well as nearby plateau/gorge systems in West Virginia. Habitats are mesic and located on gentle to steep, lower slopes along creeks in ravines, in coves or gorges, and in concave positions on protected slopes with cool aspects and acidic soils. In situations where midslopes are in protected north-facing positions, this community can range very high up straight or even convex slopes. The type often occurs in linear patches along stream bottoms and in steep ravines in complexes with rich cove communities. Although frequently associated with streams, it is not a wetland. Soils collected from plots are extremely acidic (mean pH = 4.0) and infertile, with high iron and aluminum levels and very low total base saturation. Where present, they are usually well-drained sandy loam, silt loam, loam, clay loam, or clay. The degree of soil development is highly variable. Some stands have relatively deep colluvial or residual soils, while others have a substrate of deeply piled boulders with sparse interstitial, organic soils.
Geographic Range: This community occurs in the Southern Blue Ridge and Cumberlands and peripherally in the upper Piedmont and southern Central Appalachians, ranging from southwestern Virginia and southeastern West Virginia south and west to northwestern Georgia.
Nations: US
States/Provinces: GA, NC, SC, TN, VA, WV
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.683191
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: G5
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.3 Appalachian-Interior-Northeastern Mesic Forest Macrogroup | M883 | 1.B.2.Na.3 |
Group | 1.B.2.Na.3.a American Beech - Tuliptree - Yellow Buckeye Forest Group | G020 | 1.B.2.Na.3.a |
Alliance | A3304 Eastern Hemlock - Tuliptree Forest Alliance | A3304 | 1.B.2.Na.3.a |
Association | CEGL007543 Tuliptree - Sweet Birch - Eastern Hemlock / Great Laurel Forest | CEGL007543 | 1.B.2.Na.3.a |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: > Betula lenta - Liriodendron tulipifera - Acer rubrum / Rhododendron maximum Forest (Vanderhorst et al. 2007)
> Liriodendron tulipifera - Betula lenta - Tsuga canadensis / Rhododendron maximum Forest (Vanderhorst et al. 2007)
= Liriodendron tulipifera - Betula lenta - Tsuga canadensis / Rhododendron maximum Forest (Fleming and Coulling 2001)
= Liriodendron tulipifera - Quercus montana - Tsuga canadensis / Rhododendron maximum / Galax urceolata Forest (Fleming and Moorhead 2000)
= Pinus strobus - Tsuga canadensis - Liriodendron tulipifera Forest (Patterson 1994)
= Tsuga canadensis - Betula lenta / Rhododendron maximum forest (Vanderhorst 2001b)
= Tsuga canadensis - Liriodendron tulipifera - Betula lenta / Rhododendron maximum Forest [Hemlock - Hardwood / Great Laurel Acidic Cove Forest] (Vanderhorst 2017c)
< Cove Forest (Patterson et al. 1994)
< IA5b. Southern Appalachian Hemlock Cove Forest (Allard 1990)
? Mixed Mesophytic Coves (Gettman 1974)
= Sweet Birch - Hemlock Type (Schmalzer and DeSelm 1982)
? Type 5 (Newell and Peet 1995)
< Yellow-Poplar - Eastern Hemlock: 58 (Eyre 1980)
> Liriodendron tulipifera - Betula lenta - Tsuga canadensis / Rhododendron maximum Forest (Vanderhorst et al. 2007)
= Liriodendron tulipifera - Betula lenta - Tsuga canadensis / Rhododendron maximum Forest (Fleming and Coulling 2001)
= Liriodendron tulipifera - Quercus montana - Tsuga canadensis / Rhododendron maximum / Galax urceolata Forest (Fleming and Moorhead 2000)
= Pinus strobus - Tsuga canadensis - Liriodendron tulipifera Forest (Patterson 1994)
= Tsuga canadensis - Betula lenta / Rhododendron maximum forest (Vanderhorst 2001b)
= Tsuga canadensis - Liriodendron tulipifera - Betula lenta / Rhododendron maximum Forest [Hemlock - Hardwood / Great Laurel Acidic Cove Forest] (Vanderhorst 2017c)
< Cove Forest (Patterson et al. 1994)
< IA5b. Southern Appalachian Hemlock Cove Forest (Allard 1990)
? Mixed Mesophytic Coves (Gettman 1974)
= Sweet Birch - Hemlock Type (Schmalzer and DeSelm 1982)
? Type 5 (Newell and Peet 1995)
< Yellow-Poplar - Eastern Hemlock: 58 (Eyre 1980)
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