Print Report
CEGL006049 Abies fraseri / Viburnum lantanoides / Dryopteris campyloptera - Oxalis montana / Hylocomium splendens Forest
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Fraser Fir / Hobblebush / Mountain Woodfern - Mountain Woodsorrel / Splendid Feathermoss Forest
Colloquial Name: Fraser Fir Forest (Deciduous Shrub Type)
Hierarchy Level: Association
Type Concept: This community occurs as island-like stands in the southern Appalachian Mountains. It occurs on steep ridges and mesic, north-facing slopes above 1830 m (6000 feet) elevation, although it may extend lower on some sites. Occurrences of this community have shallow, rocky soils and are often steep and bouldery with seepage areas. This forest has at least 75% of the canopy coverage composed of Abies fraseri, occurring over a sparse to moderate shrub stratum dominated by deciduous species, a diverse herb stratum, and, typically, a well-developed bryophyte layer. The tree canopy has standing dead stems of Abies fraseri and extensive patches of Abies fraseri saplings in canopy gaps. Oxalis montana, Dryopteris campyloptera, and Athyrium filix-femina are often dominant in the herbaceous stratum. Other characteristic species include Vaccinium erythrocarpum, Sambucus racemosa var. racemosa, Rubus allegheniensis, Rubus idaeus ssp. strigosus, Oclemena acuminata, Eurybia chlorolepis, Clintonia borealis, Solidago glomerata, Rugelia nudicaulis, Ageratina altissima var. roanensis, Chelone lyonii, Circaea alpina ssp. alpina, Streptopus lanceolatus var. roseus, Viola macloskeyi ssp. pallens, Geum radiatum, Huperzia lucidula, Ptilium crista-castrensis, Rhytidiadelphus triquetrus, and Hylocomium splendens. This is a relatively broadly defined community element with much structural and compositional variation.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: No Data Available
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: This needle-leaved evergreen forest has greater than 75% canopy coverage by Abies fraseri, typically with many standing dead stems. Canopy trees are of small diameter (less than 20 cm) and short stature (less than 10 m tall), giving these forests a stunted appearance. Other species that may occur in the canopy or subcanopy with low coverage are Picea rubens, Sorbus americana, Betula alleghaniensis, Prunus pensylvanica, and Acer spicatum. There may be considerable variation in the density of shrub cover, but it is typically low (<20%) and dominated by deciduous species. Typical shrub species include Viburnum lantanoides, Vaccinium erythrocarpum, Sambucus racemosa var. racemosa (= Sambucus racemosa var. pubens), Menziesia pilosa, Rubus allegheniensis, and Rubus idaeus ssp. strigosus. Where shrubs are sparse, herb cover is usually dense, with Oxalis montana, Athyrium filix-femina ssp. asplenioides, and Dryopteris campyloptera often dominant. Other common herbs include Oclemena acuminata (= Aster acuminatus), Eurybia chlorolepis (= Aster chlorolepis), Clintonia borealis, Solidago glomerata, Rugelia nudicaulis, Ageratina altissima var. roanensis, Chelone lyonii, Circaea alpina ssp. alpina, Streptopus lanceolatus (= Streptopus roseus), Viola macloskeyi ssp. pallens, Geum radiatum, and Huperzia lucidula. Mosses, liverworts, and lichens grow densely on fallen logs, tree trunks, and the forest floor, giving the community a distinctive carpeted appearance. Characteristic bryophyte species include Hylocomium splendens, Ptilium crista-castrensis, Rhytidiadelphus triquetrus, and Hylocomiastrum umbratum.
Dynamics: This community is affected by debris avalanches, wind disturbance and lightning fire. Because of the shallow soils and extreme wind exposure, this forest is susceptible to large blowdowns. Logging and damage by the balsam woolly adelgid has greatly increased the effect of natural windfall. This community is a late-successional type, but it is subject to repeated disturbance. Prunus pensylvanica is a dominant species immediately following disturbance. In later successional stages, Betula alleghaniensis increases in dominance. An exotic insect, the balsam woolly adelgid (Adelges piceae), invaded the Southern Appalachians in the late 1950s and has drastically altered the last undisturbed remnants of this community. This exotic pest kills mature Abies fraseri within seven years of infestation. Abies fraseri is the only rare plant species associated with this vegetation in Virginia. In areas where mature Abies fraseri has been lost to woolly adelgid infestation, thickets of Rubus spp., Abies fraseri seedlings and saplings, Betula alleghaniensis, and Sorbus americana are dominant. Over time, Picea rubens, Betula alleghaniensis, Abies fraseri, Acer spicatum, and Sorbus americana increase in the tree layer, while Abies fraseri, Menziesia pilosa, Rubus idaeus ssp. strigosus, and Sambucus racemosa increase in the shrub layer (White et al. 1993). Succession is especially slow after severe disturbance such as logging and slash fires. The most severely disturbed sites are predominately Prunus pensylvanica and Rubus spp. and may remain in a non-forested stage of succession for 60 years or more.
Environmental Description: This community typically occurs on steep ridges and north-facing slopes above 1830 m (6000 feet) elevation, although it may extend lower on some sites. These forests occur on all topographic positions except the steepest rocky cliffs of the highest summits. Soils that support this community are classified as Inceptisols and are shallow, rocky, and often have a thick organic layer. Moisture regimes are mesic to wet, due to high rainfall, abundant cloud cover, fog deposition, and low temperatures.
Geographic Range: This community occurs as island-like stands on the highest areas (>1830 m [6000 feet]) in the southern Appalachian Mountains of eastern Tennessee, western North Carolina, and southwestern Virginia. It is extremely limited in distribution and is restricted to the following mountain areas: Great Smoky Mountains, Black Mountains, Balsam Mountain, Plott Balsam Mountain, Grandfather Mountain, and Mount Rogers (Ramseur 1960).
Nations: US
States/Provinces: NC, TN, VA
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.684253
Confidence Level: High
Confidence Level Comments: No Data Available
Grank: G1
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.7 Sugar Maple - Yellow Birch - Eastern Hemlock Forest Macrogroup | M014 | 1.B.2.Na.7 |
Group | 1.B.2.Na.7.e Red Spruce - Fraser Fir - Yellow Birch Forest Group | G632 | 1.B.2.Na.7.e |
Alliance | A0136 Red Spruce - Fraser Fir Forest Alliance | A0136 | 1.B.2.Na.7.e |
Association | CEGL006049 Fraser Fir / Hobblebush / Mountain Woodfern - Mountain Woodsorrel / Splendid Feathermoss Forest | CEGL006049 | 1.B.2.Na.7.e |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: = Abies fraseri / Dryopteris campyloptera - Oxalis montana Forest (Fleming and Patterson 2009a)
= Abies fraseri / Dryopteris campyloptera - Oxalis montana Forest (Fleming and Coulling 2001)
? Fraser Fir (6) (USFS 1988)
< IA4b. Fraser Fir Forest (Allard 1990)
? Oligotrophic Forest (Rawinski 1992)
< Red Spruce - Fraser Fir: 34 (Eyre 1980)
= Abies fraseri / Dryopteris campyloptera - Oxalis montana Forest (Fleming and Coulling 2001)
? Fraser Fir (6) (USFS 1988)
< IA4b. Fraser Fir Forest (Allard 1990)
? Oligotrophic Forest (Rawinski 1992)
< Red Spruce - Fraser Fir: 34 (Eyre 1980)
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