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records 5041 through 5050 of 38961

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Add/Drop Name Reference Plots Description
Comm #5041
 
CEGL005193
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accession code: VB.CC.6518.CEGL005193 NOT CURRENTLY ACCEPTED
EcoArt 2002  0  
Comm #5042
 
CEGL005196
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accession code: VB.CC.6519.CEGL005196 NOT CURRENTLY ACCEPTED
EcoArt 2002  0  
Comm #5043
 
CEGL005197
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accession code: VB.CC.6520.CEGL005197 NOT CURRENTLY ACCEPTED
EcoArt 2002  0  
Comm #5044
 
CEGL008626
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accession code: VB.CC.7927.CEGL008626 NOT CURRENTLY ACCEPTED
EcoArt 2002  0  
Comm #5045
 
CEGL007886
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accession code: VB.CC.7472.CEGL007886 NOT CURRENTLY ACCEPTED
EcoArt 2002  0  
Comm #5046
 
A.293
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accession code: VB.CC.1900.A293 NOT CURRENTLY ACCEPTED
EcoArt 2002  0 This floodplain forest alliance is found in the midwestern United States. The tree canopy may be closed to moderately open. The dominant tree species include ~Quercus macrocarpa$ and ~Quercus bicolor$. ~Carya laciniosa$ is often found in stands of this alliance, along with species such as ~Fraxinus pennsylvanica, Quercus shumardii, Carya illinoinensis, Populus deltoides$, and ~Ulmus americana$. Understory species include ~Boehmeria cylindrica, Carex$ spp., ~Cinna$ spp., ~Leersia$ spp., ~Toxicodendron radicans$, and ~Uvularia sessilifolia$. Stands of this alliance are found on slackwater deposits with moderately well-drained to poorly drained soils. In Kentucky, the dominant tree species are indicators of less acidic soils with a higher base-status. 
Comm #5047
 
Conocarpus erectus - Metopium toxiferum - Acoelorraphe wrightii / Chrysobalanus icaco Forest
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accession code: VB.CC.20946.CONOCARPUSERECT
Southeastern Ecology Working Gro...  0 Wetland hammock islands surrounded by wet prairie, dominated by a 4- to 15-m tall canopy of Conocarpus erectus, Metopium toxiferum, Acoelorraphe wrightii, and Sabal palmetto. Subcanopy and shrub species include Chrysobalanus icaco, Sabal palmetto, and Myrsine floridana. Epiphytes are abundant, and include Tillandsia spp. and Encyclia tampensis. 
Comm #5048
 
Pinus aristata / Vaccinium myrtillus Woodland
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accession code: VB.CC.18886.PINUSARISTATAVA
Western Ecology Working Group of...  0  
Comm #5049
 
Pinus echinata / Schizachyrium scoparium - Solidago ulmifolia - Monarda russeliana - Echinacea pallida Woodland
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accession code: VB.CC.27990.PINUSECHINATASC
Southeastern Ecology Working Gro...  0 This upland subxeric woodland community was a matrix forest type in the Ouachita Mountains and, historically, north into parts of the Ozarks. This community occurs on a variety of sandstone and mixed sandstone/shale-derived substrates in the northern and western Ouachita Mountains and on chert/novaculite-derived substrates in the central Ouachitas. On the sharper ridges of the central Ouachitas (novaculite uplift), these woodlands are reduced in extent and bounded by submesic pine - oak forest on lower slopes and xeric oak woodlands on the ridgelines. This is a fire-maintained community where woody succession and canopy closure can be rapid with fire suppression. Virtually extirpated, these woodlands have been restored in part by thinning and prescribed burning. This woodland community has an open canopy dominated by Pinus echinata and a dense, diverse herbaceous layer. Scattered oaks (Quercus alba, Quercus stellata, Quercus velutina, Quercus marilandica) may appear in the canopy or subcanopy. These are expansive, open woodlands on gentle slopes, saddles and flatter ridgelines in eastern Oklahoma, western Arkansas, and southern Missouri. The dense herbaceous stratum is dominated by both graminoid and forb species. Dominant graminoids include Schizachyrium scoparium, Danthonia spicata, Chasmanthium sessiliflorum, Scleria triglomerata, and Dichanthelium spp. Other graminoid species include Andropogon gyrans, Andropogon gerardii, Andropogon virginicus, Chasmanthium latifolium, Gymnopogon ambiguus, Muhlenbergia schreberi, Panicum virgatum, Paspalum sp., Sorghastrum nutans, Sporobolus compositus (= Sporobolus asper), and Tridens flavus. Dominant forb species include Solidago ulmifolia, Clitoria mariana, Lespedeza repens, Antennaria plantaginifolia, Symphyotrichum anomalum (= Aster anomalus), Symphyotrichum patens (= Aster patens), Erechtites hieraciifolia, Helianthus hirsutus, and Monarda russeliana. Many other forb species are known from these woodlands. Some of the more typical ones include Acalypha virginica, Amphicarpaea bracteata, Baptisia nuttalliana, Chamaecrista fasciculata (= Cassia fasciculata), Coreopsis tinctoria, Conyza canadensis, Cunila origanoides, Dalea candida, Desmodium ciliare, Echinacea pallida, Echinacea purpurea, Euphorbia corollata, Pseudognaphalium obtusifolium (= Gnaphalium obtusifolium), Hieracium gronovii, Lespedeza spp., Liatris squarrosa, Phlox spp., Polygala alba, Pycnanthemum tenuifolium, Rudbeckia hirta, Solidago hispida, Solidago odora, Solidago radula, Stylosanthes biflora, and Tephrosia virginiana. Shrubs are sparse, especially in more frequently burned locations. Shrub density is related to fire frequency, and many shrubs are coppices, sprouting from stumps. Some common shrubs and vines include Baptisia bracteata var. leucophaea, Carya alba, Carya texana, Ceanothus spp., Crataegus crus-galli, Mimosa microphylla, Prunus serotina, Quercus stellata, Rhus copallinum, Rhus glabra, Rubus spp., Toxicodendron radicans, Ulmus alata, Vaccinium arboreum, Vaccinium pallidum, Viburnum rufidulum, and Vitis rotundifolia, but many others can occur. The type location is in Scott County, Arkansas. 
Comm #5050
 
A.1010
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accession code: VB.CC.782.A1010 NOT CURRENTLY ACCEPTED
EcoArt 2002  0  

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