Clematis addisonii

Britt.

Addison's Leatherflower

G1Critically Imperiled (G1G2) Found in 2 roadless areas NatureServe Explorer →
G1Critically ImperiledGlobal Rank
Very high - highThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.160003
Element CodePDRAN08010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single state or province
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderRanunculales
FamilyRanunculaceae
GenusClematis
Other Common Names
Addison's leather flower (EN)
Concept Reference
Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2021-03-15
Change Date2021-03-15
Edition Date2020-03-25
Edition AuthorsNancy E. Van Alstine., rev. Ludwig/Maybury (1996), rev. Nordman, C. (2012), rev. L. Oliver (2020)
Threat ImpactVery high - high
Range Extent250-1000 square km (about 100-400 square miles)
Number of Occurrences6 - 20
Rank Reasons
Clematis addisonii is endemic to western Virginia, U.S.A., where it is known now from 3 counties and may be restricted to areas underlain by Elbrook Formation dolomite. Eleven populations are known extant in the past 2 decades (1992 - 2011), and many of these are threatened by development, invasive species and habitat fragmentation. There are eight occurrences that are historical and last seen over 40 years ago.
Range Extent Comments
Clematis addisonii is known only from the counties of Montgomery, Botetourt, and Roanoke in the Ridge and Valley physiographic province of western Virginia in the United States. There is only one extant occurrence in Roanoke County. It was historically known from Rockbridge County. If historical occurrences are excluded, range extent is 699 sq km.
Occurrences Comments
There are eleven occurrences documented in the past two decades (1992 - 2011).
Threat Impact Comments
This species is threatened by development pressures, road widening projects, grazing, deer browsing, canopy closure (Copenheaver et al. 2006), drought and quarry operations, invasive plants, land-use conversion, and habitat fragmentation (J. Townsend, pers. comm., 2020, Southern Appalachian Species Viability Project 2002). A proposed highway connecting Blacksburg with Roanoke does not directly threaten the known populations, but additional field survey work would likely locate populations that are in the corridor. Urban expansion in the Blacksburg and Christiansburg Area may become increasingly severe in the future but is currently a low level threat (J. Townsend, pers. comm., 2021). Canopy closure of woodlands succeeding into forests is a threat, as the species thrives at sites with a small tree canopy and not a dense canopy forest.
Ecology & Habitat

Habitat

Thin soils, either on open outcrops or under light to moderate shade in mixed hardwood-juniper forests. All known sites are underlain by Elbrook Formation dolomite.
Terrestrial Habitats
Forest/WoodlandForest - Mixed
Other Nations (1)
United StatesN1
ProvinceRankNative
VirginiaS1Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentSmall (1-10%)Extreme or 71-100% pop. declineHigh (continuing)
1.1 - Housing & urban areasSmall (1-10%)Extreme or 71-100% pop. declineHigh (continuing)
3 - Energy production & miningSmall (1-10%)Serious or 31-70% pop. declineModerate (short-term)
3.2 - Mining & quarryingSmall (1-10%)Serious or 31-70% pop. declineModerate (short-term)
4 - Transportation & service corridorsRestricted (11-30%)Serious or 31-70% pop. declineModerate (short-term)
4.1 - Roads & railroadsRestricted (11-30%)Serious or 31-70% pop. declineModerate (short-term)
7 - Natural system modificationsRestricted (11-30%)Serious or 31-70% pop. declineHigh (continuing)
7.3 - Other ecosystem modificationsRestricted (11-30%)Serious or 31-70% pop. declineHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesLarge - restrictedSerious or 31-70% pop. declineHigh (continuing)
8.2 - Problematic native species/diseasesLarge - restrictedSerious or 31-70% pop. declineHigh (continuing)
8.2.1 - Unspecified speciesLarge - restrictedSerious or 31-70% pop. declineHigh (continuing)

Plant Characteristics
DurationPERENNIAL
Economic Value (Genus)No
Roadless Areas (2)
Virginia (2)
AreaForestAcres
Brush Mountain EastJefferson National Forest4,916
Price MountainJefferson National Forest9,119
References (6)
  1. Copenheaver, C.A., J.L. Dorr, W.T. Flatley, D.W. Garst. 2006. Temporal variability in the spatial distribution of an Eastern Red-cedar-Chinquapin Oak woodland in Virginia. Natural Areas Journal 26:274-279.
  2. Gleason, H.A. 1952. The new Britton and Brown illustrated flora of the northeastern United States and adjacent Canada. 3 volumes. Hafner Press, New York. 1732 pp.
  3. Gleason, H.A., and A. Cronquist. 1991. Manual of vascular plants of northeastern United States and adjacent Canada. New York Botanical Garden, Bronx, New York. 910 pp.
  4. Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
  5. Kral, R. 1983c. A report on some rare, threatened, or endangered forest-related vascular plants of the South. U.S. Dept. of Agriculture Forest Service Technical Publication R8-TP2, Athens, GA. 1305 pp.
  6. Southern Appalachian Species Viability Project. 2002. A partnership between the U.S. Forest Service-Region 8, Natural Heritage Programs in the Southeast, NatureServe, and independent scientists to develop and review data on 1300+ regionally and locally rare species in the Southern Appalachian and Alabama region. Database (Access 97) provided to the U.S. Forest Service by NatureServe, Durham, North Carolina.