Spiraea virginiana

Britt.

Virginia Spiraea

G2Imperiled (G2?) Found in 24 roadless areas NatureServe Explorer →
G2ImperiledGlobal Rank
Very high - highThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.135631
Element CodePDROS1Q0E0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single nation
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderRosales
FamilyRosaceae
GenusSpiraea
Other Common Names
Virginia Meadowsweet (EN) Virginia meadowsweet (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.
Taxonomic Comments
The two varieties sometimes recognized (var. serrulata and var. virginiana) are not maintained by Kartesz (1994 and 1999), nor are they recognized by any Heritage Program in the species' range, or by the U.S. Fish and Wildlife Service. LEM 7Jun95
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2021-07-28
Change Date2021-07-28
Edition Date2021-07-28
Edition AuthorsWalton, D., D. White and K. Crowley; K. Maybury; S. Norris., rev. A. Tomaino (2004), rev. L. Oliver (2017), rev. Treher (2019, 2021)
Threat ImpactVery high - high
Range Extent20,000-200,000 square km (about 8000-80,000 square miles)
Number of Occurrences21 - 80
Rank Reasons
Spiraea virginiana is a shrub that is endemic to the southern Appalachians. Although widely occurring in several Appalachian states, many of the occurrences are of poor quality and have low viability. This species exists in a pattern of a few, large clonal lineages. Little population expansion has been reported, although several occurrences are considered protected (mostly federal and state parks). It is restricted to specific riparian habitats with periodic disturbance. Many of the extant populations consist of less than 50 clumps. Range-wide, fewer than 30 different genotypes are thought to exist. It is threatened by alterations in flooding regimes within watersheds, and clearing or disturbance of streambank vegetation. Overall this species is threatened by its limited range, small number of populations, high habitat fidelity, and low genetic variation.
Range Extent Comments
Spiraea virginiana is a broad southern Appalachian endemic with isolated populations in Georgia, Kentucky, North Carolina, Ohio, Tennessee, Virginia, and West Virginia in the eastern United States. Historically, it occurred in Pennsylvania and Ohio, south to Alabama, Georgia, and Tennessee. However, it is presumably extirpated from Alabama and Pennsylvania. It occurs on streams that drain into the Ohio River and primarily within the Appalachian (Cumberland) Plateau and Blue Ridge physiographic regions, with at least one outlier in the Bluegrass Region of Kentucky. Range extent, including all historical and extirpated occurrences, is 141,600 sq km. Range extent, excluding all historical and extirpated occurrences, is 130,263 sq km.
Occurrences Comments
There are an estimated 78 extant occurrences in a total of seven states (Georgia-3, Kentucky-16 extant and 4 failed to find during last survey, North Carolina-18 and 2 failed to find during last survey, Ohio-7, Tennessee-28 extant and 3 failed to find during last survey, Virginia-5, West Virginia-13). There are an additional 2 extirpated and 4 historical populations. The species is outplanted at one additional site in Georgia.
Threat Impact Comments
Spiraea virginiana is especially vulnerable to land-use conversion and habitat fragmentation. Populations of this riparian species are isolated, consisting of sterile clones, and damming of rivers has increased this isolation over time. Lack of disturbance (succession) is also a factor, as altered river flows may affect scouring regime which if lacking allows for woody plant encroachment, or if increased interrupts establishment (Southern Appalachian Species Viability Project 2002, Horton et al. 2015). Many sites are threatened by changes in hydrology by impoundment and by impact from recreational use, hydroelectric facilities, and run-off debris (Kadis 2002). Small populations may be threatened by severe flooding that results in wash-outs of the streambank. Exotic species (Rosa multiflora, Coronilla varia, Elaeagnus umbellata, Festuca rubra, Alliaria officinalis, Rumex obtusifolius, Polygonum cuspidatum, Pueraria lobata, Lonicera japonica, Spiraea japonica, Ligustrum sinense, Miscanthus sinensis, Arthraxon hispidus, and Phalaris arundinacea) that compete with Spiraea virginiana are also a threat (Horton et al. 2015). Roadside maintenance, beaver damage, deer browse, all-terrain vehicle use and upslope timbering are also threats. One site in West Virginia is near a powerline right-of-way and may be threatened by herbicide use. Beaver herbivory can be a threat, however, it is also known to promote clonal growth and it may help disperse the species (Rossell et al. 2013).
Ecology & Habitat

Description

A clonal shrub often occurring in dense clumps. Stems are sparsely branched and are upright up to 1.2 m or arching with some stems touching the ground. The leaves are alternate, simple, and have variable serration. The cream-colored flowers are in showy corymbs.

Diagnostic Characteristics

Spiraea virginiana is distinguished from most other Spiraea by its creamy white flowers in corymbs, and its leaves which have an acute apex (Weakley 2004). The exotic Spiraea japonica, which also occurs along streams, has pink flowers and leaves with long-acuminate tips (Patrick et al. 1995). Spiraea virginiana closely resembles Spiraea betulifolia var. corymbosa (Ogle 1991). Spiraea virginiana is distinguished from Spiraea betulifolia var. corymbosa by its leaves which are more than twice as long as wide (as opposed to less than twice as long as wide in S. b. var. corymbosa) and cuneate base (as opposed to rounded base) (Weakley 2004). For a technical description see Gleason and Cronquist (1991) and Weakley (2004).

Habitat

This species occurs on periodically flood-scoured banks of high-gradient mountain streams, meander scrolls, point bars, natural levees, and braided features of lower stream reaches, and occasionally near disturbed rights-of-way (Ogle 1992). Plants are often found on geologically active areas with erosion, deposition, and slumping, along rivers with dynamic flooding regimes, sandbars, scoured river shore and flatrock habitat with crevices. These areas also are associated with cobbles, boulders, and massive rock outcrops with sandy or clay soils and can be periodically xeric. Plants are often seen in silt, mud, and sand.

Ecology

In Georgia, occurrences of Spiraea virginiana are in cracks in shelving sandstone bedrock along fast flowing creeks. Associated species include Alnus, Boykinia, Cephalanthus, Cornus amomum, Oxypolis rigidior, Viburnum cassinoides, and Xanthorhiza simplicissima.

In Ohio, occurrences of Spiraea virginiana are along slow moving streams with sandstone bedrock that are scoured during flooding, gravel bars with riparian debris. Associated with Acer saccharum, Aconitum uncinatum, Alnus serrulata, Amphicarpaea bracteata, Betula nigra, Boehmeria cylindrica, Campsis radicans, Carpinus carolinia, Cephalanthus occidentalis, Fimbristylis autumnalis, Fraxinus pennsylvanica, Glyceria striata, Onoclea sensibilis, Osmunda regalis, Pilea pumila, Polygonum amphibium, Platanus occidentalis, Saururus cernuus, Tilia americana, Toxicodendron radicans, Ulmus americana, Ulmus rubra, and Vitis riparia.

In North Carolina, Spiraea virginiana occurs along rocky bars at river edges. It grows between boulders and in fine alluvial sand and other alluvial deposits. These sites are seasonally saturated. Associated plants include Alnus serrulata, Clematis viorna, Cornus amomum, Impatiens capensis, Parthenocissus, Physocarpus opulifolius, Platanus, Rubus, Salix, Sambucus canadensis, Saponaria, Smilax, Solidago, Toxicodendron radicans, and Verbesina alternifolia.

In Tennessee, this species occurs along creek edges with margins of exposed rock and piled detritus, bars of gravel, rubble and/or boulders and including dolomitic limestone. It occurs in alluvial silt collected within cracks in the bedrock. These sites experience a regime of periodic flooding. Elevations range from 850-1420 ft. Associated species include Acer pensylvanicum, Alnus, Arisaema dracontium, Arundinaria gigantea, Conradina verticillata, Dirca palustris, Ilex verticillata, Juniperus virginiana, Liriodendron tulipifera, Orontium aquaticum, Osmunda regalis, O. cinnamomea, Phlox amoena, Salix, Senecio aureus, Silene virginica, Spiraea japonica, Toxicodendron radicans, Trautvetteria, Tsuga, Ulmus, and Viburnum dentatum.

In Virginia, occurrences of Spiraea virginiana are along flood scour zones in crevices of sandstone cobbles, boulders, and massive rock outcrop, and quartzite/feldspar boulders. Soils are sandy, silty, or clay. The elevation range is 1000-2400 ft. Associated plants include Alnus serrulata, Amphicarpaea bracteata, Betula lenta, Betula nigra, Campsis radicans, Carpinus, Cephalanthus, Cornus amomum, Dirca, Equisetum hyemale, Fraxinus, Ilex verticillata, Lobelia cardinalis, Osmunda regalis, Physocarpus, Platanus occidentalis, Polygonum punctatum, Spiraea japonica, S. tomentosa, Toxicodendron radicans, Tradescantia ohiensis, Tsuga, Verbesina alternifolia, and Xanthorhiza.

In West Virginia, occurrences are among large boulders, flatrock, and flood debris along scoured stream-sides. Soils are silt and sand. The elevation ranges from 1000-1800 ft. Associated species are Acer rubrum, Alnus serrulata, Betula nigra, Cephalanthus occidentalis, Cornus amomum, Dirca, Ilex verticillata, Osmunda regalis, Parthenocissus, Physocarpus, Platanus, Spiraea japonica, Toxicodendron radicans, Tradescantia ohiensis, Tsuga, and Xanthorhiza.

Reproduction

Although this element may flower profusely, it is clonal and almost exclusively reproduces vegetatively. Sexual reproduction will occur when genets are placed in close proximity but is rare in the native habitat (D.W. Ogle, pers. comm., 1996). Dispersal of seeds is by wind or water and requires a flooding regime (Brzyski and Cullen 2011). While clonal reproduction appears to be the primary mode, there is evidence that sexual reproduction takes place in some populations (Brzyski and Cullen 2001).
Terrestrial Habitats
Bare rock/talus/scree
Palustrine Habitats
HERBACEOUS WETLANDSCRUB-SHRUB WETLANDRiparian
Other Nations (1)
United StatesN2
ProvinceRankNative
VirginiaS1Yes
KentuckyS1Yes
PennsylvaniaSHYes
OhioS1Yes
TennesseeS2Yes
AlabamaSNRYes
GeorgiaS1Yes
North CarolinaS2Yes
West VirginiaS1Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentRestricted - smallSerious or 31-70% pop. declineHigh (continuing)
1.1 - Housing & urban areasRestricted - smallSerious or 31-70% pop. declineHigh (continuing)
4 - Transportation & service corridorsRestricted (11-30%)Moderate - slightHigh - moderate
4.1 - Roads & railroadsRestricted (11-30%)Slight or 1-10% pop. declineHigh - moderate
4.2 - Utility & service linesRestricted (11-30%)Slight or 1-10% pop. declineHigh - moderate
5 - Biological resource useLarge - restrictedModerate - slightHigh - moderate
5.3 - Logging & wood harvestingLarge - restrictedModerate - slightHigh - moderate
6 - Human intrusions & disturbanceLarge - restrictedSlight or 1-10% pop. declineHigh - moderate
6.1 - Recreational activitiesLarge - restrictedSlight or 1-10% pop. declineHigh - moderate
7 - Natural system modificationsLarge (31-70%)Serious or 31-70% pop. declineHigh - moderate
7.2 - Dams & water management/useLarge (31-70%)Serious or 31-70% pop. declineHigh - moderate
8 - Invasive & other problematic species, genes & diseasesLarge (31-70%)Slight or 1-10% pop. declineHigh - moderate
8.1 - Invasive non-native/alien species/diseasesLarge - restrictedSlight or 1-10% pop. declineHigh (continuing)
8.1.1 - Unspecified speciesLarge - restrictedSlight or 1-10% pop. declineHigh (continuing)
8.2 - Problematic native species/diseasesLarge - restrictedSlight or 1-10% pop. declineHigh (continuing)
8.2.1 - Unspecified speciesLarge - restrictedSlight or 1-10% pop. declineHigh (continuing)
9 - PollutionLarge - restrictedModerate or 11-30% pop. declineHigh (continuing)
9.3 - Agricultural & forestry effluentsLarge - restrictedModerate or 11-30% pop. declineHigh (continuing)
9.3.4 - Type unknown/unrecordedLarge - restrictedModerate or 11-30% pop. declineHigh (continuing)
11 - Climate change & severe weatherLarge - restrictedSlight or 1-10% pop. declineModerate - low
11.4 - Storms & floodingLarge - restrictedSlight or 1-10% pop. declineModerate - low

Plant Characteristics
DurationPERENNIAL
Economic Value (Genus)No
Roadless Areas (24)
Idaho (1)
AreaForestAcres
Bear CreekCaribou-Targhee National Forest118,582
North Carolina (10)
AreaForestAcres
Balsam ConePisgah National Forest10,591
BearwallowPisgah National Forest4,113
Big Indian (addition)Nantahala National Forest1,155
Cheoah BaldNantahala National Forest7,795
Chunky Gal (addition)Nantahala National Forest3,336
Little Indian (addition)Nantahala National Forest640
SnowbirdNantahala National Forest8,489
Tusquitee BaldNantahala National Forest13,670
Wesser BaldNantahala National Forest4,061
Yellowhammer Branch (add.)Nantahala National Forest1,255
Tennessee (3)
AreaForestAcres
Brushy RidgeCherokee National Forest7,469
Sampson Mountain AdditionCherokee National Forest3,064
Stone MountainCherokee National Forest5,367
Virginia (2)
AreaForestAcres
Laurel ForkGeorge Washington National Forest9,967
North Fork PoundJefferson National Forest4,757
West Virginia (8)
AreaForestAcres
Cranberry AdditionMonongahela National Forest11,123
East Fork Of GreenbrierMonongahela National Forest7,167
Falls Of Hills CreekMonongahela National Forest6,925
Little MountainMonongahela National Forest8,172
Marlin MountainMonongahela National Forest9,344
Spice RunMonongahela National Forest6,251
Tea Creek MountainMonongahela National Forest8,295
Turkey MountainMonongahela National Forest6,421
References (28)
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  2. Brzyski, J.R., and T. M. Culley. 2013. Seed germination in the riparian zone: the case of the rare shrub, <i>Spiraea virginiana</i> (Rosaceae). Castanea 78(2):87-94.
  3. Brzyski, J.R., T. M. Culley, and A. Hird. 2014. Does sexual reproduction matter for a rare clonal species in frequently disturbed habitats?. The Journal of the Torrey Botanical Society 141(4):294-301.
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  8. Glencoe, J.F. Jr. 1961. Spiraea virginiana Britton: a rare southern Appalachian endemic. M.S. thesis, West Virginia Univ., Morgantown.
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  14. Ogle, D.W. 1991b. <i>Spiraea virginiana</i> Britton: II. Ecology and species biology. Castanea 56(4): 297-303.
  15. Ogle, D.W. 1991c. Virginia's Endangered Species: Proceeding of a Symposium. Coordinated by Karen Terwilliger. Nongame and Endangered Species Program, Virginia Dept. of Game and Inland Fisheries. The McDonald and Woodward Publishing Co. Blacksburg, VA.
  16. Ogle, D.W. 1992. Virginia spiraea (<i>Spiraea virginiana </i>Britton) recovery plan. U.S. Fish and Wildlife Service, Region 5, Newton Corner, Massachusetts. 41 pp.
  17. Patrick, T.S., J.R. Allison, and G.A. Krakow. 1995. Protected plants of Georgia: an information manual on plants designated by the State of Georgia as endangered, threatened, rare, or unusual. Georgia Dept. Natural Resources, Wildlife Resources Division, Georgia Natural Heritage Program, Social Circle, Georgia. 218 pp + appendices.
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  23. Sutter, R.D., V. Frantz, and K.A. McCarthy. 1988. Atlas of rare and endangered plant species in North Carolina. North Carolina Dept. Agriculture, Plant Protection Section, Conservation Program, Raleigh, North Carolina. 174 pp.
  24. Tessel, S. 2019. Management Guidance for Endangered Species, <i>Spiraea virginiana</i> (Virginia Spiraea). Report prepared for United States Forest Service, Forest Stewardship Program.
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  28. Wiegman, P. Director, Science and Stewardship, Western Pennsylvania Conservancy, Pittsburgh, Pennsylvania.