Sarracenia oreophila

(Kearney) Wherry

Green Pitcherplant

G2Imperiled Found in 15 roadless areas NatureServe Explorer →
G2ImperiledGlobal Rank
Critically endangeredIUCN
HighThreat Impact
Green Pitcher Plant (Sarracenia oreophila). Photo by U.S. Fish & Wildlife Service, Public Domain (U.S. Government Work), via ECOS.
U.S. Fish & Wildlife Service, https://www.usa.gov/government-works
Identity
Unique IDELEMENT_GLOBAL.2.141421
Element CodePDSAR02050
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
IUCNCritically endangered
CITESAppendix I
Endemicendemic to a single nation
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderNepenthales
FamilySarraceniaceae
GenusSarracenia
Other Common Names
green pitcherplant (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
Distinct species, one of only three species of Sarracenia with a geographical distribution outside the coastal plain.
Conservation Status
Rank MethodLegacy Rank calculation - Excel v3.1x
Review Date2015-06-23
Change Date1988-06-30
Edition Date2015-06-23
Edition AuthorsRoth, E., rev. Maybury/Hilton (1996), rev. Schotz (2006), rev. L. Oliver (2015)
Threat ImpactHigh
Range Extent5000-20,000 square km (about 2000-8000 square miles)
Number of Occurrences21 - 80
Rank Reasons
The species' current range is restricted to northeastern Alabama, north Georgia, and southwestern North Carolina. A historical record exists for Tennessee. There are about 36 occurrences known to be extant, nearly all of them in Alabama. Half of these have 50 or fewer clumps of plants; only five have over 500. Land use changes, especially development, have destroyed some populations and led to fire suppression in many areas, but annual burning programs have been established at some sites that support the plant.
Range Extent Comments
Restricted to areas of the Cumberland Plateau and the Ridge and Valley province in these four regions: Coosa Valley, Lake Chatuge, Lookout Mountain, and Sand Mountain (USFWS 2013). Extent of occurrence was calculated during the 2015 conservation status review to be approximately 9,000 sq. km.
Occurrences Comments
Thirty-six extant sites known, 33 in Alabama, 1 in Georgia, and 2 in North Carolina; historic in Tennessee.
Threat Impact Comments
Several threats face Sarracenia oreophila throughout its range. The greatest threat to this species comes from development pressures from industry, agriculture, housing and recreation (Troup and McDaniel 1980). A second related threat is the disruption of natural processes on S. oreophila habitat (Troup and McDaniel 1980). Specifically, altering the natural hydrology and prevention of fires may change conditions so that a site can no longer support green pitcher plants (Troup and McDaniel 1980). Thirdly, like many species of carnivorous plants, S. oreophila is often taken by collectors (Troup and McDaniel 1980) and this threat continues (USFWS 2013). Other threats on a local scale include insect infestation hindering seed production in northern Alabama, possible water pollution affecting one Alabama population, and trampling by cows for populations on sites which are pastured (Troup and McDaniel 1980; S. Benjamin, pers. comm.)

Populations on privately owned lands are the most vulnerable to development related threats. However, even protected sites may be threatened by plant collection. A large Alabama colony of S. oreophila on public land was nearly destroyed by collectors, and the total population on that land-management unit has been reduced by one-half due to illegal collection (U.S. Fish and Wildlife Service 1985).

Additionally, Folkerts (1999) reports that reproduction small, remnant populations of S. oreophila are pollinator limited. Queen bees in the genus Bombus, and specifically B. pennsylvanicus are typical pollinators of this species (Folkerts 1999). These small, isolated populations are at risk of reduced pollen exchange if they are more than 1 mile from one another given the typical flight distance for the bees is less than 1 mile (USFWS 2013).
Ecology & Habitat

Diagnostic Characteristics

Perennial, carnivorous herb with large tubular or pitcher-shaped leaves. The hollow leaves contain liquid and digestive enzymes that enable the plant to breakdown insects into nutrients, which are gradually absorbed into the plant's tissues. Flowers are pendent with five yellow petals that are borne singly on long, leafless stems.

Habitat

Historically, the distribution of Sarracenia oreophila spanned five different geographical provinces: the Cumberland Plateau, Blue Ridge, Piedmont, Ridge and Valley, and East Gulf Coastal Plain (U.S. Fish and Wildlife Service 1985). The present distribution of S. oreophila is restricted to the Cumberland Plateau, Blue Ridge, and Ridge and Valley provinces (U.S. Fish and Wildlife Service 1985), with known, extant populations in northeastern Alabama (Jackson, Marshall, DeKalb, Cherokee and Etowah Counties), northeastern Georgia (Towns county) and adjacent North Carolina (Clay County) (Humphrey 1987).

Three distinct habitat types have been described for S. oreophila. They are sandstone streambanks, with 13 extant colonies in the Cumberland Plateau; mixed oak or pine flatwoods, with 5 extant colonies in the Cumberland Plateau; and seepage bogs, with 5 extant colonies in the Cumberland, 2 colonies in the Blue Ridge, and 2 colonies in the Ridge and Valley provinces (U.S. Fish and Wildlife Service 1985). The soils in all of these habitats are sandy and highly acidic. Woodland and bog soils are sandy clays and loams with an upper layer of organic material, while the streambank soils are composed almost purely of sand (U.S. Fish and Wildlife Service 1985). All of these habitats exhibit generally moist soil conditions, but S. oreophila does not grow in areas where flooding is regular and the soils are continually saturated (Troup and McDaniel 1980). Within the bog habitat, the green pitcher plants grow away from the wet slough (Troup and McDaniel 1980; S. Benjamin and T. Govus, pers. observ.), and along stream banks, the pitchers occur about two feet above the average summer water level (Troup and McDaniel 1980).

Within one bog habitat (Eller Preserve in North Carolina), species associated with the population of green pitcher plants include the following northern and coastal plain bog plants: Sanguisorba canadensis, Eriophorum virginicum, Utricularia cornuta, Eryngium integrifolia, and Helianthus angustifolius (Govus 1986). In addition, several woody species native to wet habitats are also found in this bog, including Alnus serrulata, Lyonia ligustrina, Aronia arbutifolia, and Rosa palustris (Govus 1986). Species associated with S. oreophila in the flatwoods habitat include Pinus palustris, Quercus spp., Rhododendron nudiflorum, Vaccinium fuscatum, Osmunda regalis, Osmunda cinnamomea, Rubus spp. Smilax spp., Liquidambar styraciflua, Xyris sp., Drosera leucantha, and Symplocos tinctoria (Troup and McDaniel 1980). Species found with S. oreophila along streambanks include Alnus serrulata, Kalmia latifolia, Rhododendron spp., Osmunda spp., Smilax spp., Lonicera japonica and Mitchella repens (Troup and McDaniel 1980).

Appropriate habitat for S. oreophila has apparently been naturally maintained through a combination of harsh environmental conditions which discourage competing plants, and periodic disturbance events. Fire is likely important in maintaining open woodland habitats (Troup and McDaniel 1980), while violent winter flooding may impede succession and eliminate competing species along mountain streambanks (U.S. Fish and Wildlife Service 1985). The natural hydrology of spring head bogs may have prevented woody succession in this habitat, or as suggested by Troup (1982), these open grassy areas may be secondary habitat for S. oreophila, dependent on human disturbance for maintaining their open condition. Because the region where S. oreophila occurs has been greatly modified by agricultural and timbering operations, it is difficult to determine the precise natural conditions which supported S. oreophila populations prior to European settlement.

Ecology

REPRODUCTION: Sarracenia oreophila reproduces both sexually and asexually, though in some situations, reproduction may be limited to asexual means, resulting in large spreading clones (Troup and McDaniel 1980). Humphrey (1987) estimates that green pitcher plants do not become sexually mature until they are 6-7 years old.

The flowers of the green pitcher plant mature in late April at lower elevations, and mature in May at higher elevations (Troup 1982). Cross pollination is needed for seed to set (Troup and McDaniel 1980). Insects associated with S. oreophila flowers which may act as pollinators include flies (Sarcophaga spp.), honeybees (Apis spp.) and bumblebees (Bombus spp.) (Troup and McDaniel 1980). Fruits mature in early autumn, but seed may not be released right away (Troup and McDaniel 1980). Seeds are apparently water dispersed (Troup and McDaniel 1980).

INTERACTIONS WITH OTHER SPECIES: Carnivory is the most striking interaction between members of the genus Sarracenia and other species, though the precise benefit to pitcher plants from this highly specialized adaption is not understood. Christensen (1976) found that when insects were fed to Sarracenia flava, there was no consequent increase in Ca, Mg, or K in the plants' leaf tissue. However, nitrogen and phosphorus did increase, indicating that carnivory may be useful in soils low in these elements. Folkerts (1982) suggests that carnivory may be used to obtain micronutrients, such as molybdenum, which are present at very low levels in a low pH environment. Folkerts (1982) also proposes that carnivory may be important at times of nutrient stress since nutrient levels in bogs decrease over the course of the growing season. Another possibility is that the breakdown of prey detritus from decaying pitchers may help fertilize the soil around the plants (Christensen 1976).

In addition to carnivory, pitcher plants have intricate relationships with several different animal taxa. Members of the genus Sarracenia are the exclusive food of at least five species of moth (Damman and French 1987), and other insects are known to live inside pitchers (U.S. Fish and Wildlife Service 1985). Troup and McDaniel (1980) describe a wasp (Olethruetes) and a moth (Exyra) as pests which are known to infest S. oreophila.
Terrestrial Habitats
Forest/WoodlandWoodland - ConiferWoodland - Mixed
Palustrine Habitats
HERBACEOUS WETLANDSCRUB-SHRUB WETLANDFORESTED WETLANDBog/fenRiparian
Other Nations (1)
United StatesN2
ProvinceRankNative
GeorgiaS1Yes
AlabamaS2Yes
North CarolinaS1Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentLarge (31-70%)Serious or 31-70% pop. declineHigh - moderate
1.1 - Housing & urban areasLarge (31-70%)Serious or 31-70% pop. declineHigh - moderate
1.2 - Commercial & industrial areasLarge (31-70%)Serious or 31-70% pop. declineHigh - moderate
1.3 - Tourism & recreation areasLarge (31-70%)Serious or 31-70% pop. declineHigh - moderate
2 - Agriculture & aquacultureLarge - restrictedSerious - moderateHigh - moderate
2.1 - Annual & perennial non-timber cropsLarge (31-70%)Serious or 31-70% pop. declineHigh - moderate
2.3 - Livestock farming & ranchingLarge - restrictedModerate or 11-30% pop. declineHigh (continuing)
5 - Biological resource useLarge (31-70%)Serious or 31-70% pop. declineHigh (continuing)
5.1 - Hunting & collecting terrestrial animalsLarge (31-70%)Serious or 31-70% pop. declineHigh (continuing)
7 - Natural system modificationsLarge (31-70%)Serious or 31-70% pop. declineHigh - moderate
7.1 - Fire & fire suppressionLarge (31-70%)Serious or 31-70% pop. declineHigh - moderate
7.2 - Dams & water management/useLarge (31-70%)Serious or 31-70% pop. declineHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesLarge - restrictedModerate or 11-30% pop. declineHigh (continuing)

Plant Characteristics
DurationPERENNIAL
Economic Value (Genus)Yes
Roadless Areas (15)
Georgia (8)
AreaForestAcres
Ben GapChattahoochee National Forest1,292
Ben GapChattahoochee National Forest1,292
Kelly RidgeChattahoochee National Forest8,325
Kelly RidgeChattahoochee National Forest8,325
Lance CreekChattahoochee National Forest9,025
Shoal BranchChattahoochee National Forest413
Tripp BranchChattahoochee National Forest615
Wilson CoveChattahoochee National Forest545
North Carolina (7)
AreaForestAcres
Boteler PeakNantahala National Forest4,205
Cherry Cove (addition)Nantahala National Forest836
Cherry Cove (addition)Nantahala National Forest836
Chunky Gal (addition)Nantahala National Forest3,336
Sharptop Ridge (addition)Nantahala National Forest600
Sharptop Ridge (addition)Nantahala National Forest600
South Mills RiverPisgah National Forest8,588
References (19)
  1. Benjamin, S.E., and R.D. Sutter. 1991. Monitoring plan for the green pitcher plant (Sarracenia oreophila) in North Carolina and Georgia. Unpublished report for The Nature Conservancy, Southeastern Regional Office, Chapel Hill, North Carolina.
  2. Christensen, N. L. 1976. The role of carnivory in Sarracenia flava L. with regard to specific nutrient deficiencies. Journal Elisha Mitchell Scientific Society 92:144-147.
  3. Damman, A. W. H. and T. W. French. 1987. The ecology of peat bogs of the glaciated northeastern United States: A community profile. U. S. Fish and Wildl. Serv. Bio. Rep. 85(7.16). 100 p.
  4. Flora of North America Editorial Committee (FNA). 2009. Flora of North America north of Mexico. Vol. 8. Magnoliophyta: Paeoniaceae to Ericaceae. Oxford University Press, New York. xxiv + 585 pp.
  5. Folkerts. D. 1999. Pitcher plant wetlands of the southeastern United States. Arthropod associates. In: D.P. Batzer, R.B. Rader, and S.A. Wissinger, eds. Invertebrates in freshwater wetlands of North America: ecology and management. John Wiley and Sons, New York, pp. 247-275.
  6. Folkerts, G.W. 1982. The Gulf Coast pitcher plant bogs. American Scientist 70: 260-267.
  7. Godfrey, R.K., and J.W. Wooten. 1981. Aquatic and wetland plants of southeastern United States: Dicotyledons. Univ. Georgia Press, Athens. 933 pp.
  8. Govus, T. 1986. Natural area reconnaissance. Unpublished report for The Nature Conservancy, Southeast Regional Office, Chapel Hill, North Carolina.
  9. Green Pitcher Plant Recovery Team. 1994. Green pitcher plant (Sarracenia oreophila) recovery plan. U.S. Fish and Wildlife Service, Jackson, Mississippi. 23 pp.
  10. Humphrey, L.D. 1987. Final report on recovery efforts for Sarracenia oreophila (green pitcher plant). Georgia Department of Natural Resources, Game and Fish Division, Social Circle, Georgia.
  11. 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.
  12. Kearney, T.J., Jr. 1900. The lower austral element in the flora of the southern Appalachian region. Science 12: 830-842.
  13. Norquist, C. Biologist, U.S. Fish and Wildlife Service, Alabama. Personal communication.
  14. Patrick, Tom. Georgia Natural Heritage Program. Personal communication.
  15. Troup, R.L. 1982. Recovery plan for the green pitcher-plant. Report for the U.S. Fish and Wildlife Service, Atlanta, Georgia.
  16. Troup, R.L. 1990. Monitoring studies of the green pitcher plant (Sarracenia oreophila). Unpublished report for the U.S. Fish and Wildlife Service, Endangered Species Office, Jackson, Mississippi.
  17. Troup, R.L., and S. McDaniel. 1980. Current status report on Sarracenia oreophila. Report for the U.S. Fish and Wildlife Service, Atlanta, Georgia.
  18. U.S. Fish and Wildlife Service (USFWS). 1985. Green pitcher plant recovery plan. Atlanta, Georgia.
  19. U.S. Fish and Wildlife Service (USFWS). 2013b. Green pitcher plant (<i>Sarracenia oreophila) </i>5-Year Review:  Summary and Evaluation, Southeast Region, Mississippi Field Office, Jackson, MS. Accessed online on June 23, 2015 at:  http://ecos.fws.gov/docs/five_year_review/doc4366.pdf