Trillium persistens
W.H.Duncan
Graphe en cours d’indexation
Calcul du tissu écologique de Trillium persistens.
Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).
Liste rouge IUCN
VU · Vulnérablecritères D2→Stable- Évaluation
- 2020 · v3.1
- Altitude
- 250 – 500 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
Surveys conducted in conjunction with the development of a recovery plan in 1984 documented 10,338 stems within the species’ four known subpopulations (U.S. Fish and Wildlife Service 1984). Later surveys suggest this figure is an underestimate of the total population. To date, the most comprehensive population census for the species was conducted in 1985 and documented 20,028 stems within the species’ range (U.S. Fish and Wildlife Service 2011). The population is thought to be stable, but additional surveys are needed to confirm the overall population trend. Existing population estimates are considerably out of date.
Menaces identifiées(10 menaces classées CMP-IUCN)
7_2_10Large damsRapid DeclinesMinority (<50%)Past, Unlikely to Return7_2_9Small damsRapid DeclinesMinority (<50%)Past, Likely to Return5_3_4Unintentional effects: (large scale) [harvest]Causing/Could cause fluctuationsUnknownPast, Likely to Return8_1_1Unspecified speciesCausing/Could cause fluctuationsUnknownOngoing8_1_2Named speciesCausing/Could cause fluctuationsUnknownOngoing6_1Recreational activitiesNegligible declinesMinority (<50%)Ongoing1_1Housing & urban areasUnknownUnknownOngoing1_2Commercial & industrial areasUnknownUnknownOngoing8_1_2Named speciesUnknownOngoing8_1_2Named speciesUnknownUnknownOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
The primary threat to the species is habitat degradation caused by forest clearance associated with construction and timber extraction. This has had documented negative impacts on subpopulations within the species’ range (U.S. Fish and Wildlife Service 2011). Forest clearance aids the spread of invasive species including Kudzu (Pueraria montana) and Japanese Honeysuckle (Lonicera japonica), resulting in further Persistent Trillium population declines and extended recovery times (U.S. Fish and Wildlife Service 2011). Threats posed by timber harvest have been largely mitigated as a result of voluntary conservation agreements made with landowners, and the purchase of land by the Georgia Department of Natural Resources (U.S. Fish and Wildlife Service 2011). English ivy (Hedera sp.) is present within the Talullah Gorge State Park and may present a substantial threat to Persistent Trillium within its entire range.
Disturbance caused by recreational usage of the species’ habitat (primarily trampling) is unlikely to impact the population as it occurs on steep, inaccessible slopes within protected areas (U.S. Fish and Wildlife Service 2011). Some efforts have been made to alleviate pressure in areas with high traffic and, at present, disturbance associated with recreational activity is not thought to present a significant threat.
The invasive Hemlock Woolly Adelgid (Adelges tsugae) may negatively impact the species by causing declines in Eastern Hemlock overstories (NatureServe 2019). As with forest clearance, die-offs of hemlock may result in increased competition with invasive plants, exacerbating population declines (U.S. Fish and Wildlife Service 2011).
Though predation by White-tailed Deer (Odocoileus virginianus) is a threat to several other species of Trillium in the eastern United States (Dávalos et al. 2014, Knight et al. 2009, Rooney and Gross 2003), it is unlikely to present a major threat to Persistent Trillium given the low densities of White-tailed Deer within the species’ range, and the steep slopes of its preferred habitat which are relatively inaccessible (U.S. Fish and Wildlife Service 2011).
Historical habitat losses caused by dam construction likely resulted in losses of large tracts of suitable habitat (NatureServe 2019). No additional dams have been proposed in the area and the ongoing threat to extant subpopulations is thought to be minimal.
Habitats préférentiels (classification IUCN)
1_4Forest - Temperate
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
Since 1978, the species has been listed as Endangered at the federal level, and is protected on public lands throughout its range (U.S. Fish and Wildlife Service 1984). At present, there is no indication that the species’ status is likely to change (U.S. Fish and Wildlife Service 2011). Since 1993, much of the species’ range (probably encompassing 75% of the total population) has also been under the protection of the Tallulah Gorge State Park, which provides adequate protection against most threats to the species (U.S. Fish and Wildlife Service 2011). An ex-situ subpopulation of 20-30 plants has been maintained at the Georgia State Botanical Garden in Athens, Georgia since 1983 (U.S. Fish and Wildlife Service 2011). Though the process is labour and cost intensive, establishment of additional ex-situ subpopulations is recommended to protect the species against stochastic events that may impact its restricted range.
The range of the species is well established, however, additional population monitoring within this range is highly recommended to better determine population trends. In addition, genetic studies are needed to determine the substructure of the population, particularly in light of the high effective subpopulations needed to sustain population stability. Continued maintenance of a low White-tailed Deer population as well as control of invasive competitors, namely Japanese Honeysuckle (L. japonica), Kudzu (P. montana), and English Ivy (Hedera sp.) are crucial to the continued survival of the species (U.S. Fish and Wildlife Service 2011). These efforts are especially important within forest edge environments along utility rights-of-way and roadsides.
Actions de conservation (1)Conservation Actions Classification Scheme — IUCNExpert
2_2Invasive/problematic species control
Stress écologiques (19)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_1Species mortality2_2Species disturbance2_3_2Competition2_3_2Competition2_3_2Competition
Usage & commerce (1)Use & Trade — IUCNExpert
13Pets/display animals, horticulturenational
Priorités de recherche (4)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology3_1Population trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Systèmes (terrestre/eau douce/marin)
Formes de croissance
Références bibliographiques (12)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2020. The IUCN Red List of Threatened Species. Version 2020-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 13 June 2020).
- NatureServe. 2019. NatureServe Explorer: An online encyclopedia of life [web application]. Arlington, Virginia Available at: <a href="http://explorer.natureserve.org">http://explorer.natureserve.org</a>. (Accessed: 3 January 2019).
- Chauhan, H. K., Bisht, A. K., Bhatt, I. D., Bhatt, A. and Gallacher, D. 2019. Trillium – toward Sustainable Utilization of a Biologically Distinct Genus Valued for Traditional Medicine. <i>The Botanical Review</i> 85(3): 252-272.
- United Plant Savers. 2018. Trillium. Available at: <a href="https://unitedplantsavers.org/trillium/">https://unitedplantsavers.org/trillium/</a>. (Accessed: 19 December 2018).
- Dávalos, A., Nuzzo, V. and Blossey, B. 2014. Demographic responses of rare forest plants to multiple stressors: the role of deer, invasive species and nutrients. <i>Journal of Ecology</i> 102(5): 1222-1233.
- U.S. Fish and Wildlife Service. 2011. Persistent Trillium (Trillium persistens) Duncan 5-Year Review: Summary and Evaluation. U.S. Fish and Wildlife Service, Athens, GA.
- Knight, T. M., Caswell, H. and Kalisz, S. 2009. Population growth rate of a common understory herb decreases non-linearly across a gradient of deer herbivory. <i>Forest Ecology and Management</i> 257(3): 1095-1103.
- Case, F. W. and Case, R. B. 2009. <i>Trilliums</i>. Timber Press, Portland, OR.
- Rooney, T. P. and Gross, K. 2003. A demographic study of deer browsing impacts on Trillium grandiflorum. <i>Plant Ecology</i> 168: 267-277.
- Flora of North America (FNA) Editorial Committee. 2002. <i>Flora of North America North of Mexico. Vol. 26. Magnoliophyta: Liliidae: Liliales and Orchidales</i>. Oxford Univ. Press, New York.
- Zettler, J. A., Spira, T. P. and Allen, C. R. 2001. Yellow Jackets (Vespula spp.) Disperse Trillium (spp.) Seeds in Eastern North America. <i>The American Midland Naturalist</i> 146(2): 444-446.
- U.S. Fish and Wildlife Service. 1984. Persistent Trillium (Trillium persistens) Recovery Plan. U.S. Fish and Wildlife Service, Atlanta, GA.
Évaluateurs & contributeurs (5)Personnes ayant contribué à l'évaluation IUCNExpert
Meredith, C.R. & Trillium Working Group 2019 2020. Trillium persistens. The IUCN Red List of Threatened Species 2020: e.T146086967A146089290. Accessed on 05 May 2026.