Neoregelia seideliana
L.B.Sm. & Reitz
Pays · région · aire protégée · écorégion · biome
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
DD · Données insuffisantes?Inconnue- Évaluation
- 2013 · v3.1
- Altitude
- 700 – 1100 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
This species is a fairly recently described species for which the size and dynamics of the population are currently unknown.
Menaces identifiées(3 menaces classées CMP-IUCN)
1_1Housing & urban areasOngoing2_3_4Scale Unknown/UnrecordedOngoing5_3_5Motivation Unknown/UnrecordedOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
Since the 16th century the Atlantic rainforest, a biodiversity hotspot (Myers et al. 2000), has suffered from uninterrupted deforestation. In addition to the relentless habitat loss to pasture, agriculture, sylviculture and urban sprawl other threats contributing to forest degradation include the harvesting of firewood, illegal logging, plant collecting, tourism and invasion by alien species. It is not known whether the taxon is harvested in the wild for its ornamental value. Filho and Tabarelli (2006), found that some ornamental bromeliads had been intensively collected and almost eliminated from forest fragments close to human settlements.
Habitats préférentiels (classification IUCN)
1_9Forest - Subtropical/Tropical Moist Montane
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This species was collected within the biological station of Santa Lucia (Epririto Santo) and within the ecological reserve of Macae do Cima (Rio de Janeiro). Both these protected areas are part of two of the biodiversity corridors which are being implemented in the Brazilian rainforest (the Central Corridor and the Serra do Mar Corridor) as part of the PP-G7 Atlantic forest subprogram (Tabarelli et al. 2005). Biodiversity corridors are landscape-level ecological corridors which consists of network of protected areas and other biodiversity friendly land uses, connecting isolated fragments of habitats (Saatchi et al. 2001). The Atlantic Rainforest has been given high priority for biodiversity conservation because it harbours an extraordinary number of endemic plants and due to the high degree of threats to its megadiversity. Field surveys should be conducted in the historical sites of collection and areas of potential occurrence to estimate the range and the real size of the population and determine whether local extinction has occurred. Samples of seed should be collected and stored as an ex situ conservation measure. The species is cultivated ex situ in botanic gardens such as in the Royal Botanic Garden, Kew.
Actions de conservation (5)Conservation Actions Classification Scheme — IUCNExpert
2_1Site/area management3_4_2Genome resource bank5_1_2National level5_1_3Sub-national level5_4_2National level
Stress écologiques (5)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation
Priorités de recherche (5)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology1_4Harvest, use & livelihoods1_5Threats3_1Population trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Neotropical
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Epiphyte
Références bibliographiques (11)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2013. IUCN Red List of Threatened Species (ver. 2013.2). Available at: <a href="http://www.iucnredlist.org">http://www.iucnredlist.org</a>. (Accessed: 13 November 2013).
- Rocha-Pessôa, T.C., Nunes-Freitas, A.F., Cogliatti-Carvalho, L. and Rocha, C.F. 2008. Species composition of Bromeliaceae and their distribution at the Massambaba restinga in Arraial do Cabo, Rio de Janeiro, Brazil. <i>Brazilian Journal of Botany</i> 68(2): 251-257.
- Martinelli, G., Magalhães Vieira, C., Gonzalez, M., Leitman, P., Piratininga, A. Ferreira da Costa, A. and Campostrini Forzza, R. 2008. Bromeliaceae da Mata Atlântica Brasileira: lista de espécies, distribuição e conservação. <i>Rodriguésia; Revista do Instituto de Biologia Vegetal, Jardim Botânico e Estaçao Biologica do Itatiaya</i> 59(1): 209-258.
- Costa da, A.F. and Wendt, T. 2007. Bromeliaceae na Regio do Macae do Cima, Nova Friburgia, Rio de Janeiro, Brazil. <i>Rodriguésia</i> 58(4): 905-939.
- Paggi, G.M., Palma-Silva, C., Silveira, L.C., Kaltchuk-Santos, E., Bodanese-Zanettini, M.H. and Bered, F. 2007. Fertility of <i>Vriseae gigantea</i> (Gaud) Bromeliaceae, in southern Brazil. <i>American Journal of Botany</i> 94(4): 683-689.
- Filho, J.A.S. and Tabarelli, M. 2006. Bromeliads species of the Atlantic Forest of northeast Brazil: losses of critical populations of endemic species. <i>Oryx</i> 40: 218-223.
- Tabarelli, M., Pinto, L.P., Silva, J.M.C., Hirota,M. and Bedê, L. 2005. Challenges and opportunities for biodiversity conservation in the Brazilian Atlantic Forest. <i>Conservation Biology</i> 19(3): 695-700.
- Fontoura, T., Costa, A. and Went, T. 1991. Preliminary checklist of the Bromeliaceae of Rio de Janeiro State, Brazil. <i>Selbyana</i> 12: 5-45.
- Smith, L.B. and Downs, R.J. 1979. <i>Bromelioideae (Bromeliaceae)</i>. The New York Botanical Garden, New York.
- Smith, L.B. and Downs, R.J. 1974. <i>Flora Neotropica, Pitcairnoideae (Bromeliaceae)</i>. Hafner Press, New York.
- Smith, L.B. 1964. Notes on Bromeliaceae XXII. <i>Phytologia</i> 10: 454-488.
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Romand-Monnier, F., Contu, S. & Lutz, M.
evaluator
Moraes, M.
Romand-Monnier, F., Contu, S. & Lutz, M. 2013. Neoregelia seideliana. The IUCN Red List of Threatened Species 2013: e.T44392635A44494679. Accessed on 05 May 2026.
Répartition mondiale
Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.