Plagiostachys sumatrensis
Ridl.
Pays · région · aire protégée · écorégion · biome
Graphe en cours d’indexation
Calcul du tissu écologique de Plagiostachys sumatrensis.
Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).
Liste rouge IUCN
DD · Données insuffisantes?Inconnue- Évaluation
- 2020 · v3.1
- Altitude
- – m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
The population is likely to be small.
Description complète des menacesTexte détaillé évaluation IUCNExpert
Most of Siberut Island is classified as National Park (Siberut National Park) (Protected Planet 2019). There is also intact forest in other parts of the island.
However, based on experience of conservation work in Singapore (J. Leong-Škorničková pers. comm. 2020), the population could have undergo a reduction; we see population sizes of certain species being reduced even in perfectly protected and undisturbed areas within a decade. Gingers, being herbs, are far more vulnerable to any sudden changes in climate and humidity, etc. than could be shrubs and trees, or changes in population of species linked to them (e.g. the current loose of a species due to recent overpopulation of wild boars, who dig rhizomes and eat them). These kind of threats for example are not perceivable these days by satellite images, and there could be other potential threats that might have affected the species without it being noticed.
Even if there are no perceivable threats, nothing is known about the original populations of this species: it is not know if the species is still there, or how common or rare it is or was, if it is bound to a specific habitat (limestone, particular habitat like stream side etc), nor what its linkages to pollinators and dispersing agents are (J. Leong-Škorničková pers. comm. 2020).
However, based on experience of conservation work in Singapore (J. Leong-Škorničková pers. comm. 2020), the population could have undergo a reduction; we see population sizes of certain species being reduced even in perfectly protected and undisturbed areas within a decade. Gingers, being herbs, are far more vulnerable to any sudden changes in climate and humidity, etc. than could be shrubs and trees, or changes in population of species linked to them (e.g. the current loose of a species due to recent overpopulation of wild boars, who dig rhizomes and eat them). These kind of threats for example are not perceivable these days by satellite images, and there could be other potential threats that might have affected the species without it being noticed.
Even if there are no perceivable threats, nothing is known about the original populations of this species: it is not know if the species is still there, or how common or rare it is or was, if it is bound to a specific habitat (limestone, particular habitat like stream side etc), nor what its linkages to pollinators and dispersing agents are (J. Leong-Škorničková pers. comm. 2020).
Habitats préférentiels (classification IUCN)
18Unknown
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This species has not been recorded by BGCI (2019) to be grown ex situ. It may occur in Siberut National Park.
Although no threats are identified to occur where the species was collected, the only record is from 1924, therefore, research on the current distribution and population are recommended.
Although no threats are identified to occur where the species was collected, the only record is from 1924, therefore, research on the current distribution and population are recommended.
Priorités de recherche (4)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_5Threats3_1Population trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Indomalayan
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Forb or Herb
Références bibliographiques (6)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).
- WCSP. 2019. World Checklist of Selected Plant Families. Available at: <a href=" http://apps.kew.org/wcsp/"> http://apps.kew.org/wcsp/</a>.
- ZRC. 2019. Zingiberaceae Resource Centre. Available at: <a href="http://padme.rbge.org.uk/ZRC/welcome">http://padme.rbge.org.uk/ZRC/welcome</a>.
- Protected Planet. 2019. Protected Planet: The World Database on Protected Areas (WDPA). Cambridge, UK Available at: <a href="www.protectedplanet.net">www.protectedplanet.net</a>. (Accessed: 2019).
- BGCI. 2018. Botanic Gardens Conservation International (BGCI) - Plant Search. Available at: <a href="https://www.bgci.org/plant_search.php">https://www.bgci.org/plant_search.php</a>.
- Boden Kloss, C. 1926. Spolia Mentawiensia. <i>Bulletin of miscellaneous information Kew</i>: 89.
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Olander, S.B.
evaluator
Leong-Škorničková, J., Nurainas & Ardiyani, M.
Olander, S.B. 2020. Plagiostachys sumatrensis. The IUCN Red List of Threatened Species 2020: e.T117417475A124283817. Accessed on 05 May 2026.
Distribution mondiale
Calcul de la distribution GBIF· ~10–60 s
Phénologie
Calcul du calendrier d'apparition· ~5–30 s