Calanthe caulescens
J.J.Sm.
Pays · région · aire protégée · écorégion · biome
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
LC · Préoccupation mineure→Stable- Évaluation
- 2018 · v3.1
- Altitude
- 1770 – 3450 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
No numerical population information is available, but one collection notes it to be plentiful in thick ground moss of low thickets and at the higher altitudes orchids can be very common in terms of individuals (Schuiteman and De Vogel 2007). It is suspected that the population is not small. This orchid has a wide geographical extent and nearly 2,000 m elevational range, it is found in several ecoregions and a variety of habitats, including higher montane forests where anthropogenic threats are generally less intense or even absent and much undisturbed montane forest and shrubland remains within its range and it is suspected that overall the population may be relatively stable.
Menaces identifiées(5 menaces classées CMP-IUCN)
11_2DroughtsCausing/Could cause fluctuationsUnknownPast, Likely to Return2_1_2Small-holder farmingNegligible declinesMinority (<50%)Ongoing3_2Mining & quarryingNegligible declinesMinority (<50%)Ongoing7_1_1Increase in fire frequency/intensityNegligible declinesMinority (<50%)Ongoing5_3_4Unintentional effects: (large scale) [harvest]UnknownMinority (<50%)Ongoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
The drivers of forest change in Papua New Guinea's forests were identified as subsistence agriculture, logging, forest fires, clearance for plantations and mine-related forest clearance (Shearman et al. 2008) and similar threats occur in Indonesian Papua. This orchid has been recorded from within a logging concession area (Sherman et al. 2009) and the process of logging, particularly clear felling, removes the shade that Calanthe species require and they are known to rapidly desiccate and die (Clayton and Cribb 2013). It has been recorded in areas where there is agricultural encroachment into forest, such as in Enga Province, Papua New Guinea, and from areas with mining activity, such as the Grasberg mine, Mt Jaya, Papua, Indonesia. Some areas are subject to threats from fire, for example, in the Mount Giluwe area, where it has been recorded, a massive fire destroyed forest along the Mount Giluwe Range in 1997 (Dudley et al. 1997). The likelihood of fire increases particularly in dry years and droughts associated with El Niño events. Impacts are becoming more frequent and severe and the area of Papua New Guinea's montane forests has been significantly reduced through burning (Shearman et al. 2008). There is a low frequency and diversity of epiphytic plants in many forests known to have been burned (Johns 1989) and the impact of drought itself may also cause decline in orchid populations (E. De Vogel pers. comm. 2017). However, this orchid has a wide geographical extent and nearly 2,000 m elevational range, it is found in several ecoregions and a variety of habitats, including higher montane forests where anthropogenic threats are generally less intense or even absent and much undisturbed montane forest and shrubland remains within its range. In view of this it is suspected that in many areas these threats will not be operational and overall declines small.
Habitats préférentiels (classification IUCN)
1_9Forest - Subtropical/Tropical Moist Montane3_7Shrubland - Subtropical/Tropical High Altitude4_7Grassland - Subtropical/Tropical High Altitude5_4Wetlands (inland) - Bogs, Marshes, Swamps, Fens, Peatlands
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This orchid has been recorded within the Lorentz National Park area, a 2.35 million ha protected area, which is the largest in South-East Asia and incorporates a continuous ecological transect from mountain peaks to the coast (UNESCO 2017). It has also been found also close to the c. 8,000 km2 Jayawijaya Wildlife Reserve and it may occur within it. The designation of additional protected areas, particularly in Papua New Guinea would be beneficial. It is not known to be conserved ex situ (BGCI 2017). Further studies are needed to give a better understanding of its life history and ecology, and population size and any specific threats. Additional surveys are needed to improve our knowledge of its current distribution.
Actions de conservation (2)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection3_4_2Genome resource bank
Stress écologiques (11)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality
Priorités de recherche (2)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Australasian
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
EpiphyteGeophyte
Références bibliographiques (15)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2018. The IUCN Red List of Threatened Species. Version 2018-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 15 November 2018).
- UNESCO (United Nations Educational, Scientific and Cultural Organnization). 2017. Lorentz National Park. Available at: <a href="http://whc.unesco.org/en/list/955">http://whc.unesco.org/en/list/955</a>.
- BGCI. 2017. PlantSearch. Botanic Gardens Conservation International, London. Available at: <a href="https://www.bgci.org/plant_search.php">https://www.bgci.org/plant_search.php</a>.
- Bishop Museum. 2015. Papuan Plants Project. Available at: <a href="http://pbs.bishopmuseum.org/papuanplants/project.html">http://pbs.bishopmuseum.org/papuanplants/project.html</a>. (Accessed: 2015).
- Clayton, D. and Cribb, P. 2013. <i>The Genus Calanthe</i>. Natural history publications (Borneo), Kota Kinabalu.
- Bachman, S., Moat, J., Hill, A.W., de la Torre, J. and Scott, B. 2011. Supporting Red List threat assessments with GeoCAT: geospatial conservation assessment tool. In: V. Smith and L. Penev (eds) e-Infrastructures for data publishing in biodiversity science. <i>Zookeys</i> 150: 117–126.
- Shearman, P.L., Ash, J., Mackey, B. Bryan, J.E. and Lokes, B. 2009. Forest Conversion and Degradation in Papua New Guinea 1972-2002. <i>Biotropica</i> 41: 379-390.
- Shearman, P., Bryan, J., Ash, J., Hunnam, P., Mackey, B. and Lokes, B. 2008. The state of the forests of Papua New Guinea. Mapping the extent and condition of forest cover and measuring the drivers of forest change in the period 1972-2002. University of Papua New Guinea, Port Moresby.
- Schuiteman, A. and De Vogel, E.F. 2007. Orchidaceae of Papua. In: Marshall, A.J. and Beehler, B.M. (eds), <i>The Ecology of Papua </i>, pp. 435-456. Periplus, Singapore.
- Johns, R.J., Edwards, P.J., Utteridge, T.M.A. and Hopkins, H.C.F. 2006. <i>A Guide to the Alpine and Subalpine Flora of Mount Jaya</i>. Kew Publishing, Kew.
- Olson, D.M., Dinerstein, E., Wikramanayake, E.D., Burgess, N.D., Powel, G.V.N., Underwood, E.C., D'Amico, J.A., Itoua, I., Strand, H.E., Morrison, J.C., Loucks, C.J., Allnutt, T.F., Ricketts, T.H., Kura, Y., Lamoreux, J.F., Wettengel, W.W., Hedao, P. and Kassem, K.R. 2001. Terrestrial ecoregions of the world: a new map of life on earth. <i>Bioscience</i> 51(11): 933-938.
- Thomas, S. 1999. <i>Calanthe</i> Section <i>Rhodochilus</i >(Orchidaceae) from New Guinea, The Solomon Islands and the Moluccas. <i>Blumea</i> 44: 25-36.
- Dudley, N., Jeanrenaud, J-P and Stolton, S. 1997. The Year the World Caught Fire. A report to WWF International .
- Johns, R.J. 1989. The Influence of Drought on Tropical Rainforest Vegetation in Papua New Guinea. <i>Mountain Research and Development</i> 9(3): 248-251.
- van Royen, P. 1979. <i>The Orchids of the High Mountains of New Guinea</i>. J.Cramer.
Évaluateurs & contributeurs (5)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Chadburn, H. & Schuiteman, A.
contributor
Baines, D., Barker, A., Black, M. & Murray, L.
evaluator
Rankou, H.
facilitators
Clarkson, J. & Hargreaves, S.
institutions
Royal Botanic Gardens, Kew
Chadburn, H. & Schuiteman, A. 2018. Calanthe caulescens. The IUCN Red List of Threatened Species 2018: e.T119252585A119262768. Accessed on 05 May 2026.
Répartition mondiale
Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.
Consulter sur les bases externes
Observations & statuts
Cartographie
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (4)— redirigent vers cette page
- Calanthe apostasioidesSchltr.
- Calanthe salmoniviridisP.Royen
- Styloglossum caulescens(J.J.Sm.) T.Yukawa & P.J.Cribb
- Styloglossum caulescns(J.J.Sm.) T.Yukawa & P.J.Cribb
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).