Freycinetia cochleatisperma
Huynh
Pays · région · aire protégée · écorégion · biome
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
NT · Quasi menacéecritères B1ab(iii)↘Décroissante- Évaluation
- 2017 · v3.1
- Altitude
- 76 – 770 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
At one specimen collection locality this species was described as abundant and at another as common. Although, no numerical population data are available it is suspected that the population is declining as there has been a significant reduction in lowland forest, a recorded habitat of this species.
Menaces identifiées(6 menaces classées CMP-IUCN)
10_1VolcanoesUnknownMinority (<50%)Unknown2_1_2Small-holder farmingUnknownUnknownOngoing2_1_3Agro-industry farmingUnknownUnknownOngoing2_2_2Agro-industry plantationsUnknownUnknownOngoing5_3_3Unintentional effects: (subsistence/small scale) [harvest]UnknownUnknownOngoing5_3_4Unintentional effects: (large scale) [harvest]UnknownUnknownOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
The lowland forest of West New Britain was noted to be threatened by large scale timber operations (Sekhran and Miller 1995). Forest has been replaced by plantations, for example palm oil plantations, and there is an active New Britain Palm Oil company with plantations in West New Britain (New Britain Palm Oil Limited 2016). In West New Britain there are also large plantations of Eucalyptus (R. Johns pers. comm. 2016). The island also has active volcanoes (WWF 2016). The scope and severity of these threats on this species are uncertain but its lowland forest habitat has certainly declined in extent and quality. It is suspected from the studies on bird species on the island that the impacts may have been considerable. Logging in the 20 years prior to 2008 had reportedly left at least 10 birds close to extinction and if this rate of deforestation continues it has been suggested that most forest below 200 m will be gone by 2060 (RSPB 2008).
Habitats préférentiels (classification IUCN)
1_6Forest - Subtropical/Tropical Moist Lowland★
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
There have been no collection from protected areas. Little information is available about this species and further surveys, research and monitoring are needed, particularly to confirm the current distribution. Creation of protected areas and raising awareness of the threats to this species also needed. Biodiversity hotspots have been identified including in some localities where this species has been found. There was one national-level REDD+ (United Nations Collaborative Programme on Reducing Emissions from Deforestation and forest Degradation in Developing countries) pilot project in West New Britain Province and investments in conservation are reported (University of the South Pacific 2012). It is hoped that this will lead to conservation action that will benefit this species in the future.
Actions de conservation (3)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection3_4_2Genome resource bank4_3Awareness & communications
Stress écologiques (11)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation2_1Species mortality2_1Species mortality2_1Species mortality2_2Species disturbance2_2Species disturbance
Priorités de recherche (5)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology1_5Threats3_1Population trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Australasian
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Vines
Références bibliographiques (15)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2017. The IUCN Red List of Threatened Species. Version 2017-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 14 September 2017).
- WCSP. 2016. World Checklist of Selected Plant Families. Facilitated by the Royal Botanic Gardens, Kew. Available at: <a href="http://apps.kew.org/wcsp/">http://apps.kew.org/wcsp/</a>.
- Global Forest Watch. 2016. Interactive Forest Change Mapping Tool. Available at: <a href="http://www.globalforestwatch.org/map/3/15.00/27.00/ALL/grayscale/loss,forestgain?tab=countries-tab&begin=2001-01-01&end=2015-01-01&threshold=30">http://www.globalforestwatch.org/map/3/15.00/27.00/ALL/grayscale/loss,forestgain?tab=countries-tab&begin=2001-01-01&end=2015-01-01&threshold=30</a>. (Accessed: 2016).
- WWF (World Wildlife Fund). 2016. Papua New Guinea, in the western Pacific Ocean . Available at: <a href="http://www.worldwildlife.org/ecoregions/aa0111">http://www.worldwildlife.org/ecoregions/aa0111</a>. (Accessed: 2016).
- New Britain Palm Oil Company. 2016. Our operations at a glance. Available at: <a href="http://www.nbpol.com.pg/?page_id=83">http://www.nbpol.com.pg/?page_id=83</a>. (Accessed: 2016).
- Richards, S.J. and Whitmore, N. (eds). 2015. A Rapid Biodiversity Asssessment of Papua New Guinea's Hindenburg Wall Region. Goroka Available at: <a href="http://png.wcs.org/">http://png.wcs.org/</a>.
- Prebble, M. and Anderson, A. 2012. The Archeobotany of Rapan Rockshelter Deposits. In: Anderson, A. and Kennett, D.J. (eds), <i>Taking the High Ground: The Archaeology of Rapa, a Fortified Island in Remote Polynesia</i>, pp. 77-96. Australian National University E Press, Canberra.
- University of the South Pacific. 2012. Ecosystem Profile East Melanesian Islands Biodiversity Hotspot. In: Critical Ecosystem Partnership Fund (ed.). University of the South Pacific.
- 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.
- RSPB (Royal Society for the Protection of Birds). 2008. Rainforest destruction leaves species seeing red. Available at: <a href="http://www.rspb.org.uk/media/releases/details.aspx?id=tcm:9-179625">http://www.rspb.org.uk/media/releases/details.aspx?id=tcm:9-179625</a>. (Accessed: 2016).
- 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.
- Huynh, K-L. 1997. The Genus Freycinetia in the Solomon Islands. <i>Candollea</i> 52(2): 359-382.
- Huynh, K-L. 1996. The genus Freycinetia (Pandanaceae) in New Guinea (part 1). <i>Botanische Jahrbücher fur Systematik</i> 118: 529-545.
- Sekhran, N.and Miller, S. (Eds). 1995. <i>Papua New Guinea country study on biological diversity</i>. Department of Environment and Conservation, Waigani, Papua New Guinea.
- Stone, B.C. 1982. New Guinea Pandanaceae: first approach to ecology and biogeography. In: Gressitt, J.L. (ed.), <i>Biogeography and ecology of New Guinea</i>, pp. 401-436. Dr W.Junk Publishers, Hague-Boston-London.
Évaluateurs & contributeurs (5)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Chadburn, H.
contributor
Baines, D.
evaluator
Johns, R.J.
facilitators
Hargreaves, S.
institutions
Royal Botanic Gardens, Kew
Chadburn, H. 2017. Freycinetia cochleatisperma. The IUCN Red List of Threatened Species 2017: e.T22486573A22487870. Accessed on 05 May 2026.
Répartition mondiale
Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.