
Castanopsis cuspidata
(Thunb.) Schottky
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Pays · région · aire protégée · écorégion · biome
Graphe en cours d’indexation
Calcul du tissu écologique de Castanopsis cuspidata.
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Liste rouge IUCN
LC · Préoccupation mineure?Inconnue- Évaluation
- 2018 · v3.1
- Altitude
- – m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
The species is common on the mainland of Japan, where it is often found inland away from the coast. It is one of two species that make up climax laurel forests on the island and hence it is assumed the species is abundant (Hiroki and Ichino 1998). The species is found in contiguous forest from the Setouchi Inland Sea coast to the Japan Sea Coast (Yamada et al. 2002). On Higashiyama hill near Kyoto C. cuspidata subpopulations are considered to be increasing. Here, from 1961 to 2004 the species range has increased from 6.9 ha to 32.1 ha (Hirayama et al. 2010). The same study by Hirayama et al. (2010) showed that the population within one forest plot had good regeneration due to a inverse J population structure, where the most abundant tree sizes were in size class 1 and 2. It is not known if the species shows range expansion and good regeneration across its whole distribution. In fact, other studies (Yamada et al. 2002) have reported decline in the area of the species native Laurel forests which has also caused them to become fragmented.
The South Korean subpopulation is likely to be smaller as the species is found only at the southern tip of the peninsular (Chang and Kim 2015). It is most common on the Southern Islands.
Overall, the C. cuspidata population is expected to contain more than 10,000 mature individuals. Due to the opposite reports of population decline and increase in Japan the species population trend cannot be confirmed.
The South Korean subpopulation is likely to be smaller as the species is found only at the southern tip of the peninsular (Chang and Kim 2015). It is most common on the Southern Islands.
Overall, the C. cuspidata population is expected to contain more than 10,000 mature individuals. Due to the opposite reports of population decline and increase in Japan the species population trend cannot be confirmed.
Description complète des menacesTexte détaillé évaluation IUCNExpert
This species is threatened by habitat loss in Japan. This is as a result of human exploitation of the forest within Japan (Yamada et al. 2002). The scale of this threat is not known. In other areas the species is known to be doing well in areas of disturbance (Hirayama et al. 2010). The species is not threatened in Korea (J. Hun pers. comm. 2017).
Habitats préférentiels (classification IUCN)
1_4Forest - Temperate
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
This species is reported from 16 ex situ collections (BGCI PlantSearch 2017). It is recommended that the population, or its native forest, is surveyed to ascertain the overall trend in the species population.
Usage & commerce (3)Use & Trade — IUCNExpert
13Pets/display animals, horticulturenational17Other (free text)national7Fuelsnational
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Nearctic
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Tree - small
Références bibliographiques (10)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2018. The IUCN Red List of Threatened Species. Version 2018-1. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 28 June 2018).
- 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>.
- GBIF. 2017. Global Biodiversity Information Facility (GBIF) Data Portal. Available at: <a href="https://www.gbif.org/">https://www.gbif.org/</a>.
- CABI. 2017. Invasive Species Compendium. Wallingford, UK Available at: <a href="http://www.cabi.org/isc/datasheet/28799">http://www.cabi.org/isc/datasheet/28799</a>. (Accessed: Jan 2017).
- BGCI. 2017. GlobalTreeSearch online database. Richmond, U.K. Available at: <a href="https://www.bgci.org/global_tree_search.php">https://www.bgci.org/global_tree_search.php</a>. (Accessed: August 2017).
- Chang, C.S. and Kim, H. 2015. The Woody Plants of Korea. Available at: <a href="http://florakorea.myspecies.info/en">http://florakorea.myspecies.info/en</a>. (Accessed: Jan 2017).
- RBG, Kew. 2014. World Checklist of Selected Plant Families (WCSP). Available at: <a href="http://apps.kew.org/wcsp/home.do">http://apps.kew.org/wcsp/home.do</a>.
- Hirayama, K., Kawamura, S., Nishimura, T. and Takahara, H. 2010. Establishment of the evergreen broad-leaved tree species Castanopsis cuspidata in an abandoned secondary forest in western Japan. <i>Journal of Plant Research</i> 123(5): 655-63.
- Yamada, H., Yamaguci, K. and Miyaura, T. 2002. iginal Article Effect of Japan Sea Climate on Geographic Distribution of Castanopsis sieboldii and C. cuspidata . <i>Journal of Forest Research</i> 7(2): 67-71.
- Hiroki, S. and Ichino, K. 1998. Comparison of growth habits under various light conditions between two climax species, Castanopsis sieboldii and Castanopsis cuspidata, with special reference to their shade tolerance. <i>Ecological Research</i> 13(1): 65-72.
Évaluateurs & contributeurs (3)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Barstow, M.
evaluator
Hun PI, J.
institutions
Botanic Gardens Conservation International
Barstow, M. 2018. Castanopsis cuspidata. The IUCN Red List of Threatened Species 2018: e.T62004530A62004533. Accessed on 05 May 2026.
Distribution mondiale
Calcul de la distribution GBIF· ~10–60 s
Phénologie
Calcul du calendrier d'apparition· ~5–30 s
Consulter sur les bases externes
Observations & statuts
Cartographie
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (32)— redirigent vers cette page
- Castanopsis cuspidata f. angustifolia(G.Nicholson) Nakai
- Lithocarpus sieboldiiNakai
- Pasaniopsis sieboldii var. pusilla(Blume) Makino
- Pasaniopsis sieboldii var. rotundifolia(Makino) Makino
- Balanoplis serrataRaf.
- Balanopsis serrataRaf.
- Castanea faurieiH.Lév. & Vaniot
- Castanopsis cuspidata f. aurescensNakai
- Castanopsis cuspidata f. latifolia(G.Nicholson) Rehder & E.H.Wilson
- Castanopsis cuspidata f. ligustrifolia(Koidz.) Nakai
- Castanopsis cuspidata f. pusilla(Blume) Nakai
- Castanopsis cuspidata f. variegata(G.Nicholson) Nakai
- Castanopsis cuspidata var. cuspidata
- Castanopsis cuspidata var. thunbergii(Makino) Nakai
- Castanopsis thunbergii(Makino) Hatus.
- Lithocarpus cuspidatus(Thunb.) Nakai
- Pasania cuspidata(Thunb.) Oerst.
- Pasania cuspidata f. pusilla(Blume) Makino
- Pasania cuspidata f. rotundifoliaMakino
- Pasania cuspidata var. cuspidata
- Pasania cuspidata var. thunbergiiMakino
- Pasania sieboldii var. pusilla(Blume) Makino
- Pasania sieboldii var. rotundifolia(Makino) Makino
- Pasaniopsis cuspidata(Thunb.) Kudô
- Quercus cuspidataThunb.
- Quercus cuspidata var. angustifoliaG.Nicholson
- Quercus cuspidata var. latifoliaG.Nicholson
- Quercus cuspidata var. pusillaBlume
- Quercus cuspidata var. variegataG.Nicholson
- Shiia cuspidata(Thunb.) Makino
- Shiia cuspidata var. murataeYanagita
- Synaedrys cuspidata(Thunb.) Koidz.
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).