Pterocarya macroptera
Batalin
Pays · région · aire protégée · écorégion · biome
Graphe en cours d’indexation
Calcul du tissu écologique de Pterocarya macroptera.
Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).
Liste rouge IUCN
VU · Vulnérablecritères C2a(i)↘Décroissante- Évaluation
- 2019 · v3.1
- Altitude
- 1100 – 3500 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
The total population of Pterocarya macroptera is estimated to be between 5,000 to 8,000 mature trees in ca. 120 localities. However, the total number of localities could differ from this estimation, because a large part of the distribution range of the species has not been fully explored by botanists and some historical localities could have already disappeared. Recent explorations show that subpopulations comprise of no more than 50 individual trees and that the species seems to reproduce mainly through cloning, with fruits being often sterile (Kozlowski et al. 2018). Based on recent field explorations (Kozlowski et al. 2018) the population size of the different stands are very small, except for one important subpopulation in Shennogjia, Hubei.
Menaces identifiées(5 menaces classées CMP-IUCN)
7_2_9Small damsRapid DeclinesFuture1_3Tourism & recreation areasNegligible declinesOngoing2_1_3Agro-industry farmingNegligible declinesOngoing2_2_2Agro-industry plantationsNegligible declinesOngoing4_1Roads & railroadsNegligible declinesFuture
Description complète des menacesTexte détaillé évaluation IUCNExpert
The main threats to Pterocarya macroptera include the destruction or artificialization of riparian habitats (Kozlowski et al. 2018). However, compared to the other species of the genus occupying the same type of environment (P. hupehensis, P. stenoptera and P. tonkinensis), P. macroptera seems less affected by human activities, as the species grows generally at higher elevations in more remote areas. Generally, forests and riparian habitats located in deep mountain valleys at higher elevations face less damage and are presently still well preserved (Kozlowski et al. 2018). This is particularly true in mountainous areas in the centre of China, but it could slightly differ in other regions of the country, such as Yunnan and Guizhou provinces where afforestation and agriculture by local communities are frequent even in higher altitudes. Another threat for the long term conservation of this tree is the low production of seeds combined with the low survival rate of the young seedlings.
Habitats préférentiels (classification IUCN)
1_4Forest - Temperate
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
The three infra-specific varieties were all assessed as Least Concern in China (Red List of Chinese Plants 2019). Field explorations are still necessary to confirm ancient indications and to estimate more precisely the total number of individuals. The species is not very common in cultivation and is reported to have at least 19 ex situ collections worldwide (BGCI PlantSearch 2019). An ex situ conservation program should be initiated to protect the genetic diversity of the species. Afforestation projects in mountainous degraded riparian habitats could play an important role to promote the species.
Actions de conservation (3)Conservation Actions Classification Scheme — IUCNExpert
3_2Species recovery3_3_1Reintroduction3_4_1Captive breeding/artificial propagation
Usage & commerce (1)Use & Trade — IUCNExpert
9Construction or structural materialssubsistance
Priorités de recherche (1)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Palearctic
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Tree - large
Références bibliographiques (7)Sources scientifiques de l'évaluation IUCNExpert
- Red List of Chinese Plants. 2019. Available at: <a href="http://www.chinaplantredlist.org/about_us.php">http://www.chinaplantredlist.org/about_us.php</a>.
- IUCN. 2019. The IUCN Red List of Threatened Species. Version 2019-3. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 10 December 2019).
- Kozlowski, G., Bétrisey, S. and Song, Y-G. 2018. <i>Wingnuts (</i>Pterocarya<i>) and walnut family. Relict trees: linking the past, present and future</i>. Natural History Museum Fribourg, Switzerland.
- CVH (Chinese Virtual Herbarium). 2018. Chinese Virtual Herbarium. Available at: <a href="http://www.cvh.org.cn/en">http://www.cvh.org.cn/en</a>. (Accessed: 2018).
- 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>.
- Fang, J., Wang, Z, Tang, Z. 2011. <i>Atlas of Woody Plants in China</i>. Higher Education Press, Beijing.
- Zheng, Y.W. and Raven, P.H. 2003. Zelkova. Flora of China. Vol. 5. Ulmaceae – Basellaceae. Missouri Botanical Garden Press, St. Louis.
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Song, Y., Bétrisey, S. & Kozlowski, G.
evaluator
Harvey-Brown, Y. & Rivers, M.C.
Song, Y., Bétrisey, S. & Kozlowski, G. 2019. Pterocarya macroptera. The IUCN Red List of Threatened Species 2019: e.T66816136A66816223. Accessed on 05 May 2026.
Distribution mondiale
Calcul de la distribution GBIF· ~10–60 s
Phénologie
Calcul du calendrier d'apparition· ~5–30 s