Ontologia

Ostrya rehderiana

Chun

CRLR Monde (IUCN)
Pays · région · aire protégée · écorégion · biome

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Calcul du tissu écologique de Ostrya rehderiana.

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Liste rouge IUCN

CR · En danger critiquecritères B1ab(i,ii,v)+2ab(i,ii,v); C2a(i,ii); DDécroissante
Évaluation complète
Évaluation
2014 · v3.1
Altitude
200400 m
Profondeur
m
État de la populationExpert
When first recorded in 1927 this species was fairly common in the woods of Tianmu Shan (Tianmu Mountain) of Zhejiang Province, China. However, there has been a rapid reduction in population size and this species is now considered an extremely rare tree. The wild population of this species is reported to consist of five individual trees (Li et al. 2013). All individuals have been drastically damaged; one of them, which is one metre in chest height diameter, has had the top of its trunk broken, and the other four have had their lower lateral branches cut off. The Flora of China (2008) notes that this species is Endangered and reports only one single known individual tree at a roadside. This assessment uses the more up to date population information from Li et al. (2013). Population decline is projected to continue. Visible damage to remaining individuals highlights continued threats.

Menaces identifiées(1 menace classée CMP-IUCN)

  • 2_1_4
    Scale Unknown/Unrecorded
    Rapid DeclinesWhole (>90%)Ongoing
Description complète des menacesExpert
The rapid reduction in the population of this species was most probably due to deforestation and planting of bamboos. The continued habitat destruction and human disturbances are a major threat to this species. Visible damage to remaining individuals shows that human disturbance continues to threaten this species. Continued habitat destruction weakens regenerative ability and results in very few seedlings beneath the remaining individuals. Competition from other species is also a threat to this species, especially bamboo which is a fast growing species reaching full size within three to four months.  

This species has been reported to have a very limited natural recruitment as well as a high mortality rate. A recent study found low levels of genetic diversities in the five extant, naturally regenerating individuals. It is unlikely the species has experienced a long-term bottleneck as the previous population was quite common, however there is evidence of inbreeding depression having an effect on offspring survival.

Habitats préférentiels (classification IUCN)

  • 1_4Forest - Temperate
Mesures de conservation recommandéesExpert
Conservation of this species, both in situ and ex situ, is essential to ensure its survival. Mount Xitianmu (West Tianmu Mountain) has been declared as a nature reserve and great attention has been given to this species. Stone fences have been erected around the trees by the roadside where individuals are extremely threatened. To stimulate natural regeneration, the public needs to be educated not to destroy and trample the existing stands. Despite efforts, they do not appear to be regenerating well naturally. Although the Hangzhou Botanical Garden and the Zhejiang College of Forestry have the species in cultivation, it is still necessary to collect additional seeds for breeding to expand the cultivation program. The species is also subject to legal protection. It has been recommended that the cutting of bamboos and trees, that compete with this species for light, be considered especially in habitats that contain both mature individuals and seedlings. Ex situ conservation is also essential to ensure survival of this species.
Actions de conservation (4)Expert
  • 2_2Invasive/problematic species control
  • 3_2Species recovery
  • 3_4_2Genome resource bank
  • 4_3Awareness & communications
Stress écologiques (5)Expert
  • 1_2Ecosystem degradation
  • 2_1Species mortality
  • 2_3_2Competition
  • 2_3_5Inbreeding
  • 2_3_7Reduced reproductive success
Niche IUCN globaleExpert

Royaumes biogéographiques

Palearctic

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

Tree - large
Références bibliographiques (10)Expert
  1. IUCN. 2014. The IUCN Red List of Threatened Species. Version 2014.3. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 13 November 2014).
  2. Missouri Botanical Garden. 2013. Tropicos. Missouri Available at: <a href="www.tropicos.org">www.tropicos.org</a>.
  3. Govaerts, R. 2013. World Checklist of Betulaceae. Facilitated by the Royal Botanic Gardens, Kew Available at: <a href="http://www.kew.org/wcsp/">http://www.kew.org/wcsp/</a>.
  4. Yuan-Yuan, L., Shen-Min, G., Shu-Zhen, Y., Yuan, L., and Xiao-Yong, C. 2012. Genetic decline and inbreeding depression in an extremely rare tree. <i>Conservation Genetics</i> 13: 343-347.
  5. The Plant List. 2010. The Plant List. Available at: <a href=" http://www.theplantlist.org/"> http://www.theplantlist.org/</a>. (Accessed: 2013).
  6. J. LÓPEZ-PUJOL & Z.-Y. ZHANG. 2009. An insight into the most threatened flora of China. <i>Collectanea Botanica (Barcelona)</i> 28: 95-110.
  7. eFloras. 2008. Flora of China. Available at: <a href="www.efloras.org">www.efloras.org</a>.
  8. Oldfield, S., Lusty, C. and MacKinven, A. (compilers). 1998. <i>The World List of Threatened Trees</i>. World Conservation Press, Cambridge, UK.
  9. Li-kuo, F. and Jian-ming, J. 1992. <i>China Plant Red Data Book – Rare and Endangered Plants 1</i>. Science Press, Beijing.
  10. Liujun. Wild germplasm resources and conservation of rare and endangered tree species endemic to east China. Research Institute of Subtropical Forestry, Chinese academy of forestry.
Évaluateurs & contributeurs (2)Expert
assessor
Shaw, K., Roy , S. & Wilson, B.
evaluator
Rivers, M.C.

Shaw, K., Roy , S. & Wilson, B. 2014. Ostrya rehderiana. The IUCN Red List of Threatened Species 2014: e.T32304A2813136. Accessed on 05 May 2026.

Répartition mondiale (heatmap GBIF)Construction en cours

0 obs · 0 cellules
Construction par partitions temporelles GBIF0%

Source : GBIF — observations agrégées par hexagones 0.2° × 0.2° (~22km). Filtre qualité : précision coordonnée < 10 km. Coloration quantile (q50/70/90/99). Fond carte : OpenFreeMap · © OpenStreetMap.

Distribution mondiale

Calcul de la distribution GBIF· ~10–60 s

Phénologie

Calcul du calendrier d'apparition· ~5–30 s

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Observations & statuts

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