Borinda mairei
(Hack. ex Hand.-Mazz.) Stapleton
Pays · région · aire protégée · écorégion · biome
Pas d'interactions documentées pour cette espèce.
Liste rouge IUCN
DD · Données insuffisantes?Inconnue- Évaluation
- 2013 · v3.1
- Altitude
- 2900 – 3600 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
The frequency and abundance of the taxon within its range are unknown. The size and dynamics of the population are unknown.
Menaces identifiées(1 menace classée CMP-IUCN)
5_2_1Intentional use (species is the target)UnknownUnknownOngoing
Description complète des menacesTexte détaillé évaluation IUCNExpert
Forests in which the taxon occurs are reported to be extensively disturbed and very degraded by human activities, such as: cultivation, firewood cutting and conversion to shrubland and meadows, even within protected areas. Between 15,000 and 20,000 km2 of forest are estimated to remain within the range of this species (Bystriakova et al. 2003).
Bamboos are an ancient group of forest plants which are intrinsically vulnerable to deforestation. The vulnerability of some species is increased by the simultaneous flowering and subsequent death of entire populations in cycles of 20-120 years. Inhabiting moister, more benign habitats in old-growth forests, they are often associated with threatened plants (Bystriakova et al. 2003). The ability of the taxon to regenerate and persist in disturbed and secondary habitats is unknown.
Many Asian bamboo species show very restricted potential ranges possibly due to scarcity of effective dispersal mechanisms, isolation of populations in often dissected, mountainous terrain and relatively recent radiation into new habitats following tectonic and orogenic activity. This suggests that many uncultivated forest bamboos may be particularly susceptible to erosion of their habitat and their genetic diversity, and therefore may need to be considered threatened. Problems of access, ownership, forest management procedures and difficulties in commercialization mean that they are more vulnerable, even though many of them are highly productive and extremely useful (Bystriakova et al. 2003).
The shoots of this species are edible, and the culms are used for weaving (Zhengui et al. 2006). The impact of shoot and culm harvesting on the population are unknown.
Bamboos are an ancient group of forest plants which are intrinsically vulnerable to deforestation. The vulnerability of some species is increased by the simultaneous flowering and subsequent death of entire populations in cycles of 20-120 years. Inhabiting moister, more benign habitats in old-growth forests, they are often associated with threatened plants (Bystriakova et al. 2003). The ability of the taxon to regenerate and persist in disturbed and secondary habitats is unknown.
Many Asian bamboo species show very restricted potential ranges possibly due to scarcity of effective dispersal mechanisms, isolation of populations in often dissected, mountainous terrain and relatively recent radiation into new habitats following tectonic and orogenic activity. This suggests that many uncultivated forest bamboos may be particularly susceptible to erosion of their habitat and their genetic diversity, and therefore may need to be considered threatened. Problems of access, ownership, forest management procedures and difficulties in commercialization mean that they are more vulnerable, even though many of them are highly productive and extremely useful (Bystriakova et al. 2003).
The shoots of this species are edible, and the culms are used for weaving (Zhengui et al. 2006). The impact of shoot and culm harvesting on the population are unknown.
Habitats préférentiels (classification IUCN)
1_4Forest - Temperate
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
It is not known whether this species occurs within any conservation units. Because traditional plant taxonomy has relied heavily upon floral characteristics, while bamboo flowers are only encountered at long intervals, bamboos are among the least studied of all higher plants. Research on biodiversity and conservation of the remaining forest bamboos has so far been very limited due to poor knowledge of bamboo identification and distribution. As a non-timber forest product bamboo is not routinely included in forest inventories. Despite the growing importance of bamboos very few studies of the conservation status of individual species have been undertaken.
Bamboo biodiversity conservation is now seen as a priority in China. Political stability makes interventions feasible and taxonomic studies are progressing. Areas such as the Upper Yangtze watershed are receiving more protection, primarily for downstream flood limitation purposes. Conservation of the forest bamboo species is necessary not only for their own intrinsic value, but also as a genetic backup in support of related cultivated bamboos.
Protection of their natural populations in situ is apparently the only feasible conservation technique at present, for threatened bamboos, as ex situ conservation techniques are currently not practical for bamboos. Bamboo seed is infrequently produced and has poor viability, and plantations are difficult to raise and protect on a large enough scale.
Field surveys are needed to determine the current range and size of the population of this species and whether it occurs within any conservation units.
Bamboo biodiversity conservation is now seen as a priority in China. Political stability makes interventions feasible and taxonomic studies are progressing. Areas such as the Upper Yangtze watershed are receiving more protection, primarily for downstream flood limitation purposes. Conservation of the forest bamboo species is necessary not only for their own intrinsic value, but also as a genetic backup in support of related cultivated bamboos.
Protection of their natural populations in situ is apparently the only feasible conservation technique at present, for threatened bamboos, as ex situ conservation techniques are currently not practical for bamboos. Bamboo seed is infrequently produced and has poor viability, and plantations are difficult to raise and protect on a large enough scale.
Field surveys are needed to determine the current range and size of the population of this species and whether it occurs within any conservation units.
Actions de conservation (4)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection2_1Site/area management3_4_1Captive breeding/artificial propagation3_4_2Genome resource bank
Stress écologiques (2)Stresses Classification — IUCNExpert
2_1Species mortality2_2Species disturbance
Usage & commerce (2)Use & Trade — IUCNExpert
1Food - humansubsistance9Construction or structural materialssubsistance
Priorités de recherche (5)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology1_4Harvest, use & livelihoods1_5Threats3_1Population trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Palearctic
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Graminoid
Références bibliographiques (7)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2013. IUCN Red List of Threatened Species (ver. 2013.2). Available at: <a href="http://www.iucnredlist.org">http://www.iucnredlist.org</a>. (Accessed: 13 November 2013).
- Chen, S.-l., Li, D.-Z., Zhu, G., Wu, Z., Lu, S.-l., Liu, L., Wang, Z.-P., Sun, B.-X., Zhu, Z.-D., Nianhe, X., Jia, L.-Z., Guo, Z., Chen, W., Chen, X., Guangyao, Y., Phillips, S.M., Stapleton, C., Soreng, R.J., Aiken, S.G., Tzvelev, N.N., Peterson, P.M., Renvoize, S.A., Olonova, M.V. and Ammann, K. (eds). 2006. Poaceae. In: Z.-y. Wu and P.H. Raven (eds), <i>Flora of China</i>, Science Press and Missouri Botanical Garden Press, Beijing and St. Louis.
- Bystriakova, N., Kapos, V., Stapleton, C. and Lysenko, I. 2003. Annex V: Woody bamboo species of the Asia-Pacific region with less than 20 000 km² of forest remaining within their ranges. In: Bamboo Biodiversity, Asean Biodiversity Network (ed.). UNEP-WCMC/INBAR.
- Bystriakova, N., Kapos, V., Stapleton, C. and Lysenko, I. 2003. Bamboo Biodiversity: information for planning conservation and management in the Asia-Pacific region. UNEP-WCMC/INBAR, Cambridge.
- Long, C., Liu, Y., Xue, J. and Li, D. 2003. A bamboo germplasm collection for community development in Central Yunnan, China. <i>Journal of Bamboo and Rattan</i> 2(1): 3-11.
- Kanglin, W. 2002. Ecology and habitats of bamboos in Yunnan, China. Kunming Institute of Botany, Kunming, Yunnan.
- Clayton, W.D., Harman, K.T. and Williamson, H. 2002. World Grass Species: Descriptions, Identification, and Information Retrieval. Available at: <a href="http://www.kew.org/data/grasses-db.html.">http://www.kew.org/data/grasses-db.html.</a>. (Accessed: 2009).
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Romand-Monnier, F. & Bachman, S.
evaluator
Liu, Q.
Romand-Monnier, F. & Bachman, S. 2013. Fargesia mairei. The IUCN Red List of Threatened Species 2013: e.T44392932A44523582. 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
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (6)— redirigent vers cette page
- Arundinaria maireiHack. ex Hand.-Mazz.
- Fargesia mairei(Hack. ex Hand.-Mazz.) T.P.Yi
- Indocalamus mairei(Hack. ex Hand.-Mazz.) McClure
- Phyllostachys mairei(Hand.-Mazz.) D.L.Fu
- Sinarundinaria mairei(Hack. ex Hand.-Mazz.) Keng f.
- Yushania mairei(Hack. ex Hand.-Mazz.) Campb.
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).