Ontologia

Carex atrofuscoides

K.T.Fu

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

Graphe en cours d’indexation

Calcul du tissu écologique de Carex atrofuscoides.

Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).

Liste rouge IUCN

LC · Préoccupation mineure?Inconnue
Évaluation complète
Évaluation
2013 · v3.1
Altitude
10004700 m
Profondeur
m
État de la populationExpert
The number of individuals and dynamics of the population are unknown. The taxon appears to be locally common (Zhang pers. comm. 2009).

Menaces identifiées(7 menaces classées CMP-IUCN)

  • 11_5
    Other impacts
    UnknownUnknownOngoing
  • 4_1
    Roads & railroads
    UnknownUnknownOngoing
  • 5_2_1
    Intentional use (species is the target)
    UnknownUnknownOngoing
  • 1_1
    Housing & urban areas
    Ongoing
  • 1_3
    Tourism & recreation areas
    Ongoing
  • 2_3_2
    Small-holder grazing, ranching or farming
    Ongoing
  • 2_3_3
    Agro-industry grazing, ranching or farming
    Ongoing
Description complète des menacesExpert
Although this species is found in areas of low human footprint (Sanderson et al. 2002, GIS data), montane and alpine ecosystems in the region are considered threatened due to their high vulnerability to ongoing climate and land use changes. Alpine meadows have been actively grazed by domestic livestock for many years and many pastures are reported to be degraded although some natural habitats remain intact. Threats to plant species in the region include: the establishment of new towns, especially on the Tibetan plateau, overgrazing and trampling by large herds of livestock (especially yaks), Governmental rangeland intensification schemes, construction of highways, tourism, soil erosion, increased frequency of landslides and the unregulated commercial harvest of medicinal plants (Ning and Richard 1999, Zhou et al. 2005). The degradation of grasslands in this region may be accelerated with global warming as indicated by some modelling studies (Zhou et al. 2005). In recent years, oral testimony in these regions indicate a general drying up of the Rangelands (Klein et al. 2004). The direct impact of these threats on the taxon and its resilience to disturbances are unknown. The taxon may not be palatable to livestock. The rhizomatous habit may confer to this plant a good regeneration potential. This species is reported to grow over a very wide altitude range and is therefore likely to be adapted to various habitats and may be more tolerant to environmental changes.

Habitats préférentiels (classification IUCN)

  • 4_4Grassland - Temperate
  • 1_4Forest - Temperate
  • 1_9Forest - Subtropical/Tropical Moist Montane
  • 3_7Shrubland - Subtropical/Tropical High Altitude
Mesures de conservation recommandéesExpert
The type was collected within the natural Reserve of the sacred mountain Taibaishan, where forests have been protected over centuries for religious reasons. The taxon may have been collected in other conservation units. The fragile alpine ecosystems in the region mostly lack effective core protection. The taxon does not benefit from any legal protection in China. Botanical surveys should be conducted in the region to estimate the current range and population size and adequately define the conservation status of this species.
Actions de conservation (3)Expert
  • 1_2Resource & habitat protection
  • 4_3Awareness & communications
  • 6_1Linked enterprises & livelihood alternatives
Stress écologiques (13)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_3Indirect ecosystem effects
  • 2_1Species mortality
  • 2_2Species disturbance
Priorités de recherche (2)Expert
  • 1_2Population size, distribution & trends
  • 3_1Population trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Palearctic

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

GeophyteGraminoid
Références bibliographiques (10)Expert
  1. 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).
  2. Dai, L.-K., Liang, S.-Y., Zhang, S., Tang, Y., Koyama, T., Tucker, G.C., Simpson, D.A., Noltie, H.J., Strong, M.T., Bruhl, J.J., Wilson, K.L. and Muasya, A.M. 2006. Flora of China, Monocots. In: W. Zhengyi and P.H. Raven (eds), <i>Flora of China</i>, Science Press, Missouri Botanical Garden Press, Beijing and St. Louis.
  3. Clayton, W.D., Harman, K.T. and Williamson, H. 2006. GrassBase - The Online World Grass Flora. Available at: <a href="http://www.kew.org/data/grasses-db.html">http://www.kew.org/data/grasses-db.html</a>. (Accessed: 10/09/2008).
  4. Zhou, H., Zhao, X., Tang, Y., Gu, S. and Zhou, L. 2005. Alpine grassland degradation and its control in the source region of the Yangtze and Yellow Rivers, China. <i>Grassland Science</i> 51(3): 151-2-163.
  5. Klein, J.A., Harte, J. and Zhao, X.Q. 2004. Experimental warming causes large and rapid species loss, dampened by simulated grazing, on the Tibetan Plateau. <i>Ecology Letters</i> 7(12): 1170-1179.
  6. Sanderson, E.W., Jaiteh, M., Levy, M.A., Redford, K.H., Wannebo, A.V. and Woolmer, G. 2002. The human footprint and the last of the wild. <i>Bioscience</i> 52(10): 891-904.
  7. Dai, L.K. and Liang, S.Y. 2001. <i>Flora Republicae Popularis Sinicae</i>. Science Press, Beijing.
  8. Ning, W. and Richard, C. 1999. The privatization process of rangeland and its impacts on pastoral dynamics in the Hindu-Kush Himalaya: The Case of Western Sichuan, China. International Rangeland Congress, Alberta.
  9. Wang, W.T., Wu, S.G., Lang, K.Y., Li, P.Q., Pu, F.T. and Chen, S.K. (eds). 1994. <i>Vascular plants of the Hengduan Mountains</i>. Science Press, Beijing.
  10. Instituto Botanico Boreali-occidentali Academiae Sinicae Edita (ed.). 1976. Flora Tsinlingensis, Tomus 1, Spermatophyta. <i>Flora Tsinlingensis</i>, Instituto Botanico Boreali - Occidentali, Beijing.
Évaluateurs & contributeurs (2)Expert
assessor
Romand-Monnier, F.
evaluator
Liu, Q.

Romand-Monnier, F. 2013. Carex atrofuscoides. The IUCN Red List of Threatened Species 2013: e.T44393131A44545701. 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

Consulter sur les bases externes

Observations & statuts

Cartographie

Bibliographie

Note nomenclaturale & synonymesExpert

Note nomenclaturale

TAXREF v18 — INPN/MNHN

Synonymes (1)— redirigent vers cette page

  • Carex malanshanensisR.F.Huang

Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).