Ontologia

Zingiber cernuum

Dalzell

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

Graphe en cours d’indexation

Calcul du tissu écologique de Zingiber cernuum.

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
300800 m
Profondeur
m
État de la populationExpert
This species is reported to be common in moist shady places, in semi-evergreen forests of the Western Ghats (Sasidharan and Sivarajan 1996). The taxon is described as a common species in Kerala (Kavitha et al. 2007). The size and dynamics of the population are unknown.

Menaces identifiées(13 menaces classées CMP-IUCN)

  • 4_1
    Roads & railroads
    UnknownUnknownOngoing
  • 1_1
    Housing & urban areas
    Ongoing
  • 1_3
    Tourism & recreation areas
    Ongoing
  • 2_1_1
    Shifting agriculture
    Ongoing
  • 2_1_3
    Agro-industry farming
    Ongoing
  • 2_2_2
    Agro-industry plantations
    Ongoing
  • 2_3_4
    Scale Unknown/Unrecorded
    Ongoing
  • 3_2
    Mining & quarrying
    Ongoing
  • 5_3_5
    Motivation Unknown/Unrecorded
    Ongoing
  • 7_1_3
    Trend Unknown/Unrecorded
    Ongoing

+ 3 menaces supplémentaires

Description complète des menacesExpert
Most of the natural forest in the region has been cleared and converted to agriculture and plantations and the remaining habitat is highly fragmented in this region where the human population density is very high. It is estimated than between 1920 and 1990 forest cover in the western Ghats declined by 40%, with a four fold increase in the number of fragments, and 83% decrease in the size of remnants (Muthuramkumar et al. 2006). Very few large blocks of intact forest remain. Hydroelectric projects have flooded large areas of forests and roads have allowed more human encroachment. Shifting cultivation has begun to clear patches of old-growth forest. Riparian habitats are often the first to be lost. Many of the remaining forest patches that harbour endemic species are being converted to rubber, Eucalyptus, coffee, teak, tea, cardamom or coconut plantations. Several endemic species are expected to become extinct in the near future, if the current alarming rates of deforestation are maintained in this biodiversity hotspot (Rawat 2001a,b; Muthuramkumar et al. 2006). Forest clearing for agriculture, mining, hydroelectric projects, road construction and human encroachment remain the biggest threats to the region's natural habitat and biodiversity. Degraded habitats are colonized by the exotic Lantana camara and Chromolaena odorata, which inhibit regeneration of native vegetation. Fires, tourism pressure, livestock grazing and trampling and illegal logging also threaten the native flora of the region. The resilience of this species to anthropogenic disturbance and its ability to persist and regenerate in disturbed, fragmented and secondary vegetation is unknown.

Habitats préférentiels (classification IUCN)

  • 1_6Forest - Subtropical/Tropical Moist Lowland
  • 1_9Forest - Subtropical/Tropical Moist Montane
Mesures de conservation recommandéesExpert
This species has been collected within several conservation units. The taxon is grown ex situ in botanical institutions and DNA is preserved for germplasm conservation. The conservation status of this species has not yet been assessed in India. It is listed as indeterminate in Karnataka. Although this species does not appear to be threatened, surveys should be conducted to determine the current range and size of the population. The population should be regularly monitored and its ability to persist and regenerate in disturbed and secondary forest should be investigated.
Actions de conservation (1)Expert
  • 2_1Site/area management
Stress écologiques (21)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 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_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
Priorités de recherche (4)Expert
  • 1_2Population size, distribution & trends
  • 1_3Life history & ecology
  • 1_5Threats
  • 3_1Population trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Indomalayan

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

Forb or Herb
Références bibliographiques (14)Expert
  1. IUCN. 2013. IUCN Red List of Threatened Species (ver. 2013.1). Available at: <a href="http://www.iucnredlist.org">http://www.iucnredlist.org</a>. (Accessed: 12 June 2013).
  2. Nair, R.A. and Thomas, G. 2007. Isolation, characterization and expression studies of resistance gene candidates (RGCs) from <i>Zingiber</i> spp. <i>TAG Theoretical and Applied Genetics</i> 116(1): 123-134.
  3. Kavitha, P.G., Nair, P., Nair, R.A., Jayachandran, B.K., Sabu, M. and Thomas, G. 2007. AFLP polymorphism and Phytium response in Zingiber species. In: R. Keshavachandran, P. Nazeem, D. Girija, P.S. John and K.V. Peter (eds), <i>Recent trends in horticultural biotechnology, Vol. II. ICAR national symposium on biotechnological interventions for improvement of horticultural crops: issues and strategies, Vellanikkara, Kerala, India, 10-12 January</i>, pp. 497-503. New India Publishing, New Dehli.
  4. Muthuramkumar, S., Ayyappan, N., Parthasarathy, N., Mudappa, D.. Shankar Raman, T.R., Arthur Selwyn, M. and Arul Pragasan, L. 2006. Plant Community Structure in Tropical Rainforest Fragments of the Western Ghats, India. <i>Biotropica</i> 38(2): 143-160.
  5. Ravindran, P.N. and Babu, K.N. 2004. <i>Ginger: the Genus </i>Zingiber<i></i>. CRC Press, Boca Raton, Fla.
  6. Jacob, T., Jebasingh, T., Venugopal, M.N. and Usha, R. 2003. High genetic diversity in the coat protein and 3′ untranslated regions among geographical isolates ofCardamom mosaic virus from south India. <i>Journal of Biosciences</i> 28(5): 589-595.
  7. Rawat, G.S. 2001. South western Ghats moist deciduous forest (IM0150). Available at: <a href="http://worldwildlife.org/ecoregions/im0150">http://worldwildlife.org/ecoregions/im0150</a>.
  8. Rawat, G.S. 2001. South Western Ghats Montane Rainforest (IM0135). Available at: <a href="http://worldwildlife.org/ecoregions/im0135">http://worldwildlife.org/ecoregions/im0135</a>.
  9. Ramaswamy, S.N. 2001. <i>Flora of Shimoga district, Karnataka</i>. University of Mysore, Mysore.
  10. Sasidharan, N. and Sivarajan, V.V. 1996. <i>Flowering Plants of Thrissur Forest (Western Ghats, Kerala, India)</i>. Scientific Publisher, Jodhpur.
  11. Lakshminarasimhan, P. 1996. <i>Flora of Maharashtra- monocotyledones</i>. Botanical survey of India, Calcutta.
  12. Saldaha, C.J. 1978. <i>Flora of Hassan District, Karnataka</i>. Amerind Pub, New Dehli.
  13. Santapau, H. 1953. <i>The Flora of Khandala</i>. Records of the Botanical Survey of India, New Dehli.
  14. Hooker, J.D. 1894. <i>Flora of British India</i>. Reeve and Co, London.
Évaluateurs & contributeurs (2)Expert
assessor
Romand-Monnier, F.
evaluator
Scott, J.A.

Romand-Monnier, F. 2013. Zingiber cernuum. The IUCN Red List of Threatened Species 2013: e.T44393388A44421584. 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

Bibliographie