Ontologia

Dipcadi concanense

(Dalzell) Baker

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

Pas d'interactions documentées pour cette espèce.

Liste rouge IUCN

EN · En dangercritères A3c; B2ab(i,ii,iii,iv,v)Décroissante
Évaluation complète
Évaluation
2022 · v3.1
Altitude
50200 m
Profondeur
m
État de la populationExpert
The species has only 2–3 remaining dense subpopulations in north and south Ratnagiri (more than 50 plants/ square meter and 1,000 or more plants in mass blooming). Other subpopulations are small (50 or less plants in scattered clumps). The flowers are pollinated by a Sphingid moth species which limits cross pollination over large distances. The seeds are large and do not disperse over large distances. More than 80% of the subpopulations occur as clumps widely separate by 2-50 kilometers. The large and continuous populations are now rare and are separated by a distance of more than 20 km, indicating severe fragmentation. Dipcadi concanense population is severely fragmented as the chances of germplasm exchange between the various subpopulations are extremely limited.  

Field studies and experimental cultivation of Dipcadi concanense indicated that seeds germinate almost immediately and produce a tuber which then undergoes dormancy and sprouts during the rainy season. Reliable estimate of first flowering in natural condition is not available. In ex-situ cultivation first flowering occurred around the 5th year, but it is likely to be less than 5 years in natural conditions and most likely to be 1–2 years. There is no reliable estimate of age to which the bulbs survive in natural or experimental conditions. To estimate the generation length we used the formula: generation length=age at first reproduction + [Z *(length of the reproductive period) ]. Calculations carried out using variable values for age of first reproduction (1–5 years), length of reproductive period (1–10 years) and z= 0.16–0.33 as proxy based upon values for different plant species given by Fung and Waples (2017). All the estimates for generation length are less than 3 years. Hence population reduction is measured over 10 years (longer than 3 generation length value) following the IUCN guidelines for the use of criteria A. 

Menaces identifiées(13 menaces classées CMP-IUCN)

  • 1_3
    Tourism & recreation areas
    Rapid DeclinesMinority (<50%)Ongoing
  • 2_1_3
    Agro-industry farming
    Rapid DeclinesMajority (50-90%)Ongoing
  • 2_3_2
    Small-holder grazing, ranching or farming
    Rapid DeclinesWhole (>90%)Ongoing
  • 4_1
    Roads & railroads
    Rapid DeclinesMajority (50-90%)Past, Likely to Return
  • 5_2_1
    Intentional use (species is the target)
    Rapid DeclinesMinority (<50%)Ongoing
  • 6_1
    Recreational activities
    Negligible declinesMinority (<50%)Ongoing
  • 3_3
    Renewable energy
    UnknownMinority (<50%)Ongoing
  • 2_1_2
    Small-holder farming
    Slow, Significant DeclinesMajority (50-90%)Ongoing
  • 6_3
    Work & other activities
    Slow, Significant DeclinesWhole (>90%)Ongoing
  • 1_1
    Housing & urban areas
    Very Rapid DeclinesMajority (50-90%)Ongoing

+ 3 menaces supplémentaires

Description complète des menacesExpert
The Kokan-Goa region is experiencing severe threat due to upcoming infrastructural projects in the region that include urbanization, industrialization along with construction of civil airports, nuclear power plant and an oil refinery. These are and will lead to large scale conversion in the habitat making it unsuitable for this species. Anecdotal information from local people indicates that previously large populations existed in and around Ratnagiri town which today only has a few clumps on the outskirts of the city. The remaining localities also have ongoing pressures for several year due to increase in rural land-uses such a mango cultivation, quarrying for laterite stone, grazing and fires. Collection of plants for flowers for making garlands is likely to reduce the pollination and hence seed formation and may reduce local abundance and germplasm diversity.

Habitats préférentiels (classification IUCN)

  • 4_6Grassland - Subtropical/Tropical Seasonally Wet/Flooded
  • 6Rocky areas (eg. inland cliffs, mountain peaks)
Mesures de conservation recommandéesExpert
Ex situ and in situ conservation of Dipcadi concanense has been successfully tried in Ratnagiri and Sindhudurg districts supported by a grant from Department of Biotechnology, Government of India. The species responds well to propagation and small populations have been established in Ratnagiri on experimental level. However, conservation of natural populations in-situ is required urgently, especially in areas marked for megadevelopment projects.
Actions de conservation (17)Expert
  • 1_1Site/area protection
  • 1_2Resource & habitat protection
  • 2_1Site/area management
  • 2_3Habitat & natural process restoration
  • 3_1_1Harvest management
  • 3_3_2Benign introduction
  • 3_4_1Captive breeding/artificial propagation
  • 4_1Formal education
  • 4_2Training
  • 4_3Awareness & communications
  • 5_1_1International level
  • 5_2Policies and regulations
  • 5_3Private sector standards & codes
  • 5_4_2National level
  • 6_3Market forces
  • 6_4Conservation payments
  • 6_5Non-monetary values
Stress écologiques (33)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_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_3Indirect ecosystem effects
  • 1_3Indirect ecosystem effects
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_1Species mortality
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_3_4Loss of pollinator
  • 2_3_4Loss of pollinator
  • 2_3_4Loss of pollinator
  • 2_3_7Reduced reproductive success
Usage & commerce (2)Expert
  • 1Food - human
    subsistance
  • 12Handicrafts, jewellery, etc.
    subsistance
Priorités de recherche (12)Expert
  • 1_2Population size, distribution & trends
  • 1_3Life history & ecology
  • 1_4Harvest, use & livelihoods
  • 1_5Threats
  • 1_6Actions
  • 2_1Species Action/Recovery Plan
  • 2_2Area-based Management Plan
  • 2_3Harvest & Trade Management Plan
  • 3_1Population trends
  • 3_2Harvest level trends
  • 3_3Trade trends
  • 3_4Habitat trends
Niche IUCN globaleExpert

Royaumes biogéographiques

Indomalayan

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

Forb or HerbGeophyte
Références bibliographiques (11)Expert
  1. IUCN. 2022. The IUCN Red List of Threatened Species. Version 2022-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 08 December 2022).
  2. Mhatre, K., Kulkarni, A. and A.Gude. 2018. Extended distribution of Dipcadi concanense (Dalzell) Baker for the state of Maharashtra. In: Dr. N. P. Tendolkar (ed.), International Conference On “Environment Development and Sustainability”, pp. 372. Devrukh.
  3. Fung, H.C. and Waples, R.S. 2017. Performance of IUCN proxies for generation length. <i>Conservation Biology</i> 31(4): 883-893.
  4. Deshpande, A., Mirgal, A., Krishnan, S., Narkhede, S., & Janarthanam, M. K. 2016. Extended distribution of Dipcadi concanense (Dalzell) Baker: A highly threatened plant taxon of the family Asparagaceae. <i>Journafl off Threaftened Taxa</i> 8(13): 9586-9588.
  5. Deshpande, A. S., Krishnan S. and M.K. Janarthanam. 2015. Systematic position of two endemic Dipcadi spp. (Asparagaceae) from northern Western Ghats of India using molecular markers. <i>Rheedea </i> 25 (2): 97-102.
  6. Patil, S. 2015. A Note on the Occurrence and Distribution of Dipcadi concanense. <i>Nelumbo</i> 57: 60-63.
  7. Deshpande A., Deshpande, S. , Krishnan S. and Janarthanam, M.K. 2015. Lectotypification of Uropetalon concanense (Asparagaceae): An endemic species from Western Ghats, India. <i>Rheedea</i> 25(2): 123-124.
  8. Gosavi, K. V. C., Yadav, U., Janarthanam, M. K. & Yadav, S. R. 2011. Karyomorphological Analysis of Recently Described Rare Species of Dipcadi Medik (Hyacinthaceae) from Northern Western Ghats. <i>Cytologia</i> 76(1): 63-66.
  9. Tetali, P., Lakshminarasimhan, P., Prasanna, P. V., & Tetali, S. 2000. Rediscovery of Dipcadi maharashtrensis Deb et Dasgupta (Liliaceae), an endemic and threatened species from Maharashtra, India. <i>RHEEDEA</i> 10(2): 127-130.
  10. Sakhare, S.S. 1991. Morphotaxonomic studies in Liliaceae genus Dipcadi Medik. species . Department of Botany, Shivaji University, Shivaji University Kolhapur.
  11. Naik, V. N. 1974. Cytological Studies in Two Species of Dipcadi Medic. from India. <i>Cytologia</i> 39: 591-596.
Évaluateurs & contributeurs (5)Expert
assessor
Mirgal, A.
contributor
Prabhu, S. & Gadkari, A.
evaluator
Canteiro, C.
facilitators
Watve, A.
institutions
IUCN SSC Western Ghats Plant Specialist Group

Mirgal, A. 2022. Dipcadi concanense. The IUCN Red List of Threatened Species 2022: e.T177963589A177969107. 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

Observations & statuts

Bibliographie

Note nomenclaturale & synonymesExpert

Note nomenclaturale

TAXREF v18 — INPN/MNHN

Synonymes (2)— redirigent vers cette page

  • Ornithogalum concanense(Dalzell) J.C.Manning & Goldblatt
  • Uropetalon concanenseDalzell

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