Dipcadi concanense
(Dalzell) Baker
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
- 2022 · v3.1
- Altitude
- 50 – 200 m
- Profondeur
- – m
État de la populationTexte officiel évaluation IUCNExpert
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.
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_3Tourism & recreation areasRapid DeclinesMinority (<50%)Ongoing2_1_3Agro-industry farmingRapid DeclinesMajority (50-90%)Ongoing2_3_2Small-holder grazing, ranching or farmingRapid DeclinesWhole (>90%)Ongoing4_1Roads & railroadsRapid DeclinesMajority (50-90%)Past, Likely to Return5_2_1Intentional use (species is the target)Rapid DeclinesMinority (<50%)Ongoing6_1Recreational activitiesNegligible declinesMinority (<50%)Ongoing3_3Renewable energyUnknownMinority (<50%)Ongoing2_1_2Small-holder farmingSlow, Significant DeclinesMajority (50-90%)Ongoing6_3Work & other activitiesSlow, Significant DeclinesWhole (>90%)Ongoing1_1Housing & urban areasVery Rapid DeclinesMajority (50-90%)Ongoing
+ 3 menaces supplémentaires
Description complète des menacesTexte détaillé évaluation IUCNExpert
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 recommandéesStratégies de conservation IUCNExpert
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)Conservation Actions Classification Scheme — IUCNExpert
1_1Site/area protection1_2Resource & habitat protection2_1Site/area management2_3Habitat & natural process restoration3_1_1Harvest management3_3_2Benign introduction3_4_1Captive breeding/artificial propagation4_1Formal education4_2Training4_3Awareness & communications5_1_1International level5_2Policies and regulations5_3Private sector standards & codes5_4_2National level6_3Market forces6_4Conservation payments6_5Non-monetary values
Stress écologiques (33)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_3Indirect ecosystem effects1_3Indirect ecosystem effects2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_1Species mortality2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance2_2Species disturbance2_3_4Loss of pollinator2_3_4Loss of pollinator2_3_4Loss of pollinator2_3_7Reduced reproductive success
Usage & commerce (2)Use & Trade — IUCNExpert
1Food - humansubsistance12Handicrafts, jewellery, etc.subsistance
Priorités de recherche (12)Research Needed Classification — IUCNExpert
1_2Population size, distribution & trends1_3Life history & ecology1_4Harvest, use & livelihoods1_5Threats1_6Actions2_1Species Action/Recovery Plan2_2Area-based Management Plan2_3Harvest & Trade Management Plan3_1Population trends3_2Harvest level trends3_3Trade trends3_4Habitat trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Royaumes biogéographiques
Indomalayan
Systèmes (terrestre/eau douce/marin)
Terrestrial
Formes de croissance
Forb or HerbGeophyte
Références bibliographiques (11)Sources scientifiques de l'évaluation IUCNExpert
- 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).
- 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.
- Fung, H.C. and Waples, R.S. 2017. Performance of IUCN proxies for generation length. <i>Conservation Biology</i> 31(4): 883-893.
- 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.
- 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.
- Patil, S. 2015. A Note on the Occurrence and Distribution of Dipcadi concanense. <i>Nelumbo</i> 57: 60-63.
- 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.
- 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.
- 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.
- Sakhare, S.S. 1991. Morphotaxonomic studies in Liliaceae genus Dipcadi Medik. species . Department of Botany, Shivaji University, Shivaji University Kolhapur.
- Naik, V. N. 1974. Cytological Studies in Two Species of Dipcadi Medic. from India. <i>Cytologia</i> 39: 591-596.
Évaluateurs & contributeurs (5)Personnes ayant contribué à l'évaluation IUCNExpert
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
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (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).