This species qualifies as Endangered because it occupies a very small, declining area of forest on just one small island. A conservation programme has resulted in it becoming well known and celebrated as the island emblem. Although its population is currently increasing, any relaxation of current conservation efforts or introduction of rats could lead to a rapid decline and reclassification to a higher category of threat.
del Hoyo, J.; Collar, N. J.; Christie, D. A.; Elliott, A.; Fishpool, L. D. C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Barcelona, Spain and Cambridge UK: Lynx Edicions and BirdLife International.
Distribution and populationEunymphicus uvaeensis
32 cm. Crested parakeet with green plumage offset by yellower underparts, bluish wings and tail, dark face mask. Crest comprises about six forward-curling black feathers. Similar spp. Introduced Rainbow Lorikeet Trichoglossus haematodus feeds in flowering trees and has red breast. Voice Nasal hooting, shrieks and chuckles. Hints Pairs seen in forest or forest edge with help from guides from the Association pour la Sauvegarde de la Perruche d'Ouvea.
is restricted to Uvea, New Caledonia (to France)
, where most birds occur in c.20 km2
of forest in the north, although c.60 km2
of habitat remains (Robinet et al.
1996). Earlier population estimates have been alarmingly low, but populations in the north and south of the island are regularly surveyed (six times since 1993) and data show a steady increase in both areas (L. Verfaille in litt.
2007). The population has steadily increased from an estimated c.600 birds in 1993 (Robinet et al.
1996) and 824 birds in 1999 (Primot 1999) to 2,090 birds in 2009 (Barré et al.
2010). Mean population density on Uvea has been estimated at 34 birds/ km2
, with density being highest in the north, where it reaches 57 birds/ km2
(Barré et al.
2010). The introductions to the adjacent island of Lifu in 1925 and 1963 failed (Robinet et al.
1995). Population justification
The population is estimated to number 2,090 mature individuals, roughly equivalent to 3,100-3,200 individuals in total.Trend justification
Barré et al.
(2010) reported the population to have increased by 29% (from 10 birds/ km2
to 34 birds/ km2
) between 1993 and 2009, which equates to a population increase of 34% over three generations.Ecology
It feeds in forest and on crops in adjacent cultivated land. It is restricted to areas of old-growth forest with nesting holes, but highest numbers occur close to gardens with papaya. An average of 2.9 eggs are laid in one or two clutches per year, of which 1.7 chicks fledge, but only 0.75 fledglings survive to 30 days (Robinet et al.
1995, Robinet et al.
, Robinet and Salas 1999). Threats
Primary forest has declined in extent by 30-50% in the last 30 years. There is an ongoing illicit pet trade, mostly for the domestic market (Primot 2000). Nesting holes are cut open to extract the nestlings, rendering them unsuitable for future breeding attempts and a lack of nesting sites is believed to be a limiting factor. However, the continuous presence of local guides is believed to be effectively preventing nest poaching (Barré et al.
2010). The invasion of the island in 1996 by bees, which compete for tree holes, is a significant threat, with 10-16% of known nests being occupied by bees in 2000-2002 (N. Barré in litt.
2003). The native Brown Goshawk Accipiter fasciatus,
and perhaps other predators, are believed to take many juveniles (Robinet et al.
1996, N. Barré in litt.
1999, P. Primot in litt.
1999, Robinet and Salas 1999). Suitable habitat is patchy and fragmented mainly as a result of coconut plantations, which do not afford protection from predation by A. fasciatus
and so act as barriers to dispersal, possibly explaining the lack of recolonisation of suitable habitat in southern Uvea (Robinet et al.
2003). Experimental egg-predation rates were four times higher on Lifu where Black Rat Rattus rattus
occurs (currently absent on Uvea) (Robinet et al.
1998). Competition with the introduced Rainbow Lorikeet Trichoglossus haematodus
is possible, however this species is restricted to open habitats and coconut plantations along the coast where Uvea parakeet does not breed and is therefore doubtful, except for introduced papaya which is favoured by both species (L. Verfaille in litt.
2007). Conservation Actions Underway
CITES Appendix I and II. The Association for the Protection of the Ouvéa Parakeet (ASPO) was created in 1993 with mostly local members. the ASPO initiatied a long-term study of the biology and ecology of the species as a basis for two recovery plans (1997-2002 and 2003-2008). Forest loss is being addressed through community awareness programmes and trials to mitigate habitat degradation and improve forest quality, particularly with regard to nest-sites. Ten guides are employed, who, amongst other duties, locate nests. Illegal trade is being successfully tackled by increased awareness and law enforcement. A captive-breeding programme has been discussed but not yet started, with the species occuring only in small numbers in captivity with very limited breeding success (Robinet 1996). A translocation programme to restock the south of Uvea was initiated in 1998, and this population now stands at 82 individuals (Primot 1999). The need to control predators established on Uvea is being investigated and measures to minimise the chance of colonisation by rats are being strengthened (Robinet and Salas 1997, P. Primot in litt.
1999, Primot 2000, L. Verfaille in litt.
2007). An updated Recovery Plan was produced in 2003, recommending amongst other things that the translocation program be cancelled, as the population is considered viable and will grow naturally; this Recovery plan has been accepted by the local native authorities (N. Barré in litt.
2003, Anon 2004). Uvea has been classified as an IBA, but a management plan and a protection programme involving communities still needs to be established (Spaggiari et al.
2007). SCO obtained funds from the British Birdwatching Fair to build and test PCV artificial nests them after the failure of the wooden nest trails. ASPO staff destroyed or removed 187 bee colonies during 2002-2008 (L. Verfaille in litt.
2007, Barré et al.
2010). The continuous presence of local guides is believed to be effectively preventing nest poaching (Barré et al.
2010).Conservation Actions Proposed
Continue population monitoring (Primot 2000). Research interactions with Trichoglossus haematodus.
Investigate non-usage of artificial nest-sites. Review and strengthen measures reducing the risk of rat colonisation. Assess progress and update plans for translocations. Review and update all aspects of Action Plan. Maintain momentum of community and island awareness and involvement (Robinet and Salas 1997). Establish an IBA project on Uvea and fund a protection programme (N. Barré in litt. 2003). Initiate a captive breeding programme to support future reintroductions.
Anon. 2004. Un exemple de gestion concertÃ©e avec les coutumiers: la perruche d'OuvÃ©a. Bilan du second sÃ©minaire d'octobre 2003. CEPA Magazine: 10-12.
BarrÃ©, N.; Theuerkauf, J.; Verfaille, L.; Primot, P.; SaoumoÃ©, M. 2010. Exponential population increase in the endangered OuvÃ©a Parakeet (Eunymphicus uvaeensis after community-based protection from nest poaching. Journal of Ornithology 151(3): 695-701.
Juniper, T.; Parr, M. 1998. Parrots: a guide to the parrots of the world. Pica Press, Robertsbridge, UK.
Primot, P. 1999. Rapport d'activite 1999.
Robinet, O.; Barre, N.; Salas, M. 1996. Population estimate for the Ouvea Parakeet Eunymphicus cornutus uvaeensis: its present range and implications for conservation. Emu 96: 151-157.
Robinet, O.; Beugnet, F.; Dulieu, D.; Chardonnet, P. 1995. The OuvÃ©a Parakeet---state of knowledge and conservation status. Oryx 29: 143-150.
Robinet, O.; Bretagnolle, V.; Clout, M. 2003. Activity patterns, habitat use, foraging behaviour and food selection of the OuvÃ©a Parakeet (Eunymphicus cornutus uvaeensis). Emu 103: 71-80.
Robinet, O.; Craig, J. L.; Chardonnet, L. 1998. Impact of rat species in Ouvea and Lifou (Loyalty Islands) and their consequences for conserving the endangered Ouvea Parakeet. Biological Conservation 86: 223-232.
Robinet, O.; Salas, M. 1997. The Ouvea Parakeet recovery plan (1997-2002).
Robinet, O.; Salas, M. 1999. Reproductive biology of the endangered Ouvea Parakeet Eunymphicus cornutus uvaeensis. Ibis 141: 660-669.
Spaggiari, J.; Chartendrault, V.; BarrÃ©, N. 2007. Zones importantes pour la conservation des oiseaux de Nouvelle-CalÃ©donie. SociÃ©tÃ© calÃ©donienne d'ornithologie, NoumÃ©a, N.C.
Further web sources of information
Alliance for Zero Extinction (AZE) species/site profile. This species has been identified as an AZE trigger due to its IUCN Red List status and limited range.
Click here for more information about the Alliance for Zero Extinction (AZE)
Explore HBW Alive for further information on this species
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Text account compilers
Derhé, M., Dutson, G., Ekstrom, J., Harding, M., Mahood, S.
Barré, N., Primot, P., Robinet, O., Spaggiari, J., Verfaille, L.
BirdLife International (2015) Species factsheet: Eunymphicus uvaeensis. Downloaded from
http://www.birdlife.org on 28/02/2015.
Recommended citation for factsheets for more than one species: BirdLife International (2015) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 28/02/2015.
This information is based upon, and updates, the information published in BirdLife International (2000)
Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004)
Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.
To provide new information to update this factsheet or to correct any errors, please email BirdLife
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