Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | C2a(ii) |
Year | Category | Criteria |
---|---|---|
2024 | Vulnerable | C2a(ii) |
2016 | Vulnerable | C2a(ii) |
2013 | Vulnerable | B1ab(ii,iii,v);C2a(ii) |
2012 | Vulnerable | B1ab(ii,iii,v);C2a(ii) |
2009 | Vulnerable | B1a+b(ii,iii,v); C2a(ii) |
2008 | Endangered | |
2004 | Endangered | |
2000 | Endangered | |
1996 | Vulnerable | |
1994 | Not Recognised | |
1988 | Not Recognised |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 10,400 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 5000-8000 mature individuals | good | estimated | 2012 |
Population trend | decreasing | poor | inferred | - |
Generation length | 6.37 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The species is described as localised and uncommon or rare (Dutson 2011). During surveys in 2003-2006, the species was recorded on 57% of the massifs in the northern province, 42% of the massifs in the southern province, and was locally common in the central part of the main dividing range (Mé Maoya Massif, Moindou-Farino area, Poindimié-Ponérihouen area) (Chartendrault and Barré 2005, 2006, Legault et al. 2011). Its numbers were poorly known prior to 2006 (Chartendrault and Barré 2005, 2006) with only two independent population estimates of 1,000-3,000 birds (Ekstrom et al. 2000) and 720 pairs (N. Barré in litt. 1999), respectively. A more recent study using distance sampling density surveys, observation records, and ecological niche modelling indicates that its distribution extends over 3,482 km2 and estimates that the population numbers 8,690 (7,934-9,445) birds (Legault et al. 2013b). This figure likely overestimates the population size due to the amount of forest cover used in this estimate, but the total population size is thought to number at least 5,000 mature individuals (V. Chartendault in litt. 2007). As such, it is here placed in the range 5,000-8,000 mature individuals.
Trend justification: The species appears to have declined since the 1880s when it was reported from all forested areas. Its range has been considerably reduced on Mt Panié, and is restricted to the north-western part of the Panié massif (Ekstrom et al. 2000, J. Theuerkauf in litt. 2012). In more recent years, densities in Riviere Bleue Provincial Park have been stable (Y. Létocart in litt. 1999), reaching approximately 21 (15-30) birds/km2 in 2008 (Legault et al. 2013a).
Forest loss detected by remote sensing data is minimal within the species' range (<1% in three generations), (Global Forest Watch 2024, using data from Hansen et al. [2013] and methods disclosed therein), however this does not take into account additional impacts of degradation. Given this species' dependence on large, mature tracts of forest it is thought to be affected by habitat degradation as a result of mining, logging, fire (Legault et al. 2012) and perhaps introduced Rusa deer Rusa timorensis (Chartendrault and Barré 2005, 2006). Black rats occasionally prey on Horned Parakeet nests (Gula et al. 2010) which may be driving additional declines. Additionally, particularly wet (La Niña) years have been shown to reduce breeding success (J. Theuerkauf et al. in litt. 2011). Future declines are also expected based on future climate projections, with currently suitable habitat expected to decline in quality and become increasingly fragmented (Legault et al. 2013b).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
New Caledonia (to France) | extant | native | yes |
Country/Territory | IBA Name |
---|---|
New Caledonia (to France) | Aoupinié |
New Caledonia (to France) | Boulinda |
New Caledonia (to France) | Bwa Opana |
New Caledonia (to France) | Entre les monts Nakada et Do |
New Caledonia (to France) | Entre les monts Rembaï et Canala |
New Caledonia (to France) | Entre Table Unio et Farino |
New Caledonia (to France) | Forêt Plate |
New Caledonia (to France) | Goro Até et haute vallée de la rivière Tchamba |
New Caledonia (to France) | Goro Jé et haute vallée de la rivière Amoa |
New Caledonia (to France) | Hautes vallées des rivières Néaoua, Koua et Kouaoua |
New Caledonia (to France) | Massif des Lèvres |
New Caledonia (to France) | Massif du Mé Kanin, Sphinx et Arago |
New Caledonia (to France) | Massif du Panié |
New Caledonia (to France) | Massifs du Grand Sud - entre le mont Humboldt et la rivière Bleue |
New Caledonia (to France) | Mé Maoya |
New Caledonia (to France) | Prokoméo |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Forest | Subtropical/Tropical Moist Montane | major | resident |
Savanna | Moist | suitable | resident |
Shrubland | Subtropical/Tropical Moist | suitable | resident |
Altitude | 0 - 1500 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Future | Whole (>90%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Rattus rattus | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Rusa timorensis | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Viral/prion-induced diseases - Beak and Feather Disease Virus (BFDV) | Timing | Scope | Severity | Impact | ||||
Future | Unknown | Unknown | Unknown | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | national, international |
Recommended citation
BirdLife International (2024) Species factsheet: Horned Parakeet Eunymphicus cornutus. Downloaded from
https://datazone.birdlife.org/species/factsheet/horned-parakeet-eunymphicus-cornutus on 08/12/2024.
Recommended citation for factsheets for more than one species: BirdLife International (2024) IUCN Red List for birds. Downloaded from
https://datazone.birdlife.org/species/search on 08/12/2024.