LC
Red-capped Coua Coua ruficeps



Taxonomy

Taxonomic note

Coua ruficeps and C. olivaceiceps (del Hoyo and Collar 2014) were previously lumped as C. ruficeps following Sibley and Monroe (1990, 1993).

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.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - -

Red List history
Year Category Criteria
2022 Least Concern
2016 Least Concern
2014 Least Concern
2012 Not Recognised
2008 Not Recognised
2004 Not Recognised
2000 Not Recognised
1994 Not Recognised
1988 Not Recognised
Species attributes

Migratory status not a migrant Forest dependency medium
Land-mass type Average mass 180 g
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 154,000 km2
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size unknown - - -
Population trend stable - suspected -
Generation length 5 years - - -

Population justification: The global population size has not been quantified, but the species is reported to be common throughout its range (del Hoyo et al. 1997, Erritzøe et al. 2011), including within Ankarafantisika National Park and other protected areas (Kirwan et al. 2020). Around Ampijoroa it is commoner in disturbed forest, with densities of up to 25.7 individuals/km2 in burned forest compared to 16.7 individuals/km2 in intact forest (Chouteau et al. 2004).

Trend justification: Although tree cover loss within the range is currently estimated at around 25% across three generations (15 years; Global Forest Watch 2021, using Hansen et al. [2013] data and methods disclosed therein), the species persists in degraded habitats and may even benefit from burning (Chouteau et al. 2004, Erritzøe et al. 2011). The population is therefore suspected to be stable in the absence of evidence for any declines or substantial threats. However, repeated monitoring over a longer timeframe is required to determine any lasting population impacts.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Madagascar extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Madagascar Andohahela National Park - Section II
Madagascar Ankarafantsika National Park and Ampijoroa
Madagascar Baly Bay National Park
Madagascar Bemamba Wetland Complex
Madagascar Bemarivo Special Reserve
Madagascar Mahavavy - Kinkony wetlands NPA
Madagascar Maningoza Special Reserve
Madagascar Port-Bergé Wetlands NPA and extension
Madagascar Tsingy de Bemaraha National Park and Strict Nature Reserve
Madagascar Tsingy de Namoroka National Park
Madagascar Wetlands of the Tsiribihina delta and upper Tsiribihina river

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Artificial/Terrestrial Subtropical/Tropical Heavily Degraded Former Forest suitable resident
Forest Subtropical/Tropical Dry suitable resident
Forest Subtropical/Tropical Moist Lowland suitable resident
Shrubland Subtropical/Tropical Dry suitable resident
Altitude 0 - 850 m Occasional altitudinal limits  

Recommended citation
BirdLife International (2024) Species factsheet: Red-capped Coua Coua ruficeps. Downloaded from https://datazone.birdlife.org/species/factsheet/red-capped-coua-coua-ruficeps on 23/11/2024.
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 23/11/2024.