Justification of Red List category
This species has a large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (Extent of Occurrence under 20,000 km² combined with a declining or fluctuating range size, habitat extent/quality, or population size and a small number of locations or severe fragmentation). The population size has not been quantified, but it is not believed to approach the thresholds for Vulnerable under the population size criterion (under 10,000 mature individuals with a continuing decline estimated to be over 10% in ten years or three generations, or with a specified population structure). Despite the fact that the population trend appears to be decreasing, the decline is not believed to be sufficiently rapid to approach the thresholds for Vulnerable under the population trend criterion (over 30% decline over ten years or three generations). For these reasons the species is evaluated as Least Concern.
Population justification
The global population size has not been quantified, but this species is described as 'fairly common but patchily distributed' (Stotz et al. 1996). This species is considered to have a high dependency on forest habitat, and tree cover is estimated to have declined by 3.1% within its mapped range over the past three generations (Global Forest Watch 2022, using Hansen et al. [2013] data and methods disclosed therein). It is therefore tentatively suspected that this rate of cover loss may have led to a decline of between 1-19% in the species' population size over the same time frame, with a best estimate of reduction being less than 5%.
Trend justification
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The species is known from at least five localities in Madre de Dios and Balta in south Ucayali, and the río Caimisea, Cuzco, south-east Peru (including Manu National Park) (H. Lloyd in litt. 1999, 2000, Ridgely and Tudor 1994), and is reasonably common on the upper rio Tejo and rio Juruá near Taumaturgo, Acre, extreme west Brazil (Whittaker and Oren 1999).
The species is found in the subcanopy of seasonally flooded swamp or floodplain forest, and terra firme forest, up to 300 m, rarely to 450 m and once to 700 m (Snow 1982, Ridgely and Tudor 1994, Stattersfield et al. 1998, H. Lloyd in litt. 1999, 2000).
Though its lowland forests are relatively intact (Stotz et al. 1996), the region has been subject to selective logging and is being opened up for development, with oil/gas extraction and mining, and associated road building and human colonisation, resulting in further degradation (Dinerstein et al. 1995).
Text account compilers
Rutherford, C.A.
Recommended citation
BirdLife International (2024) Species factsheet: Black-faced Cotinga Conioptilon mcilhennyi. Downloaded from
https://datazone.birdlife.org/species/factsheet/black-faced-cotinga-conioptilon-mcilhennyi on 23/12/2024.
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 23/12/2024.