NT
Black-headed Berryeater Carpornis melanocephala



Taxonomy

Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A., Fishpool, L.D.C., Boesman, P. and Kirwan, G.M. 2016. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 2: Passerines. Lynx Edicions and BirdLife International, Barcelona, Spain and Cambridge, UK.
SACC. 2005 and updates. A classification of the bird species of South America. Available at: https://www.museum.lsu.edu/~Remsen/SACCBaseline.htm.

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

Red List history
Year Category Criteria
2022 Near Threatened C1+2a(i)
2016 Vulnerable A2c+3c+4c;B1ab(ii,iii,iv,v);C2a(i)
2012 Vulnerable A2c+3c+4c;B1ab(ii,iii,iv,v);C2a(i)
2008 Vulnerable A2c; A3c; A4c; B1a+b(ii,iii,iv); C2a(i)
2004 Vulnerable
2000 Vulnerable
1996 Vulnerable
1994 Vulnerable
1988 Threatened
Species attributes

Migratory status not a migrant Forest dependency medium
Land-mass type continent
Average mass 64 g
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 560,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 2500-9999 mature individuals poor suspected 2018
Population trend decreasing poor suspected 2016-2029
Rate of change over the past 10 years/3 generations (longer of the two periods) 10-19% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 10-19% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 10-19% - - -
Generation length 4.22 years - - -
Number of subpopulations 5-100 - - -
Percentage of mature individuals in largest subpopulation 1-89% - - -

Population justification: The species is uncommon in Bahia, Minas Geras and Espírito Santo, rare in Rio de Janeiro and restricted to a small site in Pernambuco (per D. M. Lima in litt. 2022). It is suspected that the total population numbers less than 10,000 mature individuals, with up to 1,000 mature individuals in each subpopulation, though it cannot be ruled out that the subpopulation in the Serra de Paranapiacaba may potentially be larger (ICMBio 2018, D. M. Lima in litt. 2022).

Trend justification: The population must have declined significantly, but it remains relatively common locally (Aleixo and Galetti 1997, A. Whittaker in litt. 1999, Develey 2004). It is suspected that declines are ongoing on the basis of deforestation and forest fragmentation. Over three generations (12.7 years), 9% of tree cover is lost within the extant range (Global Forest Watch 2022, using Hansen et al. [2013] data and methods disclosed therein). Given that the species is restricted to primary forest, population declines are likely to exceed the rate of tree cover loss as a consequence of additional forest degradation. Declines are therefore precautionarily placed in the band 10-19% over three generations.


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

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Brazil Estação Ecológica de Juréia-Itatins
Brazil Ilhéus / Itabuna

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Dry suitable resident
Forest Subtropical/Tropical Moist Lowland major resident
Shrubland Subtropical/Tropical Dry suitable resident
Altitude 0 - 800 m Occasional altitudinal limits (max) 300 m

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Biological resource use Gathering terrestrial plants - Unintentional effects (species is not the target) Timing Scope Severity Impact
Ongoing Minority (<50%) Causing/Could cause fluctuations Low Impact: 5
Stresses
Indirect ecosystem effects, Ecosystem degradation
Biological resource use Logging & wood harvesting - Unintentional effects: (large scale) [harvest] Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Natural system modifications Fire & fire suppression - Increase in fire frequency/intensity Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation

Recommended citation
BirdLife International (2024) Species factsheet: Black-headed Berryeater Carpornis melanocephala. Downloaded from https://datazone.birdlife.org/species/factsheet/black-headed-berryeater-carpornis-melanocephala 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.