• Summary
• Text account
• Data table and detailed info
• Distribution map
• Reference and further resources

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.

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

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

	Estimate	Data quality
Extent of Occurrence (breeding/resident)	560,000 km2	medium
Severely fragmented?	no	-

	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	Presence	Origin	Resident	Breeding visitor	Non-breeding visitor	Passage migrant
Brazil	extant	native	yes

Country/Territory	IBA Name
Brazil	Estação Ecológica de Juréia-Itatins
Brazil	Ilhéus / Itabuna

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

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 23/11/2024.
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.