• 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.

Red List criteria met

Critically Endangered	Endangered	Vulnerable
-	-	C2a(ii)

Red List history

Year	Category	Criteria
2020	Vulnerable	C2a(ii)
2016	Endangered	B1ab(i,ii,iii,v)
2013	Endangered	B1ab(i,ii,iii,v)
2012	Endangered	B1ab(i,ii,iii,v)
2008	Endangered	B1a+b(i,ii,iii,v)
2004	Endangered
2000	Endangered
1996	Endangered
1994	Endangered
1988	Threatened

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

	Estimate	Data quality
Extent of Occurrence (breeding/resident)	10,000 km2	medium
Severely fragmented?	no	-

	Estimate	Data quality	Derivation	Year of estimate
Population size	6000-17000 mature individuals	poor	estimated	2019
Population trend	decreasing	poor	inferred	2014-2024
Rate of change over the past 10 years/3 generations (longer of the two periods)	10-15%	-	-	-
Rate of change over the future 10 years/3 generations (longer of the two periods)	10-15%	-	-	-
Rate of change over the past & future 10 years/3 generations (longer of the two periods)	10-15%	-	-	-
Generation length	3.2 years	-	-	-
Number of subpopulations	1	-	-	-
Percentage of mature individuals in largest subpopulation	100%	-	-	-

Population justification: Surveys carried out in broadleaf forest in Guatemala found a density of 33-93 individuals per km²; based on this density the population in Guatemala was estimated to number 8,250-23,250 individuals (Eisermann et al. 2011a). However, the densities used in this calculation were estimated from surveys at 1,400-1,900 m, where the species is more abundant than at 900-1,300 m, and the density estimates may have been affected by the patchy nature of forest in the survey areas (see Eisermann et al. 2011a). The relative abundance in Mexico was found to be lower; surveys at El Triunfo Biosphere Reserve recorded only 0.84 individuals per km² (Secretaría de Medio Ambiente, Vivienda e Historia Natural 2011, Enríquez et al. 2013, P. Enríquez in litt. 2019). Assuming that the population in Guatemala is much larger than the population in Mexico, the global population is tentatively placed in the band of c.10,000-25,000 individuals. This roughly equates to 6,000-17,000 mature individuals. The map of sightings of this species on eBird (eBird 2019) suggests that the species occurs in either one or two subpopulations. If it were to be considered as two subpopulations, then the largest subpopulation would probably contain significantly greater than 1,000 mature individuals. Unless new information becomes available, the species is precautionarily assumed to occur in only one subpopulation.

Trend justification: The species is thought to be in moderate decline owing to habitat loss, primarily for coffee cultivation. The population trend for this species has not been directly estimated. The rate of habitat loss within the range is placed in the band 10-15% over ten years (K. Eisermann in litt. 2019). The species is precautionarily inferred to undergo a slow population decline.

Country/Territory	Presence	Origin	Resident	Breeding visitor	Non-breeding visitor	Passage migrant
Guatemala	extant	native	yes
Mexico	extant	native	yes

Country/Territory	IBA Name
Guatemala	Atitlan
Guatemala	Santiaguito Volcano
Guatemala	Tacana - Tajumulco
Mexico	El Tacaná
Mexico	El Triunfo

Habitat (level 1)	Habitat (level 2)	Importance	Occurrence
Artificial/Terrestrial	Plantations	suitable	resident
Artificial/Terrestrial	Subtropical/Tropical Heavily Degraded Former Forest	suitable	resident
Forest	Subtropical/Tropical Moist Montane	major	resident
Altitude	1000 - 1700 m	Occasional altitudinal limits	860 - 1900 m

Threat (level 1)	Threat (level 2)	Impact and Stresses
Agriculture & aquaculture	Annual & perennial non-timber crops - Scale Unknown/Unrecorded	Timing		Scope		Severity		Impact
		Ongoing		Majority (50-90%)		Rapid Declines		Medium Impact: 7
		Stresses Ecosystem degradation, Ecosystem conversion
Climate change & severe weather	Storms & flooding	Timing		Scope		Severity		Impact
		Ongoing		Minority (<50%)		Causing/Could cause fluctuations		Low Impact: 5
		Stresses Ecosystem degradation
Energy production & mining	Mining & quarrying	Timing		Scope		Severity		Impact
		Future		Minority (<50%)		Causing/Could cause fluctuations		Low Impact: 3
		Stresses Ecosystem degradation
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 conversion
Residential & commercial development	Housing & urban areas	Timing		Scope		Severity		Impact
		Ongoing		Minority (<50%)		Causing/Could cause fluctuations		Low Impact: 5
		Stresses Ecosystem degradation, Ecosystem conversion

Purpose	Scale
Pets/display animals, horticulture	international

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Recommended citation
BirdLife International (2024) Species factsheet: Azure-rumped Tanager Tangara cabanisi. Downloaded from https://datazone.birdlife.org/species/factsheet/azure-rumped-tanager-tangara-cabanisi 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.