• 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
2023	Least Concern
2016	Near Threatened	A2c+3c+4c;B1ab(i,ii,iii,v)
2012	Near Threatened	A2c+3c+4c;B1ab(i,ii,iii,v)
2008	Near Threatened	A2c; A3c; A4c; B1a+b(i,ii,iii,v)
2004	Near Threatened
2000	Lower Risk/Near Threatened
1994	Lower Risk/Near Threatened
1988	Near Threatened

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

	Estimate	Data quality
Extent of Occurrence (breeding/resident)	22,800 km2	medium
Severely fragmented?	no	-

	Estimate	Data quality	Derivation	Year of estimate
Population size	unknown	-	-	-
Population trend	stable	poor	suspected	-
Generation length	2.66 years	-	-	-
Number of subpopulations	10-100	-	-	-
Percentage of mature individuals in largest subpopulation	1-89%	-	-	-

Population justification: The global population size has not been quantified, but this species is described as rare, uncommon and local (Schulenberg et al. 2007, Freile and Restall 2018).

Trend justification: The population trend has not been investigated, but the only known threat to the species is the loss and degradation of its habitat. While deforestation in the range was certainly prevalent in the past (Stattersfield et al. 1998), the rate of tree cover loss has been negligible over the past ten years (Global Forest Watch 2022, using Hansen et al. [2013] data and methods disclosed therein). Moreover, its preference for knife-edge ridges likely contributes to protecting it from habitat destruction (C. Witt in litt. 2012). Consequently, in the absence of evidence for any declines or substantial threats, the population is suspected to be stable.

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

Country/Territory	IBA Name
Ecuador	Acanamá-Guashapamba-Aguirre
Ecuador	Bosque Protector Colambo-Yacuri
Ecuador	Cordillera del Cóndor
Ecuador	Montañas de Zapote-Najda
Ecuador	Parque Nacional Podocarpus
Ecuador	Tapichalaca Reserve (Reserva Tapichalaca IBA)
Peru	Cerro Chinguela

Habitat (level 1)	Habitat (level 2)	Importance	Occurrence
Forest	Subtropical/Tropical Moist Montane	major	resident
Altitude	2200 - 3270 m	Occasional altitudinal limits

Threat (level 1)	Threat (level 2)	Impact and Stresses
Agriculture & aquaculture	Annual & perennial non-timber crops - Small-holder farming	Timing		Scope		Severity		Impact
		Past, Likely to Return		Minority (<50%)		Slow, Significant Declines		Past Impact
		Stresses Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture	Livestock farming & ranching - Small-holder grazing, ranching or farming	Timing		Scope		Severity		Impact
		Past, Likely to Return		Minority (<50%)		Slow, Significant Declines		Past Impact
		Stresses Ecosystem degradation, Ecosystem conversion

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Recommended citation
BirdLife International (2024) Species factsheet: Orange-banded Flycatcher Nephelomyias lintoni. Downloaded from https://datazone.birdlife.org/species/factsheet/orange-banded-flycatcher-nephelomyias-lintoni 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.