Euptilotis neoxenus 

Scope: Global
Language: English

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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Trogoniformes Trogonidae

Scientific Name: Euptilotis neoxenus (Gould, 1838)
Common Name(s):
English Eared Quetzal, Eared Trogon
Taxonomic Source(s): del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.

Assessment Information [top]

Red List Category & Criteria: Least Concern ver 3.1
Year Published: 2017
Date Assessed: 2017-10-01
Assessor(s): BirdLife International
Reviewer(s): Symes, A.
Facilitator/Compiler(s): Benstead, P., Isherwood, I., Sharpe, C.J., Taylor, J., Westrip, J., Wheatley, H.
This species has an extremely large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (extent of occurrence <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 may be moderately small to large, but it is not believed to approach the thresholds for Vulnerable under the population size criterion (<10,000 mature individuals with a continuing decline estimated to be >10% in ten years or three generations, or with a specified population structure). The population trend appears to be stable, and hence the species does not approach the thresholds for Vulnerable under the population trend criterion (>30% decline over ten years or three generations). For these reasons the species is evaluated as Least Concern.

Previously published Red List assessments:

Geographic Range [top]

Range Description:Euptilotis neoxenus occurs almost throughout the mountains of west Mexico, in Sonora, Chihuahua, Sinaloa, Durango, Nayarit, Zacatecas, Jalisco and Michoacán states, and even sporadically within Arizona and New Mexico, USA. Until recently, it was considered very uncommon and locally distributed, but this probably stemmed from a lack of field studies in appropriate areas (Lammertink et al. 1996). Surveys in 1995 showed it to be common in primary habitat, and frequent (including nesting) in disturbed areas and riparian corridors in otherwise largely logged areas (Lammertink et al. 1996). The population is believed to be stable (Lammertink et al. 1996) and a remote-sensing study found that recent forest loss in the species's range was negligible (potentially <1% over three generations; Tracewski et al. 2016).

Countries occurrence:
Mexico; United States
Additional data:
Continuing decline in area of occupancy (AOO):Unknown
Extreme fluctuations in area of occupancy (AOO):NoEstimated extent of occurrence (EOO) - km2:448000
Continuing decline in extent of occurrence (EOO):UnknownExtreme fluctuations in extent of occurrence (EOO):No
Continuing decline in number of locations:Unknown
Extreme fluctuations in the number of locations:NoLower elevation limit (metres):1800
Upper elevation limit (metres):3000
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:Partners in Flight estimated the population to number fewer than 50,000 individuals (A. Panjabi in litt. 2008), thus it is placed in the band 20,000-49,999 individuals here.

Trend Justification:  The population is believed to be stable (Lammertink et al. 1996). Tracewski et. al. (2016) found that recent forest loss in the range of this species was equivalent to <1% over three generations.
Current Population Trend:Stable
Additional data:
Continuing decline of mature individuals:No
Extreme fluctuations:NoPopulation severely fragmented:No
Continuing decline in subpopulations:Unknown
Extreme fluctuations in subpopulations:NoAll individuals in one subpopulation:No

Habitat and Ecology [top]

Habitat and Ecology:This species inhabits montane pine, pine-oak and pine-evergreen forests (del Hoyo et al. 2001). It is found in the upper and middle storeys of forest, particularly along watercourses in canyons, generally at 1,800-3,000 m, being most abundant at 2,100-2,800 m. It tends to nest in riparian corridors where habitat is generally intact. During winter in Mexico, it may move into lush subtropical and tropical evergreen habitat in barrancas and canyons. It feeds on insects, including moths, and fruit, though lizards are fed to nestlings (González-Rojas et al. 2008). Caterpillars and beetles are reportedly fed to its young. Pairs form in April-June, and breeding occurs in June-October, sometimes as early as April. It nests in tree cavities (del Hoyo et al. 2001, González-Rojas et al. 2008).

Continuing decline in area, extent and/or quality of habitat:Unknown
Generation Length (years):7.3
Movement patterns:Not a Migrant

Threats [top]

Major Threat(s): Forest destruction in the region may adversely affect the species through the removal of trees with suitable nesting cavities (Lammertink et al. 1996), a problem compounded by uncertainty over seasonal movements. Competition for cavities may be a limiting factor in breeding success (González-Rojas et al. 2008).

Conservation Actions [top]

Conservation Actions: Conservation Actions Underway
La Michilía Biosphere Reserve is one of the most important sites for the species in Mexico (del Hoyo et al. 2001). This species is on the watch list as part of the State of North America's Birds (North American Bird Conservation Initiative 2016).

Conservation Actions Proposed
Carry out surveys to assess the population size. Monitor population trends through regular surveys. Monitor rates of deforestation throughout its range. Increase the area of suitable habitat with protected status. Conduct research into the species's breeding biology. Study the species's movements and dispersal patterns.

Citation: BirdLife International. 2017. Euptilotis neoxenus. The IUCN Red List of Threatened Species 2017: e.T22682744A118368393. . Downloaded on 22 July 2018.
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