NT
Mountain Hawk-eagle Nisaetus nipalensis



Taxonomy

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.

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

Red List history
Year Category Criteria
2021 Near Threatened A3cd+4cd
2016 Least Concern
2012 Least Concern
2009 Least Concern
2008 Least Concern
2004 Least Concern
2000 Lower Risk/Least Concern
1994 Lower Risk/Least Concern
1988 Lower Risk/Least Concern
Species attributes

Migratory status full migrant Forest dependency high
Land-mass type Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 19,000,000 km2
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 1200-6700 mature individuals poor suspected 2009
Population trend decreasing - inferred 2016-2046
Rate of change over the past 10 years/3 generations (longer of the two periods) 5-15% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 15-25% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 15-25% - - -
Generation length 9.93 years - - -

Population justification: Ferguson-Lees and Christie (2001) estimated the population to be 1,001-10,000 individuals, but thought that it was most likely nearer the latter figure. This is roughly equivalent to 670-6,700 mature individuals. The Japanese population is estimated to be c. 1,800 individuals (Asai et al. 2006), equivalent to c.1,200 mature individuals. In the absence of data from other parts of its range, the global population is placed in the band 1,200-6,700 mature individuals.

Trend justification: The population is likely to be declining owing to deforestation (Ferguson-Lees and Christie 2001). During 2001-2020, 7.5% of forest cover was lost across this species’s range (Global Forest Watch 2021), equating to a loss of 11.5% over three generations (29.79 years [Bird et al. 2020]). During 2016-2020, 2.8% of forest cover was lost (Global Forest Watch 2021), equivalent to 19.7% when projected forward over three generations. This species is highly forest dependent (Ferguson-Lees and Christie 2001), therefore it is suspected to be declining at a similar rate to forest loss, although it may be tolerant of a certain level of disturbance and habitat fragmentation (Inskipp et al. 2016). In some parts of its range the species is under additional threats, such as hunting for its feathers (Taiban et al. 2019), electrocution and persecution due to poultry theft (T. R. Subedi, S. Gurung, H. S. Baral, S. Thomsett, R. Buij and M. Virani in litt. 2021), therefore the rate of decline may be greater in these areas.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Bhutan extant native yes
Cambodia extant native yes
China (mainland) extant native yes
Hong Kong (China) extant vagrant
India extant native yes
Japan extant native yes
Laos extant native yes
Mongolia extant vagrant
Myanmar extant native yes
Nepal extant native yes
Pakistan extant native yes
Russia extant native yes
Russia (Asian) extant native yes
South Korea extant vagrant
Sri Lanka extant native yes
Taiwan, China extant native yes
Thailand extant native yes
Vietnam extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Moist Lowland suitable resident
Forest Subtropical/Tropical Moist Montane suitable resident
Forest Temperate major resident
Altitude 600 - 4000 m Occasional altitudinal limits (min) 200 m

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Agriculture & aquaculture Annual & perennial non-timber crops - Agro-industry farming Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Annual & perennial non-timber crops - Small-holder farming Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Hunting & trapping terrestrial animals - Intentional use (species is the target) Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species mortality
Biological resource use Hunting & trapping terrestrial animals - Persecution/control Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species mortality
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
Invasive and other problematic species, genes & diseases Viral/prion-induced diseases - Avian Influenza Virus (H5N1 subtype) Timing Scope Severity Impact
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Species mortality
Transportation & service corridors Utility & service lines Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species mortality

Utilisation
Purpose Scale
Pets/display animals, horticulture international

Recommended citation
BirdLife International (2024) Species factsheet: Mountain Hawk-eagle Nisaetus nipalensis. Downloaded from https://datazone.birdlife.org/species/factsheet/mountain-hawk-eagle-nisaetus-nipalensis on 21/12/2024.
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 21/12/2024.