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.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2023 | Least Concern | |
2016 | Vulnerable | C2a(i) |
2013 | Vulnerable | C2a(i) |
2012 | Vulnerable | C2a(i) |
2008 | Vulnerable | C2a(i) |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Threatened |
Migratory status | altitudinal migrant | Forest dependency | medium |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 170,000 km2 | medium |
Severely fragmented? | yes | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | decreasing | poor | suspected | - |
Generation length | 8.6 years | - | - | - |
Number of subpopulations | 2-100 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The population has not been accurately quantified although a broad stroke modelling exercise identified c.80,000 km2 of suitable habitat (Bagaria et al. 2021), much of which is remote and beyond the reach of direct human impact. Although not estimated therefore, the population is likely to exceed 10,000 mature individuals.
Trend justification: This species is suspected to be declining slowly. Habitat loss and hunting were previously considered major threats to this species (BirdLife International 2001) but the vast majority of this species' range is remote and inaccessible such that these threats are probably highly localised and unlikely to be causing notable reductions in the global population size. Recent bioclimatic and species distribution modelling (Bagaria et al. 2021) suggested the species may lose c.90% of its habitat by 2070 according to RCP 4.5 and 8.5 scenarios. However, the input data for the present species were sparse and the model therefore relied on species clustering (i.e. the data are not species-specific). Consequently, the species is precautionarily suspected of experiencing ongoing declines because of climate change impacts, although the rate is not estimated.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
China (mainland) | extant | native | yes | |||
India | extant | native | yes | |||
Myanmar | extant | native | yes |
Country/Territory | IBA Name |
---|---|
China (mainland) | Biluo Xueshan |
China (mainland) | Dulong Jiang River Valley |
China (mainland) | Gaoligong Shan Nature Reserve (southern section) |
China (mainland) | Lhakhang |
China (mainland) | Meili Xueshan |
China (mainland) | Yarlung Zangbo Daxiagu Nature Reserve |
China (mainland) | ZayĆ¼ |
India | Dibang Wildlife Sanctuary |
India | Koloriang - Sarli - Damin area |
India | Magu Thingbu |
India | Mechuka - Tato |
India | Monigong - Jorgging - Tuting |
India | Nacho - Limeking - Taksing - Majha |
India | Nafra - Lada area |
India | Thungri - Chaglang - Poshingla Maji, Basti and Liak area |
Myanmar | Hkakaborazi |
Myanmar | Hponkanrazi |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Temperate | major | resident |
Grassland | Subtropical/Tropical High Altitude | suitable | resident |
Shrubland | Temperate | major | resident |
Altitude | 3000 - 4200 m | Occasional altitudinal limits | (min) 2000 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Future | Whole (>90%) | Unknown | Unknown | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Sclater's Monal Lophophorus sclateri. Downloaded from
https://datazone.birdlife.org/species/factsheet/sclaters-monal-lophophorus-sclateri on 22/11/2024.
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 22/11/2024.