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 | Near Threatened | C2a(ii) |
2016 | Vulnerable | B1ab(ii,iii,iv,v);C2a(i) |
2013 | Vulnerable | B1ab(ii,iii,iv,v);C2a(i) |
2012 | Vulnerable | B1ab(ii,iii,iv,v);C2a(i) |
2008 | Vulnerable | B1a+b(ii,iii,iv,v); C2a(i) |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
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) | 28,500 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 2500-20000, 2500-9999 mature individuals | poor | inferred | 2018 |
Population trend | decreasing | poor | suspected | 2006-2024 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 1-9% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 1-9% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 1-9% | - | - | - |
Generation length | 5.95 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The density of this species has not previously been estimated. Other Polyplectron have been recorded at densities of 3.74 birds/km2 (P. katsumatae; Gao 1998) and 4.33 calling males/km2 (P. germaini; Nguyen et al. 2018). Similar densities (spanning c.2.5-8.5 mature individuals/km2) are inferred for this species. In 2018, Savini et al. (2021) estimated the area of suitable habitat for this species as c.5,600 km2 using computation analysis of forest patches larger than 40 km2. Assuming approximately c.20-40% of suitable habitat is occupied, the population is inferred to number c.2,500-20,000 mature individuals, with a precautionary best estimate of 2,500-9,999.
Trend justification: Including only patches >40 km2 in their analysis, Savini et al. (2021) estimated a minor c.2% contraction in suitable habitat between 2000 and 2018, while Global Forest Watch (2022) indicates a similar reduction of c.3.1% forest loss over three generations (18 years; Bird et al. 2020) between 2003 and 2021. As a highly forest-dependent species, these losses are suspected of causing proportional population size impacts. The majority of these losses are at the species' lowest altitudinal limits, with higher elevation forest remaining intact. This species may be impacted by disturbances caused by roads linking hill stations and, more locally, by some moderate hunting pressures. It is suspected to be declining at an ongoing rate of 1-9% over three generation time periods.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Malaysia | extant | native | yes | |||
Thailand | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Malaysia | Bintang Range |
Malaysia | Central Titiwangsa Range |
Malaysia | Krau Wildlife Reserve |
Malaysia | Selangor Heritage Park |
Malaysia | Taman Negara National Park |
Thailand | Hala Sector, Hala-Bala Wildlife Sanctuary and Bang Lang National Park |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 820 - 1800 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Agro-industry farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Residential & commercial development | Commercial & industrial areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Transportation & service corridors | Roads & railroads | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence |
Recommended citation
BirdLife International (2024) Species factsheet: Mountain Peacock-Pheasant Polyplectron inopinatum. Downloaded from
https://datazone.birdlife.org/species/factsheet/mountain-peacock-pheasant-polyplectron-inopinatum on 23/12/2024.
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 23/12/2024.