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 | Near Threatened | A2cd+3cd+4cd |
2012 | Near Threatened | A2cd+3cd+4cd |
2010 | Near Threatened | A2c,d; A3c,d; A4c,d |
2008 | Vulnerable | A2c,d; A3c,d; A4c,d |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 673,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 20000-100000 mature individuals | poor | suspected | 2022 |
Population trend | decreasing | poor | suspected | - |
Generation length | 6.01 years | - | - | - |
Number of subpopulations | 2-50 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The population size of this species has not formerly been estimated, although Brazil (2009) suggested there were <10,000 breeding pairs, while others have suggested there may be as many as 100,000-200,000 birds (J. Fellowes in litt. 2007, He Fen-qi in litt. 2007). Survey data indicate that it can occur at a moderately high density of c.6 individuals/km2 where habitat is most suitable (Ding Ping in litt. 2005). Given the large area of forest in its range (totalling c.250,000 km2; Global Forest Watch 2022, based on Hansen et al. [2013]), the population likely numbers several tens of thousands. It is therefore suspected, somewhat precautionarily, to number 20,000-100,000 mature individuals.
Trend justification: Habitat loss was previously suspected to have caused moderately rapid population declines, however clearance of natural forest has been illegal since 1998. Although localised clearance and hunting does take place, this is thought to be causing very slow population declines at worst. With an increasing prevalence of reforestation schemes in this region of China, it is plausible that the population may even increase over the next few decades as forests mature and become suitable again. Precautionarily, hunting and some localised degradation are suspected of causing slow, but unquantified, declines.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
China (mainland) | extant | native | yes |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Temperate | major | resident |
Altitude | 200 - 1900 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, Unlikely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
|||||||||
Agriculture & aquaculture | Wood & pulp plantations - Scale Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Gathering terrestrial plants - Unintentional effects (species is not the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
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 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Slow, Significant Declines | Past Impact | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Elliot's Pheasant Syrmaticus ellioti. Downloaded from
https://datazone.birdlife.org/species/factsheet/elliots-pheasant-syrmaticus-ellioti 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.