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 |
---|---|---|
2024 | Near Threatened | A2cd+3cd+4cd |
2016 | Near Threatened | C1+2a(i) |
2012 | Near Threatened | C1+2a(i) |
2008 | Vulnerable | C2a(i) |
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) | 518,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 50000-250000 mature individuals | medium | estimated | 2023 |
Population trend | decreasing | medium | suspected | 2017-2030 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 10-29% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 10-29% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 10-29% | - | - | - |
Generation length | 4.5 years | - | - | - |
Number of subpopulations | 10-100 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: Population density variably estimated at 0.31 individuals/km2 in parts of Guangdong and Zhejiang (Zheng Guangmei and Wang Qishan 1998) to 8-10 individuals/km2 at 900-1,200 m in Longqishan (Mt. Longqi) at Jiangle in Fujian (He et al. 2007). This variation can partly be explained by altitudinal variation, but also likely differences in habitat and observer effort.
The area of remaining suitable habitat in 2018 was estimated as c.170,000 km2 by Savini et al. (2021), who removed from their analysis any forest patch <40 km2. A similar analysis using different underlying data found a very similar total suitable habitat area of c.187,000 km2 in 2020 (data from Jung et al. [2020], analysed using sRedList [2023]), although this did not apply the removal of smaller habitat patches of Savini et al. (2021). Combining density and habitat data suggests that the population size of this species numbers in the high tens, if not hundreds, of thousands. It is therefore placed in the broad band of 50,000-250,000 mature individuals.
Trend justification: The main threats to this species are habitat loss and degradation, and more locally trapping. Forest cover loss over the past three generations (14 years: 2009-2023) has been equivalent to c.9-11% (Global Forest Watch 2024, based on data from Hansen et al. [2013] and methods therein). In a similar analysis using different methods, Savini et al. (2021) estimated that between 2000 and 2018 this species lost approximately 19.4% of its habitat, equivalent to a rate of c.14-15% over three generations. Additionally, forest blocks have become significantly more isolated in the last two decades, with the number of habitat patches increasing from 116 to 156 between 2000 and 2018, and the average size of these patches nearly halving from 1,830 to 1,097 km2 (Savini et al. 2021). Given their relatively low density, fragmentation is considered to have a particularly acute effect on Galliformes and, when compounding hunting impacts are also taken into account, past rates of decline are suspected at 10-29% over the past three generations. Very little (<5%: Savini et al. 2021) of this species' range lies in protected areas, such that future declines are suspected to occur at the same rate without greater conservation interventions.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
China (mainland) | extant | native | yes |
Country/Territory | IBA Name |
---|---|
China (mainland) | Chebaling Nature Reserve |
China (mainland) | Daiyun Shan Nature Reserve |
China (mainland) | Daping Shan Nature Reserve |
China (mainland) | Dayao Shan Nature Reserve |
China (mainland) | Gupo Shan |
China (mainland) | Guxiu Nature Reserve |
China (mainland) | Huashuichong Nature Reserve |
China (mainland) | Jiuwan Shan Nature Reserve |
China (mainland) | Maozi Feng |
China (mainland) | Meihua Shan Nature Reserve |
China (mainland) | Nankun Shan Nature Reserve |
China (mainland) | Nanling mountains |
China (mainland) | Niumulin Nature Reserve |
China (mainland) | Sijian Shan Nature Reserve |
China (mainland) | Wanmulin Nature Reserve |
China (mainland) | Wuyi Shan Nature Reserve (Fujian) |
China (mainland) | Xunle Nature Reserve |
China (mainland) | Yuanbao Shan - Gunbei Laoshan |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 500 - 1700 m | Occasional altitudinal limits | 150 - 1900 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - 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 | Unknown | Unknown | Unknown | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Human intrusions & disturbance | Recreational activities | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Residential & commercial development | Tourism & recreation areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
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: Collared Partridge Arborophila gingica. Downloaded from
https://datazone.birdlife.org/species/factsheet/collared-partridge-arborophila-gingica on 20/12/2024.
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 20/12/2024.