NT
Sichuan Jay Perisoreus internigrans



Taxonomy

Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A., Fishpool, L.D.C., Boesman, P. and Kirwan, G.M. 2016. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 2: Passerines. Lynx Edicions and 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
2022 Near Threatened C2a(ii)
2016 Vulnerable C2a(i)
2012 Vulnerable C2a(i)
2008 Vulnerable C2a(i)
2004 Vulnerable
2000 Vulnerable
1996 Vulnerable
1994 Vulnerable
1988 Threatened
Species attributes

Migratory status not a migrant Forest dependency high
Land-mass type continent
Average mass 102 g
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 193,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 12000-20500, 12000-15000 mature individuals poor estimated 2021
Population trend decreasing poor suspected 2012-2026
Rate of change over the past 10 years/3 generations (longer of the two periods) 1-19% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 1-19% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 1-19% - - -
Generation length 4.6 years - - -
Number of subpopulations 1 - - -
Percentage of mature individuals in largest subpopulation 100% - - -

Population justification: Based on surveys at two sites, Jing et al. (2011) found that P. internigrans occurred at densities of 0.6-1.04 birds/km2, with suggestion that the lower bound of this figure was the most accurate based on the methodology used. This corroborates other reports of the species being rare (Sun et al. 2001). Lu et al. (2012) created a predictive niche-distribution model and estimated the area of suitable habitat in the species' range to be c.60,000 km2, however much of this is fragmented and so tentatively only 50% of suitable habitat is thought to be occupied. Combining these figures, the population size of P. internigrans is estimated at 18,000-31,200 individuals, or 12,000-20,500 mature individuals, with a best estimate of c.12,000-15,000 (accepting the lowest density and the suspicion that the population is suspected to have declined since Lu et al. [2012]).

Trend justification: This species is suspected to be declining at a slow rate, owing to forest loss and fragmentation within its range. Although the former has slowed significantly in the last two decades, the effect of fragmentation is still largely unknown with suggestion that it is impacting breeding productivity and may be causing declines (see Jing et al. 2011). Moreover, Lu et al. (2012) predicted that the range size of the species would contract by 27% (from 60,615 km2 to 44,132 km2) between 2012 and 2050 (using the mean of five scenarios of current climate and 30 of future climate change), equivalent to a rate, if constant, of c.10% over three generations. Given this species' reliance on a relatively narrow habitat type, it is suspected to decline approximately in line with habitat loss.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
China (mainland) extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
China (mainland) Babso Nature Reserve
China (mainland) Ganligahai-Zecha Nature Reserve
China (mainland) Gonjo
China (mainland) Huanglongsi Nature Reserve
China (mainland) Jiuzhaigou Nature Reserve
China (mainland) Jonê
China (mainland) Kasha Hu Nature Reserve
China (mainland) Markam
China (mainland) Mengbi Shan
China (mainland) Mengtun
China (mainland) Min Shan mountains
China (mainland) Sanjiangyuan Nature Reserve
China (mainland) Sanjiangyuan Nature Reserve
China (mainland) Têwo Nature Reserve
China (mainland) Xiaohegou Nature Reserve

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Moist Montane major resident
Altitude 3000 - 4270 m Occasional altitudinal limits  

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 Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Livestock farming & ranching - Agro-industry grazing, ranching or farming Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] Timing Scope Severity Impact
Ongoing Minority (<50%) Rapid Declines Medium Impact: 6
Stresses
Ecosystem degradation
Climate change & severe weather Habitat shifting & alteration Timing Scope Severity Impact
Ongoing Unknown Unknown Unknown
Stresses
Ecosystem degradation

Recommended citation
BirdLife International (2024) Species factsheet: Sichuan Jay Perisoreus internigrans. Downloaded from https://datazone.birdlife.org/species/factsheet/sichuan-jay-perisoreus-internigrans 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.