VU
Chinese Monal Lophophorus lhuysii



Taxonomy

Taxonomic note
Monotypic.

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.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - C2a(ii)

Red List history
Year Category Criteria
2022 Vulnerable C2a(ii)
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
Species attributes

Migratory status not a migrant Forest dependency does not normally occur in forest
Land-mass type continent
Average mass 3,008 g
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 214,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 6000-10000 mature individuals poor estimated 2017
Population trend decreasing poor inferred -
Generation length 8.9 years - - -
Number of subpopulations 1-50 - - -
Percentage of mature individuals in largest subpopulation 100% - - -

Population justification: Using MaxEnt modelling, Wang et al. (2017) predicted that suitable habitats for this species span an area of c. 2,500 km2. However, the model did not account directly for habitat degradation caused by, for example, yak farming (instead relying on proxies such as distance to habitation), thus the total area of suitable habitat may be smaller. Accounting for occupancy, the species' distribution is assumed here to cover 1,500-2,500 km2. Densities of c. 6 birds/km2 were recorded during the National Wildlife Survey of China (1995-2000). Given these counts were made in the non-breeding season, this density is thought to refer to individuals, not mature individuals. The population is therefore estimated here to number 9,000-15,000 individuals, or c. 6,000-10,000 mature individuals.

Trend justification: Overgrazing by wild yak and the collection of its food plants are degrading the species' habitat and leading to disturbance (He et al. 1986, BirdLife International 2001). This, and localised hunting pressure, is inferred to be driving an ongoing decline in the population size, although the likely rate of decline has not been estimated (Wang et al. 2017). In the future, these impacts may be compounded by climate change. Xu et al. (2020) predicted that the species' occupied range will shift to higher latitudes and altitudes under all predicted climate change scenarios tested and in emission scenarios RCP 4.5 and RCP 8.5, to suffer a net loss of 22.0% and 32.6% respectively by the 2050s. How these translate into population size reductions should be closely monitored in the future.


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) Anzihe Nature Reserve
China (mainland) Babso Nature Reserve
China (mainland) Baihe Nature Reserve
China (mainland) Baishui Jiang Nature Reserve
China (mainland) Baishuihe Nature Reserve
China (mainland) Baiyang Nature Reserve
China (mainland) Dazhubao and Dafengding
China (mainland) Fengtongzhai Qiaoqi
China (mainland) Gongga Shan Nature Reserve
China (mainland) Gonjo
China (mainland) Heishuihe Nature Reserve (Dayi)
China (mainland) Huanglongsi Nature Reserve
China (mainland) Jiuding Shan Nature Reserve
China (mainland) Jiuzhaigou Nature Reserve
China (mainland) Labahe Nature Reserve
China (mainland) Liziping Nature Reserve
China (mainland) Longxi-Hongkou Nature Reserve
China (mainland) Markam
China (mainland) Mengbi Shan
China (mainland) Mengtun
China (mainland) Min Shan mountains
China (mainland) Piankou Nature Reserve
China (mainland) Qianfoshan Nature Reserve
China (mainland) Sanjiangyuan Nature Reserve
China (mainland) Sanjiangyuan Nature Reserve
China (mainland) Tangjiahe Nature Reserve
China (mainland) Wahuishan Nature Reserve
China (mainland) Wanglang Nature Reserve
China (mainland) Wolong Nature Reserve
China (mainland) Xiaohegou Nature Reserve
China (mainland) Xiaozhaizigou Nature Reserve
China (mainland) Xuebaoding Nature Reserve
China (mainland) Yele Nature Reserve
China (mainland) Yulong Xueshan Nature Reserve
China (mainland) ZoigĂȘ (Ruo'ergai) Marshes

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Grassland Subtropical/Tropical High Altitude major resident
Shrubland Subtropical/Tropical High Altitude major resident
Altitude 3300 - 4500 m Occasional altitudinal limits 2800 - 4900 m

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Agriculture & aquaculture Livestock farming & ranching - Nomadic grazing Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation
Biological resource use Gathering terrestrial plants - Unintentional effects (species is not the target) Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species disturbance, Ecosystem degradation, Reduced reproductive success
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
Stresses
Species mortality

Utilisation
Purpose Scale
Food - human subsistence, national
Pets/display animals, horticulture international

Recommended citation
BirdLife International (2024) Species factsheet: Chinese Monal Lophophorus lhuysii. Downloaded from https://datazone.birdlife.org/species/factsheet/chinese-monal-lophophorus-lhuysii on 22/12/2024.
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 22/12/2024.