VU
Mrs Hume's Pheasant Syrmaticus humiae



Taxonomy

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(i)

Red List history
Year Category Criteria
2023 Vulnerable C2a(i)
2016 Near Threatened C2a(i)
2012 Near Threatened C2a(i)
2008 Near Threatened C2a(i)
2005 Near Threatened
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 -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 854,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 2500-9999, 7500 mature individuals medium estimated 2022
Population trend decreasing poor inferred 2012-2030
Rate of change over the past 10 years/3 generations (longer of the two periods) 20-29% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 20-29% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 20-29% - - -
Generation length 5.85 years - - -
Number of subpopulations 2-100,50-100 - - -
Percentage of mature individuals in largest subpopulation 1-89% - - -

Population justification: Estimating the population size of this species is difficult due to the inaccessibility of much of its range. The population of nominate humiae was previously suspected to number only 1,000 birds (McGowan and Garson 1995), however based on surveys covering Nagaland, Manipur and Mizoram, Choudhury (2002) estimated the population in India was likely to be c.4,000 individuals. A further c.6,000 individuals were thought to occur in north and east Myanmar (G. Gale and A. Iamsiri in litt. 2005). The population in China is unknown but based on densities at some key sites (see Lu Taichun 1991, Li Xiangtao 1996) the population probably numbers a further 4,000-5,000. The population in north-west Thailand is likely to be small and probably numbers fewer than 500 birds (BirdLife International 2001). Combining these estimates, the number of individuals is likely to be no more than c.15,000 birds, or c.10,000 mature individuals. However, the majority of these estimates were made 2000-2005 and the population has plausibly declined by 20-29% since then (see Population Trend). Consequently, the population estimate is placed in the band 2,500-9,999 mature individuals, with a best estimate of approximately 7,500.

Trend justification: Inferred to be declining due to forest loss and compounding hunting pressures. Recent data indicate that forest loss in this species' range has been moderately rapid. Including only patches >40 km2 in their computational analysis, Savini et al. (2021) estimated a c.19% contraction in suitable habitat between 2000 and 2018, while Global Forest Watch (2022) indicate similar losses of c.17-20% forest loss over three generations (c.18 years; Bird et al. 2020) between 2002 and 2021. This species is largely forest dependent and forest cover losses are thought to be indicative of equivalent reductions in population size while also increasing the accessibility to hunters of the remaining evergreen forest. Hunting is considered to be a key threat to this species, having disappeared from areas of suitable habitat where it lies in close proximity to human habitation. Only c.2% of this species' range is in protected areas (Savini et al. 2021) and consequently both habitat loss and hunting are predicted to continue. The ongoing rate of decline is therefore suspected to be 20-29% over three generations.


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

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
China (mainland) Ailaoshan
China (mainland) Buliuhe Nature Reserve
China (mainland) Cang Shan Er Hai Nature Reserve
China (mainland) Cenwang Laoshan Nature Reserve
China (mainland) Gaoligong Shan Nature Reserve (southern section)
China (mainland) Lingzhan
China (mainland) Longlin-Xilin
China (mainland) Tongbiguan
China (mainland) Wuliangshan
China (mainland) Xishuangbanna
China (mainland) Yachang
China (mainland) Yongde Daxueshan
China (mainland) Yulong Xueshan Nature Reserve
India Ango or Anko Hills
India Blue Mountain (Phawngpui) National Park
India Dzuku Valley
India Fakim Wildlife Sanctuary and Saramati area
India Kailam Wildlife Sanctuary
India Lengteng Wildlife Sanctuary
India Mount Zanibu
India Mount Ziphu
India Murlen National Park
India Pfutsero-Chizami
India Satoi Range
India Shiroi Community Forest
Myanmar Bwe Pa
Myanmar Natmataung (Mount Victoria)
Myanmar Zeihmu Range
Thailand Doi Chiang Dao
Thailand Doi Inthanon
Thailand Doi Suthep-Pui
Thailand Mae Fang
Thailand Mae Lao - Mae Sae

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Dry major resident
Forest Temperate major resident
Shrubland Subtropical/Tropical Dry suitable non-breeding
Shrubland Temperate suitable non-breeding
Altitude 700 - 2800 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 Annual & perennial non-timber crops - Shifting agriculture Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Annual & perennial non-timber crops - Small-holder farming Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Wood & pulp plantations - Scale Unknown/Unrecorded Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
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
Residential & commercial development Commercial & industrial areas Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion

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

Recommended citation
BirdLife International (2024) Species factsheet: Mrs Hume's Pheasant Syrmaticus humiae. Downloaded from https://datazone.birdlife.org/species/factsheet/mrs-humes-pheasant-syrmaticus-humiae on 23/11/2024.
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 23/11/2024.