CR
Masked Finfoot Heliopais personatus



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
C1 A2abcd+3bcd+4abcd; C1+2a(i); D A2abcd+3bcd+4abcd; C1+2a(i); D1

Red List history
Year Category Criteria
2022 Critically Endangered C1
2016 Endangered A2cd+3cd+4cd; C2a(i)
2012 Endangered A2cd+3cd+4cd;C2a(i)
2009 Endangered A2c,d; A3c,d; A4c,d
2008 Vulnerable
2004 Vulnerable
2000 Vulnerable
1996 Vulnerable
1994 Vulnerable
1988 Threatened
Species attributes

Migratory status not a migrant Forest dependency low
Land-mass type continent
Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 1,650,000 km2 medium
Number of locations 7-12 -
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 108-304 mature individuals poor estimated 2020
Population trend decreasing poor estimated 2015-2030
Rate of change over the past 10 years/3 generations (longer of the two periods) 60-79% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 60-79% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 60-79,62% - - -
Generation length 5.1 years - - -
Number of subpopulations 3 - - -
Percentage of mature individuals in largest subpopulation 1-89% - - -

Population justification: The species appears to have declined dramatically and is now known from comparatively few sites, occurring at low densities everywhere. Based on records compiled between 2008 and 2018 for the largest subpopulation in Bangladesh, supplemented with best-guesses derived from published, unpublished and anecdotal information for other sites, the total population is estimated to number 108-304 mature individuals in total (Chowdhury et al. 2020 and references therein). National population estimates include 80-160 mature individuals in the Sundarbans in Bangladesh, 12-64 mature individuals in Cambodia, 12-40 mature individuals in Myanmar, 4-30 mature individuals in Laos, 0-6 mature individuals in Viet Nam and 0-4 mature individuals in India (Chowdhury et al. 2020 and references therein). These values should however be treated with caution, as in parts of the range suitable habitat remains which has not been fully investigated (Chowdhury et al. 2020).

It is here assumed that the species forms several small subpopulations based on its localised distribution across South-East Asia: resident subpopulations in Bangladesh (80-160 mature individuals) and in Myanmar (12-40 mature individuals), and a presumed migratory population breeding in Cambodia, Laos and Viet Nam considered to function as one additional subpopulation of 16-100 mature individuals (Chowdhury et al. 2020).

Trend justification: The species is undergoing very rapid declines throughout its range. Formerly considered widespread across South-East Asia, it has suffered local extinctions in parts of its range, notably in India, Myanmar, Malaysia, Thailand and Indonesia, while the number of recordings in occupied areas has decreased substantially despite intense survey effort (Chowdhury et al. 2020). Habitat conversion is considered to be the main driver of the decline, with riverine systems amongst the most disturbed and most degraded environments in South-East Asia.

A comprehensive survey of the largest known population in Bangladesh observed a 36% decrease in nests over just seven years (Chowdhury et al. 2017). This is equivalent to an estimated one-generation decline rate of 28%, and a projected rate of 48% over two generations and 62% over three generations (15.3 years). Based on the intensity of threats acting on all populations throughout the range and the assembled evidence of similar rapid reduction and disappearance from virtually the whole range, it is considered that this rate is representative for the global population, or probably even too conservative (Chowdhury et al. 2020). As such, it is estimated that the global population is declining at a rate of 60-79% over three generations, and that this rate is expected to continue into the future.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Bangladesh extant native yes
Cambodia extant native yes yes
India possibly extant native yes
Indonesia possibly extant native yes
Laos extant native yes yes
Malaysia possibly extant native yes yes
Myanmar extant native yes
Singapore possibly extant native yes
Thailand possibly extant native yes yes
Vietnam extant native yes yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Bangladesh Sunderbans (East, South, West Wildlife Sanctuaries)
Cambodia Boeung Chhmar / Moat Khla
Cambodia Lomphat
Cambodia Prek Toal
Cambodia Snoul / Keo Sema / O Reang
Cambodia Upper Srepok Catchment
India Dum Duma, Dangori and Kumsong Reserve Forests
India Manabum and Tengapani Reserve Forests
India Sundarbans Biosphere Reserve (National Park)
India Tirap - Burhidihing
India Upper Dihing (East) Complex
Indonesia Batang Gadis
Indonesia Gunung Leuser
Indonesia Kerinci Seblat
Indonesia Pulau Rambut
Indonesia Siak Kecil
Indonesia Way Kambas
Laos Upper Xe Kaman
Laos Xe Kong Plains
Malaysia Belum-Temenggor
Malaysia Central Titiwangsa Range
Malaysia Endau-Rompin
Malaysia Krau Wildlife Reserve
Malaysia Matang coast
Malaysia North-central Selangor coast
Malaysia Sadong-Saribas coast
Malaysia South-east Pahang peat swamp forest
Malaysia Taman Negara National Park
Malaysia Ulu Muda
Myanmar Htamanthi
Myanmar Hukaung Valley
Myanmar Tanai River
Thailand Chaloem Pra Kiet (Pa Phru to Daeng)
Thailand Hala Sector, Hala-Bala Wildlife Sanctuary and Bang Lang National Park
Thailand Huai Kha Khaeng
Thailand Na Muang Krabi
Vietnam Kon Cha Rang
Vietnam Yok Don

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Mangrove Vegetation Above High Tide Level suitable resident
Wetlands (inland) Permanent Freshwater Lakes (over 8ha) suitable resident
Wetlands (inland) Permanent Freshwater Marshes/Pools (under 8ha) suitable resident
Wetlands (inland) Permanent Rivers/Streams/Creeks (includes waterfalls) suitable resident
Altitude 0 - 1220 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 Majority (50-90%) Rapid Declines Medium Impact: 7
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Marine & freshwater aquaculture - Industrial aquaculture Timing Scope Severity Impact
Ongoing Majority (50-90%) Rapid Declines Medium Impact: 7
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Hunting & trapping terrestrial animals - Intentional use (species is the target) Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Reduced reproductive success, Species mortality
Biological resource use Logging & wood harvesting - Unintentional effects: (large scale) [harvest] Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation
Climate change & severe weather Storms & flooding Timing Scope Severity Impact
Future Majority (50-90%) Rapid Declines Low Impact: 5
Stresses
Indirect ecosystem effects, Ecosystem degradation, Reduced reproductive success
Energy production & mining Mining & quarrying Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species disturbance, Ecosystem degradation, Ecosystem conversion
Human intrusions & disturbance Work & other activities Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species disturbance
Natural system modifications Dams & water management/use - Dams (size unknown) Timing Scope Severity Impact
Ongoing Minority (<50%) Rapid Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Pollution Agricultural & forestry effluents - Type Unknown/Unrecorded Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation
Pollution Industrial & military effluents - Type Unknown/Unrecorded Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation
Residential & commercial development Housing & urban areas Timing Scope Severity Impact
Ongoing Minority (<50%) Rapid Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Transportation & service corridors Shipping lanes Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Species disturbance

Utilisation
Purpose Scale
Food - human subsistence, national

Recommended citation
BirdLife International (2024) Species factsheet: Masked Finfoot Heliopais personatus. Downloaded from https://datazone.birdlife.org/species/factsheet/masked-finfoot-heliopais-personatus 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.