LC
Painted Stork Mycteria leucocephala



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
- - -

Red List history
Year Category Criteria
2023 Least Concern
2016 Near Threatened A2bcd+3bcd+4bcd
2012 Near Threatened A2bcd+3bcd+4bcd
2008 Near Threatened A2b,c,d; A3b,c,d; A4b,c,d
2006 Near Threatened
2004 Near Threatened
2000 Lower Risk/Near Threatened
1994 Lower Risk/Near Threatened
1988 Lower Risk/Least Concern
Species attributes

Migratory status not a migrant Forest dependency does not normally occur in forest
Land-mass type continent
shelf island
Average mass 3,180 g
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 8,700,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 20000-60000 mature individuals poor suspected 2023
Population trend increasing poor inferred 2004-2029
Generation length 10 years - - -
Number of subpopulations 1-2,1 - - -
Percentage of mature individuals in largest subpopulation 100% - - -

Population justification: The population size is not well known. Perennou et al. (1994) estimated populations of 15,000 individuals in South Asia, and 'fewer than 10,000 individuals' in South-East Asia, with an estimated global total of 15,000-25,000 individuals. Wetlands International (2022) now estimate 25,000 individuals in South Asia (although there is little indication that this more than arbitrary) and retain the estimate of 5,000-10,000 in South-East Asia between 1987 and 1990. Few additional data are available from India, however a report of 4,000 nesting birds at a single location (Veerapuram Village) on the Andhra Pradesh-Karnataka border (V. Santharam in litt. 2023) suggests that the estimate for South Asia from Wetlands International (2022) may be pessimistic. A wider bound of 15,000-50,000 is therefore used here. There is also additional empirical evidence to suggest that the South-East Asia estimate used by Wetlands International (2022) is too small; for example, more than 3,000 pairs (thus 6,000 mature individuals) were counted in Cambodia in 2021 (WCS unpublished data). Consequently, it is probable that the total number of birds (including non-breeding individuals) in South-East Asia is now substantially more than 7,000, and may even exceed 10,000. In the absence of other data, the values collated here are accepted, albeit with low confidence. Thus, the global population is suspected to number somewhere in a broad bracket of 20,000-60,000 mature individuals. Better data, especially from South Asia, where this species is not confined to wetland habitats, but also uses farmland and agricultural landscapes, should be a priority for future research.

Trend justification: Although numbers counted fluctuate annually (largely in response to observer effort/coverage, as well as annual shifts in distribution), numbers counted in the Asian Waterbird Census show no obvious trend (Li et al. 2009, Kar et al. 2018). Data (International Wetlands Census) from Cambodia and Thailand (see Langendoen et al. 2021) show an increase in population size for 2011-2020 (1.249) and 2002-2020 (1.0436), leading Wetlands International (2022) to regard the South-East Asian subpopulation to be increasing overall. Although the population in Malaysia (centred around Kuala Lumpur) is estimated to be increasing exponentially (Zakaria and Nor 2019), this is considered feral (Puan et al. 2020, MNS Bird Conservation Council 2021).
The trend of the South Asian population is uncertain, with no empirical trend from Wetlands International since. However, in northern India there has been no evidence for recent declines (G. Sundar in litt. 2016) and numbers counted and published via the Asian Waterbird Census have shown no obvious trend (Wetlands International South Asia 2020). In Kerala, the last two decades has seen a large influx of the species into wetlands, where they are now breeding (e.g. Moses 2015); and recent trend data from Keoladeo National Park show signs of population recovery (Dwevedi et al. 2021). There are, however, some reports of local declines in Maharashtra (G. Jathar in litt. 2023). It is acknowledged that these sources do not cover every facet of this species' conservation status, exhibiting a particular bias to wetland habitats (to which this species is not confined, being readily found in agricultural landscapes: eBird 2023, G. Sundar in litt. 2023). Nonetheless, they are suspected of being representative of broader global trends, and the noted range expansions in both South and South-East Asia indicate genuine population recovery throughout. Consequently, the global population is inferred to be slowly increasing.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Bangladesh extant native yes
Cambodia extant native yes
China (mainland) extant vagrant yes
India extant native yes
Laos extant native yes
Malaysia extant introduced yes
Myanmar extant native yes
Nepal extant native yes
Pakistan extant native yes
Singapore extant introduced yes
Sri Lanka extant native yes
Thailand extant native yes
Vietnam extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Cambodia Boeung Chhmar / Moat Khla
Cambodia Preah Net Preah / Kra Lanh / Pourk
Cambodia Prek Toal
India Bhashkarpara
India Harike Lake Bird Sanctuary
India Rangananthittu Bird Sanctuary
India Tiruppadaimarudur Conservation Reserve
India Wild Ass Wildlife Sanctuary
Myanmar Gulf of Mottama
Nepal Barandabhar forests and wetlands
Nepal Bardia National Park
Nepal Chitwan National Park
Nepal Farmlands in Lumbini area
Nepal Koshi Tappu Wildlife Reserve and Koshi Barrage
Nepal Sukla Phanta Wildlife Reserve
Thailand Inner Gulf of Thailand
Thailand Lower Central Basin
Vietnam U Minh Thuong

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Artificial/Aquatic & Marine Artificial/Aquatic - Aquaculture Ponds major resident
Artificial/Aquatic & Marine Artificial/Aquatic - Canals and Drainage Channels, Ditches suitable unset
Artificial/Aquatic & Marine Artificial/Aquatic - Irrigated Land (includes irrigation channels) suitable unset
Artificial/Aquatic & Marine Artificial/Aquatic - Ponds (below 8ha) major resident
Artificial/Aquatic & Marine Artificial/Aquatic - Salt Exploitation Sites suitable resident
Artificial/Aquatic & Marine Artificial/Aquatic - Seasonally Flooded Agricultural Land major resident
Artificial/Aquatic & Marine Artificial/Aquatic - Wastewater Treatment Areas suitable resident
Artificial/Aquatic & Marine Artificial/Aquatic - Water Storage Areas (over 8ha) suitable resident
Grassland Subtropical/Tropical Seasonally Wet/Flooded major resident
Marine Coastal/Supratidal Coastal Brackish/Saline Lagoons/Marine Lakes suitable resident
Wetlands (inland) Bogs, Marshes, Swamps, Fens, Peatlands major resident
Wetlands (inland) Permanent Freshwater Lakes (over 8ha) major resident
Wetlands (inland) Permanent Freshwater Marshes/Pools (under 8ha) major resident
Wetlands (inland) Permanent Rivers/Streams/Creeks (includes waterfalls) major resident
Wetlands (inland) Seasonal/Intermittent Freshwater Lakes (over 8ha) major resident
Wetlands (inland) Seasonal/Intermittent Freshwater Marshes/Pools (under 8ha) major resident
Wetlands (inland) Seasonal/Intermittent/Irregular Rivers/Streams/Creeks major resident
Wetlands (inland) Shrub Dominated Wetlands suitable resident
Altitude 0 - 500 m Occasional altitudinal limits  

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Biological resource use Hunting & trapping terrestrial animals - Intentional use (species is the target) Timing Scope Severity Impact
Past, Likely to Return Minority (<50%) Slow, Significant Declines Past Impact
Stresses
Species disturbance, Species mortality
Human intrusions & disturbance Work & other activities Timing Scope Severity Impact
Ongoing Minority (<50%) No decline Low Impact: 4
Stresses
Species disturbance
Natural system modifications Dams & water management/use - Abstraction of surface water (domestic use) Timing Scope Severity Impact
Ongoing Majority (50-90%) No decline Low Impact: 5
Stresses
Ecosystem degradation
Pollution Agricultural & forestry effluents - Type Unknown/Unrecorded Timing Scope Severity Impact
Ongoing Majority (50-90%) No decline Low Impact: 5
Stresses
Ecosystem degradation

Utilisation
Purpose Scale
Food - human subsistence, national

Recommended citation
BirdLife International (2024) Species factsheet: Painted Stork Mycteria leucocephala. Downloaded from https://datazone.birdlife.org/species/factsheet/painted-stork-mycteria-leucocephala on 23/12/2024.
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 23/12/2024.