VU
Blue-headed Pitta Hydrornis baudii



Taxonomy

Taxonomic note
Hydrornis baudii (del Hoyo and Collar 2016) was previously listed as Pitta baudii.

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
- - A2c+3c+4c

Red List history
Year Category Criteria
2023 Vulnerable A2c+3c+4c
2016 Vulnerable A2c+3c+4c
2012 Vulnerable A2c+3c+4c
2008 Vulnerable A2c; A3c; A4c
2004 Vulnerable
2000 Vulnerable
1994 Lower Risk/Near Threatened
1988 Near Threatened
Species attributes

Migratory status not a migrant Forest dependency medium
Land-mass type shelf island
Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 939,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size unknown poor - -
Population trend decreasing poor inferred 2010-2023
Rate of change over the past 10 years/3 generations (longer of the two periods) 25-35% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 25-35% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 25-35% - - -
Generation length 4.03 years - - -
Number of subpopulations 1-100 - - -

Population justification: The global population size has not been quantified but is believed to be large given the range and frequency of records in suitable habitat. It is a forest-dependent species and within its range the rate of forest conversion to plantations, primarily oil palm, has been very rapid over the past few decades (Global Forest Watch 2023) and as such the population is inferred to be declining. There are recent records from remaining forested areas across the range, however the extent of suitable habitat is now considerably smaller than three generations ago. Where habitat is secure the species continues to be regularly observed (eBird 2023), though observing the species away from protected areas is becoming much more difficult. In most literature, it is described as uncommon to locally common (Mann 2008, Eaton et al. 2021). Nonetheless, surveys are needed to determine a likely population size given the idiosyncrasies in density at different sites.

Trend justification: Determining the rate of population reduction in this species is difficult owing to considerable uncertainty in its true distribution and clear differences in density between sites/areas. For example, at Danum Valley Conservation Area, the species is common and the most readily-encountered pitta species (eBird 2023), but at other sites (e.g. Ulu Tempurung National Park) it is inexplicably absent, despite ostensibly suitable habitat. The species appears to be dependent on large tracts of low-lying, flat forest (even though, where this is present, it is often found in adjacent degraded habitats and on slopes) which have been the most impacted by deforestation.
In the three generations (12.1 years; Bird et al. 2020) to 2021, forest cover in this species' mapped range was reduced by c.23-25%, depending on the assumptions used (Global Forest Watch 2023, based on data from Hansen et al. [2013] and methods disclosed therein). This is considered the minimum rate of reduction given the species' preference for the lowest elevation forests (which have experienced the most rapid deforestation rates) and any impacts of degradation which is not otherwise accounted for. Moreover, at some sites it may have become scarcer even in the absence of habitat loss and degradation. Along the Kinabatangan River, for example, the encounter rate appears to have decreased over the last decade (J. Eaton in litt. 2022, eBird 2023); the cause of this is unknown, but may be explained by delayed fragmentation effects (extinction debt). Consequently, the rate of population reduction is suspected of being 25-35% in the past three generations, although there is substantial uncertainty in this. In the absence of any slowdown in forest loss between 2018 and 2021, this rate of decline is precautionarily suspected to continue in the future three generations, although may ultimately begin to subside as an increasing proportion of the species' range is encompassed by protected areas.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Brunei extant native yes
Indonesia extant native yes
Malaysia extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Brunei Belait Swamp Forest
Brunei Southern Ladan Hills
Brunei Ulu Temburong
Indonesia Betung Kerihun
Indonesia Gunung Palung
Indonesia Kayan Mentarang
Indonesia Kutai
Indonesia Ulu Barito
Malaysia Danum Valley Conservation Area
Malaysia Kabili-Sepilok
Malaysia Kinabatangan floodplain
Malaysia Lambir Hills National Park
Malaysia Lanjak Entimau Wildlife Sanctuary
Malaysia Maliau Basin Conservation Area
Malaysia Mount Kinabalu
Malaysia Mulu - Buda Protected Area
Malaysia Niah National Park
Malaysia Tabin Wildlife Reserve
Malaysia Tanjung Datu-Samunsam Protected Area
Malaysia Tawau Hills Park

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Moist Lowland major resident
Altitude 0 - 500 m Occasional altitudinal limits (max) 1200 m

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%) Rapid Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Annual & perennial non-timber crops - Shifting agriculture Timing Scope Severity Impact
Ongoing Minority (<50%) Rapid Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Wood & pulp plantations - Agro-industry plantations Timing Scope Severity Impact
Ongoing Minority (<50%) Rapid Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Logging & wood harvesting - Unintentional effects: (large scale) [harvest] Timing Scope Severity Impact
Ongoing Minority (<50%) Rapid Declines Medium Impact: 6
Stresses
Ecosystem degradation
Biological resource use Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation
Natural system modifications Fire & fire suppression - Increase in fire frequency/intensity Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation

Recommended citation
BirdLife International (2024) Species factsheet: Blue-headed Pitta Hydrornis baudii. Downloaded from https://datazone.birdlife.org/species/factsheet/blue-headed-pitta-hydrornis-baudii 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.