NT
Malay Banded Pitta Hydrornis irena



Taxonomy

Taxonomic note

Hydrornis irena (del Hoyo and Collar 2016) was previously listed as Pitta irena, following a split of P. guajana into P. guajana, P. irena and P. schwaneri, by the BirdLife Taxonomic Working Group on the basis of many strong plumage differences, some morphometric differences in guajana, and modest vocal differences, as noted by Rheindt & Eaton (2010).

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.
Rheindt, F. E.; Eaton, J. A. 2010. Biological species limits in the Banded Pitta Pita guajana. Forktail: 86-91.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - -

Red List history
Year Category Criteria
2022 Near Threatened A2cd+3cd+4cd
2016 Near Threatened A2cd+3cd+4cd
2012 Near Threatened A2cd+3cd+4cd
2011 Near Threatened A2c,d; A3c,d; A4c,d
2008 Not Recognised
2004 Not Recognised
2000 Not Recognised
1994 Not Recognised
1988 Not Recognised
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) 950,000 km2 good
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size unknown - - -
Population trend decreasing poor suspected 2016-2028
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 3.85 years - - -

Population justification: The population has not been quantified, although the species is typically described as uncommon or scarce (Wells 2007, Eaton et al. 2016). Round and Treesucon (1986) estimated a density of 10 territories in 1.6 km2, equivalent to c.12-13 mature individuals/km2, although the species appears to be more common in the northern half of the Thai-Malay Peninsula than in the southern half or on Sumatra (Wells 2007). Although no global population estimate has been calculated therefore, it is considered highly unlikely that the species has a population size that meets or approaches the threshold (<10,000 mature individuals) for listing as threatened.

Trend justification: The population is suspected to be declining because of forest loss throughout its range. Over the past three generations (11.5 years; Bird et al. 2020), forest loss in this species' range has been equivalent to 21-24% (Global Forest Watch 2022, using data from Hansen et al. [2013] and methods disclosed therein). Because this rate was similar between 2016 and 2020, with little indication that it will slow in the future, the same rate is projected over the next three generations. As a forest-dependent species, the population is suspected to be declining at a rate broadly similar to that of forest loss. There may be some additive impact of trade on this species, although it is currently thought to be <5% over three generations (Symes et al. 2018). Combining the impacts of forest loss and trade, Symes et al. (2018) reached a similar conclusion, suggesting that in Indonesia the species had declined, and was likely to continue to decline, at a rate exceeding 20% over three generations. Overall therefore, the species is suspected of declining at an ongoing rate of 20-29% over three generations.


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

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Malaysia Belum-Temenggor
Malaysia Endau-Rompin
Malaysia Krau Wildlife Reserve
Malaysia Nakawan Range
Malaysia Panti forest
Malaysia Taman Negara National Park
Malaysia Ulu Muda
Thailand Bala Sector, Hala-Bala Wildlife Sanctuary
Thailand Hala Sector, Hala-Bala Wildlife Sanctuary and Bang Lang National Park
Thailand Khao Banthad
Thailand Khao Luang
Thailand Khao Nor Chuchi

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Artificial/Terrestrial Subtropical/Tropical Heavily Degraded Former Forest marginal resident
Forest Subtropical/Tropical Moist Lowland major resident
Forest Subtropical/Tropical Moist Montane suitable resident
Altitude 0 - 600 m Occasional altitudinal limits (max) 1500 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 Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Annual & perennial non-timber crops - Small-holder farming Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
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, Ecosystem conversion
Biological resource use Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation
Natural system modifications Fire & fire suppression - Increase in fire frequency/intensity Timing Scope Severity Impact
Past, Likely to Return Minority (<50%) Slow, Significant Declines Past Impact
Stresses
Ecosystem degradation

Recommended citation
BirdLife International (2024) Species factsheet: Malay Banded Pitta Hydrornis irena. Downloaded from https://datazone.birdlife.org/species/factsheet/malay-banded-pitta-hydrornis-irena on 27/12/2024.
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 27/12/2024.