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.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
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 |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 950,000 km2 | good |
Severely fragmented? | no | - |
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 | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Indonesia | extant | native | yes | |||
Malaysia | extant | native | yes | |||
Thailand | extant | native | yes |
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 |
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 |
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 | ||||||
|
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Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
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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 | ||||||
|
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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 | ||||||
|
|||||||||
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 | ||||||
|
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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 | ||||||
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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.