Taxonomic note
The genus Paradoxornis has been moved from the family Sylviidae to Paradoxornithidae following Cai et al. (2019). Elsewhere has been treated as conspecific with P. guttaticollis by some authors, but is morphometrically quite distinct and differs in vocalizations and, especially, in habitat requirements; ranges overlap (or formerly did) in parts of NE India, but the two are ecologically separated. Monotypic.
Taxonomic source(s)
Handbook of the Birds of the World and BirdLife International. 2021. Handbook of the Birds of the World and BirdLife International digital checklist of the birds of the world. Version 6. Available at: https://datazone.birdlife.org/userfiles/file/Species/Taxonomy/HBW-BirdLife_Checklist_v6_Dec21.zip.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | B2ab(ii,iii,iv,v); C2a(i) |
Year | Category | Criteria |
---|---|---|
2024 | Vulnerable | B2ab(ii,iii,iv,v); C2a(i) |
2016 | Vulnerable | A2c+3c+4c |
2012 | Vulnerable | A2c+3c+4c |
2008 | Vulnerable | A2c; A3c; A4c |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | does not normally occur in forest |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 95,500 km2 | medium |
Area of Occupancy (breeding/resident) | 500 km2 | |
Number of locations | 5-20 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 1500-4000 mature individuals | medium | estimated | 2023 |
Population trend | decreasing | poor | inferred | - |
Generation length | 2.84 years | - | - | - |
Number of subpopulations | 4-5 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: Not formally estimated, but given the restricted extent of suitable habitat, very probably numbers in the single thousands. The largest subpopulation is believed to be hosted by D'Ering Wildlife Sanctuary, which is thought to host a few hundred individuals (Rahman et al. 2022). An area further north, 'East Siang' in Choudhury (2021) also has recent records, although the population here is unlikely large. Choudhury (2021) noted that the Lower Dibang Valley also hosts a population that is 'globally important' and the area of suitable habitat is not considerably less than that of D'Ering and this may also host several hundred birds. The area of suitable habitat in Kaziranga National Park is potentially large, although birds are infrequently seen (eBird 2023), and it is improbable that the population here is any larger than D'Ering. At Manas, the area of habitat is also large and birds are frequently observed in numbers comparable to strongholds in Arunachal Pradesh (eBird 2023). The very isolated, and recently discovered, population around Loktak Lake (mostly in Keibul Lamjao National Park) is probably small (<250 individuals), based simply on the very small area of suitable habitat. Combining reports from all parts of its range, the global population size of this species is probably between 1,500-4,000 mature individuals, with no population larger than 500-1,000 mature individuals.
Trend justification: Inferred to be declining, albeit probably slowly, in response to ongoing habitat pressures, principally in parts of its range that are not formally protected, or for which the protection is only ostensible (Choudhury 2021, Krishnan 2023). Populations are greatly fragmented, and while it is evident the species is able to persist short-term in isolated pockets of habitat, the viability of these in the long-term is unknown.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Bangladesh | possibly extinct | native | yes | |||
India | extant | native | yes |
Country/Territory | IBA Name |
---|---|
India | Barsey Rhododendron Sanctuary |
India | Bordoloni - Sampora |
India | Buxa Tiger Reserve (National Park) |
India | Chirang Reserve Forest |
India | D'Ering Memorial Wildlife Sanctuary |
India | Dibang Reserve Forest and adjacent areas |
India | Dibru - Saikhowa Complex |
India | Gorumara National Park |
India | Jaldapara Wildlife Sanctuary |
India | Kaziranga National Park |
India | Khangchendzonga National Park and Biosphere Reserve |
India | Lava - Neora Valley National Park |
India | Lowland forests of South Sikkim (Melli-Baguwa-Kitam, Jorethang-Namchi, Sombarey) |
India | Maguri and Motapung Beels |
India | Mahananda Wildlife Sanctuary |
India | Majuli |
India | Manas National Park |
India | Pabho Reserve Forest |
India | Pangolakha Wildlife Sanctuary - Zuluk - Bedang Tso - Natula Complex |
India | Pani-Dihing Bird Sanctuary |
India | Ripu Reserve Forest |
India | The Chapories of Lohit Reserve |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Grassland | Subtropical/Tropical Seasonally Wet/Flooded | major | resident |
Wetlands (inland) | Permanent Rivers/Streams/Creeks (includes waterfalls) | suitable | resident |
Wetlands (inland) | Seasonal/Intermittent/Irregular Rivers/Streams/Creeks | suitable | resident |
Altitude | 0 - 150 m | Occasional altitudinal limits |
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%) | Slow, Significant Declines | Low Impact: 5 | ||||||
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Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Agriculture & aquaculture | Livestock farming & ranching - Agro-industry grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Agriculture & aquaculture | Wood & pulp plantations - Agro-industry plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Biological resource use | Gathering terrestrial plants - Unintentional effects (species is not the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
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Climate change & severe weather | Storms & flooding | Timing | Scope | Severity | Impact | ||||
Unknown | Whole (>90%) | Unknown | Unknown | ||||||
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Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
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Recommended citation
BirdLife International (2024) Species factsheet: Black-breasted Parrotbill Paradoxornis flavirostris. Downloaded from
https://datazone.birdlife.org/species/factsheet/black-breasted-parrotbill-paradoxornis-flavirostris 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.