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.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2024 | Least Concern | |
2016 | Near Threatened | C1 |
2012 | Near Threatened | C1 |
2008 | Near Threatened | C1 |
2004 | Near Threatened | |
2000 | Lower Risk/Near Threatened | |
1994 | Lower Risk/Near Threatened | |
1988 | Near Threatened |
Migratory status | not a migrant | Forest dependency | medium |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 720,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | unknown | poor | - | - |
Generation length | 3.03 years | - | - | - |
Number of subpopulations | 2-20 | - | - | - |
Population justification: The population size of this poorly-known species has not been quantified; it is closely associated with giant honey bee colonies Apis laboriosa and is considered very rare to uncommon throughout its range. Although generally assumed to be a rare species, it is likely easily overlooked due to its inconspicuous behaviour and may be more common than the paucity of records suggest.
Trend justification: The population trend is very difficult to assess given its very specific ecological niche and the inaccessible nature of its habitat, with current knowledge restricted to a few hives close to roads (N. Kitnya and J. Praveen in litt. 2024). Over-exploitation of bees' nests for honey by human populations has been suggested as a potential threat (Underwood 1992), but the remoteness of much of its range suggests this can only be a marginal and localised threat. Bee colonies may be locally exploited and undergo declines (for example in Nepal), however harvesting of honey is very low in in other parts of the range and much of this remains inaccessible to humans (G. Otis in litt. 2024). Species distribution modelling does not suggest that bee colonies are likely to be significantly affected by climate change (Huang et al. 2022). Moreover, habitat loss and degradation has been suspected of causing declines, but remote sensing data suggest forest loss is minimal within the range [Global Forest Watch 2023, using data from Hansen et al. (2013) and methods disclosed therein]). It is unclear whether these threats are likely to be impacting the global population trend and the lack of knowledge of the species’ breeding biology, including possible hosts if it is a brood parasite, and of its behaviour away from bees’ nests, makes it difficult to assess the scope and severity of any threats (Short et al. 2020). The trend is considered unknown given the considerable uncertainty surrounding the species, though there is currently no evidence to suggest it may be declining at a rate that may approach thresholds for listing as threatened.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Bhutan | extant | native | yes | |||
China (mainland) | extant | native | yes | |||
India | extant | native | yes | |||
Myanmar | extant | native | yes | |||
Nepal | extant | native | yes | |||
Pakistan | possibly extant | native | yes |
Country/Territory | IBA Name |
---|---|
China (mainland) | Biluo Xueshan |
India | Valley of Flowers National Park |
Nepal | Annapurna Conservation Area |
Nepal | Langtang National Park |
Nepal | Mai Valley forests |
Nepal | Makalu Barun National Park |
Nepal | Tamur valley and watershed |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Dry | major | resident |
Rocky areas (eg. inland cliffs, mountain peaks) | major | resident | |
Wetlands (inland) | Permanent Rivers/Streams/Creeks (includes waterfalls) | suitable | resident |
Altitude | 1450 - 3500 m | Occasional altitudinal limits | (min) 600 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Small-holder grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Unintentional effects (species is not the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Residential & commercial development | Housing & urban areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Yellow-rumped Honeyguide Indicator xanthonotus. Downloaded from
https://datazone.birdlife.org/species/factsheet/yellow-rumped-honeyguide-indicator-xanthonotus 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.