Taxonomic note
Ninox squamipila, N. hypogramma, N. hantu and N. forbesi (del Hoyo and Collar 2014) were previously lumped as N. squamipila following Norman et al. (1998), and before then were also lumped with N. natalis as N. squamipila following Sibley and Monroe (1990, 1993). Formerly considered conspecific with N. squamipila (which see), but separable on morphological and plumage details, molecular differences and perhaps voice (Norman et al. 1998). Monotypic.
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 |
---|---|---|
- | D | D1 |
Year | Category | Criteria |
---|---|---|
2022 | Vulnerable | D1 |
2016 | Vulnerable | D2 |
2013 | Vulnerable | D2 |
2012 | Vulnerable | D2 |
2008 | Vulnerable | D2 |
2007 | Vulnerable | |
2006 | Vulnerable | |
2004 | Vulnerable | |
2000 | Critically Endangered | |
1994 | Not Recognised | |
1988 | Not Recognised |
Migratory status | not a migrant | Forest dependency | medium |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 240 km2 | medium |
Area of Occupancy (breeding/resident) | 216 km2 | |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 240-1200, 340 mature individuals | medium | estimated | 2020 |
Population trend | stable | poor | estimated | - |
Generation length | 5.02 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: About 342 mature Christmas Island Boobooks were thought to be present on the island in 2016 based on call playback at 135 sites (Morcombe 2016). This is higher than suggested by Low and Hamilton (2013) who suggested a population size in the range 1-100 pairs based on call playback surveys, but lower than the estimates of Hill and Lill (1998), who postulated a population of 820–1,200 birds based on the areas occupied by six radio-tracked individuals in the 1990s. Based on these estimates, Macgregor et al. (2021) estimate the total number of mature individuals to be in the range 240-1,200, with a best estimate of 340.
Trend justification: Control of the ants may have allowed the species' population to stabilise in the past (S. Garnett in litt. 2005), although there is no evidence of past declines or fluctuations (D. James in litt. 2007). There is currently no evidence of a continuing decline. Reporting rates and occupancy at 105 sites in 2006, annually from 2012 to 2017, and in 2019 are suggestive of an overall stable population (James and McAllan 2014, Director of National Parks unpublished, Legge and Woinarski unpublished).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Christmas Island (to Australia) | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Christmas Island (to Australia) | Christmas Island |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Shrubland | Subtropical/Tropical Moist | suitable | resident |
Altitude | 0 - 360 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Future | Whole (>90%) | Unknown | Unknown | ||||||
|
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Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Anoplolepis gracilipes | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Negligible declines | Medium Impact: 6 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Rattus rattus | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Unspecified species | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Negligible declines | Low Impact: 3 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Christmas Island Boobook Ninox natalis. Downloaded from
https://datazone.birdlife.org/species/factsheet/christmas-island-boobook-ninox-natalis on 22/12/2024.
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 22/12/2024.