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 |
---|---|---|
- | - | D1 |
Year | Category | Criteria |
---|---|---|
2023 | Vulnerable | D1 |
2016 | Vulnerable | D1 |
2012 | Vulnerable | D1 |
2008 | Vulnerable | C2a(i); D1 |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 172,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 400-999 mature individuals | medium | estimated | 2022 |
Population trend | decreasing | poor | suspected | 2016-2052 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 15-29% | - | - | - |
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 | 12 years | - | - | - |
Number of subpopulations | 1-20 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: This species is described as fairly common to rare (Dutson 2011) and sparsely distributed (Woxvold and Novera 2021). Highest numbers appear to be in the New Georgia group where a minimum territory size of 10 km2 was estimated in relatively undisturbed coastal habitat on Kolombangara (Buckingham et al. 1995), and at least two pairs are thought to be resident on Tetepare (Read 2013). Four pairs were reported on the Three Sisters (12 km2) off Makira in the 1950s (French 1957). Birds are less common inland and on larger islands, e.g. Guadalcanal and Malaita (Cain and Galbraith 1956, Buckingham et al. 1995, G. Dutson pers. obs. 1997-1998), where numbers have declined within living memory (Buckingham et al. 1995, G. Dutson pers. obs. 1997-1998). On the basis of known records, descriptions of abundance and range size, the population is likely to number less than 1,000 mature individuals. Tentatively assuming a pair occurs approximately every 20-30km2 of coastal habitat, the population size is estimated at 455-683 mature individuals, placed here in the range 400-999 mature individuals.
Trend justification: A moderate and ongoing population decline is suspected on the basis of rates of habitat destruction and additional impacts of hunting. In the period 2000-2021, remote sensing data indicate that 7-9% of forest was lost in this species' range (Global Forest Watch 2022, using data from Hansen et al. [2013] and methods disclosed therein), equivalent to 13-15% in three generations (36 years; Bird et al. 2020). This is likely to accelerate (to an equivalent rate of 21-23%) in the future based on steeper losses in 2016-2021. Although this species hunts over open habitats including deforested areas, given its significant use and dependence on forest habitat for nesting (Buckingham et al. 1995, Dutson 2011), the reduction in forest cover extent is thought broadly to be causing an equivalent loss in the population size. This species is additionally impacted by hunting which is likely to compound declines.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Papua New Guinea | extant | native | yes | |||
Solomon Islands | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Solomon Islands | East Makira |
Solomon Islands | Gizo |
Solomon Islands | Kolombangara Upland Forest |
Solomon Islands | Mount Maetambe - Kolombangara River |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Mangrove Vegetation Above High Tide Level | suitable | resident |
Forest | Subtropical/Tropical Moist Lowland | major | resident |
Forest | Subtropical/Tropical Moist Montane | suitable | resident |
Marine Intertidal | Rocky Shoreline | suitable | resident |
Marine Intertidal | Sandy Shoreline and/or Beaches, Sand Bars, Spits, Etc | suitable | resident |
Marine Intertidal | Shingle and/or Pebble Shoreline and/or Beaches | suitable | resident |
Wetlands (inland) | Permanent Freshwater Lakes (over 8ha) | suitable | resident |
Altitude | 0 - 1500 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Shifting agriculture | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Biological resource use | Hunting & trapping terrestrial animals - Persecution/control | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
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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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Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Slow, Significant Declines | Low Impact: 4 | ||||||
|
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Pollution | Agricultural & forestry effluents - Herbicides and pesticides | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Unknown | Unknown | Past Impact | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | national |
Sport hunting/specimen collecting | national |
Recommended citation
BirdLife International (2024) Species factsheet: Sanford's Sea-eagle Haliaeetus sanfordi. Downloaded from
https://datazone.birdlife.org/species/factsheet/sanfords-sea-eagle-haliaeetus-sanfordi 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.