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 |
---|---|---|
2020 | Near Threatened | D1 |
2016 | Near Threatened | D1+2 |
2015 | Near Threatened | D1+2 |
2012 | Endangered | B1ab(iii) |
2008 | Endangered | B1a+b(i,ii,iii,iv,v) |
2007 | Endangered | |
2006 | Endangered | |
2004 | Endangered | |
2000 | Endangered | |
1994 | Not Recognised | |
1988 | Not Recognised |
Migratory status | not a migrant | Forest dependency | does not normally occur in forest |
Land-mass type | Average mass | 582 g |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 301,000 km2 | medium |
Number of locations | 7 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 1600-2200 mature individuals | medium | estimated | 2019 |
Population trend | increasing | good | estimated | - |
Generation length | 5.5 years | - | - | - |
Number of subpopulations | 7 | - | - | - |
Population justification: In 2011 after a period of revised management (O'Connor et al. 2007), minimum counts completed at stronghold sites were: Northland 408 (total estimate 600); Great Barrier Island 803 (total estimate 1,000); Coromandel Peninsula 321 (total estimate 400) (Department of Conservation 2011). This gave a total population estimate of 1,500-2,500 individuals in 2011 (Williams 2013). By 2019, minimum counts completed at stronghold sites were: Northland 699 (total estimate 900), Great Barrier Island 639 (total estimate 800), Coromandel Peninsula 693 (total estimate 900). Counts from Cape Kidnappers and Motu Tapu Island added another 377 (total estimate 400) (N. Miller in litt. 2020). The total population estimate in 2019 was 2,400-3,400 individuals, which roughly equates to 1,600-2,200 mature individuals (N. Miller in litt. 2020).
Trend justification: Although once widespread and numerous, by the 1990s A. chlorotis populations were confined to two key strongholds, Great Barrier Island and Northland, with a remnant population in Fiordland and two very small (< 20 individuals) reintroduced populations on offshore islands (Williams and Dumbell 1996, Watts et al. 2016). By 2007 the population was limited to approximately 1,000 wild birds (O’Connor et al. 2007), with research indicating that the species was facing extirpation from mainland New Zealand (Parrish and Williams 2001) and showing that the population on Great Barrier Island was halving every 4.1 years (Ferreira and Taylor 2003).
The population had been falling rapidly owing to predation by introduced mammals; however, since 2003 it has been increasing as a result of intensive management. The rate of increase has not been estimated.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
New Zealand | extant | native | yes |
Country/Territory | IBA Name |
---|---|
New Zealand | Bay of Plenty Islands |
New Zealand | Cape Kidnappers |
New Zealand | Hirakimata Kotuku Peninsula |
New Zealand | Te Hauturu-o-Toi Little Barrier Island |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Aquatic & Marine | Artificial/Aquatic - Water Storage Areas (over 8ha) | suitable | resident |
Artificial/Terrestrial | Pastureland | suitable | resident |
Forest | Temperate | major | breeding |
Marine Intertidal | Sandy Shoreline and/or Beaches, Sand Bars, Spits, Etc | marginal | resident |
Wetlands (inland) | Permanent Freshwater Lakes (over 8ha) | major | resident |
Wetlands (inland) | Permanent Freshwater Marshes/Pools (under 8ha) | major | resident |
Wetlands (inland) | Permanent Rivers/Streams/Creeks (includes waterfalls) | major | resident |
Altitude | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
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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Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Rapid Declines | Past Impact | ||||||
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Climate change & severe weather | Droughts | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Canis familiaris | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Felis catus | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Mustela erminea | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Rapid Declines | Medium Impact: 6 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Mustela furo | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Rapid Declines | Medium Impact: 6 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Mustela nivalis | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Rapid Declines | Medium Impact: 6 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Trichosurus vulpecula | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Invasive and other problematic species, genes & diseases | Problematic native species/diseases | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Majority (50-90%) | Slow, Significant Declines | Past Impact | ||||||
|
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Transportation & service corridors | Roads & railroads | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Brown Teal Anas chlorotis. Downloaded from
https://datazone.birdlife.org/species/factsheet/brown-teal-anas-chlorotis on 23/11/2024.
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 23/11/2024.