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 |
---|---|---|
- | - | D2 |
Year | Category | Criteria |
---|---|---|
2020 | Vulnerable | D2 |
2016 | Endangered | D |
2013 | Endangered | D |
2012 | Endangered | D |
2011 | Endangered | D1 |
2010 | Critically Endangered | D1 |
2009 | Critically Endangered | D1 |
2008 | Critically Endangered | |
2006 | Critically Endangered | |
2004 | Critically Endangered | |
2000 | Critically 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 | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 7,300 km2 | medium |
Area of Occupancy (breeding/resident) | 10 km2 | |
Number of locations | 2 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | stable | good | inferred | - |
Generation length | 5.13 years | - | - | - |
Number of subpopulations | 2 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: Based on opportunistic observations, the population size is suspected to be greater than 500 mature individuals and to possibly number 800-1,000 mature individuals (P. J. McClelland in litt. 2019). However, since the species is secretive and no comprehensive or systematic surveys have been carried out, there is a lot of uncertainty in the population size (P. J. McClelland in litt. 2020). The population comprises at least 200 mature individuals at Campbell Island, 100-200 mature individuals at Whenua Hou/Codfish Island (P. J. McClelland in litt. 2019) and a small population, suspected in 2013 to number fewer than 30 individuals (Williams 2013a), at Dent Island. Individuals occassionally swim the 3 km from Dent Island to Campbell Island.
Trend justification: In 1990, a survey of Dent estimated a population of 60-100 birds (Goudswaard 1991), although other estimates from around the same time estimated just 30 individuals (P. McClelland in litt. 2019). It is likely that no more than 25 breeding pairs were present in 1998 (Gummer and Williams 1999). In 1999-2000, 24 captive-bred birds were released on Whenua Hou/Codfish Island to create a temporary population (Gummer and Williams 1999, Gummer 2006b). The population on Whenua Hou expanded rapidly, with egg-laying occurring in the first year (Williams 2013b). From 2004-2006, 159 birds, including some from Whenua Hou and captive-bred individuals, were reintroduced to Campbell Island (Potter 2006, P. J. McClelland in litt. 2012). The majority of birds released in 2004 were believed to have survived their first year on Campbell Island, and successful breeding was confirmed in 2006 (Anon. 2006). A survey in December 2008 confirmed that the species had established on the island (P. J. McClelland in litt. 2008). This 2008 survey, along with opportunistic observations of breeding and dispersal activity (P. J. McClelland in litt. 2008, 2010, 2011), suggested that the population size in 2012 was between 100 and 200 mature individuals. Based on opportunistic observations, the population size is currently suspected to be greater than 500 mature individuals and to possibly number 800-1,000 mature individuals (P. J. McClelland in litt. 2019). Comprehensive surveys have not been undertaken so population estimates are uncertain, but the population increase is considered to have a high level of certainty, although it may now have stabilised as carrying capacity is reached on the range islands (P. J. McClelland in litt. 2020).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
New Zealand | extant | native | yes |
Country/Territory | IBA Name |
---|---|
New Zealand | Campbell Islands |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subantarctic | suitable | resident |
Grassland | Subantarctic | major | resident |
Marine Coastal/Supratidal | Coastal Freshwater Lakes | major | resident |
Marine Intertidal | Rocky Shoreline | major | resident |
Marine Intertidal | Sandy Shoreline and/or Beaches, Sand Bars, Spits, Etc | major | resident |
Wetlands (inland) | Permanent Freshwater Marshes/Pools (under 8ha) | major | resident |
Wetlands (inland) | Permanent Rivers/Streams/Creeks (includes waterfalls) | major | resident |
Altitude | 0 - 200 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Climate change & severe weather | Storms & flooding | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Very Rapid Declines | Medium Impact: 6 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Rattus exulans | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Rapid Declines | Low Impact: 5 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Rattus norvegicus | Timing | Scope | Severity | Impact | ||||
Past, Likely to Return | Majority (50-90%) | Very Rapid Declines | Past Impact | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Unspecified species | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Rapid Declines | Low Impact: 5 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Problematic native species/diseases - Anas chlorotis | Timing | Scope | Severity | Impact | ||||
Future | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Pollution | Industrial & military effluents - Oil spills | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Rapid Declines | Low Impact: 5 | ||||||
|
Recommended citation
BirdLife International (2023) Species factsheet: Anas nesiotis. Downloaded from
http://datazone.birdlife.org/species/factsheet/campbell-teal-anas-nesiotis on 11/12/2023.
Recommended citation for factsheets for more than one species: BirdLife International (2023) IUCN Red List for birds. Downloaded from
http://datazone.birdlife.org on 11/12/2023.