Campbell Island teal

Anas nesiotis (J.H. Fleming, 1935)

Order: Anseriformes

Family: Anatidae

New Zealand status: Endemic

Conservation status: Nationally Increasing

Other names: Campbell Island flightless teal

Geographical variation: Nil

Campbell Island teal. Adult female on water. Campbell Island, March 2011. Image © Detlef Davies by Detlef Davies

Campbell Island teal. Adult female on water. Campbell Island, March 2011. Image © Detlef Davies by Detlef Davies

The Campbell Island teal was a mystery bird for 87 years following the collection of the first specimen. Was there such a thing as a Campbell Island teal, or were the few birds seen there stray Auckland Island teal from the islands of the same name, 270 km away? Did a population persist somewhere in the Campbell Island group? These questions were answered in dramatic fashion in 1973, when a tiny population was discovered on Dent Island, a 23 ha islet off Campbell Island. Eleven birds were extracted from this population, in 1983 and 1990, and a captive breeding programme ensued. In 1999-2000 24 birds were released onto Codfish Island off Stewart Island. After rats were eradicated from Campbell Island in 2001, 150 captive-bred and Codfish Island-bred teal were released onto Campbell Island in 2004-06. The captive breeding programme ceased thereafter.


The Campbell Island teal is the smallest of the three brown-plumaged teals endemic to the New Zealand region. Both sexes are darkish brown, but are sexually dimorphic in plumage and size. Males are entirely dark sepia with a green iridescence on the head and back, dark chestnut breast, a paler brown abdomen and a conspicuous white patch at the tail base. Females are a uniformly dark brown with a paler abdomen. Both sexes have a conspicuous white eye ring, dark-grey bill, legs and feet, and dark brown eye. The wings are very short, with the main wing feathers extending only about half-way along the back.

Voice: calls are similar to those of brown teal and Auckland Island teal. Male calls are soft trills or piping, given in alarm and in territorial defence. Females have a rasping growl and a high-pitched and rapid quack.

Similar species: the flighted brown teal of the New Zealand mainland is larger, more colourful when in breeding plumage, and has wings that extend to the base of the tail when folded. The flightless Auckland Island teal at the Auckland Islands is slightly larger and paler, but can only be separated from Campbell Island teal by location.

Distribution and habitat

Campbell Island teal are endemic to Campbell Island. A small population, sourced from captive-raised birds has persisted on Codfish Island, off Stewart Island, since 1999. The main population on Campbell Island is derived from birds re-introduced in 2004-06, bolstered by natural recolonisations by birds swimming from Dent Island.

Campbell Island teal are considerably more furtive than their Auckland Island relatives. They are most likely to be encountered at the shoreline picking among rocks or any beach-cast seaweed, and along peaty streams and about pools in wetlands with profuse sedge and tussock cover in Perseverance Harbour, Campbell Island. They also occurs on Six-foot Lake, at the head of Northeast Harbour and in Northwest Bay on Campbell Island and at Sealers Bay and adjacent Penguin Bay on Codfish Island.

Campbell Island teal persist on Dent Island off Campbell Island’s Northwest Bay, their sole refuge after rats invaded Campbell Island in the early 1800s. There they survive in tiny numbers in seepages amongst seabird burrows and occasionally straggle across the 3 km sea gap to Campbell Island.


Campbell Island teal are secretive at Campbell Island, making population estimation difficult. The most recent attempt to locate birds on the island (2009) indicated a minimum presence of 102 birds. Populations on Dent and Codfish Islands have not been surveyed in the past decade, but both are probably tiny (<30 birds).

Threats and conservation 

The Campbell Island teal came very close to extinction, with a tiny remnant population surviving on Dent Island after Norway rats wiped out the main population on 11,000 ha Campbell Island. The captive-breeding programme took many years to produce any young, and in the end only one of the three wild females brought into captivity produced offspring. The entire captive-bred population is descended from this one female, and the Campbell Island teals has among the lowest level of genetic variation measured in any wild bird population. Any return of rats to Campbell Island would severely threaten this species and most likely force a resumption of past captive breeding efforts.


Campbell Island teal are probably monogamous and strongly territorial, and with all reproductive activity and feeding confined to the territory. On Codfish Island, egg-laying commences at the end of November, and newly-hatched broods are encountered from early January to February. From 14 nests there, clutch size was 2-5 pale fawn eggs (mean 3.5). On Campbell Island, incubated nests containing clutches of 4 and 5 eggs have been found from mid-November to mid-December.

Eggs laid in captivity averaged 62 x 43 mm with a calculated weight of 65 g, approx. 15-20% of a wild female’s body weight. Both adults contribute parental care. Fledging period in the wild is unknown but in captivity, ducklings reach adult weight in 50-60 days.     

Behaviour and ecology

Campbell Island teal are difficult to study in the wild due to the inaccessibility of the sites where they occur, the dense vegetation they inhabit, and the birds’ furtive and nocturnal behaviour. Pairs probably maintain territories year-round. On Codfish Island a small flock sometimes gathers at the mouth of Sealers Creek. Campbell Island teal are rarely active during the day or venture far from protective cover. At night they have been observed feeding on tidal flats at the head of Perseverance Harbour, Campbell Island and fossicking along the inlet’s rocky shoreline.


The diet of Campbell Island teal is unknown in the wild, but they are probably omnivorous with a preference for invertebrates. They have been observed stripping seeds from rushes and grass seedheads and dabbling in peaty ooze and along a stream edge on Codfish Island.


BirdLife factsheet



Kear, J. 2005. Ducks, geese and swans. Vol 2.Oxford University Press,Oxford.

Gummer, H.; Williams, M. 1999. Campbell Island teal: conservation update. Wildfowl 50: 133-138.

Robertson, H.A; Baird, K.; Elliott, G.P.; Hitchmough, R.A.; McArthur, N.J.; Makan, T.; Miskelly, C.M.; O’Donnell, C.F.J.; Sagar, P.M.; Scofield, R.P.; Taylor, G.A.; Michel, P. 2021Conservation status of birds in Aotearoa New Zealand birds, 2021. New Zealand Threat Classification Series 36. Wellington, Department of Conservation. 43p.

Williams, M.; Robertson, C.J.R. 1996. The Campbell Island teal Anas aucklandica nesiotis: history and review. Wildfowl 47:134-165.

Recommended citation

Williams, M.J. 2013 [updated 2022]. Campbell Island teal. In Miskelly, C.M. (ed.) New Zealand Birds Online.

Campbell Island teal

Social structure
Breeding season
  • Jul
  • Aug
  • Sep
  • Oct
  • Nov
  • Dec
  • Jan
  • Feb
  • Mar
  • Apr
  • May
  • Jun
Nest type
ground-level platform
Nest description
Intertwined sedge or grass leaves with down-lined surface, often wedged into base of sedge plant or within fern, with an extensive overhead canopy.
Maximum number of successful broods
Clutch size (mean)
Clutch size (min)
Clutch size (max)
Mean egg dimensions (length)
63 mm
Mean egg dimensions (width)
43 mm
Egg colour
Pale fawn
Egg laying dates
  • Jul
  • Aug
  • Sep
  • Oct
  • Nov
  • Dec
  • Jan
  • Feb
  • Mar
  • Apr
  • May
  • Jun
Interval between eggs in a clutch
48-60 hours in captivity days
Incubation behaviour
female only
Incubation length (mean)
32 days (captivity)
Incubation length (min)
30 days
Incubation length (max)
34 days
Nestling type
Nestling period (mean)
1 day
Age at fledging (mean)
60-70 days (captivity)
Age at fledging (min)
55 days
Age at independence (mean)
60-70 days
Age at first breeding (min)
1 years
Maximum longevity
16 years (captivity), wild unknown
Maximum dispersal
3 km