INTRODUCTION
For the past 35+ years one of the main interests of the Hayes family has
been to help save the NZ Brown Teal (Anas chlorotis) from extinction.
During this lengthy involvement there have been many highs, many lows, and
many periods of total frustration, as we have always believed that saving
brown teal is a relatively simple conservation management exercise –
provide brown teal with a protected quality environment and they will
survive and breed for many years; just like the one we had in captivity
for 24 years! This brief article provides an insight into the dramatic
decline of the species, and its unique features, and discusses what is
being done to save brown teal from premature extinction.
Brown Teal are a unique and endemic New Zealand species of duck that was
historically widespread throughout New Zealand’s once vast wetlands and in
very large numbers. But between the early 1800’s the population began to
decline, and from being the country’s most common duck there were only
c750 surviving by 1999 – with the species was heading for total extinction
by 2015. However, since 2000 the recovery programme has been rejuvenated,
is heading in a positive direction, and at long last serious efforts are
now being been made to save this New Zealand icon from extinction
AN ALMOST FORGOTTEN SPECIES
For some unknown reason the public status accorded the NZ Brown Teal (Anas
chlorotis) has been relatively insignificant compared to the status
accorded both NZ Kiwi and NZ Blue Duck. Yet comparing the surviving
numbers of these three species there are c60,000 Kiwi (there are 6 species
within the Kiwi family), c3,500 NZ Blue Duck (Hymenolaimus malacorhynchos)
- but only c1,400 brown teal.
The brown teal is a unique endemic species that was once widespread
throughout New Zealand in very large numbers, and was historically found
in every type of New Zealand wetland.
Before humans arrived in New Zealand there were millions of brown teal,
with a population spread from Northland to Southland – and to the Chatham
Islands and to Stewart Island. Fossil research data completed in 2002 show
that brown teal were present in New Zealand at least 10,000yrs BP;
confirming what the Founder of the Wildfowl & Wetlands Trust, Sir Peter
Scott, said in 1960, that he believed brown teal were “an ancient and
primitive form of duck”. The Brown Teal Conservation Trust, founded in
2002, believes that brown teal evolved from the very beginning of life in
New Zealand.
Brown teal have many unique features that are not found in any other
species of waterfowl, and it is these unique features that place brown
teal in a class of their own.

Photo courtesy Lynda Feringa and the Wairarapa Time Age
THE RACE TOWARDS EXTINCTION
Brown teal evolved in an almost totally predator free New Zealand
environment and in a landscape which contained vast tracts of every type
of wetland.
Whilst the destruction/modification of New Zealand wetlands, together with
excessive hunting, impacted heavily on brown teal survival, the greatest
factor influencing the brown teal’s race towards extinction has been the
importation and spread of predators – firstly with rats, and then with
cats, ferrets, stoats, weasels and hedgehogs; coupled with the
ever-increasing population growth of the harrier hawk, which benefited
from protective legislation introduced in 1986. Plus the clearance of
native forests. In addition, both feral and domestic dogs have assisted
the decline/demise of teal at a number of critically important sites.
When humans first arrived in New Zealand (research is ongoing to determine
when this actually occurred) brown teal were believed to be the most
abundant species of New Zealand duck and were found throughout the
country’s vast wetlands. But with the arrivals of Europeans (accompanied
by cats, ferrets, stoats, weasels, hedgehogs, guns, etc) the brown teal
population began a significant period of decline, a decline that
accelerated from the 1950’s onwards. In spite of gaining total protection
in 1921 the population plummeted dramatically from c2,500 in 1988 to a
level where the species is now one of the world’s most endangered ducks;
perhaps the world’s fourth most endangered, and by 1999 was in imminent
danger of premature extinction, with only c750 surviving – and with the
predicted time for total extinction being 2015.
However, there is now clear, compelling and conclusive evidence to show
that brown teal can be saved from premature extinction - by eliminating
all predators at key sites, by ensuring pristine habitat, by ensuring an
adequate food chain at these habitats, and by ensuring that the whole
programme is well supported by a soundly based management structure, as
well as a soundly managed captive breeding programme – remembering that no
species of rare waterfowl has been saved without a major captive breeding
component.
For many years brown teal protagonists have attempted to promote the
philosophy that predator control at key sites will, in the short-term,
rapidly retard the decline, and in the medium-term teal populations will
expand. In the long-term such activity, in association with habitat
protection, creation, enhancement, seriously dedicated management, plus a
major captive breeding programme, will eventually result in brown teal
populations dramatically expanding and brown teal being removed from the
endangered list.
The successful survival and breeding of captive reared brown teal released
on to a number of New Zealand’s predator free offshore islands clearly
endorses this philosophy – clearly supported by the fact that the ten
pairs of teal released onto Kapiti Island in 1969 resulted in a
self-sustaining population on the island.
In simple terms, you provide brown teal with good habitat and a protected
environment and they live long healthy productive lives – just as we have
seen with captive brown teal, a number of which have lived for 16, 17, 18
and 22 years, with the record being just over 24 years!

A brown teal flock at Parekura Bay, just south of Russell in New Zealand’s
Bay of Islands, in 1984. For decades this site was an important brown teal
roost site and c100 birds could be regularly seen there. But by 1996 there
were no brown teal present – all eliminated by predators.
PREMATURE EXTINCTION
Many environmental experts have long promoted the philosophy that
extinction is a biological certainty and an intrinsic part of the
evolution process; with natural causes being the main route to extinction
— earthquakes, eruptions, floods, massive natural environmental changes,
competition for food, and so on. Historically this is, of course, very
true, but in the past c100 years the path towards extinction for many bird
and animal species has undoubtedly been hastened by the massive growth in
the world’s population, by our poor respect for the natural environment
and for the world’s wild animals and birds; together with our generally
abysmal understanding of the environment and how to successfully manage
the world’s natural resources. Nothing could be truer than with the New
Zealand situation, where New Zealand comfortably holds the world record
for a country with the highest number of endangered endemic birds - none
of which have become endangered by ‘natural causes‘. Remembering that
these endemic bird species evolved in a predator-free environment, these
species have all become endangered through mans’ interference with nature
- by introducing predators, by introducing competing bird life, by
destroying habitat, by drastically modifying/disturbing habitat, and by
excessive hunting. Many are in grave danger of ‘premature extinction’.
All of these accumulated factors have lead to the precarious state of many
New Zealand bird species, with brown teal suffering more than any other
endemic mainland waterfowl species.
BROWN TEAL BEHAVIOUR
Besides being endemic to the New Zealand landscape, it is mainly the
behavioural characteristics of brown teal that set it apart from all other
species of dabbling duck, and in a class of its own.
These behavioural characteristics can be summarised as follows
• Nocturnal behaviour
• Monogamous relationship
• Murderous nature of an established pair (In 1960 when Peter Scott
received three
brown teal at WWT Slimbridge he said that he hoped New Zealander’s were
not of
a similar nature!)
• Long-term parental attention provided to their progeny by both parents
• Great climbing ability
• Incredible vulnerability to predation
• Failure to adapt to environmental changes
• Preference (nowadays) to estuarine habitat
• Colour, body shape, size, weight, courtship, displays, and vocal sounds
• Pre and Post-Copulatory behaviour (invariably there isn’t any!)
• Feeding patterns
• What they eat
• A small clutch size
• Egg shape, size and weight
• Colour, size and weight of progeny
• Specialised bill
• Flocking behaviour
• Preference for walking instead of flying
In fact having webbed feet is really the only feature brown teal have in
common with other waterfowl.
Brown teal do not adapt readily to environmental changes, and it is
believed that the long-term protection of remaining flock sites may well
be a vital link in brown teal survival. Over the last 60, or so, years
such flock sites have been mainly in estuarine areas and mostly at the
confluence of fresh and seawater, but as already mentioned, this was not
always the case and flocks of brown teal were found in every pond, lake,
swamp, river and major wetland in New Zealand.
At a flock site progeny of the year will live quite happily together over
a period of several months and it is not until the onset of the breeding
season that aggravation amongst each other commences.
But, by far the most alarming feature of brown teal behaviour is the
species vulnerability to predators – far more vulnerable than any other
species of waterfowl.
However, in a protected environment – such as a captive one – they live
very long lives; with 14, 15, 16, 17, 18, 22 & 24 years of age being
recorded.
Just like all New Zealand endemic bird species, brown teal evolved in an
almost totally predator free environment - for millions of years - and
have never adapted to a modern environment full of predators.
SAVING BROWN TEAL
Between 1968 and 1987 the NZ Wildlife Service, which was replaced by the
Department of Conservation in 1987, was active in protecting and enhancing
brown teal habitats in Northland and on Great Barrier Island, and in 1976,
the Wildlife Service, in association with Ducks Unlimited (NZ),
established a major brown teal captive breeding programme, entitled
“OPERATION PAKEKE” (‘Pateke’ being the Maori name for brown teal).
Between 1976 and 1999 c2,000 brown teal were reared in captivity, and
c1,800 of these were released into the wild, at 29 different sites. During
this highly successful captive breeding period a unique system of ‘natural
pairing’ evolved – where each bird is allowed to choose its own partner.
Once established a pair were retained in their own special aviary. This
was so successful that in a single season participating breeders reared
153 brown teal.
Sadly, however, the intrinsic reasons for the decline of wild brown teal
were not addressed and whilst captive released birds showed great
adaptability to the wild, survived for long periods, and reared young,
they too declined in the face of huge numbers of predators, just like
their wild predecessors.
On top of this, the period 1990 to 1999 saw the recovery programme going
rapidly backwards, largely through non-existent Dept of Conservation
management, to eventually reach a point where the total wild population of
brown teal had plummeted from c2,500 birds to c750 birds – c150 in
Northland and c600 on Great Barrier Island - that by 2000 brown teal had
become one of the world’s most endangered species of duck. Between 1990
and 1999 brown teal became a FORGOTTEN SPECIES amongst wildlife
professionals.
In mid-1999 the disastrous state of the recovery programme became
glaringly apparent when two individuals took it upon themselves to promote
the plight of brown teal by appearing during prime viewing time on New
Zealand’s National Television News, on a Sunday evening in September 1999,
to clearly show that the recovery programme was really a very simple
management exercise - all that was needed was to provide brown teal with a
protected environment – but without a concerted effort brown teal would be
totally extinct within the next fifteen years
By mid-1999 the plight of the captive brown teal population also became
apparent, with the numbers in captivity having plummeted, over the
previous decade, from c140 birds to c30 birds, and the numbers being
reared annually dropping from c130 to c30.
The number of brown teal breeders, once spread from Northland to
Southland, also became in danger of premature extinction when, over the
same period, their numbers plummeted from 39 to just 9!
So, having irrevocable evidence of the dramatic decline of brown teal in
the wild and in captivity, together with the abysmal track record of the
recovery programme, those within the Department of Conservation’s
‘corridors of power’ were ‘persuaded’ to investigate the brown teal
recovery programme and in late 1999 instigated a complete review/Audit of
the whole programme. In October 2000 the Audit findings were duly
published.
THE “AUDIT”
The Audit was compiled over a six-month period and close to forty people
were interviewed. The published report was seen as a valuable and vitally
important document, and an essential ‘guide’ towards saving brown teal.
From 2000 onwards the recovery programme has undoubtedly been turned
around from one of imminent disaster to one of imminent success.
Large-scale predator control programmes were introduced at a number of
critically important sites in Northland and on Great Barrier Island. One
of the most spectacular successes was the elimination of 50 stoats in one
month at one site in Northland, and between 2001 and the end of 2004 the
Northland population had risen dramatically from c200 brown teal to c400.
2500
*
2000 *
1700
*
*
1200
*
*
950
* *
800
* *
700 *
1988 1990 1992 1994 1996 1998 2000 2002 2004 2006 2007
BROWN TEAL POPULATION DYNAMICS OVER THE PAST 18 YEARS
The graph above shows the accelerating race towards extinction. Had the
recovering programme not
been restructured in 2000 brown teal would have been totally extinct by
c2015!
THE PRESENT RECOVERY PROGRAMME
Since the AUDIT in 2000 the brown teal recovery programme has made
excellent progress and is now on a clearly defined plan that, over the
next decade, will see brown teal numbers increase steadily in the wild.
However, it is likely to take 20-30 years to reach a point where the
future of brown teal is assured and to achieve this goal predator control
programmes, habitat management and captive breeding must be ongoing
indefinitely.
Also since 2000 the brown teal captive breeding programme has bounced back
with a vengeance. C15 breeders are now actively participating and c100
birds are being reared each season. (In the words of the 2000 AUDIT “You
can never have too many brown teal in captivity!”)
Since 2000 the input into predator control programmes, and the results
being obtained, are impressive.
The results in the past 5 years confirm the Brown Teal Conservation
Trust’s belief that given suitable and protected predator-free habitat
brown teal will survive and breed very successfully.
The Trust also believes that on going research into brown teal habitat
requirements, and into what brown teal eat in the wild, are vital
ingredients to the long term survival of the species.
However, government priorities in New Zealand change with the wind and to
help ensure the long-term viability of the recovery programme a major
private sponsor may be needed.
THE
PRESENT RECOVERY PROGRAMME
Since the AUDIT in 2000 the brown teal recovery programme has made
excellent progress and is now on a clearly defined plan that, over the
next decade, will see brown teal numbers increase steadily in the wild.
However, it is likely to take 20-30 years to reach a point where the
future of brown teal is assured and to achieve this goal predator control
programmes, habitat management and captive breeding must be ongoing
indefinitely.
Also since 2000 the brown teal captive breeding programme has bounced back
with a vengeance. C15 breeders are now actively participating and c100
birds are being reared each season. (In the words of the 2000 AUDIT “You
can never have too many brown teal in captivity!”)
Since 2000 the input into predator control programmes, and the results
being obtained, are impressive.
The results in the past 5 years confirm the Brown Teal Conservation
Trust’s belief that given suitable and protected predator-free habitat
brown teal will survive and breed very successfully.
The Trust also believes that on going research into brown teal habitat
requirements, research into what brown teal eat in the wild, together with
major post-release monitoring programmes, are vital ingredients to the
long term survival of the species.
However, government priorities in New Zealand change with the wind and to
help ensure the long-term viability of the recovery programme a major
private sponsor may be needed.
PRESENT DISTRIBUTION
The unrelenting mainland expansion and spread of the main brown teal
predators - cats, mustelids, harrier hawks and rats - together with
wetlands destruction (by 1980 c90% of the country’s once vast wetlands and
60% of our indigenous forests had been systematically destroyed), and an
increasing number of waterfowl hunters, coupled with New Zealand’s rapid
population growth, resulted, from c1900 onwards, in a gradual retrenchment
of brown teal into areas that were relatively low in predator and human
numbers. But sadly, but surely, predators and humans also expanded into
such areas.
By 2000 brown teal were mainly confined to two areas of New Zealand – a
coastal area of some 30 kilometres between Whangarei and Russell in the
Northland region, where, thanks to major predator control programmes
introduced in 2001, teal numbers have risen from c150 to c400, and on
Great Barrier Island, a large island in the Hauraki Gulf where predator
control started in 2001 and where the teal population’s race towards
extinction has been retarded, with c800 now surviving.
Assuming major predator control programmes continue long-term (20-30
years) on GBI the next decade should see teal numbers return to where they
were twenty years ago – c1,500.
Great Barrier Island is c40 km long, c15 km in width and about 285 km
square, with some excellent estuarine teal habitat. There is also an
impressive and large lagoon at Okiwi Station at the northern end of the
island, and where c750 brown teal were resident in 1988.
As can be seen from the accompanying map, there are two other areas on the
NZ mainland where brown teal are present in small numbers – at Port
Charles on the Coromandel Peninsula, where wild brown teal numbers are
being well supported by the release of captive reared birds - into a
predator controlled environment. By mid-2006 four annual releases
totalling 210 birds had taken place there.
Prior to the commencement of this release programme a remnant population
of c20 wild teal survived in the district, these being survivors of a once
very large brown teal population.
Overall the level of survival of released birds has shown very positive
and encouraging results, with numerous progeny being hatched and reared by
released birds, so much so that brown teal are now being observed in an
increasing number of areas on the peninsula.
Historically, a peninsula has proven to be more readily defensible to
predators, and to the growth of predator numbers, and long-term predator
control programmes on the Coromandel Peninsula will eventually result in
large numbers of teal surviving on the peninsula.
A century ago the Coromandel Peninsula was a brown teal stronghold and
supported hundreds of brown teal in most areas of the peninsula, and Port
Charles is an ideal area for the re-establishment programme. Being
relatively close to Great Barrier Island there is unconfirmed belief that
there is an interchange of teal between the Great Barrier and the
Coromandel
Approximately 60 brown teal have also been released onto predator-free
offshore islands over the past decade and on each island they have
survived well and produced good numbers of offspring.
Islands prominent in the brown teal survival/recovery programme are –
Kapiti, off the Wellington coast, Tiritiri Matangi in the Hauraki Gulf,
Mana off the Wellington coast, Urupakapuka in the Bay of Islands, and the
Karori Wildlife Sanctuary, a mainland predator-free ‘island’ near
Wellington City, and Mayor Island, off the eastern side of the Coromandel
Peninsula. In February 2006 28 captive reared teal were also released onto
the wetlands on Mayor Island (Tuhua), which is c30 kilometres off the
lower eastern coast of the Coromandel Peninsula. Mayor Island is an almost
totally brown teal predator free extinct volcanic island and has
impressive wetland habitat. In September 2006, after only some seven
months after being released at Tuhua a brood of brown teal were seen with
their parents. But, by November 2006 indications were that a number of
teal had flown to the mainland – and were found dead – and it appears that
a high number of Tuhua Teal had been killed by harriers.
The only population outside New Zealand is held by the Wildfowl & Wetlands
Trust in the UK. WWT has been involved with brown teal since 1960 and
maintains a small captive breeding population.

SUMMARY
After at least forty-years of floundering in the dark the recovery
programme for brown teal is now advancing steadily and if the present
momentum is carried forward for the next several decades brown teal will
be saved from extinction.
Long-term predator control at key sites, habitat enhancement, habitat
protection and management, dedication to the cause, captive breeding,
together with diet research and post-release monitoring programmes will
all help to ensure that brown teal are with us for many years to come.
Brown teal are a unique and wonderful species of
waterfowl, an intrinsic part of New Zealand’s natural history and a
species that must never be allowed to become extinct
RECOMMENDED READING
Dumbell G.S. 1987: The Ecology, Behaviour and Management of New Zealand
Brown Teal, or Pateke. Unpublished PhD Thesis. University of Auckland
Dumbell G.S. 1986: New Zealand Brown Teal. Wildfowl 37:71-87
Dumbell G.S. 1988: Northland Brown Teal Progress Report Flight 5:16-19
Ducks Unlmited (NZ)
Gummer H. & Evans K. 2003: Brown teal/Pateke (Anas chlorotis) husbandry
Manual. Department of Conservation
Guthrie-Smith H. 1921: TUTIRA – The Story of a New Zealand Sheep
Station.Pages 213-
215 1999 Reprint. University of Washington Press
Halliday Tim 1978: Vanishing Birds. Hutchinson Group (NZ) Limited
Hayes F.N. 1981: The aviculture, re-establishment and status of the New
Zealand
Brown Teal (Anas aucklandica chlorotis) Ducks Unlimited (NZ) Publication
Hayes F.N. & Williams M.J.1982: The status, aviculture and
re-establishment of
Brown Teal in New Zealand. Wildfowl 33: 73-80
Hayes F.N. & Dumbell G.S. 1989: Progress in Brown Teal conservation.
Wildfowl 40: 137-140
Hayes F.N. 1994: The Status and Decline of the New Zealand Brown Teal.
NZ Outdoor magazine June/July 1994 32-38
Hayes F.N. 2002: The Rapidly Approaching Demise of the NZ Brown Teal.
NZ Outdoor magazine April/May 2002 78-79
Hayes F.N. 2002: Natural History, Captive Management & Survival of the New
Zealand Brown Teal. Brown Teal Conservation Trust publication
Hayes F.N. 2004: A Report on Progress Being Made to Save the NZ Brown Teal
from Premature Extinction. Brown Teal Conservation trust publication
Kear Janet 1990: Man & Wildfowl. T&D Poyser Ltd. London
Kear Janet (Editor) 2005: Ducks, Geese and Swans. A 2-volums set. Oxford
University Press
Kennedy M, et al, 2000: Phylogeny, biogeography, and taxonomy of
Australasian teals. Auk. 11 pages
McDowall R.M 1994: Gamekeepers for the Nation. Canterbury University Press
Moore S.J. 2003:. Brown Teal (Pateke) diet and its consequences for
releases. Unpublished
Msc thesis. Massey University, Palmerston North, New Zealand
Williams G.R. 1977: Marooning — a technique for saving threatened species
from extinction. International Zoo Yearbook. 17: 102-106
Williams M.J. 1969: Brown teal released on Kapiti Island Notornis: 16:61
Williams M.J. 1985: Brown Teal. Readers Digest ‘New Zealand Birds’ 146-147
Williams M.J. 2001 Productivity and survival within 2 declining
populations of brown
teal (Anas chlorotis) Notornis 48: 187-195
Worthy T.H. 2002: The fossil distribution of brown teal in New Zealand.
Unpublished report to the Department of Conservation March 2002

2007
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