Secure shopping
International delivery

 


 

Home
Whats new
Parker Hale
Handguns
Rifles
Shotguns
Used Guns
Sights
Black Powder
Western Action
Reloading
Cartridge Cases
Ammunition
Accessories
Protection
Clothing
Knives and Axes
Books
Links
The Brown Teal

 

 

 

 

 

 

 

New Zealand Brown Teal

Order form     Legal notices     Terms     Shipping     Currency Converter    Print Stock List

 

New Zealand Brown Teal – An Almost Forgotten Species

by F.Neil Hayes QSM – Brown Teal Conservation Trust

You can also download it as a Microsoft Word Document by clicking here

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

 

Contact details Email haltd@actrix.co.nz P.O. Box 188, Carterton. New Zealand.
Phone +64 06 379 6692. Fax +64 06 379 5316.