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  Fur Seals Factcheet

New Zealand Fur Seals - Fact Sheet

New Zealand is a country with no native land mammals, except for bats. However, we do have a number of native marine mammals, including the New Zealand fur seal. Up to two million fur seals once thronged the shores of New Zealand and its sub-Antarctic islands.

Fur seals were first hunted by Maori and then almost hunted to extinction by early European sealers. The current population is around 5 percent of the population of over 1.5 to 2 million fur seals and that was estimated to exist before 1800. Over 500,000 fur seals were taken by sealers in the early 1800s from Antipodes, Macquarie and Campbell Islands alone. Others took New Zealand (Hooker's) sea lions. The current population of fur seals - around 60,000 - is fewer than the tally killed in one season during the peak of sealing on the Antipodes lslands in the sub-Antarctic.

Two genetically distinct populations
Research into the genetic diversity of fur seals has indicated the presence of two genetically distinct subspecies. The rarer of the two based around the Snares Island but also found on the East and West Coasts of South Island. New Zealand has obligations under the Biodiversity Convention to maintain genetic diversity. The deaths of fur seals in fisheries is a threat to this genetic diversity.

Fur seal population
New Zealand fur seals are found right around our coasts and sub-Antarctic islands. The main fur seal populations are on the West Coast of the South Island, Fiordland, Solander Island and Bounty Islands. A small population of New Zealand fur seals also lives around southern parts of Australia.

While there has been an increase in numbers at the margins of the fur seal range, for example in the Nelson-Marlborough Area, Cook Strait and Otago Peninsula, the increases have been small compared to the overall population, for example around 500 pups are produced in Nelson-Marlborough area. Some large colonies, for example Solander Island and Snares Island, Open Bay Island and other West Coast South Island breeding colonies have shown little population change in the last 20 years or have declined.

The only large colony which has shown consistent increases in the past 25 years is at the Bounty Islands. This colony has been estimated at around 20,000 but is less than five percent of the number of animals that used to occur on the Bounty and Antipodes Islands based on the number of pelts taken off these islands in the early 1800s. In comparison the Antipodes Island has shown very little recovery since sealing.

Prior to the arrival of humans to New Zealand fur seals bred around the North and South Islands of New Zealand. By 1800 AD fur seals had been reduced to the south-western South Island of New Zealand as a result of hunting pressure by Maori. The current expansion in the range of fur seals is filling areas where previously seals were found.

The number of rookeries (breeding grounds) and winter haul-out or resting sites is increasing. However, it is unclear whether the total population is growing. In 1992 at Cape Palliser, near Wellington, seals bred on the North Island for the first time in over a century.

Fur seal population and by-catch
Fur seals are drowned in significant numbers in trawl nets throughout the New Zealand EEZ. Between 1989 and 2000 (the most recent year for which data is available) over 6200 fur seals are estimated to have drowned in the West Coast hoki fishery and over 12,000 throughout the EEZ (see table).

In addition to the West Coast hoki fishery large numbers have been drowned east of Stewart Island and around the Bounty Islands. The hoki fishery has had a high fur seal catch for over 10 years. The largest catch was 45 animals in one trawl net. The fur seal catch rate was higher in the second half of the 1990s than in the early 1990s on the West Coast.

Numbers of fur seals estimated caught in the trawl fisheries
Fishing
Year
West Coast
Hoki
Bycatch rate
(deaths/trawl)
Hoki
elsewhere
Hoki Total Other
fisheries
Total Ref
1999-00 561 0.073 163 (note 1) 724 328 1052 Baird 2001
1998-99 215 0.03 405 (note 2) 620 508 1128 Baird 2000a
1997-98 1032 0.13 196 1230 295 1534 Baird 1999a
1996-97 772 0.077 215 990 250 1237 ""
1995-96 1289 0.13 301 1697 407 2110 Manly et al, 02
1994-95 333 0.034 315 650 425 1073 ""
1993-94 253 0.026 204 460 700 1157 ""
1992-93 299 0.039 264 560 528 1091 ""
1991-92 142 0.020 79 210 363 584 ""
1990-91 116 0.013 270 390 15 401 ""
1989-90 342   ? ? 114 456 Baird, 1994
1988-89 900   ? ?   1000+ ""
Total 6252     7531 3933 12823  
Note 1: The fur seal captures for the non-West Coast South Island hoki fishery differ from Baird's estimates because we have used all the data available. Baird did not estimate total deaths were observer coverage was less than 10 percent of all tows in an area.
Note 2: The fur seal captures for the non-West Coast South Island hoki fishery differ from Baird's estimates because we have used all the data available. Baird did not estimate total deaths were observer coverage was less than 10 percent of all tows in an area.

Fur seals are also caught on tuna and ling longline hooks. In 1999/2000 47 fur seals were caught on observed boats. Most are reported by observers as released alive.

The populations of several fur seal colonies on the West Coast of the South Island have been declining in the last 5 years. Female seals do not breed until they are around 5-6 years old and males attain territorial status at about 10. This decline is consistent with the deaths in the hoki fishery as these colonies are the nearest to the West Coast fishery, eg. at Cape Foulwind.

Fur seal colonies adjacent hoki fishery: pup numbers
Year Wekakura
Point
Cape
Foulwind
Taumaka
Island
Total
1991 na 267 770  
1992 791 418 1325 2534
1993 942 446 1376 2764
1994 1007 392 1321 2720
1995 901 382 1442 2725
1996 1099 389 1323 2811
1997 976 283 1144 2403
1998 1048 332 1256 2636
1999 534 187 625 1346
2000 463 148 494 1105
2001        
Average 862 331 1145 12338
Source: Hon Sandra Lee: Minister of Conservation - Answer to Question for Written Answer - 19012. 6 November 2000, Parliament of New Zealand.

Why are they drowning?
Hoki, squid and southern blue whiting fisheries use nets that can have an opening the size of a rugby field and can be as long as a 14 storey building is tall. Hoki are not part of the natural diet of seals and trawling is at depths much lower than fur seals are known to dive. However, seals are often caught as the nets are played out and retrieved.

Seals have learnt that the sounds of winches hauling in heavy nets and the bright lights used to illuminate trawler decks are signposts leading to an easy meal. They are caught in the net's gaping mouth while diving for non-commercial fish species or diving for hoki that spill out from the trawl net. Once inside, the seal will either drown or be crushed to death by the fish catch as the net is hauled in.

Marine Mammal Exclusion Devices (MMED)
The fishing industry has been extremely slow in looking at alternative fishing technology that does not kill fur seals. They initially opposed research by the Department of Conservation to develop a seal exclusion device, which started in 1992.

It is unclear whether the device works and ejects live seals. If it just ejects dead or dying animals then the device could just be a means of obscuring the impact of fishing on fur seals. The industry are trialling the device in the hoki fishery in Australia but have refused to undertake this research in New Zealand. Result from the devices used in the Auckland Island squid fishery has indicated that it may mortally injure ejected sea lions.

While design changes may improve the Seal Exclusion Devices (SLED) it is very unclear whether this will be successful. More work is needed into the Marine Mammal Exclusion Devices (MMED) and the industry could play a role by undertaking research. The fishing industry has so far resisted this.

Legislative Protection
The Marine Mammals Protection Act was passed by Parliament in 1978 to protect marine mammals. It gave marine mammals a similar status to protected bird species under the Wildlife Act.

The Sixth Schedule of the Fisheries Act 1996 sets out changes to the Wildlife Act and the Marine Mammals Protection Act. The changes to both these Acts are very similar. Changes to the Fisheries Act 1996 also require the Minister of Fisheries, in consultation with the Minister of Conservation to "avoid, remedy or mitigate the effects of fishing related mortality on any protected species" for example fur seals (section 15).

The Minister of Fisheries has failed in his duty to implement measures to avoid, remedy or mitigate the effects of fishing on marine mammals.

This seal was one of the lucky few to survive being caught in a hoki trawl net.

The great majority of caught seals drown, and would experience no less terror than that of unwanted kittens thrown in a sack into the river.

Diet mainly non-commercial species
Some fishers still argue for the culling of seals on the grounds that they deplete fish stocks. Studies of the diet of fur seals have shown that they eat predominantly non-commercial species - lanternfish, anchovies, octopus and squid make up most of the diet. Commercial finfish species like hoki make up a very small proportion of the fur seal diet - this includes hoki heads and offal that is discharged by boat processing at sea.

Fur seals are capable of diving to over 200 metres depth in search of food and barracouta may seasonally be a significant finfish species in their diet.

The fishing industry claim that seals eat more fish than they catch. If seals eat 5kg of fish per day then a population of 60,000 would eat around 110,000 tonnes of fish. This is much less than the more than 550,000 tonnes of fish caught each year by commercial fishers.

Seals and salmon farms
Sea cage salmon farmers have conflicts with fur seals and have tried to remove animals rather than improve the marine farms operation.

Researchers have looked at the interaction between Australian fur seals and salmon farms around Tasmania. While the NZ fur seal is a different species the Tasmanian experience is likely to be representative of the situation in New Zealand. Their paper made a number of conclusions:

  • The vulnerability of fish-farms was influenced by their proximity to seal haul-out sites. Proximity to fishing ports and size of the fish farm had little influence.
  • The use of shooting as a protection method was inefficient and ineffective because seals usually entered fish-farms at night and showed no fear of shooters. There were many attacks in the presence of underwater acoustic seal scarers. Deterrents such as pursuit with boats, lights, seal crackers and emetics helped reduce the number of seal attacks.
  • The only way to prevent seals from attacking fish-farms is to exclude them from the vicinity of the fish pens with physical barriers that they cannot penetrate. These are currently in use, and include perimeter fences and protection nets made of steel mesh set around individual pens.
Fur seal and pup. Swimming practice for youngs seals begins in shallow pools from as early as ten days old. Seals are inquisitive and playful animals and have no natural predators on land. If you come across a seal entangled in plastic strapping or other rubbish, do not try to free the seal yourself. Notify the nearest Department of Conservation office as soon as possible.



This page was updated on 2 May, 2005



 


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