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Stock characteristics, fisheries and management of Greenland halibut

(Reinhardtius hippoglossoides (Walbaum)) in the Northeast Arctic

by

Kjell H. Nedreaas (IMR) & Oleg Smirnov (PINRO)

The 10th Norwegian – Russian Symposium

(2)

Greenland halibut distribution in Norwegian and

Barents Seas

IIb

IIa

I

(3)

Brief history of investigations in 1960-1990s

Time period Objects References

1964-1967 Area of spawning grounds, the period of mass spawning, first representative data on age-length structure of stock

Lahn-Johannessen 1965 1972,

Sorokin 1967, Nizovtsev 1968 1969 1970, Hognestad 1969,

1964-1970 Feeding Nizovtsev 1972 1989

1965-1973 Seasonal migrations between spawning and feeding grounds

Lahn-Johannessen 1965 1972, Nizovtsev 1989

1968-1971 Gametogenesis and sexual cycle Sorokin & Grigoryev1968, Fedorov1968 1969 1971

1978-1980 Nursery grounds to the northeast of

Spitsbergen and in the area of Fr. Josef Land

Borkin 1983

1980s Peculiarities of growth and maturation, dynamics of length-age structure of the stock

Kovtsova & Nizovtsev 1985, Nizovtsev 1987

1980s Migration and recruitment patterns in the Spitzbergen area

Godø & Haug 1987

1980s Distribution and feeding of larval Gr.halibut Haug & al. 1989

1990s Biological implications of a multi-gear fishery, gear selection

Nedreaas & al. 1996, Huse & al. 1997

1990s Fecundity Smirnov 1998, Gundersen & al. 1999

1990s Spawning, recruitment Hylen & Nedreaas 1995, Smirnov 1995,

Albert & al. 1997, Albert & al. 1998, Stene & al.

1999

1990s Feeding Michalsen & Nedreaas 1998, Dolgov &

Smirnov 2001

(4)

Greenland halibut distribution in Norwegian and

Barents Seas

Main spawning grounds

Nursery grounds

Feeding grounds IIb

IIa

I

Transboundary stock

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0 5 10 15 20 25 30 35 40

06- 10

16- 20

26- 30

36- 40

46- 50

56- 60

66- 70

76- 80

86- 90

96- 100 Le ng th g ro ups, c m

Frequency, %

Nurs e ry ground north and e as t of S pits be rge n Bare nts and Norwe gian S e as s he lf (de pth<500m) Main s pawning grounds (de pth>500m)

Length composition of Greenland halibut trawl catches in different areas by the data from Russian surveys (September-December 1999-2000).

Small mesh size trawls used everywhere.

(6)

0 10 20 30 40 50 60 70 80 90 100

2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17

Ag e , ye ars

Length, cm

male s fe male s

0 10 20 30 40 50 60 70 80 90 100

<=30 36- 40

46- 50

56- 60

66- 70

76- 80

Length groups, cm

Proportion of mature, %

males females

Greenland halibut length at age (mean for 1981-1997)

(Russia, age determined by scale)

Proportion mature at length (mean for 1984-1998) (Russia)

Maximum reported age and length of Greenland halibut in the Norwegian and Barents Seas are 20 years and 120 cm.

• Some differences in growth and maturation between males and females were found. From age of 6-7 years females grow faster compared to males and have longer span of life. But males become mature at younger age and smaller size.

(7)

R2 = 0,6487

0 20000 40000 60000 80000 100000 120000

45 50 55 60 65 70 75 80 85 90 95 100 Length, cm

Fecundity, eggs

Fecundity of Greenland halibut is rather low compared to other flatfish.

Estimates ranged from 6.4 to 94.4 thou. eggs per female depending on body size. Mean fecundity is evaluated by different authors at

18.1-28.1 thou. eggs.

(8)

Total egg production (TEP) by the northeast Arctic Greenland halibut stock by age in 1996-1998

(ref. Gundersen et al. 2000)

0 10 20 30 40

5 6 7 8 9 10 11 12 13 14 15+

Age TEP by age (109 )

1996 1997 1998

(9)

• Greenland halibut is a species, which has a negligible effect on the other commercial species of the Barents Sea and at the same time is not subject to their influence. The Greenland halibut were found in the diet of just three species - Greenland shark, cod and Greenland halibut itself. Besides, some sea mammals could be its potential predators.

• Food composition of the Greenland halibut in the Barents Sea includes more than 40 prey species. The main food consists of fish, mostly of herring, capelin and polar cod, as well as cephalopods and shrimp. In 1990’s an important place in the diet was occupied by wastes from the other species fishery (heads, guts etc.).

• It was calculated that with the Greenland halibut stock being nearly 100 thou. tonnes, the total food consumption constitutes about 280 thou. tonnes. The biomass of commercial species consumed (shrimp, capelin, herring, polar cod, cod, haddock, redfish, long rough dab) do not exceed from 5 to10 thou. tonnes of each species.

Position in food web

(10)

Catches of the Greenland halibut in the Barents and Norwegian Seas in 1935-2002.

0 10000 20000 30000 40000 50000 60000 70000 80000 90000 100000

1935 1941 1947 1953 1959 1965 1971 1977 1983 1989 1995 2001

Year

Catches, t

USSR/Russia Norway

Other countries Advice

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Data for stock assessment provided by

countries

Country

Kind of data

Catch in weight

Catch at age in numbers

Weight at age in the

catch

Proportion mature

by age

Length composition in

catch

Norway + + + +

Russia + + + + +

Germany +

United

Kingdom +

France +

Spain +

Portugal +

Ireland +

Greenland +

Faroe Islands +

Iceland +

Poland +

ICES Arctic Fisheries Working Group

(12)

Data available for AFWG

- Fishery statistics from 1964 onwards - Survey data:

Norwegian bottom trawl survey in August in the Barents Sea and Svalbard in fishing depths of less than 100 m and down to 500 m (from 1984).

Norwegian Greenland halibut surveys in August. The surveys cover the continental slope from 68 to 80ºN, in depths of 400–1500 m north of 70º30’N, and 400–1000 m south of this latitude (from 1994).

Norwegian bottom trawl surveys east and north of Svalbard in autumn (from 1996, from 2000 conducted as joint Norwegian-Russian survey).

Russian autumn bottom trawl surveys in the Barents Sea in fishing depths of 100–900 m (from 1984).

Spanish bottom trawl survey in the slope of Svalbard area in October (from 1997)

Norwegian Barents Sea bottom trawl survey (winter) in fishing depths of less than 100 m and down to 500 m (from 1989).

International pelagic 0-group surveys from 1970.

Norwegian experimental commercial fishery (CPUE) from 1992.

(13)

Dynamics of the Greenland halibut stock and fishing mortality

0 50000 100000 150000 200000 250000 300000 350000

1964 1968 1972 1976 1980 1984 1988 1992 1996 2000 2004

Biomass, t

0 0,1 0,2 0,3 0,4 0,5 0,6 0,7

Fbar (6-10)

Total biomass

Spawning biomass Fbar

2002 Total biomass = 82.5 thou. t

SSB (mature females)= 28.5 thou.

t

Mean 1964-2002 Total biomass = 121 thou. t SSB = 48 thou. t

Mean 1980-2002 Total biomass = 77 thou. t SSB = 26 thou. t

Prediction

(14)

Abundance indices of Greenland halibut from different surveys

(15)

Increased size of Greenland halibut in the surveys (left) and increased number of 12 year and older fish in the assessment (right),

in addition to improved recruitment, both indicators of an improving stock structure.

0 500 1000 1500 2000 2500 3000 3500 4000

1983 1986 1989 1992 1995 1998 2001

STOCK NUMBERS x 1000

Assessment of 12 years and older Greenland halibut

85 90 95 100 105 110 115

1994 1995 1996 1997 1998 1999 2000 2001 2002

Maximum length of Greenland halibut during survey (cm)

48 49 50 51 52

Mean length during continental slope survey (cm)

Maximum length Mean length

(16)

Main points and purposes of the three-year (2002-2005) Russian- Norwegian research program on Greenland halibut for

improvement of future managements and advice

Distribution and migrations.

• Life history, reproductive biology, trophic relations.

• Accuracy in determination of age and its influence on the stock assessment.

• Improvement of time series by surveys and fishery.

• Catchability of research trawls and comparative selectivity of research and fishing trawls and longlines.

• Searching the ways of improvement of stock assessment on the basis of fulfillment of all projects.

• Development of biological reference points and advice on improvement of stock assessments.

(17)

ACFM recomendations

In 2003 ACFM mentioned that neither precautionary reference points nor explicit management objectives have been established for this stock.

“As the stock is at a low level and possibly slightly recovering there is a need for the stock size to increase. In order to achieve this, the landings should be kept at the 2002 level. Additional management measures to control catches, e.g. TACs, area closures and reduced by-catch limits, need to be introduced and enforced effectively”.

(18)

Year ICES advice

Predicted catch corresp. to

advice

Agreed TAC

Official catches

1987 Precautionary TAC - - 19

1988 No decrease in SSB 19 - 20

1989 F = F(87); TAC 21 - 20

1990 F = F (89); TAC 15 - 23

1991 F at Fmed; TAC; improved expl. pattern 9 - 33

1992 Rebuild SSB (1991) 6 61 9

1993 TAC 7 71 12

1994 F < 0.1 < 12 111 9

1995 No fishing 0 2.52 11

1996 No fishing 0 2.52 14

1997 No fishing 0 2.52 10

1998 No fishing 0 2.52 13

1999 No fishing 0 2.52 19

2000 No fishing 0 2.52 14

2001 Reduce catch to rebuild stock < 11 2.52 16

2002 Reduce F substantially < 11 2.52 13

2003 Reduce catch to increase stock < 13 2.52 2004 Do not exceed recent low catches <13

Advised, agreed and actual catches in 1988-2004

(19)

Decisions of the Joint Russian – Norwegian Fishery Commission for 1978 - 1991

Year of regulation,

Session #

Main decisions Details

TAC advised by

ICES

Total catch in NEEZ

USSR/Russia

quota in NEEZ Other measures

By-catch during shrimp

fishery

1978 (4th) 40 000 30 000 12 500 - -

1979 (7th) 25 000 20 000 7 600 - -

1980 (8th) 14 000 10 500 2 000 - -

1981 (9th) 12 000 9 000 2 000 - -

1982 (10th) 12 000 9 000 2 400 - -

1983 (11th) 17 000 13 000 5 500 - -

1984 (12th) 17 000 13 000 5 500 - -

1985 (13th) 20 000 15 000 7 000 - -

1986 (14th) 20 000 15 000 7 000 - -

1987 (15th) 20 000 15 000 7 000 - -

1988 (16th) 19 000 14 750 6 600 - -

1989 (17th) 21 000 16 300 8 100+3 000 - -

1990 (18th) 15 000 12 000 4100 - -

1991 (19th) 9 000 7 000 2100 Norway introduced 45 cm as minimum legal catch size for foreign vessels fishing in NEEZ and at Jan Mayen and for

Norwegian vessels in all areas

300 spec. per 1 ton of shrimp

(20)

Year of regulation,

Session #

Main decisions Details

TAC advised by

ICES

Total catch in NEEZ

USSR/Russia quota in

NEEZ

Comments By-catch during groundfish fishery

By-catch during shrimp fishery 1992 (20th) 6 000 6 000 - The ban on the directed

Greenland halibut trawl fishery is placed

10% in haul 300 spec. per 1 ton of shrimp

1993 (21st) 7 000 7 000 - The same 10% in haul The same

1994 (22nd) <12 000 11 000 - The same 10% in haul The same

1995 (23rd) 0 2 500 - The same 5% on board The same

1996 (24rd) 0 2 500 - The same 5% on board The same

1997 (25th) 0 2 500 - The same 5% in haul The same

1998 (26th) 0 2 500 - The same 5% in haul The same

1999 (27th) 0 2 500 - The same 10% in haul The same

2000 (28rd) <11 000 2 500 - The same 10% in haul

but 5% on board

The same

2001 (29rd) <11 000 2 500 - The same 12% in haul

but 7% on board

The same

2002 (30th) <13 000 2 500 - The same 12% in haul

but 7% on board

The same

2003 (31st) <13 000 2 500 - The same 12% in haul

but 7% on board

The same

Decisions of the Joint Russian – Norwegian Fishery Commission for 1992 - 2003

Set by Norwegian authorities, from 1995 onwards this TAC relates to the traditional non-trawl coastal fishery south of 71o30 N by vessels less than 28 m. Allowable bycatch for others is additional to this.

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