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SURVEY REPORT / TOKTRAPPORT

Acoustic Survey for North Sea Herring and Sprat RV "G.O SARS" 27 June – 20 July 2002

Else Torstensen Institute of Marine Research

N-4817 His. Norway else.torstensen@imr.no

1. INTRODUCTION

The report presents the results from the Norwegian coverage of the International Herring Acoustic Survey for 2002 (Fig. 1). The time series of this survey extends back to 1984. Five countries cooperate to survey the North Sea and the Skagerrak for an acoustic abundance estimation of herring and sprat. The surveys are planned in the Planning Group for Herring Surveys (ICES 2002), a sub group under the ICES Herring Assessment Working Group for the Area South of 62oN.

Objectives: To estimate the abundance of herring and sprat in the area between latitudes 56º30'N and 62º00'N and 02º00'-06°00’E. Map the general hydrographical regime and monitor the standard profiles Oksøy - Hanstholm, Hanstholm - Aberdeen, Utsira - Start Point and Feie - Shetland.

2. SURVEY DESCRIPTION AND METHODS

2.1 Personell

Valantine Anthonypillai (Fish.lab) Karen Gjertsen (11 – 20 July) (Fish.lab)

Anne-Liv Johnsen (Fish.lab)

Sigmund Myklevoll (Fish.lab)

Henrik Myran (27 June – 11 July) (Fish.lab)

Einar Osland (Acoustic technician)

Bjørn Vidar Svendsen (Fish.lab)

Øyvind Torgersen (Acoustic expert)

Else Torstensen (Cruise leader)

Exchange of staff with “Scotia”:

Eric Armstrong, Marine Lab, Aberdeen, 4 - 17 July.

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2.2 Narrative

RV “G.O. Sars” sailed at 1400 UTC on 27 June 2002. The vessel made passage to Uggedalseide/Tysnes and anchored at 1800 UTC to calibrate the acoustic instruments.

The conditions appeared to be unfavourable for calibration and the vessel continued to the Førdesfjord, north of Haugesund. Entered at 0240 UTC without anchoring. Was positioned for a while and left the area at 0610 UTC. Again, the condition was not satisfactory for calibration as there were too much fish/jellyfish in the sea. On 28 June the vessel anchored in Rosfjord, 58° 04’ N and 7° 00’ E at 2040 UTC to calibrate the acoustic instruments on all scientific sounders. At 0500 UTC RV “G.O.Sars” left the fjord following a successful calibration of all scientific sounders and commenced the survey at 0920 UTC at 58o 3’ N and 8o 5’ E, the first CTD-station on the Oksøy – Hanstholm transect.

The survey continued with transects from south to north The weather conditions were good except for the last two days. Due to rough weather and few, small acoustic registrations in the ICES rectangles 50F2 and 51F”, the rectangle 51F3 was not covered.

A call was made in Egersund on 28 June, in Aberdeen on 3 July, in Haugesund on 11 July and in Lerwick, Shetland on 17 July. The survey finished in Bergen on 20 July 2002 at 2015 hrs UTC. About 3.600 n.mi. were covered by the survey and 100 trawl hauls and 168 CTD stations were taken. Two pelagic nets were seriously damaged.

2.3 Survey design

The survey was carried out in systematic parallel transects in the east-west direction with a distance of 13-17 n.mi. spacing progressing from south to north. Additional short transects were made in the overlapping area east of Shetland, with 7-8 n.mi.

transects spacing. North of 60° 45’ transects in a south – north direction were performed. The cruise tracks with fishing stations and CTD-stations are shown in Figures 2 and 3, respectively.

2.4 Calibration

The acoustic sounders, Simrad EK500 18, 38 and 120 kHz, were controlled and calibrated before the actual survey started. A standard sphere calibration was carried out. For calibration of the 38kHz sounder a 60 mm cupper sphere (CU60), Ts -33,7 dB, was used. Agreement between means of the calibrations this year and value from last year on the same systems, was better than 0.1 dB.

2.5 Acoustic data collection

Acoustic data were collected 24 hours per day using a SIMRAD EK500 38 kHz echo sounder with an ES38B transducer mounted on the drop keel. Additional data were collected at 18 and 120 kHz but these were not used for the present assessment. Echo integrator data was collected from 10 m below the surface (transducer at 5-7.5 m

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depth, depending on weather conditions and the keel in use) to 1 m above the seabed.

The main settings of the acoustic instruments are given in Table 1. The speed of the vessel during the acoustic sampling was 10-11 knots. The acoustic data were archived to tape. The acoustic recordings were scrutinized twice per day using the IMR BEI/SIMRAD BI500 Scientific Post Processing System (The Bergen Echo Integrator) (Foote et al. 1991). Paper records were kept for acoustic data at 38 kHz. Herring were separated from other recordings by using catch information and characteristics of the recordings..

2.6 Biological data - fishing trawls

Trawling was carried out for supporting the species identifications of acoustic scatters and for bilogical sampling. The survey started with using a “Fotö” trawl (16 x 20 m) for pelagic trawling and a Campelen 1800 equipped with a Rock hopper gear used for bottom trawling. To be able to handle pelagic trawling close to bottom as well as at surface, a “Fotø”-trawl was used.. Half-way through the survey the “Fotö”-trawl was damaged and replaced by a “Åkra”-trawl. The bottom trawl hauls were monitored using Simrad TS150 scanning net-sonde and the pelagic trawl hauls monitored by Scanmar TE40, and depth sensor D1200.

Biological samples (length, weight) were taken of the most important species according to the IMR fish sampling manual (Fotland et.al. 2000). Target species were also examined for age, sex, maturity (8 point scale), fat, stomach contents and macroscopic evidence of Ichthyophonus infection. Off the south-west coast of Norway, North Sea autumn spawners (NSAS) and Western Baltic spring spawners (WBSS) mix during summer. No system for routine stock discrimination on individual herring during the survey, is available. East of 2°00’E vertebral counts were therefor taken for stock separation.

2.7 Hydrographic data

CTD stations for temperature, salinity and density measures, were taken regularly in addition to the four standard hydrographical profiles, Oksøy-Hanstholm, Hanstholm- Aberdeen, Utsira - Start Point and Feie – Shetland.

2.8 Data analysis

Echogram scrutiny was made per 5 n.mi, in a Bergen Echo Integrator System (BEI).

The SA values were allocated to the following categories: herring, sprat, pelagic and demersal fish, plankton and other. To calculate integrator conversion factors the target strength of clupeids in the mixture were estimated using the following TS/length relationship:

TS = 20log10L -71.2 dB

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The abundance estimation is made by ICES rectangles and summed up for the whole area. Toresen et al (1998) describes the acoustic method used for the abundance estimation in this survey.

North Sea autumn spawners and Western Baltic spring spawners (WBSS) are mixed during summer in the southern part of the area covered by RV ”GOSars”. No system for routinely stock discrimination on individual herring during the survey is available.

The proportion of Baltic spring spawners and North Sea autumn spawners by age were calculated by applying the formula, WBSS= ((56,5-VS(sample))/(56.5-55.8)) (ICES 1999). All samples were worked up on board. Sampling procedures are described in Fotland et al.2000. The length-at age and weight-at age were assumed to be the same in the two stocks. The measured proportions of mature fish were applied equally to calculate the maturing part of each age group in both stocks

3. RESULTS & DISCUSSION

3.1 Hydrological data

Altogether 168 CTD-stations were taken (Fig. 3). The horizontal temperature

distributions at 5m, 50m and bottom, are shown in Figure 4a-c. The surface water in the North Sea had temperatures ranging from 12-14° C in west to 15-16° C along the Norwegian west coast. The temperatures at 5 m depth in the south eastern area were about 2°C lower than at the same time in 2001 (Torstensen, 2001). At 50 m and at bottom the temperature regime was about 1-2° C higher then last year.

3.2 Acoustic data 3.2. 1 Herring

The geographical distribution of the mean-SA values assigned to herring are presented in Figure 5. The main areas of concentration were the south western corner of the surveyed area and off the south-western Norwegian coast (Figure 6). High densities were also recorded in the ICES rectangles 47E8-E9 and 49E9, 50E9-F0, but are not included in the present estimates. While few or no schools of herring have been observed during the last surveys, large and smaller herring schools were recorded this year. The majority of the trawling positions were, however, regularly chosen with trawling at surface every 20-30 nautical miles; i.e not based on echo registration. Due to the behaviour to keep close to the surface during day-time, herring may have been under-estimated.

The abundance by ICES statistical rectangles, divided in Western Baltic spring spawners and North Sea autumn spawners, are given in Table 2. The numbers are given age disaggregated. The numbers in age groups 1, 2 and 3 are split in mature/immature parts. Table 3 presents the mean weights at age applied for biomass estimations. Total estimated number of herring by age and length are given in Table 4. The total estimated biomass per age group and stock is also given in the table.

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3.2.2 Sprat

Small values of sprat were measured in the shallow areas near Hanstholm, Denmark, in ICES square 43F8. No sprat were recorded in the target area of the Norwegian survey.

3.3 Biological data

The total number of valid trawl hauls were 99, 84 pelagic and 15 bottom trawl hauls (Fig. 2, Table 5). Of the pelagic hauls, 7 were midwater hauls, 6 hauls were taken close to the bottom and 71 were performed with large buoys for fishing in the surface.

In general 30 min hauls were made. Herring was present in 54 trawl hauls (Table 6) of which 41 had sample size >20 herring. Length distribution of herring by trawl haul east of 2ºE are given in Table 7. Age-length key with total number of otoliths by age and length class is given in Table 5. The data on age, length weight and maturity stages, were made for both stocks combined; the North Sea autumn spawners and the Western Baltic Spring Spawners. 3.678 fish were length measured and 2.047 fish were aged (otoliths).

3.4 Biomass estimates 3.4.1 Herring

Total estimates of the spawning stock biomass of North Sea herring and Western Baltic spring spawners for 1997-2002, are given in the text table below. The total herring biomass in the area was 503,000 t. Though some differences in the ICES- rectangles covered in the south-south east, the herring biomass was substantially increased from 273,000 t in 2001. This was mainly caused by high abundance of 1- ringers (2000 year class). The estimated spawning stock biomass of North Sea herring was about 90 200 t which is an increase of abt 76 % compared to the 2001-estimate.

There was a minor increase in the estimated biomass of Baltic spring spawners in the North Sea, 96 700 tonnes.

Year Herring Biomass (103 tonnes) North Sea herring SSB Western Baltic

Spring Spawners

1997 50 160

1998 73 88

1999 259 74

2000 13 51

2001 51 89

2002 90 97

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4. REFERENCES

Fotland, AA., Borge, A., Gjøsæter, H. and Mjanger, H. 2000. Manual for sampling of fish and shellfish. (In Norwegian). Ver. 3.14. Institute of Marine Research.

Foote, K.G., Knudsen, H.P., Korneliussen, R.J., Nordbø, P.E. and Røang, K. 1991.

Postprocessing system for echo integrator data. J.Acoust. Soc. Am., 90, 37-47.

ICES 1999. Report of the Herring Assessment Working Group for the Area South of 62oN. ICES CM 1999/ACFM: 12

ICES 2002. Report of the Planning Group for herring surveys. 2002/G:02

Toresen, R., Gjøsæter, H. and de Barros, P. 1998. The acoustic method as used in the abundance estimation of capelin (Mallotus villosus Müller) and herring (Clupea harengus Linné) in the Barents Sea. Fisheries Research, 34: 27-37.

Torstensen, E. 2001. Survey Report, RV “Michael Sars” 29 June- 23 July 2001. IMR.

Internal Survey Reports. 9pp.

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Table 1. Simrad EK500 and analysis settings used on the GOS2002009 herring acoustic survey.

Transceiver 1 Menu Absorption coefficient 10 dB.km-1

Pulse length Medium Bandwidth Wide Max. Power 2000 W Equivalent two-way beam angle -21.0 dB

3 dB Beamwidth 7.3/7.0 deg Alongship offset -0.05 deg Althw.Ship Offset -0.01 deg Calibration details

TS of sphere -33.6 dB (cupper 60 mm diameter) Range to sphere in calibration 23.3

Selected (sA) NASCvalue for calibration 4372 Log Menu GPS

Operation Menu

Ping interval 0.0 (all ranges) Display / Printer Menu

TVG 20 log R Integration line 1000

TS colour min. -50 dB Sv colour min. -70 dB

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Table 2. HERRING-NORTH SEA. Estimated number by age and maturity by stocks by ICES rectangles. RV “G.O.Sars”, 27 June-20 July 2002. (I= immature, M=mature)

42F2 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 1016.76 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 1016.76

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

42F3 North Sea Autumn spawners

0 1 1M 2M 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 304.64 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 304.64

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

42F4 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 267.19 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 267.19

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

42F5 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 49.94 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 49.94

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

43F2 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 1135.77 4.69 9.23 0.00 2.31 2.31 0.00 0.00 0.00 0.00 0.00 0.00 1154.31

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

43F3 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 2227.37 15.70 5.62 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 2248.70

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

43F4 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 345.48 0.00 0.87 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 346.34

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

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Table. 2. Cont.

43F5 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 131.26 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 131.26

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

44F2 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 124.52 0.00 4.37 2.18 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 131.08

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

44F3 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 2.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 2.00

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

44F4 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

44F5 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 174.67 3.16 3.79 0.45 0.65 1.72 0.00 0.00 0.00 0.00 0.00 0.00 184.43

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 91.13 1.65 9.47 1.11 1.61 4.30 0.00 0.00 0.00 0.00 0.00 0.00 109.28

45F2 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 15.66 0.42 1.45 0.24 0.17 0.46 0.00 0.00 0.00 0.00 0.00 0.00 18.40

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 5.42 0.15 1.93 0.32 0.43 1.15 0.00 0.00 0.00 0.00 0.00 0.00 9.40

45F3 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 169.27 4.53 15.64 2.61 1.87 4.98 0.00 0.00 0.00 0.00 0.00 0.00 198.90

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 58.59 1.57 20.85 3.47 4.67 12.46 0.00 0.00 0.00 0.00 0.00 0.00 101.61

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Table. 2. Cont.

45F4 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 47.56 2.13 3.05 0.38 0.77 2.06 0.00 0.00 0.00 0.00 0.00 0.00 55.96

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 12.97 0.58 12.21 1.53 1.94 5.16 0.00 0.00 0.00 0.00 0.00 0.00 34.38

45F5 North Sea Autum North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 38.11 4.48 1.64 2.30 0.00 0.00 2.82 0.00 0.00 0.00 0.00 0.70 50.06

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 10.39 1.22 2.46 3.45 3.00 8.26 0.00 0.00 0.00 0.00 0.00 0.00 28.80

46F2 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 3.26 0.00 5.72 40.07 1.26 21.46 6.22 0.00 0.00 0.00 0.00 0.00 77.99

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 2.96 0.00 0.49 3.45 0.81 13.77 0.00 0.00 0.00 0.00 0.00 0.00 21.49

46F3 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 1.77 9.74 6.14 56.77 3.12 32.28 3.12 3.12 1.56 0.00 0.00 0.00 117.63

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 1.61 8.86 0.53 4.89 2.00 20.71 0.00 0.00 0.00 0.00 0.00 0.00 38.60

46F4 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 333.78 20.03 11.44 4.00 0.00 0.00 18.69 0.00 0.00 0.00 0.00 0.00 387.95

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 98.90 5.93 55.30 19.36 30.23 39.30 0.00 0.00 0.00 0.00 0.00 2.23 251.26

46F5 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 5.84 0.46 0.26 0.09 0.00 0.00 0.36 0.00 0.00 0.00 0.00 0.05 7.06

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 1.21 0.10 1.24 0.43 0.60 0.86 0.00 0.00 0.00 0.00 0.00 0.00 4.43

47F2 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.45 0.23 0.00 9.91 0.20 7.09 0.00 0.00 0.00 0.00 0.00 0.00 17.88

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.15 0.07 0.00 0.00 0.21 7.50 3.60 2.40 1.80 1.20 0.30 0.00 17.24

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Table. 2. Cont.

47F3 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 4.39 3.13 1.69 44.68 1.19 37.99 28.56 11.43 0.00 0.00 0.00 0.00 133.05

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 1.41 1.01 0.00 0.00 0.54 17.41 0.41 0.17 5.80 4.97 0.83 0.00 32.54

47F4 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 224.98 2.88 17.66 5.89 14.39 15.29 14.87 2.18 0.70 0.00 0.00 0.00 298.83

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 37.50 0.48 44.14 14.71 20.34 21.61 21.02 3.08 0.99 0.00 0.00 0.00 163.88

48F2 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 9.79 0.09 2.18 1.09 0.33 0.91 3.10 1.22 0.73 0.31 0.05 0.21 20.01

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 1.09 0.01 0.87 0.44 1.22 3.32 1.24 0.49 0.29 0.12 0.02 0.08 9.20

48F3 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 84.35 0.81 18.75 9.38 2.86 7.81 26.75 10.54 6.28 2.69 0.45 1.79 172.46

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 9.37 0.09 7.50 3.75 10.50 28.64 10.70 4.21 2.51 1.08 0.18 0.72 79.25

48F4 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 114.75 1.05 2.15 0.00 1.12 0.32 0.00 0.00 0.00 0.00 0.00 0.00 119.39

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 16.70 0.00 7.57 2.16 5.68 0.99 0.00 0.00 0.00 0.00 33.10

49F2 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 10.38 0.18 0.48 0.36 0.26 1.40 1.01 0.19 0.06 0.25 0.00 0.00 14.57

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.64 0.48 0.12 0.69 0.35 0.07 0.02 0.09 0.00 0.00 2.46

49F3 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 28.37 0.34 0.82 0.61 0.51 2.24 1.37 0.37 0.09 0.37 0.00 0.00 35.08

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 2.18 0.03 1.09 0.82 0.27 1.17 0.72 0.19 0.05 0.19 0.00 0.00 6.70

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Table. 2. Cont.

49F4 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 174.90 2.11 5.05 3.79 3.13 13.79 8.46 2.26 0.56 2.26 0.00 0.00 216.31

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 13.45 0.16 6.73 5.05 1.64 7.20 4.42 1.18 0.29 1.18 0.00 0.00 41.29

50F2 North Sea Autumn Spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 6.63 0.13 2.34 1.43 1.69 4.29 2.99 0.65 0.26 0.52 0.00 0.00 20.92

Baltic Spring Spawner

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

50F3 North Sea Autumn Spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 4.35 0.09 1.54 0.94 1.11 2.81 1.96 0.43 0.17 0.34 0.00 0.00 13.73

50F4 North Sea Autumn Spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

51F2 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.32 0.00 3.16 2.29 2.85 7.71 3.52 0.96 0.32 0.64 0.00 0.00 21.76

51F3 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.22 0.00 2.18 1.58 1.97 5.32 2.43 0.66 0.22 0.44 0.00 0.00 15.03

52F2 North Sea Autumn spawners

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

(13)

Table 3. HERRING NORTH SEA. Weight at age and maturity by ICES rectangles.

RV “G.O.Sars”, 27 June-20 July 2002. (I=immature, M=mature)

51F3

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

93.00 113.50 126.14 127.44 156.08 155.20 188.33 142.00 226.00 144.00

51F2

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

93.00 113.50 126.14 127.44 156.08 155.20 188.33 142.00 226.00 144.00

50F3

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

64.35 106.00 107.28 117.64 117.08 149.06 140.22 195.00 161.50 225.00 93.20

50F2

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

64.35 106.00 107.28 117.64 117.08 149.06 140.22 195.00 161.50 225.00 92.80 50F0

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

148.00 173.90 187.50 181.40 211.70 229.90 271.40 193.60 50E9

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

148.00 174.20 184.40 176.80 207.90 245.80 211.00 188.30 49F4

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

66.50 93.50 98.10 124.20 88.60 136.80 129.10 211.80 181.00 229.50 81.60 49F3

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

66.50 93.50 98.10 124.20 88.60 136.80 129.10 211.80 181.00 229.50 81.60 49F2

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

67.40 93.50 98.10 124.20 93.80 136.80 129.10 225.30 181.00 229.50 92.80

49E9

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

148.00 174.20 184.40 176.80 207.90 245.80 211.00 188.30 48F4

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

63.80 101.00 86.30 101.30 108.00 121.80 111.00 71.00

(14)

Table 3. Cont.

48F3

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

74.40 81.00 96.50 178.90 104.30 180.40 166.80 229.90 263.40 252.40 208.00 358.00 134.80

48F2

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

74.40 81.00 96.50 178.90 104.30 180.40 166.80 229.90 263.40 252.40 208.00 358.00 134.80

47F4

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

63.20 186.00 78.30 156.80 78.60 169.30 156.40 189.30 275.00 94.30

47F3

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

101.90 93.60 140.50 158.10 92.00 182.50 202.70 212.30 237.30 224.00 227.00 177.90

47F2

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

108 87.5 0 160.30 85.00 190.60 196.10 203.40 235.40 227.00 227.00 182.30

46F5

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

50.60 64.70 75.70 71.70 82.30 103.80 106.60 0.00 0.00 0.00 0.00 117.00 64.50

46F4

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

52.80 64.70 75.70 71.70 82.10 103.80 106.60 117.00 65.60

46F3

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

80.00 134.10 101.50 124.40 72.70 123.90 122.00 141.50 155.00 122.40

46F2

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

66.70 100.70 133.10 93.00 126.10 152.30 124.80

45F5

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

49.90 64.70 74.60 71.70 92.50 103.10 110.70 117.00 65.40

45F4

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

78.20 76.00 84.80 91.00 88.70 93.40 81.10

45F3

0 1 1M 2I 2M 3I 3M 4 5 6 7 8 9+ Total

74.80 76.00 87.30 93.30 88.70 93.40 78.40

Referanser

RELATERTE DOKUMENTER

a result of an immigration of spring spawners or an emigration of autumn spawners is unknown. from the end of July to the beginning of September, the sprirtg

When treating the samples of North Sea autumn spawners separately, the differences in distributions of the types of weak esterase zones were found to be significant

Figure 8 Numbers (millions) of Western Baltic spring spawning herring from combined acoustic survey June - July 2002... Figure 10 Abundance of mature Western Baltic spring

The biomass and abundance by year-class estimated during the blue whiting surveys in the Norwegian Sea since 1983 are given in the text-table below... One of

a) review and update catch at age and mean weight at age data including information on proportions of North Sea autumn spawners and Western Baltic spring

HAWG was able to carry out age-based assessments on 3 of the herring stocks: North Sea autumn spawners, western Baltic spring spawners and autumn spawning herring to the west

Except in cases where the necessary data are missing, data are displayed separately for herring caught in the North Sea (including a minor amount of Western Baltic spring

While the Kattegat samples seem to consist very predominantly of spring spawners, with a possible ad- mixture of Baltic autumn spawners, those from the Skagerrak