GREATER SILVER SMELT

Argentina silus


Technical report
Published by

Marine and Freshwater Research Institute, Iceland

Published

6 June 2025

Key signals

  • Survey biomass has been increasing since 2013 and reached the highest levels in the timeseries in 2023.

  • Recruitment was higher 10 years ago, which explains the increase in survey biomass, but is around average this year.

  • Length distributions are very consistent from one year to another as measured in the autumn survey, with a mean length of ~39 cm.

  • Spawning stock biomass has been increasing since 2013 and is at an all time high, but has been above \(B_{lim}\) since 2014.

  • Fishing mortality (F) is below \(F_{MSY}\) and has been since 2017.

General information

Greater silver smelt is a rather small silvery bathypelagic species that can form large schools close to the seafloor mainly at depths >500 m. In Icelandic waters it can live to around 26 years old. Juveniles tend to aggregate in shallower depths. Greater silver smelt mainly feed on zooplankton (e.g., euphausiids, amphipods, and copepods) or small nekton (e.g., squids, jellyfish, or fish).

The Fishery

Fleets

Since 1996 between 20 and 40 trawlers have annually reported catches of greater silver smelt in Icelandic waters (Table 1). The trawlers participating in the greater silver smelt fishery also target Icelandic slope beaked redfish (Sebastes mentella) and to lesser extent Greenland halibut and blue ling. Number of hauls peaked in 2010, but have decreased since then in line with lower total catches. In the most recent years number of hauls have increased. In most years over 50% of the greater silver smelt catches are taken in hauls where the species is more than 50% of the catch (Table 1).

Table 1: Greater silver smelt in Icelandic waters. Information on the fleet reporting catches of greater silver smelt.

Year

Number of trawlers

Number of hauls

Reported catch (tonnes)

No. hauls which GSS > 50% of catch

Proportion of catch in hauls where GSS > 50%

1997

26

874

2282

355

0.822

1998

40

2683

11389

1991

0.947

1999

25

1509

4564

810

0.849

2000

23

1301

3550

608

0.797

2001

26

794

1606

245

0.692

2002

32

1160

3158

468

0.744

2003

30

1176

2005

213

0.473

2004

27

1052

2733

292

0.653

2005

30

1388

3558

335

0.707

2006

31

1554

3736

355

0.690

2007

27

1275

3470

416

0.718

2008

31

3261

8569

848

0.648

2009

34

3555

10425

1010

0.680

2010

36

4847

16500

1821

0.727

2011

34

3309

10237

961

0.715

2012

31

3395

9776

988

0.710

2013

31

2743

7247

609

0.642

2014

24

2363

6195

487

0.608

2015

24

2195

5835

356

0.574

2016

26

2096

5719

385

0.593

2017

21

1363

3894

236

0.584

2018

20

1440

3893

215

0.479

2019

28

1169

2570

143

0.506

2020

25

1170

2968

174

0.475

2021

27

1166

3439

189

0.663

2022

31

1697

6230

468

0.726

2023

25

1992

5321

348

0.652

2024

29

1966

8333

591

0.858

Targeting and mixed fisheries issues in the fishery in Icelandic waters

Mixed fisheries issues: species composition in the fishery

Redfish spp. (golden redfish (Sebastes norvegicus) and deepwater redfish (S. mentella)) are the main bycatch species in the mixed fishery encompassing greater silver smelt. Other species of lesser importance are Greenland halibut, blue ling and ling. Other species than these rarely exceed 10% of the bycatch in the greater silver smelt fishery in Icelandic waters (Table 2).

Table 2: Greater silver smelt in Icelandic waters. Proportional (%) bycatch species composition where greater silver smelt was more than 50% of the total catch in a haul.

Year

Golden redfish

Deepwater redfish

Greenland halibut

Ling

Blue ling

Other

1997

1.4

79.3

0.0

6.8

7

5.4

1998

5.2

77.5

0.0

3.5

7

6.7

1999

4.1

79.8

0.0

2.7

6

7.6

2000

4.9

70.9

0.2

0.3

10

13.7

2001

22.7

55.0

4.5

0.5

1

16.1

2002

17.3

73.9

0.4

1.2

4

3.1

2003

38.4

51.2

0.4

0.0

5

4.8

2004

24.9

68.7

0.7

0.1

1

4.8

2005

15.4

69.9

4.2

1.4

3

6.1

2006

28.8

59.8

1.4

0.9

1

8.1

2007

11.9

71.2

5.9

0.3

6

4.6

2008

26.7

60.8

2.8

1.2

5

3.3

2009

20.1

64.6

3.2

0.2

8

4.0

2010

16.0

63.7

2.0

0.9

6

11.1

2011

13.2

66.4

2.2

0.4

5

13.0

2012

8.8

67.3

1.3

0.2

8

14.8

2013

9.5

63.9

4.6

0.1

9

12.6

2014

2.5

78.3

2.8

0.3

5

10.7

2015

12.6

64.1

4.7

0.2

4

14.5

2016

10.9

73.5

5.4

0.2

3

7.1

2017

2.9

85.6

1.6

0.2

3

6.8

2018

4.7

87.7

2.0

0.0

2

4.0

2019

7.8

81.2

1.8

0.6

2

7.0

2020

5.6

87.5

1.7

0.1

1

4.2

2021

11.6

72.3

5.8

0.3

1

8.7

2022

5.7

84.0

4.0

0.2

3

2.9

2023

10.6

58.9

21.4

0.3

2

6.8

2024

9.8

64.4

5.0

0.6

4

16.3

Spatial distribution of catches through time

Most of the catches since 1997 have been taken at the southern edge of the Icelandic shelf (Figure 3). In the period, a gradual relative increase is seen in the western area and a gradual decrease in the southeastern area (Figure 3).

Spatial distribution of catches in Icelandic waters has not changed markedly in recent years (Figure 3 and Figure 4) but fishing for greater silver smelt in the NW area seems to have reduced (Figure 3).

Figure 3: Greater silver smelt. Catch distribution and proportions by area according to logbooks.
Figure 4: Greater silver smelt. Spatial distribution of catches as reported in logbooks.
Table 3: Greater silver smelt. Landings (tonnes) records from the Icelandic directorate of Fisheries and Greenland.

Year

Section 5.a

Section 14.b

Total

1988

241

0

241

1989

8

0

8

1990

113

0

113

1991

246

0

246

1992

657

0

657

1993

1526

0

1526

1994

756

0

756

1995

586

0

586

1996

881

0

881

1997

3935

0

3935

1998

15242

0

15242

1999

6681

0

6681

2000

5657

0

5657

2001

3043

0

3043

2002

4960

0

4960

2003

2680

0

2680

2004

3645

0

3645

2005

4482

0

4482

2006

4769

0

4769

2007

4227

0

4227

2008

8778

0

8778

2009

10828

0

10828

2010

16428

0

16428

2011

10516

0

10516

2012

9289

0

9289

2013

7155

0

7155

2014

6344

4

6348

2015

6058

23

6081

2016

5646

16

5662

2017

4344

666

5010

2018

4035

425

4460

2019

3209

2

3211

2020

3775

27

3802

2021

4140

15

4155

2022

6886

28

6914

2023

5268

0

5268

2024

9032

0

9032

Data available

In general, sampling from commercial catches is considered representative of the stock, as one of the requirements of owning a fishing license for greater silver smelt is the retention of scientific samples (Table 4). Samples were only obtained from bottom trawls. The sampling does seem to cover the spatial and temporal distribution of catches. In recent years there was a decline in sampling which has been improved since 2023. The sampling coverage in 2025 is shown in Figure 5.

Figure 5: Greater silver smelt. Fishing grounds as reported in logbooks and positions of samples taken from landings (asterisks).

Landings and discards

Landings by Icelandic vessels are given by the Icelandic Directorate of Fisheries. Discarding is banned in Icelandic waters, and currently there is no available information on greater silver smelt discards. It is however likely that unknown quantities of greater silver smelt were discarded prior to 1996.

Length compositions

Table 4 gives the number of samples and measurements available for calculations of catch in numbers of greater silver smelt in Icelandic waters. Mean length of greater silver smelt in catches has been rather stable from 2005 in the range of 37 – 43 cm (Figure 6). However, there was a slight increase in mean length in 2012 and again in 2018 (Figure 6).

Figure 6: Greater silver smelt. Relative length distributions from Icelandic commercial bottom trawl catches.

Age compositions

Table 4 gives the number of samples and measurements available for calculations of catch in numbers of greater silver smelt in Icelandic waters. Mean ages from catches have been variable from 2000 in the range 6 – 14 years, with relatively high mean ages when catches are low (Figure 7, Figure 8, Figure 9). The reason for these changes is not known as there is no marked difference in the spatial distribution of the fishery; however, reduced fishing pressure may be a factor.

Table 4: Greater silver smelt. Summary of sampling intensity and overview of available data.

Year

No. length samples

No. length measurements

No. otolith samples

No. aged otoliths

1997

48

4992

1447

1059

1998

148

15559

6964

889

1999

58

4163

2180

82

2000

27

2968

1011

113

2001

10

489

245

17

2002

21

2270

360

127

2003

63

5095

425

0

2004

34

997

225

84

2005

49

3708

772

0

2006

29

4186

616

525

2007

14

2158

285

272

2008

44

3726

1768

1387

2009

53

5702

1746

1574

2010

134

16353

3370

3120

2011

63

6866

1953

1774

2012

43

4440

1492

603

2013

47

4977

710

704

2014

39

4709

350

340

2015

11

1275

221

217

2016

45

5879

285

283

2017

29

3466

430

416

2018

12

1437

185

181

2019

10

1250

40

40

2020

12

1905

130

130

2021

14

1301

215

214

2022

8

603

165

165

2023

28

2789

479

476

2024

23

1964

455

448

Figure 7: Greater silver smelt. Catch weights by age from the commercial fishery in Icelandic waters.