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 |
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
Landings trends
Landings of greater silver smelt are presented in Table 1 and Figure 1. Since directed fishery started in 1997–1998, the landings increased from 800 t in 1996 to 15 200 t in 1998. Between 1999 and 2007 catches varied between 2700 to 6700 t. Since 2008 landings have increased substantially, from 4200 t in 2007 to almost 16 400 t in 2010. In 2011 landings started to decrease due to increased management actions. Since 2019, landings have increased and amounted to 9032 in 2024. Landings were reported in Greenlandic waters in 2017 and 2018; however, these exploratory directed fisheries appear to have ceased in 2019 but should be monitored for reappearance.
Greater silver smelt is mostly fished along the south and southwest coast of Iceland, at depths between 500 and 800 m, as targeted fishing is only allowed at depths greater than 400 m (Figure 2). Greater silver smelt has been caught in bottom trawls for years as a bycatch in the redfish fishery. Only small amounts were reported prior to 1997 as most of the greater silver smelt was discarded.
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).
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).
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).
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.
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).
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.
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 |