Fishery
The main fishing grounds for Atlantic wolffish are in the west and northwest part of the Icelandic shelf. From 2010, the proportion of the catch has been increasing in northwest of Iceland compared to west of Iceland. Catches at the main spawning ground (Látragrunn) west of Iceland have been decreasing since 2008 (Figure 1 and Figure 2). About 80% of the catch of Atlantic wolffish is caught at depths less than 120 m. Proportion of the catch taken at depth range 0-60 m decreased from 2003 to 2007, but since then it has been increasing. At the depth range 61-120 m the proportion of the catch has been rather stable since 2000. At depths from 121 to 180 m, which includes the main spawning ground (Látragrunn), it the proportion of the catch increased in 2003-2008 but since then it has been decreasing (Figure 3).
Landings trend
More than 97% of the Atlantic wolffish catch is taken by longliners (50-65%), demersal trawlers (20-30%) and demersal seiners (about 10%) (Figure 4). These proportions have been relatively stable through the years. However, in 2004-2008 longline and demersal trawl catches were similar (40-50%) and in the last three years catches by demersal seiners hasve been increasing and are now greater than in demersal trawlers (Figure 4). Since 2001, the number of longliners and trawlers reporting Atlantic wolffish catches of 10 tonnes/year or more has decreased. In the longline fleet, the number of vessels has dropped from 198 in 2001, down to 36 in 2023. The number of trawlers has also decreased significantly from 76 in 2000 to 49 in the last year (Table 1).
In 1994 and 1995, more than 500 vessels accounted for 95% of the annual catch of Atlantic wolffish in Icelandic waters, but this number had dropped to 200 vessels in 2008 despite higher catches. Since 2010 the number of vessels accounting for 95% of the annual catch has remained relatively constant (about 150-200 vessels), despite catch reductions (Figure 5).
| Year | nr. longlines | nr. bottom trawls | nr. seiners | nr. other gear | Catch longlines | Catch bottom trawls | Catch seiners | Catch other gear | Total |
|---|---|---|---|---|---|---|---|---|---|
| 2000 | 161 | 53 | 16 | 0 | 8687 | 3380 | 528 | 0 | 12595 |
| 2001 | 195 | 59 | 14 | 1 | 11267 | 3391 | 513 | 11 | 15182 |
| 2002 | 140 | 44 | 13 | 0 | 7773 | 3735 | 601 | 0 | 12110 |
| 2003 | 138 | 45 | 19 | 0 | 7785 | 5463 | 1066 | 0 | 14313 |
| 2004 | 103 | 34 | 29 | 0 | 4670 | 4773 | 1609 | 0 | 11052 |
| 2005 | 91 | 47 | 24 | 1 | 5445 | 6893 | 1140 | 30 | 13508 |
| 2006 | 120 | 48 | 25 | 0 | 6626 | 6286 | 1149 | 0 | 14061 |
| 2007 | 105 | 60 | 24 | 0 | 5259 | 7566 | 1338 | 0 | 14163 |
| 2008 | 87 | 60 | 22 | 3 | 4663 | 6960 | 1427 | 44 | 13093 |
| 2009 | 114 | 55 | 28 | 1 | 6708 | 5468 | 1205 | 10 | 13391 |
| 2010 | 74 | 46 | 20 | 3 | 5916 | 4436 | 842 | 92 | 11286 |
| 2011 | 64 | 37 | 18 | 0 | 5344 | 3565 | 1010 | 0 | 9918 |
| 2012 | 66 | 24 | 22 | 1 | 5328 | 2827 | 895 | 41 | 9091 |
| 2013 | 73 | 30 | 18 | 2 | 4652 | 2341 | 647 | 22 | 7662 |
| 2014 | 70 | 23 | 13 | 1 | 3681 | 1637 | 891 | 11 | 6220 |
| 2015 | 56 | 34 | 17 | 2 | 3989 | 1905 | 926 | 28 | 6848 |
| 2016 | 61 | 37 | 18 | 2 | 4848 | 1662 | 1127 | 25 | 7661 |
| 2017 | 59 | 28 | 18 | 2 | 3829 | 1102 | 1095 | 23 | 6049 |
| 2018 | 60 | 37 | 27 | 6 | 4923 | 1587 | 2186 | 74 | 8770 |
| 2019 | 64 | 34 | 21 | 1 | 4595 | 1630 | 2168 | 11 | 8404 |
| 2020 | 46 | 38 | 24 | 1 | 2491 | 2046 | 2040 | 11 | 6588 |
| 2021 | 45 | 48 | 22 | 0 | 3343 | 3021 | 2086 | 0 | 8451 |
| 2022 | 40 | 48 | 23 | 0 | 2706 | 2986 | 2275 | 0 | 7967 |
| 2023 | 36 | 49 | 20 | 0 | 3154 | 2756 | 2388 | 0 | 8298 |
Data available
The commercial catch samples taken are normally representative of the landings with most number of samples taken in areas of high catch intensity (Figure 7).
Landings and discards
Landings by Icelandic vessels are given by the Icelandic Directorate of Fisheries. Landings of Norwegian and Faroese vessels are given by the Icelandic Coast Guard. Discarding is banned by law in the Icelandic demersal fishery, as well as in Norway. Measures in the Icelandic management system such as converting quota share from one species to another are used by the Icelandic fleet to a large extent, and this is thought to discourage discards in mixed fisheries.
Sampling from commercial catches
In 1969-1997, on average 500 otoliths were sampled annually, except in 1970, 1973, and 1974 when no otoliths were sampled. In 1999, the effort of sampling Atlantic wolffish from commercial catch was increased. In the years 1999-2014 annual sampling of aged fish was 1600-3000 or on average 2200, but since 2015 this average has been around 1200 fish. In 2023, a total of 12, 21 and 25 samples were collected from longline, demersal trawl and demersal seine catches, respectively (Table 2, Figure 6).
| Year | Longline (nr. of samples) | Longline (nr. fish) | Bottom trawl (nr. of samples) | Bottom trawl (nr. fish) | Demersal seine (nr. of samples) | Demersal seine (nr. fish) |
|---|---|---|---|---|---|---|
| 2000 | 29 | 1395 | 18 | 752 | 4 | 200 |
| 2001 | 27 | 1343 | 11 | 509 | 3 | 150 |
| 2002 | 25 | 1240 | 16 | 645 | 2 | 100 |
| 2003 | 31 | 1525 | 20 | 899 | 6 | 300 |
| 2004 | 19 | 950 | 23 | 1060 | 8 | 400 |
| 2005 | 15 | 746 | 25 | 1202 | 6 | 292 |
| 2006 | 23 | 1110 | 21 | 1029 | 5 | 250 |
| 2007 | 18 | 900 | 25 | 1250 | 10 | 451 |
| 2008 | 19 | 950 | 25 | 1248 | 4 | 200 |
| 2009 | 16 | 800 | 20 | 999 | 4 | 200 |
| 2010 | 29 | 1669 | 19 | 1090 | 5 | 285 |
| 2011 | 14 | 750 | 15 | 778 | 9 | 550 |
| 2012 | 26 | 1300 | 14 | 700 | 7 | 350 |
| 2013 | 25 | 1249 | 14 | 691 | 4 | 200 |
| 2014 | 30 | 800 | 26 | 675 | 28 | 700 |
| 2015 | 25 | 625 | 19 | 479 | 19 | 474 |
| 2016 | 25 | 625 | 13 | 325 | 9 | 225 |
| 2017 | 23 | 575 | 9 | 220 | 6 | 150 |
| 2018 | 22 | 550 | 9 | 225 | 17 | 425 |
| 2019 | 22 | 550 | 11 | 276 | 20 | 500 |
| 2020 | 9 | 225 | 14 | 350 | 16 | 400 |
| 2021 | 14 | 350 | 25 | 625 | 15 | 375 |
| 2022 | 3 | 60 | 23 | 465 | 17 | 338 |
| 2023 | 12 | 240 | 21 | 420 | 25 | 499 |
Length composition
The length distribution of landed Atlantic wolffish has been relatively stable since 2005 (Figure 7).
Age composition
Age composition data are available from surveys and from commercial catch. Commercial age data are available from earlier periods (1978). In samples from commercial landings, the mean age of Atlantic wolffish was around 10.7 years in 1999. Since then, mean age in samples from commercial catches has generally been increasing to around 12 years in recent years. In 2023, 8-16 year old fish are most common in catch (Figure 8 and Figure 9)
Weight-at-age
Weight-at-age data in Icelandic waters are available from 1996. Weight of the oldest year classes has been above average for the past years (Figure 10). Catch weight are shown in Figure 11.
Catch and effort
CPUE estimates of Atlantic wolffish in Icelandic waters are not considered representative of stock abundance, as changes in fleet composition, technical improvements and differences in gear setup among other things have not been accounted for when estimating CPUE. Non-standardized estimates of CPUE in longline (kg/1000 hooks), and demersal trawl (kg/hour), are calculated as the total weight in sets or tows in which Atlantic wolffish was more than 10% of the catch, according to logbooks. Effort of demersal trawl was defined as the number hours towed, and for longline number of hooks, in both cases where Atlantic wolffish was more than 10% of the catch. CPUE in longline vessels has been similar among years prior to 2018, around 100-150 kg/1000 hooks. CPUE of demersal trawl increased from about 230 to 400 kg/h in 2000-2005, but since 2006 it has fluctuated at around 250-300 kg/h (Figure 12). Both indices have shown a sharp decrease over the past three years. Fishing effort in longline increased from 66 million hooks in 2000 to 97 million hooks in 2001. Since then it has been generally decreasing and was around 22 million hooks in 2018. In demersal trawl, fishing effort increased from about 14 thousand tow-hours in 2004 to 23 thousand tow-hours in 2008, followed by a sharp decrease to 4.8 thousand tow-hours in 2014. Since then it has increased.
Survey data
The Icelandic spring groundfish survey (hereafter spring survey, IGFS), which has been conducted annually in March since 1985, covers the most important distribution area of Atlantic wolffish in Icelandic waters. In addition, the Icelandic autumn groundfish survey (hereafter autumn survey, IAGS) was started in 1996 and expanded in 2000. However, a full autumn survey was not conducted in 2011 due to a labour strike. Because the spring survey covers the main distribution area, it is considered adequate to measure changes in abundance/biomass of Atlantic wolffish better than the autumn survey. Total biomass and harvestable biomass indices decreased from 1985-1995. In 1996, the biomass index increased to 1998, then decreased to a historical low level in 2010-2012, but since then it has been increasing Figure 14). The harvestable biomass has generally been increasing from 1995 with considerable oscillators. The recruitment index was high in the years 1992-2003, since 1999 it has been decreasing, which coincides with increasing effort and catch of trawlers at the main spawning ground west of Iceland (Látragrunn) during the spawning and incubation time. The recruitment index reached a historical low level in 2011, but since then it has been rather stable or increased slightly. This coincides with that the closed spawning/incubation area on Látragrunn was enlarged from 500 km2 (from 2002) to 1000 km2 in October 2010.
When the spring survey is conducted, Atlantic wolffish are on their feeding grounds which are commonly in relatively shallow waters. In the spring survey, the highest abundance has always been measured in the NW area (Figure 15).