| Year | nr. longlines | nr. trawlers | nr. demersal seiners | nr. other | Longline | Demersal trawl | Demersal seine | Total catch |
|---|---|---|---|---|---|---|---|---|
| 2000 | 161 | 53 | 16 | 0 | 8 687 | 3 380 | 528 | 12 595 |
| 2001 | 195 | 59 | 14 | 1 | 11 267 | 3 391 | 513 | 15 182 |
| 2002 | 140 | 44 | 13 | 0 | 7 773 | 3 735 | 601 | 12 110 |
| 2003 | 138 | 45 | 19 | 0 | 7 785 | 5 463 | 1 066 | 14 313 |
| 2004 | 103 | 34 | 29 | 0 | 4 670 | 4 773 | 1 609 | 11 052 |
| 2005 | 91 | 47 | 24 | 1 | 5 445 | 6 893 | 1 140 | 13 508 |
| 2006 | 120 | 48 | 25 | 0 | 6 626 | 6 286 | 1 149 | 14 061 |
| 2007 | 105 | 60 | 24 | 0 | 5 259 | 7 566 | 1 338 | 14 163 |
| 2008 | 87 | 60 | 22 | 3 | 4 663 | 6 960 | 1 427 | 13 093 |
| 2009 | 114 | 55 | 28 | 1 | 6 708 | 5 468 | 1 205 | 13 391 |
| 2010 | 74 | 46 | 20 | 3 | 5 916 | 4 436 | 842 | 11 286 |
| 2011 | 64 | 37 | 18 | 0 | 5 344 | 3 565 | 1 010 | 9 918 |
| 2012 | 66 | 24 | 22 | 1 | 5 328 | 2 827 | 895 | 9 091 |
| 2013 | 73 | 30 | 18 | 2 | 4 652 | 2 341 | 647 | 7 662 |
| 2014 | 70 | 23 | 13 | 1 | 3 681 | 1 637 | 891 | 6 220 |
| 2015 | 56 | 34 | 17 | 2 | 3 989 | 1 905 | 926 | 6 848 |
| 2016 | 61 | 37 | 18 | 2 | 4 848 | 1 662 | 1 127 | 7 661 |
| 2017 | 59 | 28 | 18 | 2 | 3 829 | 1 102 | 1 095 | 6 049 |
| 2018 | 60 | 37 | 27 | 6 | 4 923 | 1 587 | 2 186 | 8 770 |
| 2019 | 64 | 34 | 21 | 1 | 4 595 | 1 630 | 2 168 | 8 404 |
| 2020 | 46 | 38 | 24 | 1 | 2 491 | 2 046 | 2 040 | 6 588 |
| 2021 | 45 | 48 | 22 | 0 | 3 343 | 3 021 | 2 086 | 8 451 |
| 2022 | 40 | 48 | 23 | 0 | 2 506 | 2 981 | 2 223 | 7 710 |
| 2023 | 34 | 49 | 20 | 0 | 2 899 | 2 755 | 2 346 | 8 000 |
| 2024 | 37 | 45 | 24 | 0 | 2 405 | 2 914 | 2 826 | 8 145 |
| 2025 | 29 | 46 | 24 | 0 | 2 096 | 3 460 | 3 056 | 8 612 |
Key signals
Biomass indices have declined across all survey parameters following a peak in 2022–23, and fishing mortality now exceeds Fmsy, Fpa, and Fmgt.
Recruitment index (≤40 cm) declined to a historical minimum in 2011, recovered through 2023, and has since declined again toward critically low levels.
Spawning stock biomass still remains above Blim, Bpa, and MGT Btrigger, though current exploitation levels are slightly above reference points.
Although survey indices are declining, commercial catch data suggest that the wolffish stock remains in balance, which is confirmed by the stock assessment.
Continued closure of the Látragrunn spawning area during the spawning and incubation season is recommended.
General information
The Atlantic wolffish is a long-bodied species with a large head, characterized by prominent canine teeth for seizing prey and powerful molars for crushing it. Most individuals caught measure between 50 and 80 cm in length, although the largest specimen recorded in Icelandic waters reached 125 cm. The species is most commonly found on the continental shelf northwest of Iceland. Its feeding grounds are typically located on muddy or sandy bottoms at depths shallower than 100 meters. In contrast, spawning grounds are found on coarser substrates featuring crevices or cavities, generally at depths greater than 100 meters.
Fishery
The primary fishing grounds for Atlantic wolffish are located on the western and northwestern parts of the Icelandic continental shelf. Since 2010, the proportion of the catch taken in the northwest has increased, while it has declined in the west. Catches at the main spawning ground, Látragrunn (west of Iceland), have decreased since 2008 (Figure 1; Figure 2). Notably, part of this area has been closed to trawling during the spawning and incubation period since 2010. Approximately 80% of the Atlantic wolffish catch is taken at depths shallower than 120 m. The proportion of the catch from the 0–60 m depth range increased in 2017 and has remained stable since. In the 61–120 m depth range, the catch proportion has remained relatively stable since 2000. At depths of 121–180 m, which include the main spawning ground at Látragrunn, the catch proportion has been declining over the past decade (Figure 3). Atlantic wolffish are primarily caught by longliners, demersal trawlers, and demersal seiners (Figure 4). The relative contributions of these fleets have changed in recent years, with demersal seiners increasing their share to approximately one-third of the total catch (Figure 4). Since 2001, the number of vessels reporting annual Atlantic wolffish catches of 10 tonnes or more has declined. This reduction is mainly attributable to the longline fleet, where the number of vessels decreased from 195 in 2001 to 29 in 2025, representing the lowest level since 2000. The number of trawlers and demersal seiners has varied over time but without marked long-term trends (Table 1). In 1994 and 1995, more than 500 vessels accounted for 95% of the annual Atlantic wolffish catch in Icelandic waters. This number declined to approximately 200 vessels by 2008, despite higher catch levels. Since 2010, the number of vessels accounting for 95% of the annual catch has remained relatively stable (approximately 150–200 vessels), despite reductions in total catch (Figure 5).
Catch per unit of effort from commercial fisheries
CPUE estimates of Atlantic wolffish in Icelandic waters are not considered representative of stock abundance, as changes in fleet composition, technological improvements and differences in gear setup, among other factors, have not been accounted for in the estimation of CPUE. Non-standardized estimates of CPUE for longline (kg/1000 hooks), demersal trawl (kg/hour) and demersal seine (kg/set) are calculated as the total catch weight from sets or tows in which Atlantic wolffish constituted more than 10% of the catch, according to logbook records.
CPUE for longline vessels was relatively stable prior to 2018, fluctuating around 75 kg/1000 hooks; however, it doubled between 2020 and 2025 and has remained high since. CPUE of demersal trawl was highest in 2005 and 2015, at approximately 270-300 kg/hour. Between these years, it dropped below 200 kg/hour and has remained around that level since. CPUE of demersal seine increased from just under 400 kg/set to around 650 kg/set during 2020-2023 and is currently at its highest level (Figure 6).
In summary, there is a contrast in recent trends among gear types: over the past five years, CPUE for bottom trawl has remained stable, while CPUE for demersal seine and longline has increased.
CPUE data are not used in the stock assessment, as they do not reliably reflect trends in stock abundance.
Landings and discards
Landings by Icelandic vessels are obtained from 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. Measures in the Icelandic management system such as converting quota from one species to another are used by the Icelandic fleet to a large extent, and is thought to discourage discards in mixed fisheries.
Data and sampling
Commercial data
The commercial catch samples taken should be representative of the landings with most number of samples taken in areas of high catch intensity. In general, sampling from commercial catches is considered acceptable from the main gears (demersal seines and trawls). The sampling seems to follow the spatial and seasonal distribution of catches (Figure 8 and Figure 7).
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. The number of length and age samples from landed Atlantic wolffish was reduced in 2014 (Table 2 and Table 3). 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 2025, a total of 4, 29 and 32 samples were collected from longline, bottom trawl and demersal seine catches, respectively (Table 3, Figure 8).
| Year |
Bottom Trawl
|
Demersal Seine
|
Long Line
|
|||
|---|---|---|---|---|---|---|
| Num. samples | Num. lengths | Num. samples | Num. lengths | Num. samples | Num. lengths | |
| 2000 | 22 | 2 852 | 4 | 468 | 29 | 3 698 |
| 2001 | 13 | 1 806 | 3 | 376 | 33 | 4 147 |
| 2002 | 37 | 4 912 | 2 | 281 | 44 | 5 151 |
| 2003 | 36 | 4 270 | 7 | 1 251 | 42 | 6 433 |
| 2004 | 33 | 3 932 | 12 | 1 505 | 23 | 3 241 |
| 2005 | 57 | 7 732 | 16 | 1 684 | 33 | 5 089 |
| 2006 | 43 | 5 829 | 7 | 754 | 44 | 5 882 |
| 2007 | 44 | 5 935 | 17 | 1 839 | 33 | 3 963 |
| 2008 | 64 | 9 903 | 13 | 1 355 | 24 | 3 351 |
| 2009 | 52 | 8 470 | 14 | 1 674 | 33 | 4 464 |
| 2010 | 54 | 9 640 | 13 | 1 666 | 30 | 3 911 |
| 2011 | 20 | 3 015 | 12 | 1 391 | 17 | 2 524 |
| 2012 | 41 | 9 684 | 12 | 1 206 | 26 | 3 574 |
| 2013 | 20 | 3 175 | 5 | 671 | 26 | 3 711 |
| 2014 | 31 | 4 296 | 31 | 3 623 | 30 | 3 748 |
| 2015 | 20 | 2 358 | 20 | 1 984 | 26 | 3 168 |
| 2016 | 13 | 1 596 | 10 | 970 | 26 | 2 806 |
| 2017 | 9 | 956 | 6 | 633 | 24 | 2 973 |
| 2018 | 9 | 817 | 17 | 1 687 | 22 | 2 654 |
| 2019 | 12 | 1 128 | 23 | 2 349 | 23 | 2 677 |
| 2020 | 18 | 1 833 | 17 | 1 652 | 9 | 1 007 |
| 2021 | 25 | 2 987 | 15 | 1 070 | 14 | 1 277 |
| 2022 | 23 | 2 420 | 17 | 1 235 | 3 | 269 |
| 2023 | 22 | 2 365 | 25 | 2 203 | 12 | 1 039 |
| 2024 | 33 | 3 646 | 26 | 2 075 | 11 | 1 174 |
| 2025 | 40 | 4 725 | 32 | 2 972 | 4 | 354 |
| Year |
Longline
|
Bottom trawl
|
Demersal seine
|
|||
|---|---|---|---|---|---|---|
| num. samples | num. otoliths. | num. samples | num. otoliths. | num. samples | num. otoliths. | |
| 2000 | 29 | 1 395 | 18 | 752 | 4 | 200 |
| 2001 | 27 | 1 343 | 11 | 509 | 3 | 150 |
| 2002 | 25 | 1 240 | 16 | 645 | 2 | 100 |
| 2003 | 31 | 1 525 | 20 | 899 | 6 | 300 |
| 2004 | 19 | 950 | 23 | 1 060 | 8 | 400 |
| 2005 | 15 | 746 | 25 | 1 202 | 6 | 292 |
| 2006 | 23 | 1 110 | 21 | 1 029 | 5 | 250 |
| 2007 | 18 | 900 | 25 | 1 250 | 10 | 451 |
| 2008 | 19 | 950 | 25 | 1 248 | 4 | 200 |
| 2009 | 16 | 800 | 20 | 999 | 4 | 200 |
| 2010 | 29 | 1 669 | 19 | 1 090 | 5 | 285 |
| 2011 | 14 | 750 | 15 | 778 | 9 | 550 |
| 2012 | 26 | 1 300 | 14 | 700 | 7 | 350 |
| 2013 | 25 | 1 249 | 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 |
| 2024 | 11 | 220 | 29 | 580 | 26 | 508 |
| 2025 | 4 | 80 | 29 | 580 | 32 | 632 |
Length compositions
The length distribution of landed Atlantic wolffish has been relatively stable since 2005 in all gears (Figure 9).