Atlantic wolffish

Anarhichas lupus


Technical report
Published by

Marine and Freshwater Research Institute, Iceland

Published

7 June 2024

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).

Figure 1: Atlantic wolffish. Geographical distribution of the Icelandic fishery since 2008. Reported catch from logbooks.

Figure 2: Atlantic wolffish. Spatial distribution of the Icelandic fishery by fishing area since 2000 according to logbooks. All gears combined.

Figure 3: Atlantic wolffish. Depth distribution of demersal trawl, longline and demersal seine catches according to logbooks.

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).

Figure 4: Atlantic wolffish. Total catch (landings) by fishing gear since 1994, according to statistics from the Directorate of Fisheries.

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).

Table 1: Atlantic wolffish. Number of Icelandic boats and catches by fleet segment participating in the Atlantic wolffish fishery from logbooks.
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

Figure 5: Atlantic wolffish. Number of vessels (all gear types) accounting for 95% of the total catch annually since 1994. Left: Plotted against year. Right: Plotted against total catch. Data from the Directorate of Fisheries.

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).

Figure 6: Atlantic wolffish. Spatial distribution of length samples (black dots) from commercial catches in Icelandic waters (upper) and numbers of samples taken per month by project (bars) and proportion of landings per month (black line) (lower).

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).

Table 2: . Atlantic wolffish. Number of samples and aged fish from landed catch of Atlantic wolffish.
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).

Figure 7: Atlantic wolffish. Length distribution from the Icelandic fleet from 2005-2023.

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)

Figure 8: Atlantic wolffish. Catch at age from the commercial fishery in Iceland waters. Bar size is indicative of the catch in numbers and bars are coloured by cohort.

Figure 9: Atlantic wolffish. Catch at age from the commercial fishery in Iceland waters. Biomass caught by year and age; bars are coloured by cohort.

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.

Figure 10: Atlantic wolffish. Mean weight at age in the catch from the commercial fishery in Icelandic waters. Bars are coloured by cohort.

Figure 11: Atlantic wolffish. Catch weights by age from the commercial fishery in Icelandic waters.

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.

Figure 12: Atlantic wolffish. Non-standardized estimates of CPUE for demersal trawl (left, kg/h) and longline (right, kg/1000 hooks).

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).

Figure 13: Atlantic wolffish. Location and abundance of ling in the spring survey (SMB) in 2024 and the autumn survey (SMH) in 2023.

Figure 14: Atlantic wolffish. Total biomass indices (upper left) and harvestable biomass indices (≥60 cm, upper right), large fish biomass indices (≥80 cm, lower left) and juvenile abundance indices (≤40 cm, lower right), from the spring survey (blue) and the autumn survey (red), along with the standard deviation.