BLUE LING Molva dypterygia


Technical report
Published by

Marine and Freshwater Research Institute, Iceland

Published

12 June 2026

Key signals

  • Following a peak in landings from 2008-2013, landings since 2017 have been at historically low levels.

  • Biomass indices from the Icelandic Autumn Survey declined from 2009 to 2022, and have increased in the past three years.

  • From 2010 to 2020 recruitment levels were minimal or low. These have since increased to levels seen in early 2000s.

  • Spawning stock biomass (SSB) has increased since 2020 and is currently at a similar level to 2010.

  • Biomass levels are expected to increase under current conditions due to improved recruitment.

General information

Blue ling (Molva dypterygia) in ICES Division 5.a and Subarea 14 are assessed as one stock. Blue ling is a deep-water gadoid species primarily distributed along the continental shelves and slopes of the Northeast Atlantic, particularly around Iceland, the Faroe Islands, Norway, the British Isles, and off East Greenland. In Icelandic waters, it is commonly found in deeper regions over soft seabeds in the southeast, south, and west of Iceland, at depths greater than 500 meters. The majority of the population is concentrated between 300 and 800 meters, and it is rarely found at depths shallower than 200 meters. During the winter months, blue ling tends to stay at deeper depths, while in the spring and summer, it ascends to shallower areas.

The blue ling is smaller than the common ling (Molva molva), reaching an average length of approximately 80 cm and a maximum length of around 150 cm, according to the Icelandic autumn groundfish survey. Blue ling is a slow-growing species, living up to 20 years or more. Sexual maturity is typically reached when individuals are 75-90 cm. Sexual dimorphism is notable with females growing faster and reaching maturity at larger sizes and older ages than males. Spawning occurs in the spring at depths of 500-1000 meters or deeper, in waters with temperatures ranging from 5-8°C, outside the continental shelf off the southern coast of Iceland, south and west of the Faroe Islands, west of Norway, and west of Scotland to Northern Ireland. Off Iceland, blue ling spawns from February to April, peaking in March in waters with temperatures of 5-6°C. Known spawning grounds include depths of 600-1000 meters south of the Westman Islands and along the fishing limits of the Reykjanes Ridge (Franshóll). The eggs are pelagic, measuring 1.3-1.5 mm in diameter, and hatch in the upper layers of the ocean. The larvae drift long distances west and north, traveling far into the open sea toward Greenland, where they grow alongside the larvae of cod, herring, capelin, silver hake, and common skates. The juvenile fish settle on the seabed when they reach 8-10 cm in length, typically between August and October (Jónsson and Pálsson (2013))

Fishery

Spatial and temporal patterns

The main bottom trawl fishing grounds are located northwest of Iceland close to the shelf break, and southwest of Iceland at the base of Reykjanes Ridge (Figure 4). Fisheries also operate along the continental shelf south and southeast of Iceland, and directly west of Iceland (Figure 4, Figure 6). Most of the catches by trawlers are taken in waters between 200 m and 700 m (Figure 3). When targeting blue ling, longliners typically operated in waters from 200 m to 500 m (Figure 3), and catches were distributed in deeper waters west, southwest and south of Iceland (Figure 4, Figure 6).

Figure 4: Blue ling in Division 5.a and and Subarea 14. Geographical distribution of the bottom trawl fishery from 2004-2025. The 100 m, 500m and 1000 m depth contours are shown. Reported catch from logbooks.
Figure 5: Blue ling in Division 5.a and and Subarea 14. Geographical distribution of the longline fishery from 2004-2025. The 100 m, 500m and 1000 m depth contours are shown. Reported catch from logbooks.
Figure 6: Blue ling in Division 5.a and and Subarea 14. Annual catch per area. Catch distribution and proportions by area according to logbooks.
Figure 7: Blue ling in Division 5.a and and Subarea 14. 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.
Table 1: Blue ling in Division 5.a and and Subarea 14. Number of Icelandic vessels landing blue ling, and all landed catch divided by gear type.
Year Nr. Bottom Trawl Bottom Trawl Nr. Long Line Long Line Nr. Other Other Total catch
2000 108 801 44 808 36 25 1 634
2001 110 597 39 131 48 34 762
2002 105 986 41 256 25 23 1 264
2003 105 883 47 197 33 17 1 098
2004 112 894 53 145 45 44 1 083
2005 106 1 261 60 108 51 126 1 496
2006 105 1 477 69 151 47 107 1 734
2007 97 1 544 90 374 64 76 1 995
2008 95 2 111 92 1 454 61 88 3 653
2009 89 2 242 87 1 677 69 211 4 129
2010 85 2 202 96 3 978 73 198 6 378
2011 81 1 630 97 4 140 58 134 5 904
2012 79 1 449 78 2 425 52 332 4 207
2013 75 1 300 72 1 420 45 48 2 769
2014 72 923 74 628 36 43 1 594
2015 67 821 78 868 36 22 1 712
2016 66 701 54 213 31 10 925
2017 57 436 53 169 26 14 619
2018 65 363 60 132 20 7 502
2019 58 238 54 161 27 16 415
2020 58 264 47 71 21 9 344
2021 59 286 41 33 20 4 323
2022 55 338 37 86 20 2 427
2023 52 304 36 96 20 4 404
2024 55 427 28 42 16 3 473
2025 52 555 25 43 20 24 622

Catch per unit of effort from commercial fisheries

Effort and nominal catch per unit effort (CPUE) data from the Icelandic trawl and longline fleet are given in Figure 8. Due to changes in the fishery (expansion into new areas, fleet behaviour, etc.) and technical innovations, CPUE is not considered a reliable index of biomass abundance of blue ling and therefore no attempt has been made to standardize the series. However, looking at fluctuations in CPUE and effort may be informative regarding the development of the fishery. CPUE from longlines was high from 2008-2013 but has decreased markedly since. CPUE from trawls has been gradually decreasing over time. Effort from bottom trawls peaked in 2009 and has since declined to the same level observed in the early 2000s. Effort from longlines peaked in 2011 but has remained relatively stable since.

Figure 8: Blue ling in Division 5.a and and Subarea 14. Catch per unit of effort for bottom trawl (BMT) and longline (LLN). The dashed blue lines are based on locations where more than 10% of the catch was blue ling and the solid red lines on all records where blue ling were caught. Note that a change took place in September 1999, when all vessels were required to submit a catch logbook. Before that time, vessels smaller than 10 gross tons were exempt from this requirement.

Landings and discards

Landings data before 1982 (and foreign landings until 2005) are sourced from the ICES STATLANT database. Icelandic landings from 1982–1993 were collected by the Fisheries Association of Iceland, and from 1994 onward by the Directorate of Fisheries. Foreign landings were recorded by the Coast Guard before 2014 and by the Directorate of Fisheries thereafter.

Discard rates of blue ling are unknown. Discarding is prohibited by law. Management measures, such as inter-species quota transfers and landing flexibility, discourage discarding. To help prevent high grading and quota mismatches, fisheries are permitted to land catches that are exempt from quota deductions, provided that the proceeds from their sale are transferred to a government-managed fund. More information is available at https://www.responsiblefisheries.is/seafood-industry/fisheries-management.

Data and sampling

Commercial data

Fishing areas and sampling locations are shown in Figure 9 and Figure 10. In 2025, 7 samples were collected from bottom trawls and 0 from longlines (Figure 10, Table 2). As of January 2026, the sampling frequencies for blue ling from longline were increased to improve coverage.

Figure 9: Blue ling in Division 5.a and and Subarea 14. Distribution of catches in 2025 and location of samples.