Blue whiting Micromesistius poutassou
Publication of Advice: 30 September 2026. Published by Marine and Freshwater Research Institute.
Advice
ICES advises that when the long-term management strategy agreed by Norway, the European Union, the Faroe Islands, Iceland, and UK is applied, catches in 2027 should be no more than 1064191 tonnes.
Stock development
Fishing pressure on the stock is above FMSY and Fpa; spawning-stock size is above MSY Btrigger, Bpa, and Blim.
Blue whiting. Total and Icelandic catches, recruitment at age 1, fishing mortality and spawning stock biomass (SSB). Shaded areas and error bars show 95% confidence interval.The catch estimate for 2026 is preliminary. The assumed recruitment value for 2026 is shaded in a lighter colour. The spawning stock biomass value for 2026 is calculated from the assessment and assumed recruitment for 2026.
Basis of assessement and reference points
Basis of the advice | Long-term management strategy |
Management plan | A long-term management strategy was agreed by the European Union, the Faroe Islands, Iceland, and Norway, and subsequently by UK in 2021 (Anon 2021). ICES evaluated the strategy and found it to be precautionary (ICES 2016, 2017) |
Assessment type | Age-based analytical assessment (SAM) |
Input data | Commercial catches, preliminary estimate of catch-at-age in the year (Q1-Q2) in which the assessment is carried out. One survey index (International Blue Whiting Spawning Stock Survey [IBWSS; A1142] ages 1–8, 2004–2026, excluding 2010 and 2020). Time invariant maturity at age was estimated in 1994 by combining maturity ogives from the southern and northern areas. Weight at age estimated annually from commercial data, including preliminary estimates of weight-at-age in the year of the assessment (Q1-Q2). Time invariant natural mortality fixed at 0.2 for all ages, derived in the 1980s from age compositions before the targeted fishery started. |
Approach | Reference point | Value | Basis |
|---|---|---|---|
MSY | MSY Btrigger | 2 250 000 | BPA |
FMSY | 0.32 | Stochastic simulations with segmented regression stock–recruitment relationship capped to FP05 | |
Precautionary approach | Blim | 1 500 000 | Approximately Bloss |
BPA | 2 250 000 | Blim × exp(1.645 × s), s = 0.246 | |
FPA | 0.32 | FP05; the F that leads to SSB ≥ Blim with 95% probability | |
Long-term management strategy | SSBmgt_lower | 1 500 000 | Blim |
SSBmgt | 2 250 000 | BPA | |
Fmgt_lower | 0.05 | Arbitrary low F | |
Fmgt | 0.32 | FMSY |
Prospects
Blue whiting. Assumptions made for the interim year and in the forecast.
Variable | Value | Notes |
|---|---|---|
Fages 3–7 (2026) | 0.4 | From the assessment (based on assumed catch in 2026). |
SSB (2027) | 5 060 667 | From the forecast for 2027; in tonnes. |
Rage 1 (2026) | 39 366 774 | 75th percentile of the geometric mean (1996–2025); in thousands. |
Rage 1 (2027–2028) | 22 790 977 | Geometric mean (1996–2025); in thousands. |
Total catch (2026) | 1 110 513 | As estimated by ICES, based on declared national quotas and expected uptake; in tonnes. |
Blue whiting. Projection of SSB (tonnes) based on annual catch scenarios. All weights are in tonnes.
Basis | Catch (2027) | Fishing mortality (2027) | SSB (2028) | % SSB change1) | % Change in catch2) | Advice change3) |
|---|---|---|---|---|---|---|
Long-term management strategy: Catch2027 = advice2026 + 25% | 1 064 191 | 0.30 | 5 585 532 | 10.4 | -4.2 | 25 |
Long-term management strategy: F = Fmgt | 1 112 531 | 0.32 | 5 540 154 | 9.5 | 0.2 | 31 |
F=F2026 | 1 351 452 | 0.40 | 5 316 586 | 5.1 | 22.0 | 59 |
1) SSB in 2028 relative to SSB in 2027 | ||||||
2) Advice value for 2027 relative to expected catch in 2026 (1 110 513 t) | ||||||
3) Advice value for 2027 relative to advice value for 2026 (851 344 t) | ||||||
The advice for 2027 is higher than in 2026 because of an estimated increase in stock biomass from 2026 to 2027, an upward revision of the perception of stock biomass over the recent years and a good incoming year class (2024). A cap of +25% was applied to the catch advice according to the long-term management plan.
Quality of the assessment
This year’s assessment shows a downward revision of the estimated fishing mortality and an upward revision of the estimated recruitment and stock biomass over recent years. These revisions are caused by a higher proportional catch of age 1 in 2025 in the final catch data (13%) compared to the preliminary catch data (5%). Additionally, the survey index (IBWSS) indicated a low recruitment in 2025 (year class 2024) but relatively high numbers for the same year class as age 2 in 2026. This contributed to the upward revision of the 2025 recruitment.
The survey index indicated a good recruitment for 2026 (2025 year class). The model used for the current assessment subsequently estimated recruitment in 2026 to be 24.7 billion, which is slightly higher than the long-term geometric mean (22.8 billion) but lower than the recruitment estimate for 2025 (38.7 billion). Other surveys that substantially correlate with the assessment model recruitment estimates and are currently not used in the assessment (International Ecosystem Survey in the Nordic Seas in May (A3675 [IESNS]), International Ecosystem Summer Survey in the Nordic Seas in July (A7806 [IESSNS])) point towards a higher recruitment in 2026 compared to 2025. It was therefore decided to replace the recruitment estimate of the assessment model for 2026 with the 75th percentile of the long-term geometric mean (39.4 billion), as done previously under similar circumstances for this stock (ICES, 2014).
Blue whiting. Current assessment (red line) compared with previous estimates (2022–2025).
Other Information
Since 2018, the sum of the unilateral quotas, and the resulting catches, have consistently exceeded the ICES advice based on the long-term management strategy. The evaluation of the management strategy (ICES, 2016a) did not implement this consistent overshoot of the TAC prescribed by the management strategy.. Therefore, failing to adhere to the advised catches as derived from the application of the maximum sustainable yield (MSY) approach or the long-term management strategy may not be precautionary. Specifically, this may result in an increased risk for the stock to fall below Blim and loss of catch in the medium-to-long term.
Both the 2020 and 2021 year classes are among the highest in the time series and were fully recruited to the fishery in 2026. In 2027, the fishery will to some extent still depend on them, with 10% and 21% of the catch predicted to consist of fish from the 2020 and 2021 year classes, respectively. The highest year class recruited to the fishery will be from 2024 and is predicted to contribute with 23% of the catches in 2027. The history of the stock shows that subsequent years of low recruitment after a period of high recruitment may cause the spawning-stock biomass (SSB) to drop quickly to lower levels and would lead to a reduction in future advice. The year classes 2022 and 2023 are estimated by the assessment model to be small and the 2024 year class to be strong. Recruitment survey indices not used in the assessment but used as additional indicators indicate a stronger 2025 year class compared to 2022 and 2023 (Joint Norwegian-Russian survey Barents Sea (G5348), Icelandic bottom-trawl survey in spring (G3239 [IS-SMB])) or even stronger than 2024 (International Ecosystem Survey in the Nordic Seas in May (A3675 [IESNS]), International Ecosystem Summer Survey in the Nordic Seas in July (A7806 [IESSNS]), the Faroese bottom-trawl survey in spring (G1264 [FO-GFS-Q1])); though not as high as those from 2020 and 2021.
Advice, TAC and Catch
Blue whiting. Recommended TAC, national TAC and catches (tonnes).
Year | Recommended TAC | Iceland national TAC | Catches Iceland | Total national TAC | Total catch |
|---|---|---|---|---|---|
1987 | 950 000 | ||||
1988 | 832 000 | ||||
1989 | 630 000 | ||||
1990 | 600 000 | ||||
1991 | 670 000 | ||||
1992 | |||||
1993 | 490 000 | ||||
1994 | 485 000 | 650 000 | |||
1995 | 518 000 | 369 | 650 000 | 578 905 | |
1996 | 500 000 | 501 | 650 000 | 645 982 | |
1997 | 540 000 | 10 646 | 672 437 | ||
1998 | 650 000 | 68 681 | 1 128 969 | ||
1999 | 650 000 | 160 425 | 1 256 228 | ||
2000 | 800 000 | 260 938 | 1 412 927 | ||
2001 | 628 000 | 365 099 | 1 780 170 | ||
2002 | 0 | 282 000 | 286 430 | 1 556 792 | |
2003 | 600 000 | 318 000 | 501 496 | 2 321 406 | |
2004 | 925 000 | 713 000 | 422 078 | 2 380 161 | |
2005 | 1 075 000 | 345 000 | 265 515 | 2 034 309 | |
2006 | 1 500 000 | 352 600 | 314 768 | 2 100 000 | 1 976 176 |
2007 | 980 000 | 299 710 | 237 854 | 1 847 000 | 1 625 255 |
2008 | 835 000 | 202 836 | 163 793 | 1 250 000 | 1 260 615 |
2009 | 384 000 | 95 739 | 120 202 | 606 000 | 641 818 |
2010 | 540 000 | 87 625 | 87 908 | 548 000 | 526 357 |
2011 | 223 000 | 6 507 | 5 882 | 40 000 | 103 620 |
2012 | 391 000 | 63 447 | 63 056 | 391 000 | 384 021 |
2013 | 643 000 | 104 339 | 104 918 | 643 000 | 628 169 |
2014 | 948 950 | 194 722 | 182 879 | 1 200 000 | 1 155 279 |
2015 | 839 886 | 202 958 | 214 870 | 1 260 000 | 1 396 244 |
2016 | 776 391 | 163 570 | 186 914 | 1 147 000 | 1 183 187 |
2017 | 1 342 330 | 264 000 | 228 935 | 1 675 400 | 1 558 061 |
2018 | 1 387 872 | 275 971 | 292 952 | 1 727 964 | 1 711 477 |
2019 | 1 143 629 | 226 727 | 268 351 | 1 483 208 | 1 515 527 |
2020 | 1 161 615 | 230 111 | 243 725 | 1 478 358 | 1 495 248 |
2021 | 929 292 | 196 081 | 190 147 | 1 157 604 | 1 143 450 |
2022 | 752 736 | 174 557 | 191 813 | 752 736 | 1 038 736 |
2023 | 1 359 629 | 273 442 | 292 853 | 1 359 629 | 1 737 098 |
2024 | 1 529 754 | 309 524 | 321 572 | 1 529 754 | 1 816 792 |
2025 | 1 447 054 | 293 287 | 286 760 | 1 447 054 | 1 110 513 |
2026 | 851 344 | 186 157 | 851 344 | ||
2027 | 1 064 191 |
References and further reading
Anon 2021. Agreed record of conclusions of fisheries consultations between the European Union, the Faroe Islands, Iceland, Norway and UK on the management of blue whiting in the north-east Atlantic in 2022. https://www.regjeringen.no/contentassets/2ea04e97a8fd45c2b1758e2602e79c46/blue-whiting-agreed-record-october-2021.pdf
ICES. 2014. Blue whiting in Subareas I–IX, XII, and XIV. In Report of the ICES Advisory Committee, 20214. ICES Advice 2014, Book 9, whb-comb. https://doi.org/10.17895/ices.advice.27202938
ICES. 2016. Report of the Workshop on Blue Whiting (Micromesistius poutassou) Long Term Management Strategy Evaluation (WKBWMS), 30 August 2016, ICES HQ, Copenhagen, Denmark. ICES CM 2016/ACOM:53. 104 pp.
MFRI Assessment Reports 2026. Blue whiting. Marine and Freshwater Research Institute, 30 september 2026.
ICES. 2026. Blue whiting (Micromesistius poutassou) in subareas 1–9, 12, and 14 (Northeast Atlantic and adjacent waters). In Report of the ICES Advisory Committee, 2026. ICES Advice 2026, whb.27.1-91214, https://doi.org/10.17895/ices.advice.30932450
ICES. 2026. Working Group on Widely Distributed Stocks (WGWIDE). ICES Scientific Reports. https://doi.org/10.17895/