NORWEGIAN SPRING-SPAWNING HERRING
Clupea harengus
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 the European Union, the UK, the Faroe Islands, Iceland, Norway, and the Russian Federation is applied, catches in 2027 should be no more than 588004 tonnes.
Stock development over time
Fishing pressure on the stock is below FMSY. Spawning-stock size is below MSY Btrigger, and between Bpa and Blim.
Norwegian spring-spawning herring. Catch by Iceland and others, recruitment, fishing mortality and spawning stock biomass (SSB). Shaded areas and error bars show 95 % confidence intervals.
Basis of assessement and reference points
Basis of the advice | Management strategy. |
Management plan | A long-term management strategy was agreed by coastal states in 2018 (Anon, 2018) and subsequently by the UK (Anon, 2020). |
Assessment type | Age-based analytical model (SAM). |
Input data | Commercial catches-at-age (stock weight-at-age from surveys and, since 2009, from catch sampling). Four survey indices: Norwegian acoustic survey on spawning grounds in February/March (NASF [A7918] 1988–1989, 1994–1996, 1998–2000, 2005–2008, 2015–2026), International Ecosystem Survey in the Nordic Seas (IESNS A3675) covering the adult stock in the Nordic seas (1996–2026), and the juvenile stock in the Barents Sea (1991–2002, 2005–2007, 2009–2019, 2021,2024,2026) the Norwegian and Russian Barents Sea ecosystem surveys in August-October (BESS [A5216], 2004–2025) covering the juvenile stock in the Barents Sea and a time series of tagging indices based on RFID (TAGHER [S8417], 2017–2025). Maturity ogive variable by year-class strength. Natural mortalities are fixed values from historical analyses (age 2 = 0.9, ages greater than 2 = 0.15). |
Approach | Reference point | Value | Basis |
|---|---|---|---|
MSY approach | MSY Btrigger | 3 | Bpa; in million tonnes. |
FMSY | 0.21 | Stochastic simulations, capped to FP05. | |
Precautionary approach | Blim | 2 | Lowest spawning-stock biomass (SSB) that produced large recruitment, determined as SSB corresponding to the 1991 year class; in million tonnes; in million tonnes. |
BPA | 3 | Based on Blim and assessment uncertainties.BPA = Blim × exp(1.645 × s), s = 0.2 ; in million tonnes. | |
FPA | 0.21 | FP05. the F that leads to SSB ≥ Blim with 95% probability. | |
Long-term management strategy | F mgt | 0.14 | Precautionary HCR evaluated by MSE. Note it has not been fully tested whether it remains precautionary with the reference points updated in 2025. |
SSB mgt_lower | 2 | Precautionary HCR evaluated by MSE. Note it has not been fully tested whether it remains precautionary with the reference points updated in 2025. SSB values in million tonnes. | |
SSB mgt | 3 | Precautionary HCR evaluated by MSE. Note it has not been fully tested whether it remains precautionary with the reference points updated in 2025. SSB values in million tonnes. | |
F mgt_lower | 0.05 | Precautionary HCR evaluated by MSE. Note it has not been fully tested whether it remains precautionary with the reference points updated in 2025. |
Prospects
Norwegian spring-spawning herring. Assumptions made for the interim year and in the forecast.
Variable | Value | Notes |
|---|---|---|
F5-12+ (2026) | 0.164 | Based on assumed catches in 2026. |
SSB (2027) | 3.223 | From the assessment model; in million tonnes. |
Recruitment age 2 (2026) | 15.27 | Point estimate from the assessment model; billions. |
Recruitment age 2 (2027) | 9.005 | Median stochastic recruitment based on the years 1988–2024; billions. |
Catch (2026) | 584 025 | Sum of declared unilateral quotas; tonnes. |
Norwegian spring-spawning herring. Annual catch scenarios. All weights are in tonnes.
Basis | Total catch | Fishing pressure | SSB | % change | Probability of SSB2028 < Blim (%) | ||
|---|---|---|---|---|---|---|---|
2027 | 2027 | 2028 | SSB1) | Advice2) | Catch3) | ||
Agreed management strategy | 588 004 | 0.140 | 3 341 564 | 3.7 | 10 | 0.70 | 4.1 |
MSY approach | 847 221 | 0.210 | 3 119 560 | -3.2 | 59 | 45 | 8.3 |
F=F2026 | 679 132 | 0.164 | 3 267 552 | 1.4 | 27 | 16 | 5.1 |
1) SSB in 2028 relative to SSB in 2027 (3 223 000 tonnes) | |||||||
2) Advice value for 2027 relative to advice value for 2026 (533 914 tonnes) | |||||||
3) Catch in 2027 relative to catch in 2026 (419 205 tonnes) | |||||||
The advice for 2027 is higher than the advice for 2026 because the 2021 and 2022 year classes, which are stronger than average, are recruiting to the spawning stock. Spawning-stock biomass (SSB) is predicted to be above the long-term management strategy Btrigger at the start of 2027, so Fmgt is applied without reduction.
Quality of the Assessement
The 2021 and 2022 year classes are both estimated to be above average. With another year of radio-frequency identification (RFID) tagging data, the 2021 year class has been revised downward and the 2022 slightly upward. SSB in 2020 and 2021 has been revised downward because maturity at age has now been recalculated for the 2016 and 2017 year classes and is lower than previously assumed.
The 2026 recruitment estimate from the model is above average but remains highly uncertain. This has, however, only a negligible impact on the advised catches for 2027, as at age 3 its contribution to the fishery and SSB is negligible.
Norwegian spring-spawning herring. Current assessment (red line) compared with previous estimates (2022–2025). The reference points were revised in 2025 following a benchmark, and only assessment results from the last year should be compared to the reference points indicated.
Other Information
Since 2013, catches have been consistently above the levels adviced by ICES. The advice for 2027 is based on the target fishing mortality in the long-term management strategy agreed by the European Union, the Faroe Islands, Iceland, Norway, and the Russian Federation; it does not consider the deviations from the long-term management strategy as evident from the sum of declared unilateral quotas. During the evaluation of the long-term management strategy (ICES, 2018a), a consistent overshooting of the total allowable catch (TAC) was not included in the simulations. Therefore, failing to adhere to the advised catches as derived from the application of 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 long term.
A Management strategy evaluation (MSE) with the updated reference points has not been undertaken, and the simulations do not account for catches consistently exceeding ICES advice. Nevertheless, the management strategy remains appropriate for 2027 advice, as the probability of SSB falling below Blim in 2028 is lower with the plan (p = 4.1%) than with the maximum sustainable yield (MSY) approach (p = 8.3%).
Advice, TAC and Catch
Norwegian spring-spawning herring. Recommended TAC, national TAC, and catches (tonnes).
Year | Recommended TAC ICES | Iceland national TAC | Catches Iceland | Total national TAC | Total catch |
|---|---|---|---|---|---|
2011 | 1 170 000 | 145 000 | 151 074 | 988 000 | 992 998 |
2012 | 833 000 | 121 000 | 120 956 | 833 000 | 825 999 |
2013 | 619 000 | 90 000 | 90 729 | 692 000 | 684 743 |
2014 | 418 487 | 61 000 | 58 828 | 436 893 | 461 306 |
2015 | 283 013 | 41 000 | 42 626 | 328 206 | 328 740 |
2016 | 316 876 | 46 000 | 50 418 | 376 612 | 383 174 |
2017 | 437 364 | 103 000 | 90 400 | 805 142 | 721 566 |
2018 | 384 197 | 72 428 | 83 392 | 546 448 | 592 899 |
2019 | 588 562 | 102 174 | 107 889 | 773 750 | 777 165 |
2020 | 525 594 | 91 243 | 98 173 | 693 915 | 720 937 |
2021 | 651 033 | 117 707 | 114 299 | 881 097 | 851 813 |
2022 | 598 588 | 108 225 | 112 739 | 827 963 | 813 798 |
2023 | 511 171 | 90 954 | 92 197 | 692 942 | 680 193 |
2024 | 390 010 | 61 395 | 62 967 | 446 928 | 457 129 |
2025 | 401 794 | 62 491 | 65 859 | 435 010 | 419 857 |
2026 | 533 914 | 83 291 | 584 025 | ||
2027 | 588 004 |
References and further reading
Anon. 2018. Agreed record of conclusions of fisheries consultations between Iceland, the European Union, the Faroe Islands, Norway and the Russian Federation on the management of the Norwegian spring-spawning (Atlanto-Scandian) herring stock in the North-East Atlantic in 2019. London, 6 November 2018. 6 pp. see here
Anon. 2020. Agreed record of conclusions of fisheries consultations between Norway, the European Union, the Faroe Islands, Iceland, the Russian Federation and the United Kingdom on the management of the Norwegian spring-spawning (Atlanto-Scandian) herring in the North-East Atlantic in 2021. Video-conference, 20-21 October 2020. 7 pp. see here
ICES. 2016. Report of the Benchmark Workshop on Pelagic Stocks (WKPELA), 29 February–4 March 2016, ICES Headquarters, Copenhagen, Denmark. ICES CM 2016/ACOM:34. 106 pp. https://doi.org/10.17895/ices.pub.5581
ICES. 2018a. Report of the Workshop on a long-term management strategy for Norwegian Spring-spawning herring (WKNSSHMSE), 26–27 August 2018, Torshavn, Faroe Islands. ICES CM 2018/ACOM:53. 113 pp. https://doi.org/10.17895/ices.pub.5583.
ICES. 2018b. Report of the Workshop on the determination of reference points for Norwegian Spring Spawning Herring (WKNSSHREF), 10–11 April 2018, ICES Headquarters, Copenhagen, Denmark. ICES CM 2018/ACOM:45. 83 pp. https://doi.org/10.17895/ices.pub.5582
ICES. 2025a. Benchmark workshop on Mackerel and Norwegian spring-spawning herring (WKBMACNSSH). ICES Scientific Reports. 7:64. 509 pp. https://doi.org/10.17895/ices.pub.29279615
ICES. 2025b. Working Group on Widely Distributed Stocks (WGWIDE). ICES Scientific Reports. 6:81. https://doi.org/10.17895/ices.pub.30233824
ICES. 2025c. Herring (Clupea harengus) in subareas 1, 2, 5, and divisions 4.a and 14.a, Norwegian spring-spawning herring (the Northeast Atlantic and Arctic Ocean). In Report of the ICES Advisory Committee, 2025. ICES Advice 2025, her.27.1-24a514a. https://doi.org/10.17895/ices.advice.27202611
MFRI Assessment Reports 2026. NORWEGIAN SPRING-SPAWNING HERRING. Marine and Freshwater Research Institute, 30. September 2026.