Stock Name: Beaked redfish in ICES subareas 1 and 2 (Northeast Arctic)
Advice on fishing opportunities
The ad hoc Joint Russian-Norwegian working group on Arctic Fisheries (JRN-AFWG) advises that when the status quo approach is applied, catches in 2023 should be no more than 66 779 tonnes, and catches in 2024 should be no more than 70 164 tonnes.
Stock development over time
Fishing pressure on the stock is above FMSY19+ and spawning-stock size is above Bpa and Blim.
Catch scenarios
Variable | Value | Notes |
---|---|---|
Fages19+ (2022) | 0.097 | Fsq =F2021 . From assessment |
SSB (2023) | 1 018 117 | Short-term forecast |
Rage 2 (2022) | 307 756 | Regression surveys vs. recruitment |
Rage 2 (2023) | 328 242 | 10-years average |
Rage 2 (2024) | 328 242 | 10-years average |
Total catch (2022 ) | 64 159 | Short-term forecast |
Basis | Total catch (2023) | Ftotal (2023) | SSB (2024) | % SSB change * | % TAC change ** | % Advice change *** | |
---|---|---|---|---|---|---|---|
Advice basis | |||||||
F2023 = F2022 | 66 779 | 0.097 | 1 040 323 | 6.5 | -0.6 | -0.6 | |
Other scenarios | |||||||
Precautionary Approach | 41 886 | 0.060 | 1 063 318 | 8.8 | -37.7 | -37.7 | |
F = 0 | 0 | 0.000 | 1 102 083 | 12.8 | -100.0 | -100.0 | |
F2023 = 1.1 × F2022 | 73 190 | 0.107 | 1 034 405 | 5.9 | 8.9 | 8.9 | |
F2023 = 1.2 × F2022 | 79 555 | 0.117 | 1 028 534 | 5.3 | 18.4 | 18.4 | |
F2023 = 0.9 × F2022 | 60 320 | 0.088 | 1 046 286 | 7.1 | -10.3 | -10.3 | |
F2023 = 0.8 × F2022 | 53 814 | 0.078 | 1 052 295 | 7.7 | -19.9 | -19.9 | |
F = 0.08 | 55 428 | 0.080 | 1 050 804 | 7.6 | -17.5 | -17.5 | |
F = 0.084 | 58 112 | 0.084 | 1 048 325 | 7.3 | -13.5 | -13.5 | |
F = 0.10 | 68 767 | 0.100 | 1 038 488 | 6.3 | 2.3 | 2.3 | |
Suggested 50 000 t cap for all evaluated HCRs | 50 000 | 0.072 | 1 055 819 | 8.1 | -25.6 | -25.6 | |
* SSB 2024 relative to SSB 2021 (976 956 tonnes). | |||||||
** Catch in 2023 relative to TAC set by Norway and Russia for 2022 (67 210 tonnes). | |||||||
*** Advice value for 2023 relative to the advice value for 2022. |
Basis | Total catch (2024) | Ftotal (2024) | SSB (2025) | % SSB change * | % TAC change ** | % Advice change *** |
---|---|---|---|---|---|---|
Advice basis | ||||||
F 2024 = F2023 | 70 164 | 0.097 | 1 055 435 | 8.0 | 5.1 | 5.1 |
Other scenarios | ||||||
F = 0.06 | 45 191 | 0.060 | 1 101 812 | 12.8 | -32.3 | -32.3 |
F = 0.08 | 58 950 | 0.080 | 1 076 409 | 10.2 | -11.7 | -11.7 |
F = 0.084 | 61 627 | 0.084 | 1 071 423 | 9.7 | -7.7 | -7.7 |
F = 0.10 | 72 098 | 0.100 | 1 051 791 | 7.7 | 8.0 | 8.0 |
Suggested 50 000 t cap for all evaluated HCRs | 50 000 | 0.072 | 1 092 973 | 11.9 | -25.1 | -25.1 |
* SSB 2025 relative to SSB 2021 (976 956 tonnes).
** Catch in 2024 relative to TAC in 2023 under the status quo scenario (66 779 tonnes).
*** Advice value for 2024 relative to the advice value for 2023.
The advice for 2023 is 0.9% higher than the advice for 2021 due to increasing stock size and status quo advice but 0.6% lower than the advice for 2022.
Basis of the advice
Advice basis | Status quo |
Management plan | There is no agreed management plan for this stock. Long-term management plan options have been evaluated by ICES (ICES, 2018a). |
Quality of the assessment
The stock was benchmarked in 2018. The choice of a scaling coefficient for the Norwegian–Russian ecosystem survey is a source of potential bias of up to 50%, but the advice is robust to this uncertainty.
Data from the pelagic survey in the Norwegian Sea was reviewed in the recent benchmark assessment and the survey is now included in the assessment model. However, the survey series still does not appropriately cover the geographical distribution of the adult population, and further inclusion of the slope survey should be prioritized.
Age determination is lacking for some surveys and catches in recent years. To account for the lack of catch-at-age data in some years a procedure using length distribution and a time-averaged age-length key was applied.
To smooth out spurious variations in SSB, caused by limited sample size in the weight-at-age of the 19+ group, a fixed weight-at-age function (i.e. common across years) was adopted for the assessment model during the Arctic Fisheries Working Group (AFWG) meeting in 2018 (ICES 2018b).
Issues relevant for the advice
Due to the suspension of Russian scientists from ICES, the assessment was conducted by a Joint Russian-Norwegian working group on Arctic Fisheries (JRN-AFWG) consisting of scientists from VNIRO (Russia) and IMR (Norway) (Howell et al., 2022).
This advice has been conducted outside ICES and should not be considered as ICES advice. However, the assessment has been conducted following the previous procedures and based on the methodology agreed at the ICES benchmark in 2018 (ICES, 2018c).
There has been a significant change in the selectivity, with the fraction of the catch in the 19+ age class increasing in recent years (since 2017) and especially since the last assessment. Any evaluation of a FMSY or Fpa value is conditional on the Fbar and selectivities used in the evaluation. As a result of the changing selectivity, applying the same target Fbar will result in a reduction of the catch as a fraction of the fishable stock. Given that the catch is close to advice, and the SSB is relatively stable, we therefore propose F19+ status quo as an approximation to maintain the same overall fraction of the stock being caught. We note that this stock is due for a benchmark in 2024 prior to the next release of advice, and the advice basis should be revised at that time.
Long-term management plan options have been proposed by Norway and Russia and evaluated by ICES (ICES, 2018a). In the absence of an agreed management plan, the advice is based on the MSY approach. The advice has been based on F19+ = 0.06. This is the highest fishing mortality of those tested during the MSE evaluations (ICES, 2018a) that was found to be precautionary. The present advice is above F19+ = 0.06, due to the selectivity issues mentioned above and has led to a rise in biomass.
There is no international agreement on the sharing of TAC among countries and between national and international waters.
Bycatch of the endangered golden redfish (Sebastes norvegicus) should be kept at a minimum to allow for rebuilding of that stock.
Reference points
Framework | Reference point | Value | Technical basis | Source |
---|---|---|---|---|
MSY approach | MSY Btrigger | 315 000 t | Bpa | ICES (2018a) |
FMSY | 0.084 | F0.1 | ICES (2018a) | |
Precautionary approach | Blim | 227 000 t | ~Bloss (SSB in 1992) | ICES (2018a) |
Bpa | 315 000 t | ~Blim×e(1.645 × 0.2) | ICES (2018a) | |
Flim | ||||
Fpa | ||||
Management plan | SSBmgt | |||
Fmgt |
Basis of the assessment
ICES stock data category | 1 (ICES, 2016) |
---|---|
Assessment type | Statistical catch-at-age model |
Input data | Commercial catches: international landings (tonnes), age frequencies and weight-at-age from catch sampling of the pelagic and demersal fisheries and from the survey; survey indices: numbers-at-age from BS-NoRu-Q1-Btr, Eco-NoRu-Q3-Btr, Ru-Q4-Btr; proportion-at-age from deep pelagic ecosystem survey annual maturity data from BS-NoRu-Q1-Btr, Eco-NoRu-Q3-Btr, and commercial catch sampling; natural mortalities were fixed at 0.05. |
Discards and bycatch | Discarding and bycatch are assumed negligible. |
Other information | Last benchmark was in January 2018 (WKREDFISH; ICES, 2018c). Proposed management plans were evaluated in 2018 (WKREBMSE; ICES, 2018a). |
Working group | Joint Russian-Norwegian working group on Arctic Fisheries (JRN-AFWG) |
History of the advice, catch, and management
Year | ICES advice | Predicted catch corresponding to advice | Agreed TAC | ICES catches |
---|---|---|---|---|
1987 | Precautionary TAC | 70000* | 85000 | 35000 |
1988 | F = F0.1; TAC | 11000 | - | 41000 |
1989 | Status quo F; TAC | 12000 | - | 47000 |
1990 | Status quo F; TAC | 18000 | - | 63000 |
1991 | F at Fmed; TAC | 12000 | - | 68000 |
1992 | If required, precautionary TAC | 22000 | - | 32000 |
1993 | If required, precautionary TAC | 18000 | 18000 | 12814 |
1994 | If required, precautionary TAC | - | - | 12721 |
1995 | Lowest possible F | - | - | 10284 |
1996 | Catch at lowest possible level | - | - | 8075 |
1997 | Catch at lowest possible level | - | - | 8598 |
1998 | No directed fishery, reduce bycatch | - | - | 14045 |
1999 | No directed fishery, reduce bycatch | - | - | 11209 |
2000 | No directed fishery, bycatch at lowest possible level | - | - | 10075 |
2001 | No directed fishery, bycatch at lowest possible level | - | - | 18418 |
2002 | No directed fishery, bycatch at lowest possible level | - | - | 6993 |
2003 | No directed fishery, bycatch at lowest possible level | - | - | 2520 |
2004 | No directed trawl fishery and low bycatch limits | - | - | 5493** |
2005 | No directed trawl fishery and low bycatch limits | - | - | 8465** |
2006 | No directed trawl fishery and low bycatch limits | - | - | 33261** |
2007 | No directed trawl fishery and low bycatch limits | - | 15500^ | 20219** |
2008 | Protection of juveniles, no directed trawl fishery and low bycatch limits | - | 14500^ | 1309 6 ** |
2009 | Protection of juveniles, no directed trawl fishery and low bycatch limits | - | 10500^ | 10246** |
2010 | Protection of juveniles, no directed trawl fishery and low bycatch limits | - | 8600^ | 11924** |
2011 | Protection of juveniles, no directed trawl fishery and low bycatch limits | - | 7900^ | 12962** |
2012 | Protection of juveniles, no directed fishery and low bycatch limits | - | 7500^ | 11059** |
2013 | F0.1 | < 47000 | 19500^ | 9 389 ** |
2014 | Status quo catch | < 24000 | 36800^^ | 18 426 ** |
2015 | Precautionary approach | < 30000 | 30000# | 25 570 |
2016 | Precautionary approach | < 30000 | 30000# | 3 4754 |
2017 | Precautionary approach | < 30000 | 30000# | 3 0783 |
2018 | Precautionary approach | < 32658 | 32658# | 38 046 |
2019 | Precautionary approach | < 53757 | 53757# | 45 640 |
2020 | Precautionary approach | < 55860 | 55860# | 53631 |
2021 | Precautionary approach | < 66158 | 66158# | 63482 ^^^ |
2022 | Precautionary approach | < 67210 | 67210# | |
2023 | Status quo approach | < 66779^^^ | ||
2024 | Status quo approach | < 70164^^^ |
* Includes both Sebastes mentella and S. norvegicus .
** Includes the pelagic catches in the Norwegian Sea outside the EEZ.
^ TAC set by the North-East Atlantic Fisheries Commission (NEAFC) for an Olympic fishery in international waters.
^^ Sum of TAC set by NEAFC in international waters and by Norway in the Norwegian Economic Zone.
^^^ In 2022 assessment and advice was carried out by the Joint Russian-Norwegian working group on Arctic Fisheries (JRN-AFWG) which compiled catches for 2021 and gave advice for 2023 and 2024.
# TAC set by jointly by Norway and Russia
History of catch and landings
Year | Inside the NEAFC RA (tonnes) | Outside the NEAFC RA (tonnes) | Total catches (tonnes) | Proportion inside the NEAFC RA (%) |
---|---|---|---|---|
2019 | 6060 | 39580 | 45640 | 13. 3 % |
2020 | 5469 | 48162 | 53631 | 10.2 % |
2021 | 2872 | 60610 | 63482 | 4.5 % |
Year | Other countries | Denmark | Estonia | Faroe Islands | France | Germany | Greenland | Iceland | Ireland | Latvia | Lithuania | Netherlands | Norway | Poland | Portugal | Russia | Spain | UK | Total | |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
England & Wales | Scotland ** | |||||||||||||||||||
1993 | Can. 8 | 4 | 13 | 50 | 35 | 1 | 5182 | 963 | 6260 | 5 | 293 | - | 12814 | |||||||
1994 | 28 | 4 | 74 | 18 | 1 | 3 | 6511 | 895 | 5021 | 30 | 124 | 12 | 12721 | |||||||
1995 | 3 | 16 | 176 | 2 | 4 | 2646 | 927 | 6346 | 67 | 93 | 4 | 10284 | ||||||||
1996 | 4 | 75 | 119 | 3 | 2 | 6053 | 467 | 925 | 328 | 76 | 23 | 8075 | ||||||||
1997 | 4 | 37 | 81 | 16 | 6 | 4657 | 1 | 474 | 2972 | 272 | 71 | 7 | 8598 | |||||||
1998 | 20 | 73 | 100 | 14 | 9 | 9733 | 13 | 125 | 3646 | 177 | 93 | 41 | 14045 | |||||||
1999 | 73 | 26 | 202 | 50 | 3 | 7884 | 6 | 65 | 2731 | 29 | 112 | 28 | 11209 | |||||||
2000 | 50 | 12 | 62 | 29 | 48 | 1 | 6020 | 2 | 115 | 3519 | 87 | 130 | 10075 | |||||||
2001 | 74 | 16 | 198 | 17 | 3 | 4 | 13937 | 5 | 179 | 3775 | 90 | 120 | 18418 | |||||||
2002 | 15 | 75 | 58 | 99 | 18 | 41 | 4 | 2152 | 8 | 242 | 3904 | 190 | 188 | 6993 | ||||||
2003 | 64 | 22 | 32 | 8 | 5 | 5 | 1210 | 7 | 44 | 952 | 47 | 124 | 2520 | |||||||
2004 | Swe. 1 | 588 | 13 | 10 | 4 | 10 | 3 | 1375 | 42 | 235 | 2879 | 257 | 76 | 5493 | ||||||
2005 | 5 | 1147 | 46 | 33 | 39 | 4 | 4 | 7 | 1760 | 140 | 5023 | 163 | 95 | 8465 | ||||||
2006 | Can. 433 | 396 | 3808 | 215 | 2483 | 63 | 2513 | 4 | 341 | 845 | 4710 | 2496 | 1804 | 11413 | 710 | 1027 | 33261 | |||
2007 | 684 | 2197 | 234 | 520 | 29 | 1587 | 17 | 349 | 785 | 3209 | 1081 | 1483 | 5660 | 2181 | 202 | 20219 | ||||
2008 | 1849 | 187 | 16 | 25 | 9 | 9 | 267 | 117 | 13 | 2220 | 8 | 713 | 7117 | 463 | 83 | 13096 | ||||
2009 | EU 889 | 1343 | 15 | 42 | 33 | 3 | 2677 | 338 | 806 | 3843 | 177 | 80 | 10246 | |||||||
2010 | 979 | 175 | 21 | 12 | 2 | 243 | 457 | 2065 | 293 | 6414 | 1184 | 79 | 11924 | |||||||
2011 | 984 | 175 | 835 | 2 | 536 | 565 | 2471 | 11 | 613 | 5037 | 1678 | 55 | 12962 | |||||||
2012 | 259 | 517 | 36 | 447 | 449 | 2114 | 318 | 1038 | 4101 | 1780 | 11059 | |||||||||
2013 | 697 | 80 | 21 | 1 | 280 | 262 | 1750 | 84 | 1078 | 3677 | 1459 | 9389 | ||||||||
2014 | 743 | 215 | 446 | 15 | - | 215 | 167 | 3 | 13149 | 103 | 505 | 1704 | 1162 | 18426 | ||||||
2015 | 657 | 49 | 242 | 48 | 3 | 537 | 192 | 3 | 19433 | 5 | 678 | 1142 | 2529 | 52 | 25570 | |||||
2016 | 502 | 134 | 493 | 74 | 24 | 0 | 1243 | 1065 | 18191 | 208 | 1066 | 8419 | 3213 | 3213 | 34754 | |||||
2017 | 4 | 443 | 45 | 763 | 66 | 3 | 562 | 790 | 17077 | 102 | 1060 | 6593 | 2838 | 2838 | 30783 | |||||
2018 | 425 | 67 | 2473 | 82 | 10 | 1020 | 1010 | 374 | 18594 | 275 | 699 | 10497 | 2457 | 2457 | 38046 | |||||
2019 | 156 | 370 | 1599 | 615 | 10 | 653 | 244 | 23844 | 471 | 1422 | 13444 | 2222 | 2222 | 45640 | ||||||
2020 | 149 | 163 | 1807 | 62 | 5 | 2 | 1081 | 1483 | 32950 | 4 | 870 | 13874 | 744 | 744 | 53631 | |||||
2021* | 290 | 218 | 1166 | 85 | 6 | 1379 | 43797 | 2 | 381 | 14887 | 615 | 615 | 63482 ^ |
* Provisional figures. ** Includes UK (E&W) since 2000
^ In 2022 assessment and advice was carried out by the Joint Russian-Norwegian working group on Arctic Fisheries (JRN-AFWG) which compiled catches for 2021 and gave advice for 2023 and 2024.
Summary of the assessment
Year | Recruitment | Spawning-stock biomass | Total | Fishable | Catches | Fishing mortality | ||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
Recruitment age 2 | High 95% | Low 95% | SSB | High 95% | Low 95% | Biomass Ages-2+ | Biomass Ages-6+ | F ages 19+ | High 95% | Low 95% | ||
thousands | tonnes | |||||||||||
1992 | 429977 | 547252 | 337834 | 272832 | 370101 | 201127 | 578519 | 538268 | 15590 | 0.042 | 0.058 | 0.03 |
1993 | 289490 | 365156 | 229503 | 323633 | 427869 | 244791 | 625353 | 574249 | 12814 | 0.031 | 0.041 | 0.023 |
1994 | 209655 | 264337 | 166284 | 408052 | 528118 | 315282 | 683931 | 633320 | 12721 | 0.027 | 0.036 | 0.02 |
1995 | 200014 | 251339 | 159170 | 469927 | 600659 | 367648 | 749296 | 703309 | 10284 | 0.02 | 0.027 | 0.015 |
1996 | 159840 | 200852 | 127203 | 388973 | 505507 | 299303 | 815380 | 783244 | 8075 | 0.014 | 0.018 | 0.011 |
1997 | 111468 | 139928 | 88797 | 478373 | 606875 | 377080 | 879859 | 855375 | 8598 | 0.013 | 0.017 | 0.01 |
1998 | 57486 | 72381 | 45655 | 540768 | 678977 | 430692 | 939125 | 917192 | 14045 | 0.019 | 0.024 | 0.015 |
1999 | 46459 | 58519 | 36885 | 608797 | 755222 | 490761 | 987290 | 970504 | 11209 | 0.014 | 0.018 | 0.011 |
2000 | 36893 | 46354 | 29364 | 705479 | 866531 | 574360 | 1028121 | 1016753 | 10075 | 0.011 | 0.014 | 0.009 |
2001 | 35692 | 45505 | 27995 | 655042 | 807472 | 531387 | 1061862 | 1055391 | 18418 | 0.02 | 0.025 | 0.016 |
2002 | 42423 | 54032 | 33309 | 738944 | 902669 | 604915 | 1076126 | 1070770 | 6993 | 0.007 | 0.009 | 0.006 |
2003 | 45546 | 58175 | 35658 | 815196 | 989820 | 671379 | 1092350 | 1087725 | 2520 | 0.003 | 0.003 | 0.002 |
2004 | 61313 | 77705 | 48379 | 821177 | 994104 | 678332 | 1105561 | 1100773 | 5493 | 0.006 | 0.007 | 0.004 |
2005 | 117600 | 148460 | 93155 | 876777 | 1057921 | 726650 | 1111756 | 1105858 | 8465 | 0.008 | 0.01 | 0.007 |
2006 | 228265 | 288780 | 180431 | 863053 | 1042471 | 714514 | 1114103 | 1106351 | 33261 | 0.042 | 0.057 | 0.031 |
2007 | 341155 | 437321 | 266135 | 1006505 | 1212420 | 835563 | 1093005 | 1080772 | 20219 | 0.024 | 0.033 | 0.018 |
2008 | 379932 | 490519 | 294277 | 943961 | 1141892 | 780338 | 1086510 | 1065557 | 13096 | 0.018 | 0.025 | 0.014 |
2009 | 381522 | 497778 | 292418 | 981572 | 1185259 | 812888 | 1089978 | 1056792 | 10246 | 0.012 | 0.017 | 0.009 |
2010 | 484675 | 642042 | 365879 | 934873 | 1130950 | 772791 | 1102470 | 1058427 | 11924 | 0.013 | 0.018 | 0.01 |
2011 | 585041 | 790237 | 433126 | 924087 | 1117215 | 764345 | 1121726 | 1072615 | 12962 | 0.015 | 0.021 | 0.01 |
2012 | 514156 | 707787 | 373497 | 918287 | 1108923 | 760423 | 1150236 | 1097864 | 11059 | 0.013 | 0.018 | 0.009 |
2013 | 277390 | 394846 | 194875 | 870554 | 1053448 | 719413 | 1193293 | 1132140 | 9389 | 0.011 | 0.016 | 0.008 |
2014 | 301447 | 440457 | 206309 | 818776 | 992986 | 675129 | 1251414 | 1186181 | 18426 | 0.023 | 0.032 | 0.016 |
2015 | 287730 | 456560 | 181331 | 839740 | 1014367 | 695176 | 1306128 | 1251762 | 25570 | 0.032 | 0.043 | 0.024 |
2016 | 261768 | 455820 | 150328 | 896320 | 1076019 | 746632 | 1349036 | 1314328 | 34754 | 0.044 | 0.058 | 0.033 |
2017 | 267611 | 505336 | 141719 | 872141 | 1049785 | 724558 | 1385571 | 1349432 | 30783 | 0.042 | 0.058 | 0.031 |
2018 | 273985 | 609408 | 123181 | 892107 | 1072432 | 742104 | 1426595 | 1392068 | 38046 | 0.054 | 0.073 | 0.04 |
2019 | 277225 | 733569 | 104767 | 919610 | 1105110 | 765248 | 1458710 | 1426141 | 45640 | 0.066 | 0.087 | 0.049 |
2020 | 271416 | 936334 | 78676 | 950770 | 1143785 | 790328 | 1482233 | 1449024 | 53631 | 0.085 | 0.116 | 0.063 |
2021 | 265735 | 1155311 | 61122 | 976956 | 1179110 | 809461 | 1497178 | 1463463 | 63482 | 0.097 | 0.135 | 0.07 |
2022 | 307756 * | 996124 |
* Assumed value ( regression between survey indices and recruitment time series)
References
ICES. 2016. Advice basis. In Report of the ICES Advisory Committee, 2016. ICES Advice 2016, Book 1, Section 1.2.
ICES. 2018a. Workshop on the evaluation of harvest control rules for Sebastes mentella in ICES areas 1 and 2 (WKREBMSE). June –August 2018, by correspondence. ICES CM 2018/ACOM:52, IN PRESS.
ICES. 2018b. Report of the Arctic Fisheries Working Group (AFWG), 18–24 April 2018, JRC, Ispra, Italy. ICES CM 2018/ACOM:06, 857 pp.
ICES. 2018c. Report of the Benchmark Workshop on Redfish Stocks (WKREDFISH). 29 January –2 February 2018, Copenhagen, Denmark. ICES CM 2018/ACOM:34, 174 pp.