COD Gadus morhua

Advice 2026/2027

201 674

tonnes

Advice 2025/2026

203 822

tonnes

Advice change

-1 %

Publication of Advice: 12th June 2026. Published by Marine and Freshwater Research Institute.


Advice

MFRI and ICES advise that when the Icelandic management plan is applied, catches in the fishing year 2026/2027 should be no more than 201 674 tonnes.

Stock development

Fishing pressure is at HRMGT, and below HRMSY and HRpa; spawning stock size is above MSY Btrigger, Bpa, and Blim.

Cod. Catch by gear type, recruitment, harvest rate, reference stock biomass (B4+) and spawning stock biomass (SSB). Shaded areas and error bars show 95% confidence intervals.

Basis of the assessment and reference points

Basis of the advice

Management plan

Management plan

TAC set as the average of last year’s TAC and 20% of reference biomass

Assessment type

Statistical catch at age model

Input data

Catch in numbers and age disaggregated indices (IS-SMB, IS-SMH)

Approach

Reference point

Value

Basis

MSY approach

MSY Btrigger

265 000

The fifth percentile on the distribution of SSB when the TAC is based on HRMGT

HRMSY

0.22

Stochastic HCR evaluation. Percentage of Bage 4+

Management plan

MGT Btrigger

220 000

Management plan

HRMGT

0.2

Management plan

Precautionary approach

Blim

125 000

Bloss

Bpa

160 000

Blim x e1.645 * 0.15

HRpa

0.39

HR leading to P(SSB > Blim) = 95 % with Btrigger

Prospects

The Icelandic Ministry of Industries has a fisheries management plan for Icelandic cod. The plan, which aims at providing maximum sustainable yield, was re-evaluated by ICES and found to be consistent with both the precautionary principle and ICES MSY approach (ICES, 2021). According to the management plan, the TAC for the fishing year Y/Y+1 (01 September of year Y to 31 August of year Y+1) is calculated as follows:

\[ \text{TAC}_{Y/Y+1} = \frac{\text{min}\left(\frac{\text{SSB}_Y}{\text{MGT B}_{\text{trigger}}},1\right) \text{HR}_{\text{MGT}}B_{4+,y} + \text{TAC}_{Y-1/Y}}{2} \]

where B4+,y is the biomass of cod aged 4 and older in year y and MGT Btrigger = 220 000 tonnes.

The expected range of the realized harvest rate (HR) when following the management plan (HRMGT) is between 0.15 and 0.27 (ICES, 2021).

Cod. Assumptions made for the interim year and in the forecast.

Variable

Value

Notes

Reference biomass (2027)

1 001 790

Short term forecast; in tonnes

Recruitment age 3 (2027)

133 469

Estimated by the model; in thousands

Harvest rate (2026)

0.2

Annual HR, based on estimated catch in 2026.

SSB (2027)

370 011

Short term forecast; in tonnes

Recruitment age 3 (2028)

115 513

Estimated by the model; in thousands

Catch (2026)

202 367

Estimated catch until the end of the fishing year (31 August 2026) and estimated catch in the first four months of the next fishing year (1 September–31 December 2026); tonnes

Cod. Projection of reference biomass and SSB (tonnes) based on adopted harvest control rule.

Basis

Catch (2026/2027)

Harvest rate (2026/2027)

SSB (2028)

% SSB change1)

Advice change2)

Management plan

201 674

0.2

362 203

-2

-1

1) SSB in 2028 relative to SSB in 2027

2) Advice value for 2026/2027 relative to advice value for 2025/2026 (203822 t)

Quality of the assessment

This year’s assessment is in line with previous assessments.

Cod. Current assessment (red line) compared with previous estimates (2022–2025).

Other information

Stock and catch weights-at-ages have been lower than the long-term average for most ages over the past three years, especially in the age classes that currently dominate the reference biomass. As capelin is known to be a major prey source for cod in Icelandic waters (Pálsson and Björnsson, 2011) and capelin stock levels have been linked to cod growth (Frater et al., 2019), the reduction in cod weights is likely linked to low levels of capelin (cap.27.2a514) in Icelandic waters in recent years.

Recent and historical patterns of common cohort strength shared between this stock and the East Greenland–Iceland offshore spawning cod stock (cod.21.27.1.14; ICES, 2026) suggest linkages in productivity and periodic migrations. These linkages have not been quantified but may affect assumptions of stock boundaries, stock productivity, and sustainable fishing rates.

Advice, TAC and Catch

Cod. Recommended TAC according to management plan, national TAC, and catches (tonnes).

Fishing year

Recommended TAC

National TAC

Catches Iceland

Catches other nations1)

Total catch

1984

200  000

242  000

281  696

2  387

281  696

1985

200  000

263  000

322  750

2  457

322  750

1986

300  000

300  000

365  909

2  781

365  909

1987

300  000

330  000

389  936

2  449

389  936

1988

300  000

350  000

375  908

2  335

375  908

1989

300  000

325  000

354  195

2  324

354  195

1990

250  000

300  000

333  870

2  042

333  870

1991

240  000

245  000

243  369

1  871

243  369

1991/1992

250  000

265  000

272  172

1  105

272  172

1992/1993

154  000

205  000

297  487

7  357

301  812

1993/1994

150  000

165  000

196  929

12  431

209  712

1994/1995

130  000

155  000

164  113

7  076

168  441

1995/1996

155  0002)

155  000

169  673

6  495

179  080

1996/1997

186  0002)

186  000

203  915

2  716

205  661

1997/1998

218  0002)

218  000

227  800

1  238

228  401

1998/1999

250  0002)

250  000

254  729

1  477

254  942

1999/2000

247  0002)

250  000

255  692

132

255  724

2000/2001

203  0002)

220  000

221  740

1  267

221  792

2001/2002

190  0002)

190  000

216  864

1  330

216  907

2002/2003

179  0002)

179  000

196  652

2  434

196  678

2003/2004

209  0002)

209  000

219  389

3  480

219  395

2004/2005

205  0002)

205  000

209  333

3  019

209  457

2005/2006

198  000

198  000

201  839

1  807

201  857

2006/2007

178  000

193  000

186  762

1  847

186  762

2007/2008

130  0003)

130  000

138  702

2  080

139  125

2008/2009

124  0003)

160  000

168  515

1  383

168  515

2009/2010

150  0003)

155  000

167  467

1  456

167  467

2010/2011

160  0003)

160  000

164  719

1  426

164  734

2011/2012

177  0003)

177  000

182  486

1  428

182  494

2012/2013

196  0003)

195  000

210  361

1  543

210  510

2013/2014

215  0003)

214  000

223  964

1  475

225  088

2014/2015

218  0003)

218  000

221  061

1  544

222  605

2015/2016

239  0003)

239  000

249  934

1  951

251  885

2016/2017

244  0003)

244  000

234  649

2  605

237  254

2017/2018

257  5723)

257  572

267  135

2  612

269  747

2018/2019

264  4373)

264  437

262  888

2  013

264  901

2019/2020

272  4113)

272  411

269  328

2  044

271  372

2020/2021

256  5933)

256  593

269  423

2  365

271  788

2021/2022

222  3733)

222  373

235  685

2  620

238  305

2022/2023

208  8463)

208  846

218  176

2  359

220  535

2023/2024

211  3093)

211  309

218  778

2  486

221  264

2024/2025

213  2143)

213  214

223  087

2  408

225  495

2025/2026

203  8223)

203  822

2026/2027

201  6743)

1) Landings of other nations before 2014 is by calendar year

2) 25 % harvest control rule

3) 20 % harvest control rule

References and further reading

ICES. 2021. Workshop on the re-evaluation of management plan for the Icelandic cod stock (WKICE-COD). ICES Scientific Reports. 3:30. 85 pp. https://doi.org/10.17895/ices.pub.7987

ICES. 2026. Northwestern Working Group (NWWG). ICES Scientific Reports.

MFRI Assessment Reports 2026. Cod. Marine and Freshwater Research Institute, 12 June 2026.

Pálsson ÓK, Björnsson H. 2011. Long-term changes in trophic patterns of Iceland cod and linkages to main prey stock sizes. ICES Journal of Marine Science, 68(7), 1488–1499. https://doi.org/10.1093/icesjms/fsr057

Frater, P. N., Hrafnkelsson, B., Elvarsson, B. T., & Stefansson, G. 2019. Drivers of growth for Atlantic cod (Gadus morhua L.) in Icelandic waters–A Bayesian approach to determine spatiotemporal variation and its causes. Journal of Fish Biology, 95(2), 401-410.