North-East Atlantic Commission NEA(18)10. Presentation of the ICES Advice for the North-East Atlantic stocks to the Commission

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North-East Atlantic Commission NEA(18)10 Presentation of the ICES Advice for the North-East Atlantic stocks to the Commission

sal.27.neac Atlantic salmon from Northeast Atlantic

Terms of Reference 2. With respect to Atlantic salmon in the North-East Atlantic Commission area: 2.1 describe the key events of the 2017 fisheries; 2.2 review and report on the development of age-specific stock conservation limits, including updating the time-series of the number of river stocks with established CLs by jurisdiction; 2.3 describe the status of the stocks, including updating the time-series of trends in the number of river stocks meeting CLs by jurisdiction; 2.4 provide catch options or alternative management advice for the 2018/19-2020/21 fishing seasons, with an assessment of risks relative to the objective of exceeding stock conservation limits, or pre-defined NASCO Management Objectives, and advise on the implications of these options for stock rebuilding; and 2.5 update the Framework of Indicators used to identify any significant change in the previously provided multi-annual management advice.

Background Northeast Atlantic Commission (NEAC) stocks are combined into two groups for the provision of management advice for fisheries at West Greenland and Faroes Southern group (Southern NEAC) : UK (Scotland) UK (England and Wales) UK (N. Ireland) Ireland France Iceland (south/west regions) Northern group (Northern NEAC) : Russia Finland Norway Sweden Iceland (north/east regions)

Nominal catch (t) 2.1 Key Events 2017 Fisheries No significant changes in the gear types used. No fishery Faroes since 2000 NEAC Reported Nominal Catch (sal.27.neac: Table 1, Figure 1): 1039 t 162 t in Southern NEAC (lowest in time series) 5000 877 t in Northern NEAC 4500 4000 Unreported catch: 317 t Southern Northern Total Faroes NEAC NEAC NEAC 2017 nominal catch (t) 162 877 0 1039 Catch as % of NEAC total 16 84 0 Unreported catch (t) 16 301-317 Location of catches % in-river 58 65-64 % in estuaries 20 0-3 % coastal 23 35-33 3500 3000 2500 2000 1500 1000 500 0 1971 1976 1981 1986 1991 1996 2001 2006 2011 2016 Southern NEAC Southern 5-year mean Northern NEAC Northern 5 year-mean

2.1 Key Events 2017 Fisheries Declining trend in catch of 1SW salmon over time series (1987-2017) Exploitation rates deceased since early 1980s, 1SW and MSW salmon have become similar N-NEAC S-NEAC N-NEAC S-NEAC sal.27.neac: Figure 2 sal.27.neac: Figure 3

2.2 Stock Conservation Limits (CLs) River-specific CLs (egg or spawner requirements): France, Ireland, UK (England & Wales), UK (Northern Ireland), Finland, Norway, and Sweden CLs summed to country level Interim approach: Updates: Russia, UK (Scotland), and Iceland UK (Scotland) currently developing modelling approach for river specific CLs Russia preliminary results from a few rivers sal.27.neac: section from Table 4 Country or jurisdiction Northern NEAC Number of rivers with CLs Number of rivers assessed for compliance Russia 85 8 Finland/Norway (Tana/Teno) 24 14 Norway 439 174 Sweden 24 22 Southern NEAC UK (Scotland) 171 171 UK (Northern Ireland) 16 11 UK (England & Wales) 64 64 Ireland 143 143 France 35 35

2.2 Stock Conservation Limits (CLs) and Spawner Escapement Reserves (SERs) National CLs summed to four NEAC stock complexes SER (Spawner Escapement Reserves ) Number of fish prior to fisheries to meet CLs when they return to homewaters CLs increased to account for natural mortality (M = 0.03 per month) between 1 January of first winter and return to homewaters sal.27.neac: Table 3 Complex Sea age group CL (number of fish) SER (number of fish) Northern NEAC Southern NEAC 1SW 137 330 173 601 MSW 120 953 206 201 1SW 654 921 830 559 MSW 324 126 550 081

2.3 Stock Status Pre-Fishery Abundance (PFA) : abundance at 1 January of first winter at sea by sea age group (maturing 1SW and non-maturing 1SW (MSW) salmon) by stock complex (Northern NEAC and Southern NEAC) and individual country PFA relative to SER (Spawner Escapement Reserve: CLs adjusted for natural mortality) Spawners relative to CLs Risk Assessment Framework Full Reproductive Capacity : lower bound of the 90% confidence interval of the estimate above reference point equivalent to a probability of at least 95% of meeting reference point At Risk of Suffering Reduced Reproductive Capacity: lower bound of the confidence interval is below reference point, but the midpoint is above Suffering Reduced Reproductive Capacity: midpoint is below reference point

2.3 Stock Status: Northern NEAC (N-NEAC) N-NEAC: 2017 PFA Declining trend PFA > SER Both complexes at full reproductive N-NEAC: 2017 Spawners Spawners > CLs Both complexes at full reproductive 1SW spawners lowest in time series sal.27.neac: Figure 5

2.3 Stock Status: Southern NEAC (S-NEAC) S-NEAC: 2017 PFA Declining trend Mat 1SW: suffering reduced reproductive Non-mat 1SW: at risk of suffering reduced reproductive S-NEAC: 2017 Spawners 1SW spawners: suffering reduced reproductive MSW spawners: at risk of suffering reduced reproductive sal.27.neac: Figure 5

2.3 Stock Status: PFA by Country Northern NEAC 2017: Non-mat. 1SW: full reproductive Mat. 1SW: full reproductive in Iceland and Norway, others at risk or suffering reduced reproductive Southern NEAC 2017: Non-mat. 1SW: full reproductive in UK (England and Wales and N. Ireland), others at risk or suffering reduced reproductive Mat. 1SW: full reproductive in UK (N. Ireland), others at risk or suffering Full Risk suffering reduced reproductive > 100 > 100 reduced < 100 sal.27.neac: Figure 6 reproductive reproductive Suffering reduced reproductive

2.3 Stock Status: 1SW by Country Northern NEAC 2017: 1SW spawners at risk of (Iceland) or suffering (Russia, Sweden, Teno/Finland) reduced reproductive Southern NEAC 2017: With exception of UK (N. Ireland), 1SW spawners suffering reduced reproductive sal.27.neac: Figure 7 Full reproductive Risk suffering reduced reproductive > 100 > 100 < 100 Suffering reduced reproductive

2.3 Stock Status: MSW by Country Northern NEAC 2017: MSW spawners: full reproductive : Norway and Iceland at risk: Sweden suffering: Finland and Russia Southern NEAC 2017: MSW spawners: full reproductive : UK (England and Wales, N. Ireland) suffering reduced reproductive : Full Risk suffering France, Ireland, and UK (Scotland) > 100 > 100 < 100 sal.27.neac: Figure 8 reproductive reduced reproductive Suffering reduced reproductive

2.3 Stock Status: Trends in Rivers Meeting CLs nine jurisdictions with river-specific CLs (sal.27.neac: Table 4, Figure 4) Spawners assessed against CLs Country or jurisdiction Number rivers assessed Number attaining CL % attaining CL Trend statement Northern NEAC Russia 8 7 88 stable Finland/Norway 0% attainment to 2013, variable 14 4 29 (Tana/Teno) since 2014 (20% to 40%) Norway 174 142 82 increasing Sweden 22 12 55 increasing (data for 2016 and 2017 only) Southern NEAC UK (Scotland) 171 47 27 Decreasing UK (Northern Ireland) 11 6 55 Increasing UK (England & Wales) 64 50 32 increasing since 2014 Ireland 143 44 31 decreasing since 2014 France 35 21 60 Increasing

Standardised return rates (%) of smolts to 1SW and 2SW salmon 2.3 Stock Status: Return Rates (Marine Survival) 1SW declining trend since 1980 2SW no trend Little improvement of stock status over time Mainly a consequence of continuing poor survival in the marine environment sal.27.neac: Figure 9 18 16 14 12 10 8 6 4 2 North Wild 1SW North Wild 2SW 0 1980 1985 1990 1995 2000 2005 2010 2015 25 20 15 10 5 South Wild 1SW South Wild 2SW 0 Year of smolt migration 1980 1985 1990 1995 2000 2005 2010 2015 12 10 8 6 4 2 North Hatchery 1SW North Hatchery 2SW 0 1980 1985 1990 1995 2000 2005 2010 2015 18 16 14 12 10 Year of smolt migration 8 6 4 2 South Hatchery 1SW 0 1980 1985 1990 1995 2000 2005 2010 2015

2.4 Catch Options: Multi-Year Catch Agreement 2015-2018 NASCO 2015 multi-year regulatory agreement for the Faroese salmon fishery (http://www.nasco.int/pdf/2015%20papers/nea_15_10.pdf) 2018 is the third and final year of this agreement A full assessment of stock status and catch advice was conducted to inform a potential new multi-year agreement.

2.4 Catch Options: PFA Forecasts 2017-2021 Northern NEAC (sal.27.neac: Table 6, Figure 10) Without any fisheries 2018-2021, Potential 1SW spawners: < 95% probability of meeting CLs (84% - 89%) Potential MSW spawners: > 95% probability of meeting CLs (96% - 99%)

2.4 Catch Options: PFA Forecasts 2017-2021 Southern NEAC (sal.27.neac: Table 6, Figure 11) Without any fisheries 2018-2021, Potential 1SW and MSW spawners: < 95% probability of meeting CLs 1SW: 17% - 30% MSW: 37% - 55%

2.4 Catch Options: N-NEAC MSW: 95% probability of achieving SERs at Faroes Catch option of 20t No catch option ensures a >95% probability of all complexes achieving SERs simultaneously (10% at 0 t) By Country (sal.27.neac: Tables 7 and 8): 1SW all less than 95% probability of meeting CLs at 0 t MSW most less than 95% probability of meeting CLs at 0 t (exceptions Norway and Iceland) ICES CM 2018/ACOM:21 WGNAS Figure 3.5.1.1

2.4 Catch Options: ICES advises that, in line with the management objectives agreed by NASCO and consistent with the Maximum Sustainable Yield Approach (MSY), there are no mixed-stock fishery options on the NEAC complexes/countries at the Faroes in 2018/2019 to 2020/2021 Even in the absence of a fishery at Faroes, the abundance of many stocks remains low and particular care should be taken to ensure that homewater fisheries are managed to protect stocks that are below their CLs

2.5 Framework of Indicators In the intermediate years of a multiyear catch agreement, an interim assessment is conducted to determine whether a full reassessment of stock status and new catch advice might be required. This assessment relies on a framework of indicators (FWI) that was updated in 2018 FWI could be applied for the next two years, in January 2019 and 2020, based on new assessment data in 2018 and 2019 (e.g. returns, counts, catch) only N-NEAC 1SW salmon and S-NEAC 1SW and MSW are included in the assessments (forecasts below CLs resulting in no catch option for Faroes) full reassessment required if any of these NEAC stock complexes suggest an increase in PFA abundance that is above the 75th percentile of the forecasted PFA