Norway lobster (Nephrops norvegicus) in Division 4.b, Functional Unit 6 (central North Sea, Farn Deeps)

Similar documents
Norway lobster (Nephrops norvegicus) in Division 4.b, Functional Unit 6 (central North Sea, Farn Deeps)

Norway lobster (Nephrops norvegicus) in Division 4.a, Functional Unit 7 (northern North Sea, Fladen Ground)

Norway lobster (Nephrops norvegicus) in Division 4.a, Functional Unit 32 (northern North Sea, Norway Deep)

Norway lobster (Nephrops norvegicus) in Division 3.a, functional units 3 and 4 (Skagerrak and Kattegat)

Please note: The present advice replaces the advice given in June 2017 for catches in 2018.

Norway lobster (Nephrops norvegicus) in Division 4.a, Functional Unit 10 (northern North Sea, Noup)

Saithe (Pollachius virens) in subareas 4 and 6, and in Division 3.a (North Sea, Rockall and West of Scotland, Skagerrak and Kattegat)

Norway lobster (Nephrops norvegicus) in divisions 8.a b, FUs (Bay of Biscay North and Central)

Plaice (Pleuronectes platessa) in Subarea 4 (North Sea) and Subdivision 20 (Skagerrak)

Plaice (Pleuronectes platessa) in Subarea 4 (North Sea) and Subdivision 20 (Skagerrak)

ICES advice on fishing opportunities

Whiting (Merlangius merlangus) in Subarea 4 and Division 7.d (North Sea and eastern English Channel)

Plaice (Pleuronectes platessa) in Subarea IV (North Sea) and Division IIIa (Skagerrak)

Whiting (Merlangius merlangus) in divisions 7.b c and 7.e k (southern Celtic Seas and western English Channel)

EU request to ICES on in-year advice on haddock (Melanogrammus aeglefinus) in Division 7.a (Irish Sea)

Plaice (Pleuronectes platessa) in Division 7.e (western English Channel)

Whiting (Merlangius merlangus) in Division 6.a (West of Scotland)

ICES advises that when the MSY approach is applied, catches in 2019 should be no more than tonnes.

Witch (Glyptocephalus cynoglossus) in Subarea 4 and divisions 3.a and 7.d (North Sea, Skagerrak and Kattegat, eastern English Channel)

Haddock (Melanogrammus aeglefinus) in divisions 7.b k (southern Celtic Seas and English Channel)

Spurdog (Squalus acanthias) in the Northeast Atlantic

Cod (Gadus morhua) in subdivisions 24 32, eastern Baltic stock (eastern Baltic Sea) *

Advice June Sole in Division IIIa and Subdivisions (Skagerrak, Kattegat, and the Belts)

Advice October 2014

Golden redfish (Sebastes norvegicus) in subareas 5, 6, 12, and 14 (Iceland and Faroes grounds, West of Scotland, North of Azores, East of Greenland)

Striped red mullet (Mullus surmuletus) in Subarea 4 and divisions 7.d and 3.a (North Sea, eastern English Channel, Skagerrak and Kattegat)

Plaice (Pleuronectes platessa) in subdivisions (Baltic Sea, excluding the Sound and Belt Seas)

5.3.2 White anglerfish (Lophius piscatorius) in divisions 7.b k, 8.a b, and 8.d (southern Celtic Seas, Bay of Biscay)

6.3.4 Cod (Gadus morhua) in Subarea IV and Divisions VIId and IIIa West (North Sea, Eastern English Channel, Skagerrak)

Roundnose grenadier (Coryphaenoides rupestris) in Division 3.a (Skagerrak and Kattegat)

Blue whiting (Micromesistius poutassou) in subareas 1 9, 12, and 14 (Northeast Atlantic and adjacent waters)

Advice June 2014

ICES Advice on fishing opportunities, catch, and effort Celtic Seas and Greater North Sea Ecoregions Published 24 October 2017

Advice October 2014

(update) Advice November 2014

Black-bellied anglerfish (Lophius budegassa) in divisions 7.b k, 8.a b, and 8.d (west and southwest of Ireland, Bay of Biscay)

ICES advises that when the MSY approach is applied, catches in 2019 should be no more than tonnes.

8.3.6 Flounder (Platichtys flesus) in Subdivisions 24 and 25 (West of Bornholm, Southern Central Baltic West)

ICES Advice on fishing opportunities, catch, and effort Celtic Seas and Greater North Sea ecoregions Published 30 June 2016

Ling (Molva molva) in subareas 6 9, 12, and 14, and in divisions 3.a and 4.a (Northeast Atlantic and Arctic Ocean)

Beaked redfish (Sebastes mentella) in subareas 1 and 2 (Northeast Arctic)

Advice October 2013

Sprat (Sprattus sprattus) in Subarea 4 (North Sea)

Sandeel (Ammodytes spp.) in Divisions 3a, 4a, and 4b, SA 3 (Skagerrak and Kattegat, North and Central North Sea)

White anglerfish (Lophius piscatorius) in divisions 8.c and 9.a (Cantabrian Sea and Atlantic Iberian waters)

Blue whiting (Micromesistius poutassou) in subareas 1 9, 12, and 14 (Northeast Atlantic and adjacent waters)

Sprat (Sprattus sprattus) in Subarea 4 (North Sea)

Cod (Gadus morhua) in subareas 1 and 2 (Northeast Arctic)

Sprat (Sprattus sprattus) in subdivisions (Baltic Sea)

ICES advice on fishing opportunities. ICES advises that when the MSY approach is applied, total removals in 2018 should be no more than 880 tonnes.

ICES advice on fishing opportunities

3.3.2 Cod (Gadus morhua) in subareas 1 and 2 (Northeast Arctic)

Sprat (Sprattus sprattus) in Division 3.a (Skagerrak and Kattegat)

Herring (Clupea harengus) in Subarea 4 and divisions 3.a and 7.d, autumn spawners (North Sea, Skagerrak and Kattegat, eastern English Channel)

Sandeel (Ammodytes spp.) in Division 4a, SA 5 (Northern North Sea, Viking and Bergen banks)

Boarfish (Capros aper) in subareas 6 8 (Celtic Seas, English Channel, and Bay of Biscay)

Sandeel (Ammodytes spp.) in Divisions 4a and 4b, SA 4 (North and Central North Sea)

Lesser-spotted dogfish (Scyliorhinus canicula) in Subarea 6 and divisions 7.a c and 7.e j (Celtic Seas)

ICES Advice on fishing opportunities, catch, and effort Greater North Sea Ecoregion Published 30 September 2015

Horse mackerel (Trachurus trachurus) in Division 9.a (Atlantic Iberian waters)

Mackerel (Scomber scombrus) in subareas 1 8 and 14, and in Division 9.a (the Northeast Atlantic and adjacent waters)

ICES Advice on fishing opportunities, catch, and effort Greater North Sea Ecoregion Published 23 February 2015

Herring (Clupea harengus) in subdivisions and 32 (central Baltic Sea, excluding Gulf of Riga)

Herring (Clupea harengus) in subdivisions 20 24, spring spawners (Skagerrak, Kattegat, and western Baltic)

Advice June 2013 Version 2,

Undulate ray (Raja undulata) in divisions 7.d e (English Channel)

Sandeel (Ammodytes spp.) in Divisions IIIa, IVa, and IVb, SA 3 (Skagerrak and Kattegat, North and Central North Sea)

Herring (Clupea harengus) in subdivisions 20 24, spring spawners (Skagerrak, Kattegat, and western Baltic)

7.3.5 Blue jack mackerel (Trachurus picturatus) in Subdivision 10.a.2 (Azores)

Anchovy (Engraulis encrasicolus) in Subarea 8 (Bay of Biscay)

Beaked redfish (Sebastes mentella) in subareas 1 and 2 (Northeast Arctic)

ICES Advice on fishing opportunities, catch, and effort Celtic Seas Ecoregion Published 30 June 2016

Advice June, revised September Herring in Division IIIa and Subdivisions (Western Baltic spring spawners)

6.3.8 Advice May 2014 Version 2, ECOREGION North Sea STOCK Herring in Division IIIa and Subdivisions (western Baltic spring spawners)

Mixed-fisheries advice for divisions 7.b c and 7.e k (Celtic Sea) Summary Figure 1

Undulate ray (Raja undulata) in divisions 8.a b (northern and central Bay of Biscay)

Advice June 2012

6.4 Stock summaries Advice June 2012

9.4.5 Advice September Widely distributed and migratory stocks Herring in the Northeast Atlantic (Norwegian spring-spawning herring)

Overview 10/8/2015. October Pelagic Advice Pelagic AC 7 October 2015

Advice May Herring in Subdivisions and 32 (excluding Gulf of Riga herring)

Why has the cod stock recovered in the North Sea?

Predicted catch for 2016, per stock and scenario overshoot (hatched) and undershoot (below zero)

3.4.3 Advice June Barents Sea and Norwegian Sea Cod in Subareas I and II (Norwegian coastal waters cod)

Northeast Atlantic Mackerel, Handlines

Advice October 2012

Advice June 2012

Report of the Working Group on Mixed Fisheries Advice for the North Sea (WGMIXFISH)

Seabass (Dicentrarchus labrax) in divisions 8.c and 9.a (southern Bay of Biscay and Atlantic Iberian waters)

7/14/2014. ICES advice for herring stocks in Template (as in previous years) State of stock table (as previous years) Advice online

Report of the Working Group on Widely Distributed

Advice October 2014 Version 2, December-2014

Advice June Capelin in Subareas V and XIV and Division IIa west of 5 W (Iceland East Greenland Jan Mayen area).

2.3.1 Advice May Capelin in Subareas V and XIV and Division IIa west of 5 W (Iceland East Greenland Jan Mayen area).

1. Regarding your decisions on the 2017 fishing opportunities we call on you to:

ICES WGMIXFISH-ADVICE REPORT Report of the Working Group on Mixed Fisheries Advice (WGMIXFISH-ADVICE)

14 NEPHROPS IN DIVISION VIIa

Baltic Stock Advice. 14 May John Simmonds ICES ACOM Vice Chair

ICES Advisory Approach

3.4 Stock Summaries Advice June 2011

Transcription:

ICES Advice on fishing opportunities, catch, and effort Greater North Sea Ecoregion Published 14 November 2017 DOI: 10.17895/ices.pub.3524 Norway lobster (Nephrops norvegicus) in Division 4.b, Functional Unit 6 (central North Sea, Farn Deeps) ICES stock advice Please note: The present advice replaces the advice given in June 2017 for catches in 2018. ICES advises that when the MSY approach is applied, and assuming that discard rates and fishery selection patterns do not change from the average of 2014 2016, catches in 2018 should be no more than 1876 tonnes. In order to ensure the stock in Functional Unit (FU) 6 is exploited sustainably, management should be implemented at the functional unit level. Any substantial transfer of the current surplus fishing opportunities from other FUs to FU 6 could rapidly lead to over-exploitation. Stock development over time The stock abundance index has increased since 2015, and currently it is just above MSY Btrigger. Harvest rates have been above the MSY level since 2008. Figure 1 Norway lobster in Division 4.b, Functional Unit 6. Summary of the stock assessment. Long-term trends in catches, harvest rate, and underwater TV survey (UWTV) abundance for animals greater than 17 mm (used as F and SSB proxies). Discard data have only been included since 2000. Orange lines show proxies for MSY B trigger and F MSY. UWTV abundance is calculated with a geostatistical method (2007 2017). Shaded areas for abundance are ±1.96 standard deviations (95% confidence intervals). Confidence intervals for harvest rates are derived from the confidence intervals for abundance. ICES Advice 2017 1

Stock and exploitation status Table 1 Norway lobster in Division 4.b, Functional Unit 6. State of the stock and fishery relative to reference points. Catch options The latest estimate of stock abundance (902 million, value from the survey conducted in June 2017) is above the MSY Btrigger value (858 million). The ICES MSY approach states that under such conditions the FMSY harvest rate (8.12% for FU 6 Norway lobster) should apply for 2018. Table 2 Norway lobster in Division 4.b, Functional Unit 6. The basis for the catch options. Variable Value Source Notes Stock abundance 902 million individuals ICES (2017a) UWTV 2017 Mean weight in landings 29.09 g ICES (2017a) Average 2014 2016 Mean weight in discards 10.88 g ICES (2017a) Average 2014 2016 Mean weight in unwanted catch MCS* 13.64 g ICES (2017a) Average 2014 2016 Mean weight in unwanted catch < MCS 6.91 g ICES (2017a) Average 2014 2016 Discard rate (total) 24.18% ICES (2017a) Average 2014 2016 (proportion by number) Discard rate ( MCS) 14.26% ICES (2017a) Average 2014 2016 (proportion by number) Discard rate (< MCS) 9.92% ICES (2017a) Average 2014 2016 (proportion by number) Discard survival rate 15% ICES (2017a) Only applies in scenarios where discarding is allowed. Dead discard rate (total) 21.33% ICES (2017a) Average 2014 2016 (proportion by number); only applies in scenarios where discarding is allowed. Dead discard rate Average 2014 2016 (proportion by number); only applies in 8.56% ICES (2017a) (< MCS) scenarios where discarding is allowed for de minimus exemptions. * MCS = Minimum conservation size. Table 3 Norway lobster in Division 4.b, Functional Unit 6. Annual catch options. All weights are in tonnes. Catch options for 2018 assuming zero discards Basis Total catch Wanted catch* Unwanted catch* Harvest rate** ICES advice basis MSY approach 1808 1615 193 8.12% Other options F 2014 2016 2819 2518 300 12.66% * Wanted and unwanted catch are used to described Norway lobster that would be landed and discarded in the absence of the EU landing obligation, based on average discard rate estimates for 2014 2016. ** Calculated for dead removals and applied to total catch. ICES Advice 2017 2

Discarding assumed to continue at recent average Basis Total catch Dead removals Landings Dead discards Surviving discards Harvest rate* L+DD+SD L+DD L DD SD for L+DD ICES advice basis MSY approach 1876 1846 1676 170 30 8.12% Other options F 2014 2016 2925 2878 2613 265 47 12.66% * Calculated for dead removals and applied to total catch. Discarding assumed below MCS only* Dead Unwanted Dead discards Harvest rate Total catch Landings Surviving discards Basis removals > MCS ** < MCS *** L+U+DD+SD L+U+DD L U DD SD for L+U+DD ICES advice basis MSY approach 1835 1828 1640 145 43 8 8.12% Other options F 2014 2016 2861 2849 2556 225 68 12 12.66% * Assumed for all fleets. ** Unwanted landings (U) are animals > MCS that have historically been discarded. *** Calculated for dead removals. All harvest rates are calculated in numbers and refer to the dead removals. The difference in catch weights between catch options with the same harvest rates is related to the fact that, in the scenario allowing for discarding, a proportion of the discards are assumed to survive (15%). Basis of the advice Table 4 Norway lobster in Division 4.b, Functional Unit 6. The basis of the advice. Advice basis ICES MSY approach Management plan ICES is not aware of any agreed precautionary management plan for Norway lobster in this area. Quality of the assessment Market sampling misses portions of the tailed category of landings which tend to be smaller individuals; the market sampling data may thus be biased towards larger sizes. For this reason the assessment only uses data from samples of the full unsorted catch when estimating the size composition of removals. Data from the latest UWTV survey (June 2017) have been used as the most up-to-date indicator of stock abundance. Issues relevant for the advice The results of the 2017 UWTV survey became available in September 2017 and showed a significant increase in abundance compared to the 2016 level. The advice for 2018 has therefore been updated to reflect the more recent data. From 2016 the EU landing obligation was applied to traps and trawl gears (80 99 mm mesh) fishing for Norway lobster in ICES Subarea 4. A de minimis exemption was made for individuals below the 25 mm minimum conservation size (MCS), up to a maximum of 6% of total landings. Other gears and mesh sizes are not under the landing obligation. In November 2016, ICES advised on fishing opportunities assuming that discarding would only occur below the MCS. Observations from the 2016 fishery indicate that discarding above the MCS continues and has not changed markedly (Table 11 and Figure 3). Consequently, ICES is providing advice for 2018 assuming average discard rates observed over the last three years, which is considered to be a more realistic assumption. It is expected that, under the EU landing obligation, below minimum size individuals that would formerly have been discarded would now be reported as below minimum size (BMS) landings in logbooks. However, BMS landings reported to ICES may be lower than expected for several reasons: minimum size individuals could either not have been landed and ICES Advice 2017 3

not recorded in logbooks, or have been landed but not recorded as BMS. Furthermore, BMS landings recorded in logbooks may not have been reported to ICES. In 2016, no Norway lobster were recorded as below MCS (BMS category) in FU 6 despite catches having been observed below the MCS (Figure 3). Results from a North Sea mixed-fisheries analysis are presented in ICES (2017b); this analysis has not been updated. The analysis for or 2018, assuming a strictly implemented discard ban (corresponding to the Minimum scenario), indicated that whiting would be the most limiting stock, being estimated to constrain 24 out of 42 fleet segments. Haddock is the second most limiting stock, constraining eight fleet segments. Additionally, if Norway lobster was managed by separate TACs for the individual functional units (FUs), Norway lobster in FU 6 would be considered the most limiting stock for ten fleet segments. Conversely, in the Maximum scenario, saithe and eastern English Channel plaice would be the least limiting for 20 and 11 fleet segments, respectively. Finally, if Norway lobster was managed by separate TACs, Norway lobster in FUs 7, 5, 33, and outside the FUs in Subarea 4 would be the least limiting for nine, two, one, and two fleet segments, respectively. For those demersal fish stocks for which the FMSY range is available, a Range scenario is presented that minimizes the potential for TAC mismatches in 2018 within the FMSY range. This scenario returns a fishing mortality by stock which, if used for setting single-stock fishing opportunities for 2018, may reduce the gap between the most and the least restrictive TACs, thus reducing the potential for quota over- and undershoot. This Range scenario suggests that the potential for mixed-fisheries mismatch would be lowered with a 2018 TAC in the lower part of the FMSY range for eastern English Channel plaice and saithe, and in the upper part of the range for cod and North Sea plaice. Norway lobster was not included in the Range scenario. There is a single total allowable catch (TAC) for all of ICES Subarea 4, except for the Norway Deep. Management should be implemented at the functional unit level to ensure that fishing opportunities are in line with the scale of the resource for each of the stocks and the corresponding MSY approach. Figure 2 Norway lobster functional units in the North Sea and Skagerrak/Kattegat region. ICES Advice 2017 4

Reference points Table 5 Norway lobster in Division 4.b, Functional Unit 6. Reference points, values, and their technical basis. Framework Reference point Value Technical basis Source MSY B trigger 858 million UWTV survey index at start of current decline (2007) ICES (2010) MSY Harvest rate approach F MSY Proxy, equivalent to F 8.12% * 35%SPR males ICES (2010) B lim Not defined Precautionary B pa Not defined approach F lim Not defined F pa Not defined Management SSB mgt Not defined plan F mgt Not defined * Previously reported as the rounded value, 8.1%. Basis of the assessment Table 6 Norway lobster in Division 4.b, Functional Unit 6. Basis of the assessment and advice. ICES stock data category 1 (ICES, 2016) Assessment type Underwater TV survey linked to yield-per-recruit analysis from length data (ICES, 2017a). One survey index (UWTV); Length frequency data from the fishery. Commercial catches (international landings and length frequencies from English catch sampling, covering 90% of the landings); maturity Input data data from commercial catch sampling. Natural mortalities from Morizur (1982): 0.3 for males and immature females, and 0.2 for mature females for all years. Included in the assessment, data series from the majority of the fleet/main fleets (covering 90% of the Discards, BMS landings, landings in 2016). BMS landings, where reported, are included as dead removals in the assessment from and bycatch 2016. Indicators Sex ratio, length frequencies The latest benchmark was performed in 2013 (ICES, 2013). The latest UWTV survey (June 2016) Other information information was used to provide advice. Working group Working Group on the Assessment of Demersal Stocks in the North Sea and Skagerrak (WGNSSK) Information from stakeholders There is no additional available information. History of the advice, catch, and management Table 7 Norway lobster in Division 4.b, Functional Unit 6. ICES advice and official landings. All weights are in tonnes. Year ICES advice Landings advice Catch advice ICES landings ICES total BMS reported discards* to ICES 2004 2153 615 2005 3094 715 2006 No increase in effort 4903 1051 2007 No increase in effort, harvest rate < 15% 3500 2966 432 2008 No new advice, same as for 2007 3500 1220 166 2009 No increase in effort and landings (2007) < 3000 2713 461 2010 Harvest rate no greater than that equivalent to fishing at < 1200 1443 201 F 2008 2011 MSY transition < 1900 2070 246 2012 MSY transition < 1400 2460 345 2013 MSY transition < 1400 2982 450 ICES Advice 2017 5

Year ICES advice Landings advice Catch advice ICES landings ICES total BMS reported discards* to ICES 2014 MSY transition < 1026 2503 198 2015 (update November) MSY approach < 1127 1371 190 2016 MSY approach < 680 738** 1854 272 0 2017 MSY approach 1143*** 2018 MSY approach 1876^ * Dead + surviving discards. ** Assuming all catches are landed and selection patterns do not change. *** Assuming discarding below MCS only. ^ Assuming discard rates average of the last three years. History of the catch and landings Table 8 Norway lobster in Division 4.b, Functional Unit 6. Catch distribution by fleet in 2016 as estimated by ICES. Catch (2016) Landings Unwanted catch 98% dead 2% surviving Almost entirely taken in demersal trawl fisheries 85% dead 15% surviving 2126 t 1854 t 272 t Table 9 Norway lobster in Division 4.b, Functional Unit 6. History of commercial catch and landings; ICES estimated values are presented by country. All weights are in tonnes. Year UK England & N. Ireland UK Scotland Other countries** Total landings Discards BMS reported to ICES 1981 1006 67 0 1073 1982 2443 81 0 2524 1983 2073 5 0 2078 1984 1471 8 0 1479 1985 2009 18 0 2027 1986 1987 28 0 2015 1987 2158 33 0 2191 1988 2390 105 0 2495 1989 2930 168 0 3098 1990 2306 192 0 2498 1991 1884 179 0 2063 1992 1403 60 10 1473 1993 2941 89 0 3030 1994 3530 153 0 3683 1995 2478 90 1 2569 1996 2386 96 1 2483 1997 2109 80 0 2189 1998 2029 147 1 2177 1999 2197 194 0 2391 2000 1947 231 0 2178 1805 2001 2319 255 0 2574 2393 2002 1739 215 0 1954 795 2003 2031 214 0 2245 716 2004 1952 201 0 2153 615 2005 2936 158 0 3094 715 2006 4430 434 39 4903 1051 2007 2525 437 4 2966 432 2008 976 244 0 1220 166 2009 2299 414 0 2713 461 2010 1258 185 0 1443 201 2011 1806 250 14 2070 246 ICES Advice 2017 6

Year UK England & N. Ireland UK Scotland Other countries** Total landings Discards BMS reported to ICES 2012 2177 256 27 2460 345 2013 2666 305 11 2982 450 2014 2104 345 54 2503 198 2015 1186 174 11 1371 190 2016* 1726 125 3 1854 272 0 * Provisional. ** Other countries includes the Netherlands, Belgium, and Denmark. Summary of the assessment Table 10 Year UWTV abundance index* (millions) Norway lobster in Division 4.b, Functional Unit 6. Assessment summary. Weights are in tonnes. 2 standard deviations Landings Discard rate (by numbers) Mean weight landings (g) Mean weight Discards (g) Number removed (millions) Harvest rate 2001 1685 67 2574 66.60% 20.67 9.62 373 22.1% 2002 1048 112 1953 46.10% 20.00 9.50 181 17.3% 2003 1085 90 2245 42.10% 21.89 9.56 177 16.3% 2004 1377 101 2152 41.70% 23.14 9.22 160 11.6% 2005 1657 148 3094 34.50% 23.58 10.32 200 12.1% 2006 1244 114 4858 31.30% 22.53 10.58 314 25.2% 2007 858 23 2966 25.00% 24.95 10.89 159 18.5% 2008 987 39 1213 24.90% 26.63 10.97 61 6.1% 2009 682 38 2711 29.30% 24.45 10.54 157 23.0% 2010 785 21 1443 23.00% 25.18 11.74 74 9.5% 2011 878 17 2072 22.60% 27.05 11.02 99 11.3% 2012 758 13 2457 27.42% 27.30 10.16 124 16.4% 2013 706 18 2982 29.80% 27.60 9.80 154 21.8% 2014 755 18 2503 14.90% 29.90 13.50 98 13.0% 2015 565 13 1371 28.97% 29.39 9.99 66 11.6% 2016 697 19 1854 28.65% 27.97 10.23 93 13.3% 2017 902 21 * For animals greater than 17 mm. Table 11 Norway lobster in Division 4.b, Functional Unit 6. Discard rate as a proportion of total catch (in numbers), and also given below and above MCS. Year Proportion of total catch (%) < MCS MCS total 2000 32.94 30.21 63.15 2001 38.29 28.27 66.55 2002 26.89 19.22 46.11 2003 24.24 17.95 42.19 2004 24.83 16.94 41.76 2005 17.13 17.42 34.56 2006 14.49 16.84 31.33 2007 11.32 13.70 25.03 2008 11.41 13.47 24.87 2009 13.76 14.53 28.29 2010 7.89 15.08 22.97 2011 8.37 14.23 22.60 2012 11.55 15.88 27.43 2013 14.68 15.20 29.88 2014 2.90 12.02 14.92 2015 13.78 15.19 28.97 2016 13.09 15.56 28.65 average 2014 2016 9.92 14.26 24.18 ICES Advice 2017 7

Figure 3 Norway lobster in Farn Deeps (FU 6). Catch length frequency distribution and mean size in catches and landings. Vertical lines are minimum landing size (25 mm) and 35 mm. Sources and references ICES. 2010. Report of the Working Group on the Assessment of Demersal Stocks in the North Sea and Skagerrak (WGNSSK), 5 11 May 2010, ICES Headquarters, Copenhagen, Denmark. ICES CM 2010/ACOM:13. 1058 pp. ICES. 2013. Benchmark Workshop on Nephrops Stocks (WKNEPH), 25 February 1 March 2013, Lysekil, Sweden. ICES CM 2013/ACOM:45. 230 pp. ICES. 2016. Advice basis. In Report of the ICES Advisory Committee, 2016. ICES Advice 2016, Book 1, Section 1.2. ICES. 2017a. Report of the Working Group on the Assessment of Demersal Stocks in the North Sea and Skagerrak (WGNSSK), 26 April 5 May 2017, ICES Headquarters, Copenhagen, Denmark. ICES CM 2017/ACOM:21. 1077 pp. ICES. 2017b. Report of the Working Group on Mixed-Fisheries Advice for the North Sea (WGMIXFISH-ADVICE), 22 26 May 2017, ICES Headquarters, Copenhagen, Denmark. ICES CM 2017/ACOM:18. In preparation. ICES. 2017c. Norway lobster (Nephrops norvegicus) in Division 4.b, Functional Unit 6 (central North Sea, Farn Deeps). June advice. In Report of the ICES Advisory Committee, 2017. ICES Advice 2017,. DOI: 10.17895/ices.pub.3166. Morizur, Y. 1982. Estimation de la mortalité pour quelque stocks de langoustine, Nephrops norvegicus. ICES CM 1982/K:10. 19 pp. ICES Advice 2017 8