THE DUBLIN BAY PRAWN AND ITS FISHERY
Transcription
THE DUBLIN BAY PRAWN AND ITS FISHERY
THE DUBLIN BAY PRAWN AND ITS FISHERY (Norway Lobster) Dr Richard Briggs (AFBI – Retired) Overview 1. Biology 2. The Fishery 3. Stock Assessment and Management Advice 4. Technical Conservation 5. Conclusions 1. Biology • Nephrops norvegicus • Dublin Bay prawn • Norway Lobster • Scampi • Langoustine • Cigala Probably not Nephrops Nephrops is NOT a fish!! Phylum: Arthropoda Class: Crustacea Order: Decapoda Super Family: Nephropsidea 1. A lobster with typical hard exoskeleton which is periodically shed (ecdysis). There are no persistent hard structures with growth rings 2. Kidney shaped eye (from the Greek nephros = kidney and op = eye) 3. Live within burrows in seabed sediment . 4. RangeFrom Iceland to Mediterranean Dublin Bay prawn (Nephrops norvegicus) Cod (Gadus morhua) Life Cycle 2. The Fishery Captured by otter trawls (single or multiple) or by creels (pots) About 60,000 tonnes caught of which 10,000 tonnes from Irish Sea Irish Sea Nephrops grounds 55.0N North Channel Cumbria 54.5N 35 2 30 54.0N 17 15 207 8 7 109 20 10 101 102 107 200 53.5N 106104 306 302 303 301 307 309 308 304 305 1 209 208 108 250 IRISH SEA 103 105 Nephrops Grounds 53.0N 6.5W 6.0W 5.5W 5.0W 4.5W 4.0W 3.5W 3.0W Nephrops landings from the western Irish Sea 12,000 10,508 10,000 8,491 Tonnes Landed 8,370 8,000 7,441 6,793 10,162 9,198 8,963 7,561 7,065 7,270 6,554 6,000 4,000 2,000 0 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 Year Value of Northern Ireland Marine Fisheries Value of top 15 trawled species 14 Value of all trawled species = £21.5 millions 12 Nephrops = 53.5% of total 1st sale value 10 6 4 2 Turbot Cockles Velvet crab Monks or Anglers Horse Mackerel Haddock Queen Scallops Hake Lobsters Brown Crab Cod Scallops Herring Mackerel 0 Nephrops Value (£m) 8 3. Stock Assessment Functional Units as defined by ICES 1 2 11 10 7 9 12 32 4 8 13 18 15 14 17 16 19 20-22 3 33 6 5 23 24 31 25 26 27 36 37 35 28 29 30 34 41 38 39 40 Irish Sea Nephrops TAC: Sub-Area VII Western Irish Sea = FU15 Sub Area VII MA FU J 14 15 L 16 17 18 19 M 20 21 22 55.00 18 54.00 53.00 16 15 14 17 52.00 51.00 19 20-22 50.00 49.00 48.00 -18.00 -16.00 -14.00 -12.00 -10.00 -8.00 -6.00 -4.00 -2.00 0.00 2.00 Assessment Methods Catch (millions) (1) Commercial Data Nephrops Size Compostion 35 30 25 20 15 10 5 Weakness in that ages were unreliable. Growth Parameters (K, Linf ) L2AGE SLICING MODEL length/weight relationship Nominal Age composition 200 150 100 50 0 1 2 3 4 5 Age in years 6 7 7+ 48 46 44 42 40 38 36 34 32 30 28 26 24 22 20 18 16 14 12 Carapace alength mm Number (millions) Computer-based models using growth parameters were used to slice size frequency data into age classes. Which were input to similar procedures to those used to assess whitefish stocks. Such as Virtual Population Analysis (VPA). 10 0 (2) Larval Production Using fecundity data to back calculate the number of females required to produce the amount of larvae observed during surveys. Labour intensive and costly. Completed one-off as an EU funded project. Number of Larvae in plankton = Spawning Biomass (SSB) Fecundity (number of eggs per gram of female) Female Nephrops Spawning Stock Biomass estimates from different methods (vertical bar = 95% confidence range) 10000 9000 SSB (tonnes) 8000 7000 6000 5000 4000 3000 2000 1000 0 ALP LCA VPA Assessment Method Portaferry work Briggs, R. P., Armstrong, M.J., Dickey-Collas, M., Allen, McQuaid, N. and Whitmore, J. (2002). Estimation of Nephrops Biomass in the Western Irish Sea from Annual Larval Production. ICES Journal of Marine Research, 59: 109-119. Maturity and Fecundity (Nuala McQuaid, PhD) Relationship between realised fecundity and carapace length for eastern and western Irish Sea stocks.. Maturity ogive of females from western Irish Sea The dotted curve represents maturity estimated from presence of spermatophores and the solid line represents females with ovaries of stage 3 or above McQuaid, N., Briggs, R.P., Roberts, D., (2009) Estimation of fecundity in Nephrops norvegicus (L.) from the Irish Sea. Journal of the Marine Biological Association of the UK 89(6), 1181-1188. McQuaid, N. and Briggs, R.P. and Roberts, D., (2006). The Size at Onset of Maturity in Nephrops norvegicus from the Irish Sea. Fisheries Research 81: 26-36 (3) Camera Surveys Adopted by ICES since 2005 Underwater video used to count Nephrops burrow clusters Adults inhabit burrows in offshore sediment from which they only emerge to feed and to mate. Research in Scotland suggests that one adult Nephrops occupies a single burrow cluster and unoccupied burrows are quickly filled by sediment. By counting burrow clusters over a known area it is possible to provide a fishery independent index of Nephrops abundance and to map the Nephrops grounds. The Ships AFBI & Marine Institute Now 10 years data RV Corystes RV Celtic Voyager Camera sledge deployment The AFBI camera sledge being deployed at sea Stations • 3.5km apart • Camera towed for 10 mins at each station Results Western Irish Sea (FU15) burrow abundance estimate (Error bars = cv) 8 7 6 Billions 5 4 3 6.3 6.3 6.5 6.2 5.9 4.9 5.3 5.7 5.6 2010 2011 2 1 0 2003 2004 2005 2006 2007 Survey 2008 2009 Contour plots of burrow densities using geostatistics (2009 – 2011) (krigged density plots) REF: Annika Clements (2009) Broad-scale ecological investigation of Nephrops norvegicus (L.) burrow distribution in the western Irish Sea. PhD Thesis Queens University of Belfast Burrow densities from different areas Moray Firth Firth of Forth Fladen Ground Farn Deeps Celtic Sea Aran Grounds Irish Sea West Clyde South Minch North Minch 0 0.2 0.4 0.6 0.8 Burrow Density (number m-2) 1 1.2 Summary of data analysis Landings Size distribution Bias Adjusted Burrow Count Catch Option in numbers Mean Nephrops weight in catch Harvest Rates from Model Catch Data Growth and Maturity Parameters Predicted Landings = TAC Justification for choice of Harvest Rate ie proportion of stock safe to catch Fmax Frecent 4 F0.1 yield 3 2 1 0 0.0 0.5 1.0 1.5 2.0 2.5 3.0 Fmult Maximum Sustainable Yield (MSY): now forming ICES advice basis. Not possible to estimate directly for Nephrops as no age or SSB trend data. MSY proxy therefore established Evidence for Harvest Rate at Fmax as Proxy for MSY Commercial Fishery Data indicates that the fishery has been sustained at about Fmax for many years Landings - International Effort - Different fleets UK Northern Ireland Nephrops trawlers 250 15000 International Landings Rep. of Ireland Rep. of Ireland - All gears 9000 6000 3000 0 1950 1955 1960 1965 80 1970 1975 1980 1985 1990 1995 2000 2005 200 150 100 50 0 1980 2010 1985 LPUE - Different fleets Mean size (mm carapace length) 50 40 30 Rep. of Ireland - LPUE UK Northern Ireland - LPUE 10 0 1960 1995 2000 2005 2010 ROI - Catch - Males ROI - Catch - Females UK NI - Catch - Mal UK NI - Catch - Fem 34 60 20 1990 Mean sizes - Different fleets 70 CPUE or LPUE (kg/hour trawling) Landings (tonnes) 12000 Effort ('000 hours trawling) UK - All gears 32 30 28 26 24 22 20 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010 Trawl Survey Data E5 E4 E3 54.8N 38 54.6N 54.4N 1 37 35 2 54.2N 30 54.0N 207 8 53.8N 107 53.6N 106104 200 17 15 209 208 109 20 10 101 210 7 108 102 36 103 105 35 53.4N 6.4W 6.2W 6.0W 5.8W 5.6W 5.4W Figure 1: Western Irish Sea Nephrops stations 5.2W 5.0W 4.8W 4.6W Trawl Surveys: catch rates Average catch (kg) per nm 140 (Vertical bars = SE) 120 80 60 40 20 2011 2010 2009 2008 2007 2006 2005 2004 2003 2002 2001 2000 1999 1998 0 1997 Kg per nm 100 Mean carapace length from August surveys 35 30 25 20 15 2007 2008 2009 2010 2011 2007 2008 2009 2010 2011 2006 2004 2003 2002 2001 2000 1999 1998 100 90 80 70 60 50 40 30 20 10 0 Mean percentage females in August 2006 2004 2003 2002 2001 2000 1999 1998 (error bars = SD) 1997 Percentage females (%) 1997 10 2005 August males August females 2005 carapace length (mm) (error bars = SD) 4. Technical Conservation Mixed fishery The western Irish Sea is a whitefish spawning and nursery area enhanced by a gyre. Catches include cod, haddock, whiting and small non-commercial species Discards of undersized and non-commercial species is therefore a problem. Michelle Allen (2009). An Investigation of sampling techniques within marine fisheries discards. PhD Thesis Queens University of Belfast Allen, M., Kilpatrick, D., Armstrong, M., Briggs, R., Course, G. and Pérez, N. (2002). Multistage cluster sampling design and optimal sample sizes for estimation of fish discards from commercial trawlers. Fisheries Research 55, 11-24 Square mesh escape panels To develop more selective fishing gears. Many of the novel net designs include the incorporation of square shaped meshes in trawl nets which do not distort during towing Strip of diamond mesh in centre (12 meshes wide) 8.85m 82mm 1.5m 4mm P/E 4.5m 84x5.6mm compact netting 120 round Briggs, R.P. (2010) A novel escape panel for trawl nets used in the Irish Sea Nephrops Fishery. Fisheries Research. 105: 118-124 Recent SEAFISH study– Spring 2012 Box Extension – 300mm SMP Large square mesh top panel Diamond mesh side and bottom panels Standard two panel extension and codend 4 panel (boxed) extension section Main body of the trawl Bulk (kg) 250 Boxed extension section 150 100 50 0 1 2 3 4 5 6 Tow 7 8 9 10 11 12 EXPERIMENTAL CONTROL 14 Number of cod Bulk - Kg 200 : Cod catch 16 EXPERIMENTAL CONTROL 12 10 8 6 4 2 0 1 2 3 4 5 6 7 Tow 8 9 10 11 12 5. Conclusions Irish Sea Nephrops are withstanding exploitation levels • Historical data from 1960s when the fishery was in its infancy shows little change in size composition of catches • Larval production studies in 1995 showed that 440 billion larvae were produced suggesting high recruitment potential • The Irish Sea Gyre (whirlpool effect) retains both larvae and sediment enhancing recruitment success Why is this? 1. Management legislation - MLS, TAC, Minimum mesh size 2. Live within burrows in seabed sediment . 3. Crepuscular ie active at dawn and dusk and seldom emerge during strong tides 4. Females remain in burrows whilst incubating eggs (9 months) 5. Juveniles (0-group) remaining burrowed for at their 1st year 6. When cod stocks were high (1980s) they could have consumed as much Nephrops as the fishery (Armstrong, 1990). Cod are now at a low level, though there are recent signs of a recovery! QUESTIONS?