FIRMS Stock Status and Trend Summaries (extracted from reports), results for: "Atlantic redfishes nei" |
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Title | Factsheet | Exploitation Rate | Abundance Level | Exploitation State |
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Sea cucumber - Lagoon of Mauritius and Rodrigues, 2009 | FAO, 2009 | | | Depleted | Little tuna - Maldives, 2009 | FAO, 2009 | | | Underexploited | Prawns - Ungwana bay, 2009 | FAO, 2009 | | | Fully exploited | Scads - Mid-water of Saya de Malha and Nazareth banks, 2009 | FAO, 2009 | | | Underexploited | Rock and spiny lobsters - Kenya, 2009 | FAO, 2009 | | | Overexploited | Shrimps, lobsters and crabs - Comoros, 2009 | FAO, 2009 | | | Underexploited | Shrimps, lobsters and crabs - Comoros, 2009 | FAO, 2009 | | | Underexploited | Northern Bluefin tuna - Western Atlantic, 2014 | ICCAT, 2014 | F2010-2012/F0.1: Low potential recruitment = 0.60 (0.50-0.72) | SSB2013/SSBFMSY: Low potential recruitment =2.25 (1.92-2.68) / High potemtial recruitment =0.48 (0.35-0.72) | | Atlantic horse mackerel - Northwest Africa, 2014 | FAO, 2014 | Fcur/F0.1 = 104% ; Fcur/FMSY = 93% ; | Bcur/B0.1 = 105% ; Bcur/BMSY = 115% | Fully exploited | Penaeus shrimps - Nigeria, 1998 | FAO, 1998 | | | Overexploited | Demersal resources - Kenya, 2009 | FAO, 2009 | | | Fully exploited | Sea cucumber - Seychelles (Mahe and Admirantes stocks), 2009 | FAO, 2009 | | | Overexploited | Small pelagics - Kenya, 2009 | FAO, 2009 | | | Fully exploited | Rays - Tanzania, 2009 | FAO, 2009 | | | Moderately exploited | Sea cucumber - Tanzania, 2009 | FAO, 2009 | | | Overexploited | Sharks - Seychelles offshore, 2009 | FAO, 2009 | | | Overexploited | West African croakers - Guinea-Bissau and Guinea, 2009 | FAO, 2009 | Fcur/F0.1 = 105% ; Fcur/FMSY = 95% | Bcur/B0.1 = 65% ; Bcur/BMSY = 72% | Overexploited | West African croakers - Senegal and Gambia, 2012 | FAO, 2012 | | | Uncertain/Not assessed | Sea cucumber - Kenya, 2009 | FAO, 2009 | | | Overexploited | Pelagic sharks - Tanzania, 2009 | FAO, 2009 | | | Moderately exploited | Demersal sharks - Tanzania, 2009 | FAO, 2009 | | | Moderately exploited | Seabreams - Guinea-Bissau and Guinea, 2009 | FAO, 2009 | Fcur/F0.1 = 58% ; Fcur/FMSY = 52% | Bcur/B0.1 = 93% ; Bcur/BMSY = 103% | Not fully exploited | Beaked redfish - Iceland and Faroe grounds, North of Azores, East Greenland and Northwest Atlantic (deep slope), 2015 | ICES, 2015 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Reduced reproductive capacity | | Cod - Barents and Norwegian Seas (coastal waters), 2018 | ICES, 2018 | F<sub>MSY</sub>: Undefined | MSY B<sub>trigger</sub>: Undefined | | Herring - Bothnian Sea, 2015 | ICES, 2015 | F<sub>MSY</sub>: Appropriate | B<sub>lim</sub>: Full reproductive capacity | | Spring Spawning Herring - Skagerrak and Kattegat, 2008 | ICES, 2008 | Undefined | Undefined | | Atlantic horse mackerel - Morocco (North of 26° N), 2004 | FAO, 2004 | | | | Shark, Smooth-hounds - Cape Verde, 1995 | FAO, 1995 | | | Moderately exploited | Cat fish - Tanzania, 2009 | FAO, 2009 | | | Moderately exploited | Dentex - São Tomé e Príncipe, 2010 | FAO, 2010 | | | Uncertain/Not assessed | Tonguesole - Guinea-Bissau and Guinea, 2009 | FAO, 2009 | Fcur/F0.1 = 41% ; Fcur/FMSY = 37% ; | Bcur/B0.1 = 140% ; Bcur/BMSY = 154% | Not fully exploited | Herring - Bothnian Bay, 2015 | ICES, 2015 | F<sub>MSY</sub>: Undefined | MSY B<sub>Trigger</sub>: Undefined | | Icelandic Cod - Icelandic grounds, 2018 | ICES, 2018 | HR<sub> MSY</sub>: Below | B<sub>lim</sub>: Full reproductive capacity | | Cod - Faroe Bank, 2015 | ICES, 2015 | F<sub>MSY</sub>: Undefined | MSY B<sub>Trigger</sub>: Undefined | | Redfish - Southwestern Grand Bank, 2015 | NAFO, 2015 | None-Low Fishing Mortality | Unknown Stock Size | | Tuna and tuna-like species - Global, 2009 | FAO, 2009 | | | | Sharks and Rays - Kenya, 2009 | FAO, 2009 | | | Fully exploited | Penaeus shrimps - Nigeria and Cameroon, 2004 | FAO, 2004 | | | Fully exploited | Cuttlefish - Sierra Leone and Liberia, 2004 | FAO, 2004 | | | Overexploited | Coastal groundfishes - Antigua and Barbuda, 2003 | FAO, 2003 | | | Overexploited | Sea urchins - Grenada, 2003 | FAO, 2003 | | | Overexploited | Small pelagics - Tanzania, 2009 | FAO, 2009 | | | Moderately exploited | Barracudas - Seychelles, 2009 | FAO, 2009 | | | | Herring - Iceland, 2018 | ICES, 2018 | F<sub>MSY</sub>: Below | B<sub>lim</sub>: Increased risk | | Bivalves - Kenya, 2009 | FAO, 2009 | | | Fully exploited | Shrimps - South Africa Eastern, 2009 | FAO, 2009 | | | Overexploited | Cod - Barents Sea, Norwegian Sea, Spitzbergen and Bear Island, 2018 | ICES, 2018 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Full reproductive capacity | | Bluespotted seabass, West African goatfish, Sand steenbras, Axillary seabream, Atlantic bigeye - Cape Verde, 2004 | FAO, 2004 | | | | Spring Spawing herring - Norwegian Sea, 2008 | ICES, 2008 | Harvested sustainably | Full reproductive capacity | | Sharks - Seychelles inshore (Mahe Plateau, Amirantes, Outer Islands), 2009 | FAO, 2009 | | | Depleted | Northern Bluefin tuna - East Atlantic and Mediterranean Sea, 2014 | ICCAT, 2014 | F2013/F0.1 = 0.4 | SSB2013/SSBF0.1: Medium recruitment (1950-2006) =1.10 / Low recruitment (1970s)=1.60 / High recruitment (1990s)=0.67 | | Deep slope groundfishes - Antigua and Barbuda, 2003 | FAO, 2003 | | | | Octopus - Seychelles (Granitic Islands), 2009 | FAO, 2009 | | | | Atlantic horse mackerel - Morocco, Mauritania, Senegal, Gambia, Guinea Bissau and Guinea (between 26° and 10° N), 2004 | FAO, 2004 | | | | Atlantic Cod - Grand Bank, 2017 | NAFO, 2017 | None-Low Fishing Mortality | Depleted Stock Size | | Cod - North Sea, Eastern English Channel and Skagerrak, 2015 | ICES, 2015 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Full reproductive capacity | | Beaked redfish - Iceland and Faroe grounds, North of Azores, East Greenland and Northwest Atlantic (upper slope), 2015 | ICES, 2015 | F<sub>MSY</sub>: Undefined | MSY B<sub>Trigger</sub>: Undefined | | Octopus and Squid - Kenya, 2009 | FAO, 2009 | | | Fully exploited | Bivalves - Tanzania, 2009 | FAO, 2009 | | | Overexploited | Cod - Irish Sea, 2018 | ICES, 2018 | F<sub>MSY</sub>: Undefined | MSY B<sub>trigger</sub>: Undefined | | Sandeel - Skagerrak and Kattegat, 2008 | ICES, 2008 | Undefined | Undefined | | Cuttlefish - Ghana and Benin, 2004 | FAO, 2004 | | | | Atlantic cod - Northeast Newfoundland Shelf and Northern Grand Bank, 2000 | NAFO, 2000 | | | | West African croakers - Guinea, 2004 | FAO, 2004 | | | Fully exploited | Seabreams, Groupers - Equatorial Guinea, 1999 | FAO, 1999 | | | | Cuttlefish - Cap Blanc stock (21°N - 16°N), 2012 | FAO, 2012 | Fcur/F0.1 = 47% ; Fcur/FMSY = 42% | Bcur/B0.1 = 145% ; Bcur/BMSY = 160% | Not fully exploited | Cod - Faroe Plateau, 2018 | ICES, 2018 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Full reproductive capacity | | Other skates and rays - Rockall, Northwest Coast of Scotland and North Ireland, Irish Sea, West of Ireland, Porcupine Bank, Western English Channel, Bristol Channel, Celtic Sea and Southwest of Ireland, 2015 | ICES, 2015 | F<sub>MSY</sub>: Undefined | MSY B<sub>Trigger</sub>: Undefined | | Sandeel - Shetland Area, 2008 | ICES, 2008 | Undefined | Undefined | | Sandeel - North Sea, 2008 | ICES, 2008 | Undefined | Increased risk | | White marlin Atlantic, 2010 | ICCAT, 2010 | F2010/FMSY = 0.72-0.99 | B2010/BMSY = 0.5-0.32 | | Atlantic sailfish - East Atlantic, 2014 | ICCAT, 2014 | F2014/FMSY = 0.33-2.85 | B2014/MSY = 0.22-0.70 | | Rockcods and seabass - South Africa Eastern, 2009 | FAO, 2009 | | | Depleted | Angler fish - Bay of Biscay and Iberian Basin, 2008 | ICES, 2008 | Undefined | Undefined | | Redfish - North and Southeastern Grand Bank, 2013 | NAFO, 2013 | None-Low Fishing Mortality | Intermediate Stock Size | | Bigeye scad, Atlantic horse mackerel, Scad - Cape Verde, 1997 | FAO, 1997 | | | | Redfish - Flemish Cap, 2016 | NAFO, 2016 | None-Low Fishing Mortality | Intermediate Stock Size | | Emperors and Snappers - Northern Shelf of Mauritius, 2009 | FAO, 2009 | | | Overexploited | Reef fishes - Tanzania, 2009 | FAO, 2009 | | | Fully exploited | Cardinal Fish - South East Atlantic, 2009 | SEAFO, 2009 | Uncertain/Not assessed | Uncertain/Not assessed | Uncertain | Atlantic Cod - Flemish Cap, 2017 | NAFO, 2017 | None-Low Fishing Mortality | Intermediate Stock Size | | Mullet, Barracuda and Milkfish - Kenya, 2009 | FAO, 2009 | | | Fully exploited | Spiny and rock lobsters - Somalia, 2009 | FAO, 2009 | | | Overexploited | Other Octopuses - South Africa Eastern, 2009 | FAO, 2009 | | | | Beaked redfish - Southeast Greenland, 2018 | ICES, 2018 | F<sub>MSY</sub>: Undefined | MSY B<sub>trigger</sub>: Undefined | | Squid - South East Atlantic, 2009 | SEAFO, 2009 | Uncertain/Not assessed | Uncertain/Not assessed | Uncertain | Atlantic sailfish - West Atlantic, 2014 | ICCAT, 2014 | F2014/FMSY = 0.33 or 0.63 | B2014/MSY = 1.81 or 1.16 | | Penaeus shrimp - Equatorial Guinea, 2004 | FAO, 2004 | | | Overexploited | Penaeus shrimps - Cameroon, 2004 | FAO, 2004 | | | | Oceanic pelagic fishes - Antigua and Barbuda, 2003 | FAO, 2003 | | | | Octopus - South East Atlantic, 2009 | SEAFO, 2009 | Uncertain/Not assessed | Uncertain/Not assessed | Uncertain | Scads - Guinea-Bissau, Guinea, Sierra Leone and Liberia, 2012 | FAO, 2012 | Fcur/F0.1 = 176% ; Fcur/FMSY = 158% | Bcur/B0.1 = 73% | Overexploited | Skates - South East Atlantic, 2009 | SEAFO, 2009 | Uncertain/Not assessed | Uncertain/Not assessed | Uncertain | Cod - Western English Channel, Bristol Channel, Celtic Sea and Southwest of Ireland, 2018 | ICES, 2018 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Reduced reproductive capacity | | Mackerel - Bay of Biscay and Portuguese waters, 2008 | ICES, 2008 | Increased risk | Full reproductive capacity | | Cuttlefish - Senegal and Gambia, 2012 | FAO, 2012 | Fcur/F0.1 = 37% ; Fcur/FMSY = 33% | Bcur/B0.1 = 117% ; Bcur/BMSY = 128% | Not fully exploited | Flat fish - Tanzania, 2009 | FAO, 2009 | | | Fully exploited | Clyde herring - West of Scotland, 2008 | ICES, 2008 | Undefined | Undefined | | Atlantic chub mackerel - Northwest Africa, 2014 | FAO, 2014 | Fcur/F0.1 = 101% ; Fcur/FMSY = 91% | Bcur/B0.1 = 135% ; Bcur/BMSY = 148% | Fully exploited | West African croakers - Liberia, 2004 | FAO, 2004 | | | | Tounguesole - Guinea, 2004 | FAO, 2004 | | | Overexploited | Sardinellas - Equatorial Guinea, 1999 | FAO, 1999 | | | | Sharks - Global, 2009 | FAO, 2009 | | | | Cuttlefish - Dakhla stock (26°N - 21°N), 2012 | FAO, 2012 | Fcur/F0.1 = 59% ; Fcur/FMSY = 53% | Bcur/B0.1 = 124% ; Bcur/BMSY = 137% | Not fully exploited | Herring - Irish Sea North of 52°30’N, 2018 | ICES, 2018 | F<sub>MSY</sub>: Below | B<sub>lim</sub>: Full reproductive capacity | | Herring - Irish Sea South of 52°30’N, Celtic Sea and Southwest of Ireland, 2018 | ICES, 2018 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Reduced reproductive capacity | | Cod - West of Scotland, 2018 | ICES, 2018 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Reduced reproductive capacity | | Megrim - Northern North Sea and West of Scotland, 2018 | ICES, 2018 | F<sub>MSY</sub>: Below | B<sub>lim</sub>: Full reproductive capacity | | Megrim - Rockall, 2018 | ICES, 2018 | F<sub>MSY</sub>: Below proxy | B<sub>lim</sub>: Above possible reference points | |
Deep water Redfish - Rockall Bank and Reykjanes Ridge
, 2006 | ICES, 2006 | Undefined | Undefined | | Seabob - Coast of French Guiana to the Orinoco delta, 2017 | FAO, 2017 | F/Fmsy = 1 | B/Bmsy = 1.25 | Maximally sustainably fished | Cod - Kattegat, 2018 | ICES, 2018 | F<sub>MSY</sub>: Undefined | MSY B<sub>trigger</sub>: Undefined | | Herring - Gulf of Riga, 2019 | ICES, 2019 | F<sub>MSY</sub>: Below | B<sub>lim</sub>: Full reproductive capacity | | Horse mackerel - North Sea, Eastern English Channel, Skagerrak and Kattegat, 2018 | ICES, 2018 | F<sub>MSY</sub>: Above proxy | MSY B<sub>trigger</sub>: Undefined | | Herring - North Sea, Eastern English Channel, Skagerrak and Kattegat, 2019 | ICES, 2019 | F<sub>MSY</sub>: Below | B<sub>lim</sub>: Full reproductive capacity | | Beaked redfish - East Greenland and Icelandic Slope, 2018 | ICES, 2018 | F<sub>MSY</sub>: Undefined | MSY B<sub>trigger</sub>: Undefined | | Horse mackerel - Portuguese Waters East, 2019 | ICES, 2019 | F<sub>MSY</sub>: Below | B<sub>lim</sub>: Full reproductive capacity | | Cod - Baltic Sea (Eastern part), 2019 | ICES, 2019 | F<sub>MSY</sub>: Undefined | B<sub>lim</sub>: Reduced reproductive capacity | | Herring - Skagerrak, Kattegat, Sound and Belt Sea, Baltic West of Bornholm, 2019 | ICES, 2019 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Reduced reproductive capacity | | Cod - Baltic Sea (Western part), 2019 | ICES, 2019 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Increased risk | | Herring - Central Baltic Sea, 2019 | ICES, 2019 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Increased risk | | Mackerel - Northeast Atlantic, 2017 | ICES, 2017 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Full reproductive capacity | | Horse mackerel - Norwegian Sea, Northern North Sea, Faroes Grounds, West of Scotland, Irish Sea, West of Ireland, Porcupine Bank, Western English Channel, Bristol Channel, Celtic Sea, Southwest of Ireland, 2018 | ICES, 2018 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Increased risk | | Rays and skates (mainly thornback ray) - Azores Ground, North of Azores, 2018 | ICES, 2018 | F<sub>MSY</sub>: Unknown | B<sub>lim</sub>: Unknown | | Cod - West Greenland, offshore, 2018 | ICES, 2018 | F<sub>MSY</sub>: Undefined | MSY B<sub>trigger</sub>: Undefined | | Sandeel - Central and Southern North Sea (Sandeel Area 1r), 2019 | ICES, 2019 | F<sub>MSY</sub>: Undefined | B<sub>lim</sub>: Reduced reproductive capacity | | Sandeel - Skagerrak, Central and Southern North Sea (Sandeel Area 2r), 2019 | ICES, 2019 | F<sub>MSY</sub>: Undefined | B<sub>lim</sub>: Reduced reproductive capacity | | Sandeel - Skagerrak, Northern and Central North Sea (Sandeel Area 3r), 2019 | ICES, 2019 | F<sub>MSY</sub>: Undefined | B<sub>lim</sub>: Full reproductive capacity | | Sandeel - Northern and Central North Sea (Sandeel Area 4), 2019 | ICES, 2019 | F<sub>MSY</sub>: Undefined | B<sub>lim</sub>: Increased risk | | Sandeel - Skagerrak, Kattegat and Belt Sea (Sandeel Area 6), 2018 | ICES, 2018 | F<sub>MSY</sub>: Undefined | B<sub>lim</sub>: Unknown | | Sandeel - Northern North Sea and Shetland (Sandeel Area 7r), 2018 | ICES, 2018 | F<sub>MSY</sub>: Undefined | B<sub>lim</sub>: Unknown | | Sandeel - Viking and Bergen Bank area (Sandeel Area 5r), 2018 | ICES, 2018 | F<sub>MSY</sub>: Undefined | B<sub>lim</sub>: Unknown | | Starry smooth-hound - Northeast Atlantic, 2018 | ICES, 2018 | F<sub>MSY</sub>: Unknown | B<sub>lim</sub>: Unknown | | Herring - Gulf of Bothnia, 2019 | ICES, 2019 | F<sub>MSY</sub>: Unknown | B<sub>lim</sub>: Unknown | | Beaked redfish - Barents and Norwegian Seas, 2019 | ICES, 2019 | F<sub>MSY</sub>: Undefined | B<sub>lim</sub>: Full reproductive capacity | | Cod - Rockall, 2019 | ICES, 2019 | F<sub>MSY</sub>: Unknown | B<sub>lim</sub>: Unknown | | Sandeel - West of Scotland, 2017 | ICES, 2017 | F<sub>MSY</sub>: Unknown | B<sub>lim</sub>: Unknown | | Herring - Barents Sea, Norwegian Sea, Spitzbergen and Bear Island, Iceland and Faore Grounds, Northern North Sea and Northeast Greenland, 2019 | ICES, 2019 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Full reproductive capacity | | Herring - Northwest of Scotland, 2012 | ICES, 2012 | Below target | Above limit | | Herring - West of Scotland, 2012 | ICES, 2012 | Above target | Undefined | | Herring - West of Scotland, West of Ireland and Porcupine Bank, 2019 | ICES, 2019 | FMSY: Undefined | MSY Btrigger: Undefined | | Cod - Davies Strait and Denmark Strait, 2019 | ICES, 2019 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Full reproductive capacity | | Cod - West Greenland, Inshore, 2019 | ICES, 2019 | F<sub>MSY</sub>: Above | B<sub>lim</sub>: Full reproductive capacity | | Other skate and rays - Bay of Biscay and Portuguese Waters East, 2019 | ICES, 2019 | F<sub>MSY</sub>: Unknown | B<sub>lim</sub>: Unknown | | Other rays and skates - North Sea, Skagerrak, Kattegat and Eastern English Channel, 2018 | ICES, 2018 | F<sub>MSY</sub>: Unknown | B<sub>lim</sub>: Unknown | | Alfonsino - Northeast Atlantic, 2015 | ICES, 2015 | F<sub>MSY</sub>: Undefined | MSY B<sub>Trigger</sub>: Undefined | | Deepwater demersal resources - Southwest Pacific, 2017 | SPRFMO, 2017 | | | | Elasmobranchs - Bay of Biscay and Iberian waters, 2008 | ICES, 2008 | Undefined | Undefined | | Elasmobranchs - North Sea, Skagerrak, and Eastern English Channel, 2008 | ICES, 2008 | Undefined | Undefined | | Elasmobranchs - Celtic Sea and West of Scotland, 2008 | ICES, 2008 | Undefined | Undefined | | Deep-sea red crab - South East Atlantic, 2020 | SEAFO, 2020 | | | |
Status and Trend Summaries (extracted from reports) Results for domain [resource] keyword=[Atlantic redfishes nei] 151 result(s) resource | Fact sheets | biological state & trend |
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Sea cucumber - Lagoon of Mauritius and Rodrigues, 2009 | FAO, 2009 | Exploit State: Depleted | | Little tuna - Maldives, 2009 | FAO, 2009 | Exploit State: Underexploited | | Prawns - Ungwana bay, 2009 | FAO, 2009 | Exploit State: Fully exploited | | Scads - Mid-water of Saya de Malha and Nazareth banks, 2009 | FAO, 2009 | Exploit State: Underexploited | | Rock and spiny lobsters - Kenya, 2009 | FAO, 2009 | Exploit State: Overexploited | | Shrimps, lobsters and crabs - Comoros, 2009 | FAO, 2009 | Exploit State: Underexploited | | Shrimps, lobsters and crabs - Comoros, 2009 | FAO, 2009 | Exploit State: Underexploited | | Northern Bluefin tuna - Western Atlantic, 2014 | ICCAT, 2014 | Exploit Rate: F2010-2012/F0.1: Low potential recruitment = 0.60 (0.50-0.72) Abundance Level: SSB2013/SSBFMSY: Low potential recruitment =2.25 (1.92-2.68) / High potemtial recruitment =0.48 (0.35-0.72) | | Atlantic horse mackerel - Northwest Africa, 2014 | FAO, 2014 | Exploit State: Fully exploitedExploit Rate: Fcur/F0.1 = 104% ; Fcur/FMSY = 93% ; Abundance Level: Bcur/B0.1 = 105% ; Bcur/BMSY = 115% | Complete description  Fcur/F0.1: Ratio between the observed fishing mortality coefficient during the last year of the series and F0.1. Fcur/FMSY: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a maximum sustainable yield over the long term. Bcur/B0.1: Ratio between the estimated biomass for the last year and the biomass corresponding to F0.1. Bcur/BMSY: Ratio between the estimated biomass for the last year and the biomass corresponding to FMSY. Unless otherwise indicated, the indicators were based on the Schaefer dynamic production stock assessment model. | | Penaeus shrimps - Nigeria, 1998 | FAO, 1998 | Exploit State: Overexploited | | Demersal resources - Kenya, 2009 | FAO, 2009 | Exploit State: Fully exploited | | Sea cucumber - Seychelles (Mahe and Admirantes stocks), 2009 | FAO, 2009 | Exploit State: Overexploited | | Small pelagics - Kenya, 2009 | FAO, 2009 | Exploit State: Fully exploited | | Rays - Tanzania, 2009 | FAO, 2009 | Exploit State: Moderately exploited | | Sea cucumber - Tanzania, 2009 | FAO, 2009 | Exploit State: Overexploited | | Sharks - Seychelles offshore, 2009 | FAO, 2009 | Exploit State: Overexploited | | West African croakers - Guinea-Bissau and Guinea, 2009 | FAO, 2009 | Exploit State: OverexploitedExploit Rate: Fcur/F0.1 = 105% ; Fcur/FMSY = 95% Abundance Level: Bcur/B0.1 = 65% ; Bcur/BMSY = 72% | Complete description  Fcur/F0.1: Ratio between the observed fishing mortality coefficient during the last year of the series and F0.1. Fcur/FSYcur: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a sustainable yield at the current biomass level. Fcur/FMSY: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a maximum sustainable yield over the long term. Bcur/B0.1: Ratio between the estimated biomass for the last year and the biomass corresponding to F0.1. Bcur/BMSY: Ratio between the estimated biomass for the last year and the biomass corresponding to FMSY. Unless otherwise indicated, the indicators were based on the Schaefer dynamic production stock assessment model. | | West African croakers - Senegal and Gambia, 2012 | FAO, 2012 | Exploit State: Uncertain/Not assessed | | Sea cucumber - Kenya, 2009 | FAO, 2009 | Exploit State: Overexploited | | Pelagic sharks - Tanzania, 2009 | FAO, 2009 | Exploit State: Moderately exploited | | Demersal sharks - Tanzania, 2009 | FAO, 2009 | Exploit State: Moderately exploited | | Seabreams - Guinea-Bissau and Guinea, 2009 | FAO, 2009 | Exploit State: Not fully exploitedExploit Rate: Fcur/F0.1 = 58% ; Fcur/FMSY = 52% Abundance Level: Bcur/B0.1 = 93% ; Bcur/BMSY = 103% | Complete description  Fcur/F0.1: Ratio between the observed fishing mortality coefficient during the last year of the series and F0.1. Fcur/FSYcur: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a sustainable yield at the current biomass level. Fcur/FMSY: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a maximum sustainable yield over the long term. Bcur/B0.1: Ratio between the estimated biomass for the last year and the biomass corresponding to F0.1. Bcur/BMSY: Ratio between the estimated biomass for the last year and the biomass corresponding to FMSY. Unless otherwise indicated, the indicators were based on the Schaefer dynamic production stock assessment model. | | Beaked redfish - Iceland and Faroe grounds, North of Azores, East Greenland and Northwest Atlantic (deep slope), 2015 | ICES, 2015 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Reduced reproductive capacity | | Cod - Barents and Norwegian Seas (coastal waters), 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>trigger</sub>: Undefined | | Herring - Bothnian Sea, 2015 | ICES, 2015 | Exploit Rate: F<sub>MSY</sub>: Appropriate Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Spring Spawning Herring - Skagerrak and Kattegat, 2008 | ICES, 2008 | Exploit Rate: Undefined Abundance Level: Undefined | | Atlantic horse mackerel - Morocco (North of 26° N), 2004 | FAO, 2004 | | Complete description  Probably Fully exploited. | | Shark, Smooth-hounds - Cape Verde, 1995 | FAO, 1995 | Exploit State: Moderately exploited | | Cat fish - Tanzania, 2009 | FAO, 2009 | Exploit State: Moderately exploited | | Dentex - São Tomé e Príncipe, 2010 | FAO, 2010 | Exploit State: Uncertain/Not assessed | | Tonguesole - Guinea-Bissau and Guinea, 2009 | FAO, 2009 | Exploit State: Not fully exploitedExploit Rate: Fcur/F0.1 = 41% ; Fcur/FMSY = 37% ; Abundance Level: Bcur/B0.1 = 140% ; Bcur/BMSY = 154% | Complete description  Fcur/F0.1: Ratio between the observed fishing mortality coefficient during the last year of the series and F0.1. Fcur/FSYcur: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a sustainable yield at the current biomass level. Fcur/FMSY: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a maximum sustainable yield over the long term. Bcur/B0.1: Ratio between the estimated biomass for the last year and the biomass corresponding to F0.1. Bcur/BMSY: Ratio between the estimated biomass for the last year and the biomass corresponding to FMSY. Unless otherwise indicated, the indicators were based on the Schaefer dynamic production stock assessment model. | | Herring - Bothnian Bay, 2015 | ICES, 2015 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>Trigger</sub>: Undefined | | Icelandic Cod - Icelandic grounds, 2018 | ICES, 2018 | Exploit Rate: HR<sub> MSY</sub>: Below Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Cod - Faroe Bank, 2015 | ICES, 2015 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>Trigger</sub>: Undefined | | Redfish - Southwestern Grand Bank, 2015 | NAFO, 2015 | Exploit Rate: None-Low Fishing Mortality Abundance Level: Unknown Stock Size | | Tuna and tuna-like species - Global, 2009 | FAO, 2009 | | Complete description  The following classification of the status of stocks is used throughout this document.
- U Non-fully exploited.
- F Fully exploited.
- O Overexploited.
For Further clarifications on the criteria for the classification of fish stock status, see the Source Report (Appendix - Assessment methodology, Table 1)
A summary on the status of various stocks of tuna and tuna-like species is given in
Table D19. It was obtained by interpreting results of stock assessments according to the
classification procedure adopted by FAO in this review. Those assessments available
at the time of preparation of this review (end of March 2011) were taken mostly from
Web pages of: -
Commission for the Conservation of Southern Bluefin Tuna (CCSBT );
-
Inter-American Tropical Tuna Commission (IATTC ) for the
eastern Pacific;
-
International Commission for the Conservation of Atlantic Tunas (ICCAT );
-
Indian Ocean Tuna Commission (IOTC );
-
Western Central Pacific Fishery Commission (WCPFC ).
The knowledge and data on the principal market tunas are generally much better than
those for other species of tuna and tuna-like species. They have been studied for many
years and more research effort is devoted to them. However, even for these species,
significant uncertainties exist in the basic biological knowledge and data. For example,
relatively recent research indicates that the life span of southern bluefin tuna, one of
the best studied tuna, may be considerably longer than previously believed. Moreover,
for this species, as compared with trade statistics, the catches were substantially
under reported for a number of years. For Atlantic bluefin tuna, another well-studied
species, officially reported catches might be significantly smaller in the past than those
actually taken. This conclusion is based on information from a trade-based statistical
programme introduced by ICCAT (Miyake, 1998) as well as from capacity estimates
(ICCAT, 2009). When considering the information on the stock status, uncertainties in
stock assessment need to be taken into account.
Most tuna stocks are fully exploited, some are overexploited. Generally, some
temperate tuna species (i.e. Atlantic and southern bluefins [most desired for sashimi])
are much more overexploited (depleted) than any of the tropical tuna species. For the
Pacific bluefin (also used for sushimi), the yield-per-recruit could be increased if the
number of small bluefin caught by trolling and purse seining can be reduced.
The stocks of albacore (temperate species) used mostly for canning are not fully
exploited in the South Pacific but they are fully exploited in the Indian Ocean and the
South Atlantic and overexploited in the North Atlantic and the North Pacific. The
status of albacore in the Mediterranean Sea is unknown. Generally, most tropical principal market tunas have reacted well to exploitation
owing to their very high reproductive potential, wide geographical distribution,
opportunistic behaviour and other population dynamics characteristics that make them
highly productive. With proper management, they are capable of sustaining high yields.
There may still be potential for increasing catches of skipjack in the western and
central Pacific with lower potential in the other oceans. However, skipjack are caught
together with tuna species that are fully exploited or overexploited. Therefore, until
more selective fishing methods are developed, it is not desirable to increase the catches
of skipjack.
Most other stocks of tropical tunas have become fully exploited and a few are
overexploited. Generally, a possibility of further deterioration in the status of tropical
tunas should not be underestimated. Concerns are increasing over the exploitation of
bigeye in all oceans. This is another species that is highly desired for sashimi and has a
shorter life span than bluefin. In addition to possibly causing overfishing in the future,
the increasing purse seine catches of small bigeye may negatively affect the yield per
recruit.
The status of many tuna and tuna-like species other than the principal tunas is highly
uncertain or simply unknown. Therefore, the intensification of their exploitation
raises concerns. Significant uncertainties in the status of many billfishes represent a
serious conservation problem. Some stocks are overexploited in the Atlantic and
the Pacific, while their status is mainly unknown in the Indian Ocean. Because of
commercial exploitation, there is more known about swordfish than other billfishes. In
the Mediterranean Sea, the swordfish stock seems to be overexploited, but the overall
situation in the remainder of the Atlantic and Pacific is more optimistic. However, in
the Indian Ocean, there are concerns about the intensification of swordfish fishing
owing to the risk of potential local overexploitation.
| | Sharks and Rays - Kenya, 2009 | FAO, 2009 | Exploit State: Fully exploited | | Penaeus shrimps - Nigeria and Cameroon, 2004 | FAO, 2004 | Exploit State: Fully exploited | | Cuttlefish - Sierra Leone and Liberia, 2004 | FAO, 2004 | Exploit State: Overexploited | | Coastal groundfishes - Antigua and Barbuda, 2003 | FAO, 2003 | Exploit State: Overexploited | | Sea urchins - Grenada, 2003 | FAO, 2003 | Exploit State: Overexploited | | Small pelagics - Tanzania, 2009 | FAO, 2009 | Exploit State: Moderately exploited | | Barracudas - Seychelles, 2009 | FAO, 2009 | | | Herring - Iceland, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Below Abundance Level: B<sub>lim</sub>: Increased risk | | Bivalves - Kenya, 2009 | FAO, 2009 | Exploit State: Fully exploited | | Shrimps - South Africa Eastern, 2009 | FAO, 2009 | Exploit State: Overexploited | | Cod - Barents Sea, Norwegian Sea, Spitzbergen and Bear Island, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Bluespotted seabass, West African goatfish, Sand steenbras, Axillary seabream, Atlantic bigeye - Cape Verde, 2004 | FAO, 2004 | | Complete description  Fully exploited for Cephalopholis taeniops and moderately exploited for others. | | Spring Spawing herring - Norwegian Sea, 2008 | ICES, 2008 | Exploit Rate: Harvested sustainably Abundance Level: Full reproductive capacity | | Sharks - Seychelles inshore (Mahe Plateau, Amirantes, Outer Islands), 2009 | FAO, 2009 | Exploit State: Depleted | | Northern Bluefin tuna - East Atlantic and Mediterranean Sea, 2014 | ICCAT, 2014 | Exploit Rate: F2013/F0.1 = 0.4 Abundance Level: SSB2013/SSBF0.1: Medium recruitment (1950-2006) =1.10 / Low recruitment (1970s)=1.60 / High recruitment (1990s)=0.67 | | Deep slope groundfishes - Antigua and Barbuda, 2003 | FAO, 2003 | | Complete description  Probably fully exploited. | | Octopus - Seychelles (Granitic Islands), 2009 | FAO, 2009 | | | Atlantic horse mackerel - Morocco, Mauritania, Senegal, Gambia, Guinea Bissau and Guinea (between 26° and 10° N), 2004 | FAO, 2004 | | Complete description  Probably Fully exploited. | | Atlantic Cod - Grand Bank, 2017 | NAFO, 2017 | Exploit Rate: None-Low Fishing Mortality Abundance Level: Depleted Stock Size | Complete description  The spawning biomass increased noticeably between 2010 and 2015 but has subsequently declined and the 2018 estimate of 18,537 t represents only 31% of Blim (60,000 t). The 2006 year class remains relatively strong and at age 12 in 2018 makes up more than half of the estimated SSB. Subsequent year classes are much weaker, suggesting that the medium-term prospects for the stock are not good. Fishing mortality values over the past decade have been low and well below Flim (0.3). | | Cod - North Sea, Eastern English Channel and Skagerrak, 2015 | ICES, 2015 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Beaked redfish - Iceland and Faroe grounds, North of Azores, East Greenland and Northwest Atlantic (upper slope), 2015 | ICES, 2015 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>Trigger</sub>: Undefined | | Octopus and Squid - Kenya, 2009 | FAO, 2009 | Exploit State: Fully exploited | | Bivalves - Tanzania, 2009 | FAO, 2009 | Exploit State: Overexploited | | Cod - Irish Sea, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>trigger</sub>: Undefined | | Sandeel - Skagerrak and Kattegat, 2008 | ICES, 2008 | Exploit Rate: Undefined Abundance Level: Undefined | | Cuttlefish - Ghana and Benin, 2004 | FAO, 2004 | | Complete description  | | Atlantic cod - Northeast Newfoundland Shelf and Northern Grand Bank, 2000 | NAFO, 2000 | | Complete description  | | West African croakers - Guinea, 2004 | FAO, 2004 | Exploit State: Fully exploited | | Seabreams, Groupers - Equatorial Guinea, 1999 | FAO, 1999 | | Complete description  | | Cuttlefish - Cap Blanc stock (21°N - 16°N), 2012 | FAO, 2012 | Exploit State: Not fully exploitedExploit Rate: Fcur/F0.1 = 47% ; Fcur/FMSY = 42% Abundance Level: Bcur/B0.1 = 145% ; Bcur/BMSY = 160% | Complete description  Fcur/F0.1: Ratio between the observed fishing mortality coefficient during the last year of the series and F0.1. Fcur/FMSY: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a maximum sustainable yield over the long term. Bcur/B0.1: Ratio between the estimated biomass for the last year and the biomass corresponding to F0.1. Bcur/BMSY: Ratio between the estimated biomass for the last year and the biomass corresponding to FMSY. Unless otherwise indicated, the indicators were based on the Schaefer dynamic production stock assessment model. | | Cod - Faroe Plateau, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Other skates and rays - Rockall, Northwest Coast of Scotland and North Ireland, Irish Sea, West of Ireland, Porcupine Bank, Western English Channel, Bristol Channel, Celtic Sea and Southwest of Ireland, 2015 | ICES, 2015 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>Trigger</sub>: Undefined | | Sandeel - Shetland Area, 2008 | ICES, 2008 | Exploit Rate: Undefined Abundance Level: Undefined | | Sandeel - North Sea, 2008 | ICES, 2008 | Exploit Rate: Undefined Abundance Level: Increased risk | | White marlin Atlantic, 2010 | ICCAT, 2010 | Exploit Rate: F2010/FMSY = 0.72-0.99 Abundance Level: B2010/BMSY = 0.5-0.32 | | Atlantic sailfish - East Atlantic, 2014 | ICCAT, 2014 | Exploit Rate: F2014/FMSY = 0.33-2.85 Abundance Level: B2014/MSY = 0.22-0.70 | | Rockcods and seabass - South Africa Eastern, 2009 | FAO, 2009 | Exploit State: Depleted | | Angler fish - Bay of Biscay and Iberian Basin, 2008 | ICES, 2008 | Exploit Rate: Undefined Abundance Level: Undefined | | Redfish - North and Southeastern Grand Bank, 2013 | NAFO, 2013 | Exploit Rate: None-Low Fishing Mortality Abundance Level: Intermediate Stock Size | Complete description  The stock is estimated to be at 1.4 x Bmsy. There is a low risk of the stock being below Bmsy. Fishing mortality is below Fmsy (0.22 Fmsy), and the probability of being above Fmsy is very low. Recent recruitment (2005 – 2013) appears to be above average. | | Bigeye scad, Atlantic horse mackerel, Scad - Cape Verde, 1997 | FAO, 1997 | | Complete description  Fully exploited (for Selar). | | Redfish - Flemish Cap, 2016 | NAFO, 2016 | Exploit Rate: None-Low Fishing Mortality Abundance Level: Intermediate Stock Size | | Emperors and Snappers - Northern Shelf of Mauritius, 2009 | FAO, 2009 | Exploit State: Overexploited | | Reef fishes - Tanzania, 2009 | FAO, 2009 | Exploit State: Fully exploited | | Cardinal Fish - South East Atlantic, 2009 | SEAFO, 2009 | Exploit State: UncertainExploit Rate: Uncertain/Not assessed Abundance Level: Uncertain/Not assessed | | Atlantic Cod - Flemish Cap, 2017 | NAFO, 2017 | Exploit Rate: None-Low Fishing Mortality Abundance Level: Intermediate Stock Size | | Mullet, Barracuda and Milkfish - Kenya, 2009 | FAO, 2009 | Exploit State: Fully exploited | | Spiny and rock lobsters - Somalia, 2009 | FAO, 2009 | Exploit State: Overexploited | | Other Octopuses - South Africa Eastern, 2009 | FAO, 2009 | | | Beaked redfish - Southeast Greenland, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>trigger</sub>: Undefined | | Squid - South East Atlantic, 2009 | SEAFO, 2009 | Exploit State: UncertainExploit Rate: Uncertain/Not assessed Abundance Level: Uncertain/Not assessed | | Atlantic sailfish - West Atlantic, 2014 | ICCAT, 2014 | Exploit Rate: F2014/FMSY = 0.33 or 0.63 Abundance Level: B2014/MSY = 1.81 or 1.16 | | Penaeus shrimp - Equatorial Guinea, 2004 | FAO, 2004 | Exploit State: Overexploited | | Penaeus shrimps - Cameroon, 2004 | FAO, 2004 | | Complete description  Fully exploited in Nigeria, Overexploited in Cameroon. | | Oceanic pelagic fishes - Antigua and Barbuda, 2003 | FAO, 2003 | | Complete description  Unknown, maybe not fully exploited. | | Octopus - South East Atlantic, 2009 | SEAFO, 2009 | Exploit State: UncertainExploit Rate: Uncertain/Not assessed Abundance Level: Uncertain/Not assessed | | Scads - Guinea-Bissau, Guinea, Sierra Leone and Liberia, 2012 | FAO, 2012 | Exploit State: OverexploitedExploit Rate: Fcur/F0.1 = 176% ; Fcur/FMSY = 158% Abundance Level: Bcur/B0.1 = 73% | Complete description  Fcur/F0.1: Ratio between the observed fishing mortality coefficient during the last year of the series and F0.1. Fcur/FMSY: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a maximum sustainable yield over the long term. Bcur/B0.1: Ratio between the estimated biomass for the last year and the biomass corresponding to F0.1. Unless otherwise indicated, the indicators were based on the Schaefer dynamic production stock assessment model. | | Skates - South East Atlantic, 2009 | SEAFO, 2009 | Exploit State: UncertainExploit Rate: Uncertain/Not assessed Abundance Level: Uncertain/Not assessed | | Cod - Western English Channel, Bristol Channel, Celtic Sea and Southwest of Ireland, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Reduced reproductive capacity | | Mackerel - Bay of Biscay and Portuguese waters, 2008 | ICES, 2008 | Exploit Rate: Increased risk Abundance Level: Full reproductive capacity | | Cuttlefish - Senegal and Gambia, 2012 | FAO, 2012 | Exploit State: Not fully exploitedExploit Rate: Fcur/F0.1 = 37% ; Fcur/FMSY = 33% Abundance Level: Bcur/B0.1 = 117% ; Bcur/BMSY = 128% | Complete description  Fcur/F0.1: Ratio between the observed fishing mortality coefficient during the last year of the series and F0.1. Fcur/FMSY: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a maximum sustainable yield over the long term. Bcur/B0.1: Ratio between the estimated biomass for the last year and the biomass corresponding to F0.1. Bcur/BMSY: Ratio between the estimated biomass for the last year and the biomass corresponding to FMSY. Unless otherwise indicated, the indicators were based on the Schaefer dynamic production stock assessment model. | | Flat fish - Tanzania, 2009 | FAO, 2009 | Exploit State: Fully exploited | | Clyde herring - West of Scotland, 2008 | ICES, 2008 | Exploit Rate: Undefined Abundance Level: Undefined | | Atlantic chub mackerel - Northwest Africa, 2014 | FAO, 2014 | Exploit State: Fully exploitedExploit Rate: Fcur/F0.1 = 101% ; Fcur/FMSY = 91% Abundance Level: Bcur/B0.1 = 135% ; Bcur/BMSY = 148% | Complete description  Fcur/F0.1: Ratio between the observed fishing mortality coefficient during the last year of the series and F0.1. Fcur/FSYcur: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a sustainable yield at the current biomass level. Fcur/FMSY: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a maximum sustainable yield over the long term. Bcur/B0.1: Ratio between the estimated biomass for the last year and the biomass corresponding to F0.1. Unless otherwise indicated, the indicators were based on the Schaefer dynamic production stock assessment model. | | West African croakers - Liberia, 2004 | FAO, 2004 | | Complete description  Fully exploited, Overexploited | | Tounguesole - Guinea, 2004 | FAO, 2004 | Exploit State: Overexploited | | Sardinellas - Equatorial Guinea, 1999 | FAO, 1999 | | Complete description  Probably Moderately exploited. | | Sharks - Global, 2009 | FAO, 2009 | | Complete description  | | Cuttlefish - Dakhla stock (26°N - 21°N), 2012 | FAO, 2012 | Exploit State: Not fully exploitedExploit Rate: Fcur/F0.1 = 59% ; Fcur/FMSY = 53% Abundance Level: Bcur/B0.1 = 124% ; Bcur/BMSY = 137% | Complete description  Fcur/F0.1: Ratio between the observed fishing mortality coefficient during the last year of the series and F0.1. Fcur/FMSY: Ratio between the observed fishing mortality coefficient during the last year of the series and the coefficient that would give a maximum sustainable yield over the long term. Bcur/B0.1: Ratio between the estimated biomass for the last year and the biomass corresponding to F0.1. Bcur/BMSY: Ratio between the estimated biomass for the last year and the biomass corresponding to FMSY. Unless otherwise indicated, the indicators were based on the Schaefer dynamic production stock assessment model. | | Herring - Irish Sea North of 52°30’N, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Below Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Herring - Irish Sea South of 52°30’N, Celtic Sea and Southwest of Ireland, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Reduced reproductive capacity | | Cod - West of Scotland, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Reduced reproductive capacity | | Megrim - Northern North Sea and West of Scotland, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Below Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Megrim - Rockall, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Below proxy Abundance Level: B<sub>lim</sub>: Above possible reference points | |
Deep water Redfish - Rockall Bank and Reykjanes Ridge
, 2006 | ICES, 2006 | Exploit Rate: Undefined Abundance Level: Undefined | Complete description 
In the absence of reference points the state of the stock cannot be fully evaluated. Commercial cpue indicates a general decrease in stock biomass from the late 1980s to the early 1990s; after this it has been relatively stable. All available survey biomass indices have been stable in the last 5 years.
| | Seabob - Coast of French Guiana to the Orinoco delta, 2017 | FAO, 2017 | Exploit State: Maximally sustainably fishedExploit Rate: F/Fmsy = 1 Abundance Level: B/Bmsy = 1.25 | Complete description  • Both Suriname and Guyana stocks are fluctuating at or above their MSY level (Figure 1). • However, both stocks are low compared to the unexploited state and on average is below the 40% SSB0 (Figure 2), although this is precautionary for finfish rather than shrimp. • There is some evidence of seasonality in spawning stock biomass (Figure 3). Although seasonality is present in the recruitment, this pattern is weaker. The seasonality is opposite between Suriname and Guyana. • There is no evidence that recruitment has been reduced significantly by fishing (Figure 4). • Fishing mortality has tended to be higher than FMSY for Suriname but fluctuating around or lower than FMSY for Guyana in recent years (Figure 5). • Suriname has dome-shaped, but highly uncertain, selectivity. Guyana selectivity is logistic in shape and appears more typical for trawl (Figure 6). | | Cod - Kattegat, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>trigger</sub>: Undefined | | Herring - Gulf of Riga, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Below Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Horse mackerel - North Sea, Eastern English Channel, Skagerrak and Kattegat, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Above proxy Abundance Level: MSY B<sub>trigger</sub>: Undefined | | Herring - North Sea, Eastern English Channel, Skagerrak and Kattegat, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Below Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Beaked redfish - East Greenland and Icelandic Slope, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>trigger</sub>: Undefined | | Horse mackerel - Portuguese Waters East, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Below Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Cod - Baltic Sea (Eastern part), 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: B<sub>lim</sub>: Reduced reproductive capacity | | Herring - Skagerrak, Kattegat, Sound and Belt Sea, Baltic West of Bornholm, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Reduced reproductive capacity | | Cod - Baltic Sea (Western part), 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Increased risk | | Herring - Central Baltic Sea, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Increased risk | | Mackerel - Northeast Atlantic, 2017 | ICES, 2017 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Horse mackerel - Norwegian Sea, Northern North Sea, Faroes Grounds, West of Scotland, Irish Sea, West of Ireland, Porcupine Bank, Western English Channel, Bristol Channel, Celtic Sea, Southwest of Ireland, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Increased risk | | Rays and skates (mainly thornback ray) - Azores Ground, North of Azores, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Unknown Abundance Level: B<sub>lim</sub>: Unknown | | Cod - West Greenland, offshore, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>trigger</sub>: Undefined | | Sandeel - Central and Southern North Sea (Sandeel Area 1r), 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: B<sub>lim</sub>: Reduced reproductive capacity | | Sandeel - Skagerrak, Central and Southern North Sea (Sandeel Area 2r), 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: B<sub>lim</sub>: Reduced reproductive capacity | | Sandeel - Skagerrak, Northern and Central North Sea (Sandeel Area 3r), 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Sandeel - Northern and Central North Sea (Sandeel Area 4), 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: B<sub>lim</sub>: Increased risk | | Sandeel - Skagerrak, Kattegat and Belt Sea (Sandeel Area 6), 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: B<sub>lim</sub>: Unknown | | Sandeel - Northern North Sea and Shetland (Sandeel Area 7r), 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: B<sub>lim</sub>: Unknown | | Sandeel - Viking and Bergen Bank area (Sandeel Area 5r), 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: B<sub>lim</sub>: Unknown | | Starry smooth-hound - Northeast Atlantic, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Unknown Abundance Level: B<sub>lim</sub>: Unknown | | Herring - Gulf of Bothnia, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Unknown Abundance Level: B<sub>lim</sub>: Unknown | | Beaked redfish - Barents and Norwegian Seas, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Cod - Rockall, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Unknown Abundance Level: B<sub>lim</sub>: Unknown | | Sandeel - West of Scotland, 2017 | ICES, 2017 | Exploit Rate: F<sub>MSY</sub>: Unknown Abundance Level: B<sub>lim</sub>: Unknown | | Herring - Barents Sea, Norwegian Sea, Spitzbergen and Bear Island, Iceland and Faore Grounds, Northern North Sea and Northeast Greenland, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Herring - Northwest of Scotland, 2012 | ICES, 2012 | Exploit Rate: Below target Abundance Level: Above limit | | Herring - West of Scotland, 2012 | ICES, 2012 | Exploit Rate: Above target Abundance Level: Undefined | | Herring - West of Scotland, West of Ireland and Porcupine Bank, 2019 | ICES, 2019 | Exploit Rate: FMSY: Undefined Abundance Level: MSY Btrigger: Undefined | | Cod - Davies Strait and Denmark Strait, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Cod - West Greenland, Inshore, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Above Abundance Level: B<sub>lim</sub>: Full reproductive capacity | | Other skate and rays - Bay of Biscay and Portuguese Waters East, 2019 | ICES, 2019 | Exploit Rate: F<sub>MSY</sub>: Unknown Abundance Level: B<sub>lim</sub>: Unknown | | Other rays and skates - North Sea, Skagerrak, Kattegat and Eastern English Channel, 2018 | ICES, 2018 | Exploit Rate: F<sub>MSY</sub>: Unknown Abundance Level: B<sub>lim</sub>: Unknown | | Alfonsino - Northeast Atlantic, 2015 | ICES, 2015 | Exploit Rate: F<sub>MSY</sub>: Undefined Abundance Level: MSY B<sub>Trigger</sub>: Undefined | | Deepwater demersal resources - Southwest Pacific, 2017 | SPRFMO, 2017 | | | Elasmobranchs - Bay of Biscay and Iberian waters, 2008 | ICES, 2008 | Exploit Rate: Undefined Abundance Level: Undefined | Complete description 
The stock boundaries for demersal elasmobranch species in Subareas VIII and IX are unknown.
| | Elasmobranchs - North Sea, Skagerrak, and Eastern English Channel, 2008 | ICES, 2008 | Exploit Rate: Undefined Abundance Level: Undefined | Complete description 
In the absence of defined reference points, the status of the stocks of demersal skates and rays (members of the family Rajidae) and demersal sharks (of the genera Scyliorhinus
,
Mustelus, and Squatina) cannot be evaluated. The following provides a qualitative summary of the general status of the major species based on surveys and landings:
| | Elasmobranchs - Celtic Sea and West of Scotland, 2008 | ICES, 2008 | Exploit Rate: Undefined Abundance Level: Undefined | Complete description  In the absence of defined reference points, the status of the stocks of demersal skates and rays and demersal sharks cannot be evaluated. The following provides a qualitative summary of the general status of the major species based on survey and landings data. | | Deep-sea red crab - South East Atlantic, 2020 | SEAFO, 2020 | | |
|