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Overview
Brief Summary
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Biology
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Description
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Comprehensive Description
Biology
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Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba 1990 FAO species catalogue. Vol. 10. Gadiform fishes of the world (Order Gadiformes). An annotated and illustrated catalogue of cods, hakes, grenadiers and other gadiform fishes known to date. FAO Fish. Synop. 125(10). Rome: FAO. 442 p. (Ref. 1371)
http://www.fishbase.org/references/FBRefSummary.php?id=1371&speccode=25
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Description
Atlantic cod are productive breeders. Spawning occurs between February and April when 3 to 6 million buoyant eggs are released, often forming great swarms that can be transported miles by ocean currents before hatching after 12 days. The larval stage of this species is also planktonic and will be carried by currents for up to 2 months before settling on the seabed where the Atlantic cod spend most of their life (Dipper, 2001).
Young Gadus morhua feed mainly on copeopods but become increasingly dependant on fish as they age, eating the likes of herring, capelin, haddock and even other cod (Dipper, 2001; Wheeler, 1969).Sub-species Gadus morhua morhua is the most common, and is found from both the western and eastern north Atlantic. Gadus morhua callarias is a low salinity non-migratory race found in the Baltic, and Gadus morhua marisalba occurs in the White Sea.
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Description
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Distribution
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Leewis, R. (2002). Flora en fauna van de zee [Marine flora and fauna]. Veldgids, 16. KNNV Uitgeverij: Utrecht, The Netherlands. ISBN 90-5011-153-X. 320 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1116
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Müller, Y. (2004). Faune et flore du littoral du Nord, du Pas-de-Calais et de la Belgique: inventaire. [Coastal fauna and flora of the Nord, Pas-de-Calais and Belgium: inventory]. Commission Régionale de Biologie Région Nord Pas-de-Calais: France. 307 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=9269
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Hayward, P.J.; Ryland, J.S. (Ed.) (1990). The marine fauna of the British Isles and North-West Europe: 1. Introduction and protozoans to arthropods. Clarendon Press: Oxford, UK. ISBN 0-19-857356-1. 627 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1
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Massin, C.; Norro, A.; Mallefet, J. (2002). Biodiversity of a wreck from the Belgian Continental Shelf: monitoring using scientific diving. Preliminary results. Bull. IRSNB (Biologie) 72, pp 67-72.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1187
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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Hostens, K. (2000). Spatial patterns and seasonality in the epibenthic communities of the Westerschelde (Southern Bight of the North Sea). J. Mar. Biol. Ass. U.K. 80: 27-36
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1139
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Hostens, K.; Hamerlynck, O. (1994). The mobile epifauna of the soft bottoms in the subtidal Oosterschelde estuary: structure, function and impact of the storm-surge barrier. Hydrobiologia 282-283: 479-496
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1142
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ILVO epifauna en demersale visdata: epifauna en demersale vismonitoring op het Belgisch deel van de Noordzee sinds 1979
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=132964
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Maes, J.; Taillieu, A.; Van Damme, P.A.; Ollevier, F.P. (1997). The composition of the fish and crustacean community of the Zeeschelde estuary (Belgium). Belg. J. Zool. 127(1): 47-55
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=133007
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Van Damme, P.A.; Hostens, K.; Ollevier, F.P. (1994). Fish species of the lower Zeeschelde (Belgium): a comparison with historical checklists. Belg. J. Zool. 124(2): 93-103
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=132986
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Simons, E.; Simons, G.; Corstanje, H. (1988). Report on the beach excursion at Oostduinkerke (Belgium) on 2 November 1988 [Verslag van de strandexcursie te Oostduinkerke op 2 november 1988]. De Strandvlo 8(4): 206-209
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=138809
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Cattrijsse, A.; Vincx, M. (2001). Biodiversity of the benthos and the avifauna of the Belgian coastal waters: summary of data collected between 1970 and 1998. Sustainable Management of the North Sea. Federal Office for Scientific, Technical and Cultural Affairs: Brussel, Belgium. 48 pp.
http://www.marinespecies.org/mollusca/aphia.php?p=sourcedetails&id=61
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Hamerlynck, O.; Hostens, K.; Arellano, R.V.; Mees, J.; Vandamme, P.A. (1993). The mobile epibenthic fauna of soft bottoms in the Dutch Delta (south-west Netherlands): spatial structure. Pp 343-358 in Meire, P.; Vincx, M. (Ed.): Marine and estuarine gradients: ECSA 21: Proceedings of the 21th Symposium of the Estuarine and Coastal Sciences Association held in Gent, 9-14 september 1991. Neth. J. Aquat. Ecol., 27(2-4). Netherlands Society of Aquatic Ecology: Bilthoven, The Netherlands.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1140
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van der Land, J.; Costello, M.J.; Zavodnik, D.; Santos, R.S.; Porteiro, F.M.; Bailly, N.; Eschmeyer, W.N.; Froese, R. (2001). Pisces, in: Costello, M.J. et al. (Ed.) (2001). European register of marine species: a check-list of the marine species in Europe and a bibliography of guides to their identification. Collection Patrimoines Naturels, 50: pp. 357-374
http://www.marbef.org/data/aphia.php?p=sourcedetails&id=1411
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Nozères C., Archambault D., Chouinard P.-M., Gauthier J., Miller R., Parent E., Schwab P., Savard L., and Dutil J.-D. 2010. Identification guide for marine fishes of the estuary and northern Gulf of St. Lawrence and sampling protocols used during trawl surveys between 2004 and 2008. Can. Tech. Rep. Fish. Aquat. Sci. 2866: xi + 243 p
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=145051
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Johnson CL, Runge JA, Curtis KA, Durbin EG, Hare JA, Incze LS, Link J, Melvin GD, O'Brien TD, Van Guelpen, L (in revision) Biodiversity and ecosystem function in the Gulf of Maine: pattern and role of zooplankton and pelagic nekton. PLoS One.
http://www.vliz.be/vmdcdata/masdea/masdea.php?p=sourcedetails&id=148111
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MEDIN (2011). UK checklist of marine species derived from the applications Marine Recorder and UNICORN, version 1.0.
http://www.marinespecies.org/asteroidea/aphia.php?p=sourcedetails&id=149081
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Guiry, M.D. & Guiry, G.M. (2011). Species.ie version 1.0 World-wide electronic publication, National University of Ireland, Galway (version of 15 March 2010).
http://www.marinespecies.org/ascidiacea/aphia.php?p=sourcedetails&id=149068
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Ramos, M. (ed.). 2010. IBERFAUNA. The Iberian Fauna Databank
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=149024
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Kedra, M. (2010). A Checklist of marine species occurring in Polish marine waters, compiled in the framework of the PESI EU FP7 project.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=149084
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Siferd, Tim. 2010. Central and Arctic multi-species stock assessment surveys. In OBIS Canada Digital Collections. Bedford Institute of Oceanography, Dartmouth, Nova Scotia. OBIS Canada Ver1
http://www.marinespecies.org/ophiuroidea/aphia.php?p=sourcedetails&id=155140
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North/South Consultants 2006. Potential dispersal of aquatic invasive species into Hudson Bay from ballast water from ships travelling from ports in Europe and North America. A report prepared for Fisheries and Ocean Canada File No. F2408-050083
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=155160
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Breine, J.; Stevens, M.; Van den Bergh, E.; Maes, J. (2011). A reference list of fish species for a heavily modified transitional water: The Zeeschelde (Belgium) Belg. J. Zool. 141(1): 44-55
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=156540
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Miller, Roberta. 2012. The museum collection database, Fisheries and Oceans Canada digital collections, Maurice Lamontagne Institute, Quebec
http://www.marinespecies.org/asteroidea/aphia.php?p=sourcedetails&id=163928
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Dyntaxa (2013) Swedish Taxonomic Database. Accessed at www.dyntaxa.se [15-01-2013].
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=165516
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Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba 1990 FAO species catalogue. Vol. 10. Gadiform fishes of the world (Order Gadiformes). An annotated and illustrated catalogue of cods, hakes, grenadiers and other gadiform fishes known to date. FAO Fish. Synop. 125(10). Rome: FAO. 442 p. (Ref. 1371)
http://www.fishbase.org/references/FBRefSummary.php?id=1371&speccode=25
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Geographic Range
Gadus morhua is commonly known as Atlantic cod and can be found along the eastern and northern coasts of North America, along the coasts of Greenland, and from the Bay of Biscay north to the Arctic Ocean, including the Atlantic waters around Iceland, the North Sea, and the Barents Sea.
Biogeographic Regions: atlantic ocean (Native )
- 2005. "Wikipedia: Encyclopedia" (On-line). Accessed October 13, 2005 at http://en.wikipedia.org/wiki/Atlantic_cod.
- Wildscreen, U.K. Charity, 2004. "ArKive: Gadus Morhua" (On-line). Accessed October 11, 2005 at http://www.arkive.org/species/ARK/fish/Gadus_morhua/more_info.html.
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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National Distribution
Canada
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
United States
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
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- Bigelow, H.B. and Schroeder, W.C., 1953; Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba, 1990; Kjesbu, O.S., H. Kryvi, S. Sundby and P. Solemdal, 1992.
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Range
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Physical Description
Morphology
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Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba 1990 FAO species catalogue. Vol. 10. Gadiform fishes of the world (Order Gadiformes). An annotated and illustrated catalogue of cods, hakes, grenadiers and other gadiform fishes known to date. FAO Fish. Synop. 125(10). Rome: FAO. 442 p. (Ref. 1371)
http://www.fishbase.org/references/FBRefSummary.php?id=1371&speccode=25
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Physical Description
Atlantic cod reach a maximum length of 150 to 200 cm. On average, cod weigh 40 kg and the greatest recorded weight is 96 kg. The color of Atlantic cod varies with respect to the enviroment in which the fish lives. Water with large volumes of algae will yield a red to greenish skin color. A pale grey color is more prevalent for fish found on the ocean floor or on sandy bottoms. The Atlantic cod has 1 chin barbel, 3 dorsal fins, and 2 anal fins. It also has a pronounced lateral line from the gills to the tail (Wildscreen and U.K. Charity 2004). The coloring of cod is often shaded from top to bottom. The dorsal area of the fish may be a rich brown to green and fade to silver towards the ventral side. Some cod may have brown/red spots on the sides and back.
Range mass: 96 (high) kg.
Average mass: 40 kg.
Range length: 200 (high) cm.
Other Physical Features: ectothermic ; heterothermic ; bilateral symmetry
Sexual Dimorphism: sexes alike
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Size
Max. size
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Frimodt, C. 1995 Multilingual illustrated guide to the world's commercial coldwater fish. Fishing News Books, Osney Mead, Oxford, England. 215 p. (Ref. 9988)
http://www.fishbase.org/references/FBRefSummary.php?id=9988&speccode=2065
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Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba 1990 FAO species catalogue. Vol. 10. Gadiform fishes of the world (Order Gadiformes). An annotated and illustrated catalogue of cods, hakes, grenadiers and other gadiform fishes known to date. FAO Fish. Synop. 125(10). Rome: FAO. 442 p. (Ref. 1371)
http://www.fishbase.org/references/FBRefSummary.php?id=1371&speccode=25
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Muus, B.J. and P. Dahlström 1974 Collins guide to the sea fishes of Britain and North-Western Europe. Collins, London, UK. 244 p. (Ref. 173)
http://www.fishbase.org/references/FBRefSummary.php?id=173&speccode=24
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- Bigelow, H.B. and Schroeder, W.C., 1953; Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba, 1990; Kjesbu, O.S., H. Kryvi, S. Sundby and P. Solemdal, 1992.
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Diagnostic Description
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Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba 1990 FAO species catalogue. Vol. 10. Gadiform fishes of the world (Order Gadiformes). An annotated and illustrated catalogue of cods, hakes, grenadiers and other gadiform fishes known to date. FAO Fish. Synop. 125(10). Rome: FAO. 442 p. (Ref. 1371)
http://www.fishbase.org/references/FBRefSummary.php?id=1371&speccode=25
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Ecology
Habitat
Habitat: benthopelagic. This species is widely distributed in a variety of habitats from the shoreline to well down the continental shelf. Two stocks are recognized in the brackish Baltic Sea. Cod feeds at dawn or dusk on invertebrates and fish, including young cod. Forms schools during the day. Spawns once a year. Marketed fresh, dried/salted, smoked and frozen; eaten steamed, fried, broiled, boiled, microwaved and baked (Ref. 9988).
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Environment
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Riede, K. 2004 Global register of migratory species - from global to regional scales. Final Report of the R&D-Projekt 808 05 081. Federal Agency for Nature Conservation, Bonn, Germany. 329 p. (Ref. 51243)
http://www.fishbase.org/references/FBRefSummary.php?id=51243&speccode=4683
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FAO-FIGIS 2001 A world overview of species of interest to fisheries. Chapter: Gadus morhua. Retrieved on 30 May 2005, from www.fao.org/figis/servlet/species?fid=2218. 4p. FIGIS Species Fact Sheets. Species Identification and Data Programme-SIDP, FAO-FIGIS (Ref. 54441)
http://www.fishbase.org/references/FBRefSummary.php?id=54441&speccode=69
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Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba 1990 FAO species catalogue. Vol. 10. Gadiform fishes of the world (Order Gadiformes). An annotated and illustrated catalogue of cods, hakes, grenadiers and other gadiform fishes known to date. FAO Fish. Synop. 125(10). Rome: FAO. 442 p. (Ref. 1371)
http://www.fishbase.org/references/FBRefSummary.php?id=1371&speccode=25
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Atlantic cod are marine benthopelagic fish, living near the bottom and in the open ocean (Riede 2004). Cod also inhabit brackish waters. Cod can be found in a wide range of habitats within the ocean, from the shoreline down to the continental shelf. They can be found at depths of 500 to 600 meters in coastal waters and are also numerous in open ocean waters. These fish are located in a temperate climate with a range in temperature from 0 to 20 degrees Celsius. Geographically the majority of the population lies within a latitude of 80 to 35 degrees north (Frimodt 1995).
Range depth: 600 (high) m.
Habitat Regions: temperate ; saltwater or marine
Aquatic Biomes: pelagic ; benthic ; brackish water
- Riede, K. 2004. Global register of migratory species - from global to regional scales. Final Report of the R&D-Projekt:Federal Agency for Nature Conservation, 808 05 081: 329. Accessed October 13, 2005 at http://www.fishbase.org/Summary/SpeciesSummary.php?id=69.
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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Water temperature and chemistry ranges based on 253450 samples.
Environmental ranges
Depth range (m): -9 - 975
Temperature range (°C): -2.072 - 15.532
Nitrate (umol/L): 1.139 - 26.300
Salinity (PPS): 6.094 - 35.639
Oxygen (ml/l): 0.573 - 8.544
Phosphate (umol/l): 0.223 - 3.328
Silicate (umol/l): 0.987 - 72.643
Graphical representation
Depth range (m): -9 - 975
Temperature range (°C): -2.072 - 15.532
Nitrate (umol/L): 1.139 - 26.300
Salinity (PPS): 6.094 - 35.639
Oxygen (ml/l): 0.573 - 8.544
Phosphate (umol/l): 0.223 - 3.328
Silicate (umol/l): 0.987 - 72.643
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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From 1 to 600 meters.
Habitat: benthopelagic. This species is widely distributed in a variety of habitats from the shoreline to well down the continental shelf. Two stocks are recognized in the brackish Baltic Sea. Cod feeds at dawn or dusk on invertebrates and fish, including young cod. Forms schools during the day. Spawns once a year. Marketed fresh, dried/salted, smoked and frozen; eaten steamed, fried, broiled, boiled, microwaved and baked (Ref. 9988).
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- Bigelow, H.B. and Schroeder, W.C., 1953; Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba, 1990; Kjesbu, O.S., H. Kryvi, S. Sundby and P. Solemdal, 1992.
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Stellwagen Bank Pelagic Community
The species associated with this page are major players in the pelagic ecosystem of the Stellwagen Bank National Marine Sanctuary. Stellwagen Bank is an undersea gravel and sand deposit stretching between Cape Cod and Cape Ann off the coast of Massachussets. Protected since 1993 as the region’s first National Marine Sanctuary, the bank is known primarily for whale-watching and commercial fishing of cod, lobster, hake, and other species (Eldredge 1993).
Massachusetts Bay, and Stellwagen Bank in particular, show a marked concentration of biodiversity in comparison to the broader coastal North Atlantic. This diversity is supported from the bottom of the food chain. The pattern of currents and bathymetry in the area support high levels of phytoplankton productivity, which in turn support dense populations of schooling fish such as sand lance, herring, and mackerel, all important prey for larger fish, mammals, and seabirds (NOAA 2010). Sightings of many species of whales and seabirds are best predicted by spatial and temporal distribution of prey species (Jiang et al 2007; NOAA 2010), providing support for the theory that the region’s diversity is productivity-driven.
Stellwagen Bank is utilized as a significant migration stopover point for many species of shorebird. Summer visitors include Wilson’s storm-petrel, shearwaters, Arctic terns, and red phalaropes, while winter visitors include black-legged kittiwakes, great cormorants, Atlantic puffins, and razorbills. Various cormorants and gulls, the common murre, and the common eider all form significant breeding colonies in the sanctuary as well (NOAA 2010). The community of locally-breeding birds in particular is adversely affected by human activity. As land use along the shore changes and fishing activity increases, the prevalence of garbage and detritus favors gulls, especially herring and black-backed gulls. As gull survivorship increases, gulls begin to dominate competition for nesting sites, to the detriment of other species (NOAA 2010).
In addition to various other cetaceans and pinnipeds, the world’s only remaining population of North Atlantic right whales summers in the Stellwagen Bank sanctuary. Right whales and other baleen whales feed on the abundant copepods and phytoplankton of the region, while toothed whales, pinnipeds, and belugas feed on fish and cephalopods (NOAA 2010). The greatest direct threats to cetaceans in the sanctuary are entanglement with fishing gear and death by vessel strikes (NOAA 2010), but a growing body of evidence suggests that noise pollution harms marine mammals by masking their acoustic communication and damaging their hearing (Clark et al 2009).
General threats to the ecosystem as a whole include overfishing and environmental contaminants. Fishing pressure in the Gulf of Maine area has three negative effects. First and most obviously, it reduces the abundance of fish species, harming both the fish and all organisms dependent on the fish as food sources. Secondly, human preference for large fish disproportionately damages the resilience of fish populations, as large females produce more abundant, higher quality eggs than small females. Third, by preferentially catching large fish, humans have exerted an intense selective pressure on food fish species for smaller body size. This extreme selective pressure has caused a selective sweep, diminishing the variation in gene pools of many commercial fisheries (NOAA 2010). While the waters of the SBNMS are significantly cleaner than Massachusetts Bay as a whole, elevated levels of PCBs have been measured in cetaceans and seabird eggs (NOAA 2010). Additionally, iron and copper leaching from the contaminated sediments of Boston Harbor occasionally reach the preserve (Li et al 2010).
- Clark CW, Ellison WT, Southall BL, Hatch L, Van Parijs SM, Frankel A, Ponirakis D. 2009. Acoustic masking in marine ecosystems: intuitions, analysis and implication. Inter-Research Marine Ecology Progress Series 395:201-222.
- Eldredge, Maureen. 1993. Stellwagen Bank: New England’s first sanctuary. Oceanus 36:72.
- Jiang M, Brown MW, Turner JT, Kenney RD, Mayo CA, Zhang Z, Zhou M. Springtime transport and retention of Calanus finmarchicus in Massachusetts and Cape Cod Bays, USA, and implications for right whale foraging. Marine Ecology 349:183-197.
- Li L, Pala F, Mingshun J, Krahforst C, Wallace G. 2010. Three-dimensional modeling of Cu and Pb distributions in Boston Harbor, Massachusetts and Cape Cod Bays. Estuarine Coastal & Shelf Science. 88:450-463.
- National Oceanographic & Atmospheric Administration. 2010. Stellwagen Bank National Marine Sanctary Final Management Plan and Environmental Assessment. “Section IV: Resource States” pp. 51-143. http://stellwagen.noaa.gov/management/fmp/pdfs/sbnms_fmp2010_lo.pdf
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Stellwagen Bank Benthic Community
The species associated with this article partially comprise the benthic community of Stellwagen Bank, an undersea gravel and sand deposit stretching between Cape Cod and Cape Ann off the coast of Massachusetts. Protected since 1993 as part of the Stellwagen Bank National Marine Sanctuary, the bank is known primarily for whale-watching and commercial fishing of cod, lobster, hake, and other species (Eldredge 1993).
The benthic community of Stellwagen Bank is diverse and varied, depending largely on the grain size of the substrate. Sessile organisms such as bryozoans, ascidians, tunicates, sponges, and tube worms prefer gravelly and rocky bottoms, while burrowing worms, burrowing anemones, and many mollusks prefer sand or mud surfaces (NOAA 2010). Macroalgae, such as kelps, are exceedingly rare in the area — most biogenic structure along the bottom is provided by sponges, cnidarians, and worms. The dominant phyla of the regional benthos are Annelida, Mollusca, Arthropoda, and Echinodermata (NOAA 2010).
Ecologically, the Stellwagen Bank benthos contributes a number of functions to the wider ecosystem. Biogenic structure provided by sessile benthic organisms is critical for the survivorship of juveniles of many fish species, including flounders, hake, and Atlantic cod. The benthic community includes a greater than average proportion of detritivores — many crabs and filter-feeding mollusks — recycling debris which descends from the water column above (NOAA 2010). Finally, the organisms of the sea-bed are an important source of food for many free-swimming organisms. Creatures as large as the hump-backed whale rely on the benthos for food — either catching organisms off the surface or, in the whale’s case, stirring up and feeding on organisms which burrow in sandy bottoms (Hain et al 1995).
As a U.S. National Marine Sanctuary, Stellwagen Bank is nominally protected from dredging, dumping, major external sources of pollution, and extraction of mammals, birds or reptiles (Eldredge 1993). The benthic habitat remains threatened, however, by destructive trawling practices. Trawl nets are often weighted in order that they be held against the bottom, flattening soft surfaces, destroying biogenic structure, and killing large numbers of benthic organisms. There is also occasional threat from contaminated sediments dredged from Boston harbor and deposited elsewhere in the region (NOAA 2010). The region benefits from close observation by NOAA and the Woods Hole Oceanographic Institute, however, and NOAA did not feel the need to make any special recommendations for the preservation of benthic communities in their 2010 Management Plan and Environmental Assessment.
- Eldredge, Maureen. 1993. Stellwagen Bank: New England’s first sanctuary. Oceanus 36:72.
- Hain JHW, Ellis SL, Kenney RD, Clapham PJ, Gray BK, Weinrich MT, Babb IG. 1995. Apparent bottom feeding by humpback-whales on Stellwagen Bank. Marine Mammal Science 11, 4:464-479.
- National Oceanographic & Atmospheric Administration. 2010. Stellwagen Bank National Marine Sanctary Final Management Plan and Environmental Assessment. “Section IV: Resource States” pp. 51-143. http://stellwagen.noaa.gov/management/fmp/pdfs/sbnms_fmp2010_lo.pdf
- National Oceanographic & Atmospheric Administration. 2010. Stellwagen Bank National Marine Sanctary Final Management Plan and Environmental Assessment. “Appendix J: Preliminary Species List for the SBNMS” pp. 370-381. http://stellwagen.noaa.gov/management/fmp/pdfs/sbnms_fmp2010_lo.pdf
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Migration
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Riede, K. 2004 Global register of migratory species - from global to regional scales. Final Report of the R&D-Projekt 808 05 081. Federal Agency for Nature Conservation, Bonn, Germany. 329 p. (Ref. 51243)
http://www.fishbase.org/references/FBRefSummary.php?id=51243&speccode=4683
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Non-Migrant: No. All populations of this species make significant seasonal migrations.
Locally Migrant: No. No populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).
Locally Migrant: No. No populations of this species make annual migrations of over 200 km.
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Trophic Strategy
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Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba 1990 FAO species catalogue. Vol. 10. Gadiform fishes of the world (Order Gadiformes). An annotated and illustrated catalogue of cods, hakes, grenadiers and other gadiform fishes known to date. FAO Fish. Synop. 125(10). Rome: FAO. 442 p. (Ref. 1371)
http://www.fishbase.org/references/FBRefSummary.php?id=1371&speccode=25
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Food Habits
The diet of Atlantic cod is best described as opportunistic because they feed on anything they are capable of capturing. At all life stages, however, they eat primarily other animals. During the larval stage they feed on smaller organisms such as zooplankton. Juveniles feed on shrimp and other small crustaceans. Adult Atlantic cod consume squid, mussels, clams, tunicates, comb jellies, brittle stars, sand dollars, sea cucumbers, and polychaetes, and are also cannibalistic. The choice of prey included in the diet seems to play a role in determining the skin color of cod. Those that feed on crustaceans tend to appear more brownish in color whereas a blue-green pigment may be the result of a diet consisting primarily of fish.
Animal Foods: fish; mollusks; aquatic or marine worms; aquatic crustaceans; echinoderms; other marine invertebrates; zooplankton
Plant Foods: phytoplankton
Primary Diet: carnivore (Piscivore , Eats non-insect arthropods)
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- Bigelow, H.B. and Schroeder, W.C., 1953; Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba, 1990; Kjesbu, O.S., H. Kryvi, S. Sundby and P. Solemdal, 1992.
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Associations
Ecosystem Roles
The main role that Atlantic cod have in the ecosystem is their involvement in the food chain. Atlantic cod feed upon a variety of organisms such as invertebrates, crustaceans, and zooplankton. Larger marine organisms (i.e. sharks, seals) prey upon and consume Atlantic cod. The interplay between predators and prey is the key way in which cod influence their ecosystem. No information concerning specific relationships (mutualism, parasitism, etc.) was available.
- Campbell, D. 2005. "Atlantic Cod" (On-line). Marinebio.org. Accessed October 18, 2005 at http://marinebio.org/species.asp?id=206.
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Predation
Atlantic cod populations respond differently to predators depending on what region of the Atlantic Ocean they occupy. Atlantic cod are susceptible to being consumed by large marine mammals (harp and harbor seals) and sharks. In the northwest Atlantic Ocean most of the large predatory fish have been removed and cod (and similar species) act as dominant predators in this region. In other parts of the Atlantic Ocean with large harp seal populations the number of Atlantic cod has been greatly reduced due to consumption by seals. Cod larvae are vulnerable to smaller predators such as zooplankton. Juveniles are preyed on by species such as dogfish, squid, and halibut. Cannibalistic behavior becomes apparent as adult Atlantic cod readily consume juveniles. Although adult Atlantic cod have relatively few predators compared to their young, they still must be on the lookout for large marine animals. The greatest predatory threats to cod are those that lurk above the surface. Humans are responsible for drastically lowering Atlantic cod populations through well-developed fisheries. The economy of several regions is dependent upon these fisheries and the great demand for large numbers of Atlantic cod has resulted in overfishing and reduced cod stocks.
Known Predators:
- sharks (Chondrichthyes)
- harp and harbor seals (Phoca)
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Diseases and Parasites
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Froese, R., S. Rosenboom and B. Ueberschär 1982 Fischkrankheiten in Verbindung mit Umweltparametern in der westlichen Ostsee. Semesterabschlußarbeit, Institute of Marine Science, Kiel. 56 p. (Ref. 5494)
http://www.fishbase.org/references/FBRefSummary.php?id=5494&speccode=69
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Dethlefsen, V. 1989 Krankheiten des Dorsches (Gadus morhua) der Ostsee. Infn Fischw. 36(2):62-67. (Ref. 6024)
http://www.fishbase.org/references/FBRefSummary.php?id=6024&speccode=69
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Dethlefsen, V. 1989 Krankheiten des Dorsches (Gadus morhua) der Ostsee. Infn Fischw. 36(2):62-67. (Ref. 6024)
http://www.fishbase.org/references/FBRefSummary.php?id=6024&speccode=69
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Waluga, D., T. Wlasow, E. Dyner and A. Swiatecki 1986 Studies on the etiopathogenesis of fish diseases in the Baltic Sea. Acta Ichthyol. Pisc. 16(2):53-72. (Ref. 6025)
http://www.fishbase.org/references/FBRefSummary.php?id=6025&speccode=69
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Froese, R., S. Rosenboom and B. Ueberschär 1982 Fischkrankheiten in Verbindung mit Umweltparametern in der westlichen Ostsee. Semesterabschlußarbeit, Institute of Marine Science, Kiel. 56 p. (Ref. 5494)
http://www.fishbase.org/references/FBRefSummary.php?id=5494&speccode=69
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Lannan, C.N., J.L. Batholomew and J.L. Fryer 1999 Chlamydial infections of fish: Epitheliocystis. p.255-267. In P.T.K. Woo and D.W. Bruno (eds.) Fish Diseases and Disorders Vol. 3: Viral, bacterial and fungal infections. CABI Int'l. (Ref. 48851)
http://www.fishbase.org/references/FBRefSummary.php?id=48851&speccode=2594
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Haarder, S. 2012 Fish disease photos. Unpublished, personal communication. (Ref. 89841)
http://www.fishbase.org/references/FBRefSummary.php?id=89841&speccode=24
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Froese, R., S. Rosenboom and B. Ueberschär 1982 Fischkrankheiten in Verbindung mit Umweltparametern in der westlichen Ostsee. Semesterabschlußarbeit, Institute of Marine Science, Kiel. 56 p. (Ref. 5494)
http://www.fishbase.org/references/FBRefSummary.php?id=5494&speccode=69
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Larsson, P.-O. 1990 Diseases of cod observed on Swedish surveys in the Baltic. ICES C.M./E:21. (Ref. 5927)
http://www.fishbase.org/references/FBRefSummary.php?id=5927&speccode=69
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Lang, T. 1988 Hysterothylacium aduncum (Nematoda) in Baltic cod (Gadus morhua L.). ICES C.M. 1988/J:20. (Ref. 6022)
http://www.fishbase.org/references/FBRefSummary.php?id=6022&speccode=69
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General Ecology
DMS in the odor landscape of the sea
Dimethyl Sulfide or DMS is present throughout the ocean(1). It’s an important odor component of many fish and shellfish, including clams, mussels, oysters, scallops, crabs and shrimp(2-9). Where does it come from? Usually from the marine plants they feed on.
Many species of plants and algae produce DMS, but not all species produce significant amounts of it. Nearly all of these are marine, and they tend to be in closely related groups with other DMS-producers, including Chlorophyte (green) seaweeds, the Dinophyceae in the dinoflagellates, and some members of the Chrysophyceae and the Bacillariophyceae (two classes of diatoms). Other large groups, like cyanobacteria and freshwater algae, tend not to produce DMS. (10,11)
Why do these groups produce DMS? In algae, most researchers believe a related chemical, DMSP, is used by the algae for osmoregulation- by ensuring the ion concentration inside their cells stays fairly close to the salinity in the seawater outside, they prevent osmotic shock. Otherwise, after a sudden exposure to fresh water (rain at the sea surface, for instance) cells could swell up and explode. In vascular plants, like marsh grasses and sugar cane, it’s not clear what DMS is used for. (12,13)
Freshly harvested shellfish can smell like DMS because DMSP has accumulated in their tissue from the algae in their diet. Some animals, including giant Tridacna clams and the intertidal flatworm Convoluta roscoffensis, harbor symbiotic algae in their tissues, which produce DMSP; this may not be important to their symbioses, but for Tridacna, the high DMS levels can be a problem for marketing the clams to human consumers. After death, DMSP begins to break down into DMS. A little DMS creates a pleasant flavor, but high concentrations offend the human palate.(2,14)
Not all grazers retain DMS in their tissues, though. At sea, DMS is released when zooplankton feed on algae. It’s been shown in the marine copepods Labidocera aestiva and Centropages hamatus feeding on the dinoflagellate Gymnodinium nelson that nearly all the DMS in the consumed algae is quickly released during feeding and digestion.(15) This has a disadvantage for the grazing zooplankton. Marine predators, like procellariiform seabirds, harbor seals, penguins, whale sharks, cod, and coral reef fishes like brown chromis, Creole wrasse and boga, can use the smell of DMS to locate zooplankton to feed on. (8,16,17)
It’s not easy to measure how much DMS is released from the Ocean into the air every year. Recent estimates suggest 13-37 Teragrams, or 1.3-3.7 billion kilograms. This accounts for about half the natural transport of Sulfur into the atmosphere, is the conveyor belt by which Sulfur cycles from the ocean back to land. In the atmosphere, DMS is oxidized into several compounds that serve as Cloud Condensation Nuclei (CCN). The presence of CCN in the air determines when and where clouds form, which affects not only the Water cycle, but the reflection of sunlight away from the Earth. This is why climate scientists believe DMS plays an important role in regulating the Earth’s climate. (12,18)
- 1) BATES, T. S., J. D. Cline, R. H. Gammon, and S. R. Kelly-Hansen. 1987. Regional and seasonal variations in the flux of oceanic dimethylsulfide to the atmosphere. J. Geophys. Res.92: 2930- 2938
- 2) Hill, RW, Dacey, JW and A Edward. 2000. Dimethylsulfoniopropionate in giant clams (Tridacnidae). The Biological Bulletin, 199(2):108-115
- 3) Brooke, R.O., Mendelsohn, J.M., King, F.J. 1968. Significance of Dimethyl Sulfide to the Odor of Soft-Shell Clams. Journal of the Fisheries Research Board of Canada, 25:(11) 2453-2460
- 4) Linder, M., Ackman, R.G. 2002. Volatile Compounds Recovered by Solid-Phase Microextraction from Fresh Adductor Muscle and Total Lipids of Sea Scallop (Placopecten magellanicus) from Georges Bank (Nova Scotia). Journal of Food Science, 67(6): 2032–2037
- 5) Le Guen, S., Prost, C., Demaimay, M. 2000. Critical Comparison of Three Olfactometric Methods for the Identification of the Most Potent Odorants in Cooked Mussels (Mytilus edulis). J. Agric. Food Chem., 48(4): 1307–1314
- 6) Piveteau, F., Le Guen, S., Gandemer, G., Baud, J.P., Prost, C., Demaimay, M. 2000. Aroma of Fresh Oysters Crassostrea gigas: Composition and Aroma Notes. J. Agric. Food Chem., 48(10): 4851–4857
- 7) Tanchotikul, U., Hsieh, T.C.Y. 2006. Analysis of Volatile Flavor Components in Steamed Rangia Clam by Dynamic Headspace Sampling and Simultaneous Distillation and Extraction. Journal of Food Science, 56(2): 327–331
- 8) Ellingsen, O.F., Doving, K.B. 1986. Chemical fractionation of shrimp extracts inducing bottom food search behavior in cod (Gadus morhua L.). J. Chem. Ecol., 12(1): 155-168
- 9) Sarnoski, P.J., O’Keefe, S.F., Jahncke, M.L., Mallikarjunan, P., Flick, G. 2010. Analysis of crab meat volatiles as possible spoilage indicators for blue crab (Callinectes sapidus) meat by gas chromatography–mass spectrometry. Food Chemistry, 122(3):930–935
- 10) Malin, G., Kirst, G.O. 1997. Algal Production of Dimethyl Sulfide and its Atmospheric Role. J. Phycol., 33:889-896
- 11) Keller, M.D., Bellows, W.K., Guillard, R.L. 1989. Dimethyl Sulfide Production in Marine Phytoplankton. Biogenic Sulfur in the Environment. Chapter 11, pp 167–182. ACS Symposium Series, Vol. 393. ISBN13: 9780841216129eISBN: 9780841212442.
- 12) Yoch, D.C. 2002. Dimethylsulfoniopropionate: Its Sources, Role in the Marine Food Web, and Biological Degradation to Dimethylsulfide. Appl Environ Microbiol., 68(12):5804–5815.
- 13) Otte ML, Wilson G, Morris JT, Moran BM. 2004. Dimethylsulphoniopropionate (DMSP) and related compounds in higher plants. J Exp Bot., 55(404):1919-25
- 14) Van Bergeijk, S.A., Stal, L.J. 2001. Dimethylsulfonopropionate and dimethylsulfide in the marine flatworm Convoluta roscoffensis and its algal symbiont. Marine Biology, 138:209-216
- 15) Dacey , J.W.H. and Stuart G. Wakeham. 1986. Oceanic Dimethylsulfide: Production during Zooplankton Grazing on Phytoplankton. Science, 233( 4770):1314-1316
- 16) Nevitt, G. A., Veit, R. R. & Kareiva, P. (1995) Dimethyl Sulphide as a Foraging Cue for Antarctic Procellariiform Seabirds. Nature 376, 680-682.
- 17) Debose, J.L., Lema, S.C., & Nevitt, G.A. (2008). Dimethylsulfionoproprianate as a foraging cue for reef fishes. Science, 319, 1356.
- 18) Charlson, R.J., Lovelock, J.E., Andraea, M.O., Warren, S.G. 1987. Oceanic phytoplankton, atmospheric sulphur, cloud albedo and climate. Nature, 326:655-661
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Life History and Behavior
Behavior
Communication and Perception
There is limited information available on the communication among cod. Atlantic cod are hypothesized to communicate through the production of sound via drumming muscles. Sound production is correlated with mate selection during spawning season. It is hypothesized that the degree to which males are able to produce acoustic sound is positively associated with the overall fitness of the males, with those having larger drumming muscles producing greater sound waves and out-competing others.
Communication Channels: acoustic
Perception Channels: acoustic
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Life Cycle
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Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba 1990 FAO species catalogue. Vol. 10. Gadiform fishes of the world (Order Gadiformes). An annotated and illustrated catalogue of cods, hakes, grenadiers and other gadiform fishes known to date. FAO Fish. Synop. 125(10). Rome: FAO. 442 p. (Ref. 1371)
http://www.fishbase.org/references/FBRefSummary.php?id=1371&speccode=25
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Development
Atlantic cod pass through a series of four life history stages as they develop. Initially they begin as pelagic eggs which are located in harbors, bays, and offshore banks. The eggs are associated with an incubation temperature around 2 to 8.5 degrees Celsius. The eggs are buoyant and remain close to the surface waters. Studies have shown that egg mortality is independent of temperature but increases at lower salinities. Next, the larval stage takes place. Larvae are located in pelagic waters and their growth is correlated with the volume of zooplankton which can feed upon the sac larvae at this stage. During the third stage, juveniles occur in coastal and offshore waters in the summer and deeper waters in the winter. They are tolerant of temperature changes from 6 to 20 degrees Celsius and they often use vegetation as a predator avoidance strategy. The final stage is adulthood. They live at temperatures less than 10 degrees Celsius and primarily inhabit the ocean floor.
- Fahay, M., P. Berrien, D. Johnson, W. Morse. 1999. Atlantic Cod (Gadus Morhua) Life History and Habitat Characteristics. National Ocean and Atomospheric Administration Technical Memorandum, 122-152: 1-35. Accessed October 13, 2005 at http://www.nefsc.noaa.gov/nefsc/publications/tm/tm124/tm124.pdf.
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Life Expectancy
Lifespan/Longevity
Atlantic cod can reach a maximum lifespan in excess of 20 years, with a minimum lifespan of a few hours/days (shortly after the eggs are released). Within the last 100 years typical lifespans have changed drastically as a result of commercial cod fisheries. Most recently, fisheries have begun harvesting younger fish.
Range lifespan
Status: wild: 0 to 20 years.
Average lifespan
Status: wild: 16.0 years.
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Reproduction
There is a limited amount of information on Atlantic cod spawning behavior which may suggest complex mating systems. Researchers are aware that mating behavior in Atlantic cod can include reproductive strategies such as sound production by males and mate selection by females. Although these behaviors have been observed, the causes and consequences of such behavior, and their specific interplay within the mating systems continue to be studied. Atlantic cod are considered "batch-spawners", as females only release 5 to 25% of their total egg complement at any time.
One study on the acoustic sound production of Atlantic cod provides some insight into possible mating behaviors. Drumming muscles are present in both males and females, yet males tend to have more pronounced muscles. The mass of the drumming muscles increases in males prior to spawning and larger males have larger muscles. This suggests that the amplitude of sound production might be a determinant in the success of spawning and selection by females. Observations of Atlantic cod behavior support the hypothesis that females are responsible for mate selection. The biology of the drumming muscles in males, as well as the circling behavior of numerous males around prospective females supports the female selection hypothesis. It is worth noting that dominance hierarchies can also be established. Males with greater body sizes and those who were successful in spawning sometimes appear to dominate the population and act aggressively towards “lesser” males.
Recent research suggests that anthropogenic noise pollution in the water (via oil/gas exploration and drilling) could pose a threat to the success of sound production and the role it plays in the reproduction process.
Mating System: polygynandrous (promiscuous)
Many stocks of cod exhibit migratory behavior during their reproduction season due to seasonal variations in water temperature. Typically, a cod population moves into warmer waters during winter and early spring to begin spawning. Although spawning can occur year round, peak spawning levels occur in the winter and spring. As the population moves inshore it may disperse temporarily to feed if large amounts of prey are present. Cod spawn annually, and spawning takes place within a three month period. Cod employ a ventral mount position in which a male uses his pelvic fins to clasp onto a female and then position himself properly beneath her. Cod spawn in dense concentrations of more than 1 fish per cubic meter and multiple pairs of fish can be observed spawning in the same water column. Spawning occurs near the ocean bottom in temperatures between 5 to 7 degrees Celsius. The eggs that are produced are pelagic, and drift (often towards the surface) for approximately 2 to 3 weeks before hatching and reaching the larval stage. There is some debate as to the age of sexual maturity for cod. Age and size at maturity often vary amongst different populations with northeastern populations maturing around 5 to 7 years and southern populations maturing between 2 to 3 years. A recent finding suggests that cod are moving towards a reduction in age and size for sexually mature fish. In 1959 the median age of maturity was 6.3 years for females and 5.4 years for males. In 1979 the age of maturity was listed as 2.8 years for both sexes. Now, the median age of sexual maturity is between 1.7 to 2.3 years and corresponds to a length of 32 to 41 cm.
Breeding interval: Spawning takes place once a year for a duration of 3 weeks to 3 months.
Breeding season: Breeding csn occur year round; peak spawning recorded in winter/spring months.
Range number of offspring: 9 million (high) .
Average time to hatching: 2 to 3 weeks.
Range age at sexual or reproductive maturity (female): 1.7 to 5.4 years.
Range age at sexual or reproductive maturity (male): 1.7 to 7 years.
Key Reproductive Features: iteroparous ; year-round breeding ; gonochoric/gonochoristic/dioecious (sexes separate); sexual ; fertilization (External ); oviparous
There is no indication that any parental involvement exists on the behalf of either females or males after the eggs are released. The high mortality rate of the offspring (eggs) is attributed, in part, to the lack of parental care. The reproductive strategy of high fecundity levels may be a response to the absence of protection the eggs receive once released into the water. Although the survival rate is low, the sheer number of eggs produced is huge.
Parental Investment: no parental involvement; pre-fertilization (Provisioning, Protecting: Female)
- Committee on the Status of Endangered Wildlife in Canada (COSEWIC). Assessment and Update Report on Gadus Morhua (Atlantic Cod). xi + 76pp. Ottawa: COSEWIC. 2003. Accessed October 17, 2005 at http://www.sararegistry.gc.ca/virtual_sara/files/cosewic/sr_atlantic_cod_e.pdf.
- Fahay, M., P. Berrien, D. Johnson, W. Morse. 1999. Atlantic Cod (Gadus Morhua) Life History and Habitat Characteristics. National Ocean and Atomospheric Administration Technical Memorandum, 122-152: 1-35. Accessed October 13, 2005 at http://www.nefsc.noaa.gov/nefsc/publications/tm/tm124/tm124.pdf.
- Rowe, S., J. Hutchings. 2004. The function of sound production by Atlantic Cod as inferred from patterns in variation of drumming muscle mass. Canadian Journal of Zoology, 82: 1391-1398. Accessed October 17, 2005 at http://article.pubs.nrc-cnrc.gc.ca/ppv/RPViewDoc?_handler_=HandleInitialGet&journal=cjz&volume=82&calyLang=eng&articleFile=z04-119.pdf.
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- Bigelow, H.B. and Schroeder, W.C., 1953; Cohen, D.M., T. Inada, T. Iwamoto and N. Scialabba, 1990; Kjesbu, O.S., H. Kryvi, S. Sundby and P. Solemdal, 1992.
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Molecular Biology and Genetics
Molecular Biology
Barcode data: Gadus morhua
There are 8 barcode sequences available from BOLD and GenBank. Below is a sequence of the barcode region Cytochrome oxidase subunit 1 (COI or COX1) from a member of the species. See the BOLD taxonomy browser for more complete information about this specimen and other sequences.
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Download FASTA File
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Statistics of barcoding coverage: Gadus morhua
Public Records: 22
Specimens with Barcodes: 91
Species With Barcodes: 1
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Conservation
Conservation Status
IUCN Red List Assessment
Red List Category
Red List Criteria
Version
Year Assessed
- Needs updating
Assessor/s
Reviewer/s
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Atlantic cod was listed as a vulnerable species in 1996. In the early 1990’s many cod populations collapsed in areas where commercial fishing was intense. The collapse is attributed to overfishing, and specifically to the commercial fishing of older/larger cod which resulted in a smaller population of fertile females and the harvesting of young fish before they have had a chance to mature and reproduce. The prosperity that fishermen enjoyed prior to the collapse lured many into the commercial fisheries and as a result the cod population was negatively affected.
Some efforts have been made to help certain cod populations rebound. Moratoriums and fishing regulations were placed in regions of Canada but were unsuccessful in maintaining or increasing population size. The main deterrent in properly managing cod stocks relates to the geographic range which the cod occupy. Cod are found throughout the waters of the Atlantic, and since these are international waters it makes it difficult for any one region to impose certain regulations. Research shows that populations can easily fall below the “Safe Biological Limits,” which represent the number of fish needed to maintain a proper population. Biologists argue that regulation alone will not be enough to keep the cod population at a sustainable level, but it is a start. Suggestions such as no-catch zones in areas of spawning and along migration routes may be helpful if enacted. As cod stocks move towards critically low levels, it is apparent that serious conservation efforts must be put into place to prevent the devastation of this important fish species.
US Federal List: no special status
CITES: no special status
IUCN Red List of Threatened Species: vulnerable
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National NatureServe Conservation Status
Canada
Rounded National Status Rank: N3 - Vulnerable
United States
Rounded National Status Rank: NNR - Unranked
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Status
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Threats
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IUCN 2006 2006 IUCN red list of threatened species. www.iucnredlist.org. Downloaded July 2006.
http://www.fishbase.org/references/FBRefSummary.php?id=57073
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Comments: In Canada, threats to persistence include fishing (now halted), predation by fish and seals, and natural and fishing-induced changes to the ecosystem; Cod in Arctic waters, which occur mostly in a few coastal salt lakes, are sensitive to human activities, and poorly regulated fishing is a potential threat (COSEWIC, May 2003, http://www.cosewic.gc.ca/htmlDocuments/Detailed_Species_Assessment_e.htm).
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Management
Conservation
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Relevance to Humans and Ecosystems
Benefits
Importance
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Garibaldi, L. 1996 List of animal species used in aquaculture. FAO Fish. Circ. 914. 38 p. (Ref. 12108)
http://www.fishbase.org/references/FBRefSummary.php?id=12108&speccode=4683
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International Game Fish Association 1991 World record game fishes. International Game Fish Association, Florida, USA. (Ref. 4699)
http://www.fishbase.org/references/FBRefSummary.php?id=4699&speccode=2590
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Food and Agriculture Organization of the United Nations 1992 FAO yearbook 1990. Fishery statistics. Catches and landings. FAO Fish. Ser. (38). FAO Stat. Ser. 70:(105):647 p. (Ref. 4931)
http://www.fishbase.org/references/FBRefSummary.php?id=4931&speccode=228
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Kinzer, J. 1983 Aquarium Kiel: Beschreibungen zur Biologie der ausgestellten Tierarten. Institut für Meereskunde an der Universität Kiel. pag. var. (Ref. 12253)
http://www.fishbase.org/references/FBRefSummary.php?id=12253&speccode=2501
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Economic Importance for Humans: Negative
Although Atlantic cod have been an economic asset to humans, they can also create problems for economies based solely on cod fisheries. Those who depend upon the success of cod fisheries as a source of income can be hurt financially if fisheries fail. The collapse of the cod fisheries in the 1990’s took a toll on the economies of New England and Canada. In this case, the stocks were not managed properly and resulted in a 96% decrease in population size since 1850. Fishermen who rely on the cod population to make a living are left with financial burdens when the stock collapses.
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Economic Importance for Humans: Positive
Atlantic cod provide an extremely important fishery in many regions especially in the northwest Atlantic. The success of this commercial fishery has been the main source of economic wealth for areas such as New England and Canada, with Atlantic cod even being labeled “Newfoundland currency”. Up until the 1990’s, Atlantic cod was not only an economic mainstay for many people but also a dominant member of the food chain within the waters of the Atlantic. Atlantic cod is marketed widely, primarily for human consumption. The flesh is mild and Atlantic cod are a popular table fish. The liver of Atlantic cod is also processed to produce cod liver oil which is used as a vitamin supplement.
Positive Impacts: food
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Atlantic Cod with Miso
I hope that you will give this recipe a try, because it’s definitely worth the time and effort.
There are essentially only 4 ingredients that you will need to marinate the fish.
Combine 1/4 cup sake, 1/4 cup mirin, 4 tbsp of miso paste, and 3 tbsp of sugar.
Take 4 pieces of cod and put it into a ziploc bag with the miso marinade. Leave it in the fridge overnight.
When it's ready to be cooked, sear both sides of the cod on a skillet until you see the highlights of sugar caramelization.
The fish goes into a 400-degree oven for about 7-10 minutes.
We wanted to add a side of vegetables with our fish, so we made honey-ginger carrots. Julienne the carrots and blanch them in boiling water for about 5-7 minutes until soft. Melt 2 tbsp of butter together with 1 tbsp honey and 1 tbsp minced ginger. Then add the carrots and mix together.
Place the cod on a bed of honey-ginger carrots and drizzle with some of the marinade (heat the marinade in the skillet first since it touched raw fish).
You will be amazed at how delicate and refreshing the flavors are. This is surely one of my favorite fish recipes.
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Wikipedia
Atlantic cod
The Atlantic cod (Gadus morhua) is a well-known benthopelagic food fish belonging to the family Gadidae. It is also commercially known as cod, codling or haberdine.[2]
In the western Atlantic Ocean, cod has a distribution north of Cape Hatteras, North Carolina, and around both coasts of Greenland; in the eastern Atlantic, it is found from the Bay of Biscay north to the Arctic Ocean, including the Baltic Sea, the North Sea, Sea of the Hebrides,[3] areas around Iceland and the Barents Sea.
It can grow to 2 meters in length and weigh up to 96 kilograms (210 lb). It can live for 25 years and sexual maturity is generally attained between ages two and four,[4] but can be as late as eight years in the northeast Arctic.[5] Colouring is brown to green, with spots on the dorsal side, shading to silver ventrally. A lateral line is clearly visible. Its habitat ranges from the shoreline down to the continental shelf.
Several cod stocks collapsed in the 1990s (declined by >95% of maximum historical biomass) and have failed to recover even with the cessation of fishing.[6] This absence of the apex predator has led to a trophic cascade in many areas.[6] Many other cod stocks remain at risk. The "Atlantic cod" is labelled VU (vulnerable) on the IUCN Red List of Threatened Species.[7]
Contents |
Lifecycle [edit]
Adult cod form spawning aggregations from late winter to spring.[8][9] Females release their eggs in batches,[10] and males compete to fertilize them.[11][12][13] Fertilized eggs drift with ocean currents and develop into larvae. Age of maturation varies between cod stocks, from ages two to four in the west Atlantic,[14] but as late as eight years in the northeast Arctic.[5] Cod can live for 13 years or more.[15]
Parasites [edit]
Atlantic cod act as intermediate, paratenic or definitive hosts to a large number of parasite species: 107 taxa listed by Hemmingsen and MacKenzie (2001)[16] and seven new records by Perdiguero-Alonso et al. (2008).[16] The predominant groups of cod parasites in the northeast Atlantic were trematodes (19 species) and nematodes (13 species), including larval anisakids, which comprised 58.2% of the total number of individuals.[16] Parasites of Atlantic cod include copepods, digeneans, monogeneans, acanthocephalans, cestodes, nematodes, myxozoans and protozoans:[16]
Fisheries [edit]
Northwest Atlantic cod [edit]
The northwest Atlantic cod has been regarded as heavily overfished throughout its range, resulting in a crash in the fishery in the United States and Canada during the early 1990s.
Newfoundland's northern cod fishery can be traced back to the 16th century. On average, about 300,000 tonnes of cod were landed annually until the 1960s, when advances in technology enabled factory trawlers to take larger catches. By 1968, landings for the fish peaked at 800,000 tonnes before a gradual decline set in. With the reopening of the limited cod fisheries in 2006, nearly 2,700 tonnes of cod were hauled in. In 2007, offshore cod stocks were estimated at one per cent of what they were in 1977.[18]
Technologies that contributed to the collapse of Atlantic cod include engine-powered vessels and frozen food compartments aboard ships. Engine-powered vessels had larger nets, greater range, and better navigation. The capacity to catch fish became limitless. In addition, sonar technology gave an edge to catching and detecting fish. Sonar was originally developed during WWII to locate enemy submarines, but was later applied to locating schools of fish. These new technologies, as well as bottom trawlers that destroyed entire ecosystems, contributed to the collapse of Atlantic cod. They were vastly different from old techniques used, such as hand lines and long lines.[19]
The fishery has yet to recover, and may not recover at all because of a possibly stable change in the food chain. Atlantic cod was a top-tier predator, along with haddock, flounder and hake, feeding upon smaller prey, such as herring, capelin, shrimp and snow crab.[6] With the large predatory fish removed, their prey have had population explosions and have become the top predators, affecting the survival rates of cod eggs and fry.
In the winter of 2011-2012, the cod fishery succeeded in convincing NOAA to postpone for one year the planned 82% reduction in catch limits. Instead the limit will be reduced by 22%. The fishery brought in $15.8 million in 2010, coming second behind Georges Bank haddock among the region’s 20 regulated bottom-dwelling groundfish. Data released in 2011 indicated that even closing the fishery would not allow populations to rebound by 2014 to levels required under federal law. Restrictions on cod effectively limit fishing on other groundfish species with which the cod swim, such as flounder and haddock.[21]
Cod populations or stocks can differ significantly both in appearance and biology. For instance, the cod stocks of the Baltic Sea are adapted to low-salinity water. Organisations such as the Northwest Atlantic Fishery Organization (NAFO) and ICES divide the cod into management units or stocks; however, these units are not always biologically distinguishable stocks. Some major stocks/management units on the Canadian/US shelf (see map of NAFO areas) are the Southern Labrador-Eastern Newfoundland stock (NAFO divisions 2J3KL), the Northern Gulf of St. Lawrence stock (NAFO divisions 3Pn4RS), the Northern Scotian Shelf stock (NAFO divisions 4VsW), which all lie in Canadian waters, and the Georges Bank and Gulf of Maine stocks in United States waters. In the European Atlantic, the numerous separate stocks are on the shelves of Iceland, the coast of Norway, the Barents Sea, the Faroe Islands, off western Scotland, the North Sea, the Irish Sea, the Celtic Sea and in the Baltic Sea.
Northeast Atlantic cod [edit]
The northeast Atlantic has the world's largest population of cod. By far, the largest part of this population is the northeast Arctic cod, as it is labelled by the ICES, or the Arcto-Norwegian cod stock, also referred to as skrei, a Norwegian name meaning something like "the wanderer", distinguishing it from coastal cod. The northeast Arctic cod is found in the Barents Sea area. This stock spawns in March and April along the Norwegian coast, about 40% around the Lofoten archipelago. Newly hatched larvae drift northwards with the coastal current while feeding on larval copepods. By summer, the young cod reach the Barents Sea where they stay for the rest of their life, until their spawning migration. As the cod grow, they feed on krill and other small crustaceans and fish. Adult cod primarily feed on fish such as capelin and herring. The northeast Arctic cod also shows cannibalistic behaviour. Estimated stock size was 2.26 million tonnes in 2008.
The North Sea cod stock is primarily fished by European Union member states and Norway. In 1999, the catch was divided among Denmark (31%), Scotland (25%), the rest of the United Kingdom (12%), the Netherlands (10%), Belgium, Germany and Norway (17%). In the 1970s, the annual catch rose to between 200,000 and 300,000 tons. Due to concerns about overfishing, catch quotas were repeatedly reduced in the 1980s and 1990s. In 2003, ICES stated there is a high risk of stock collapse if then current exploitation levels continued, and recommended a moratorium on catching Atlantic cod in the North Sea during 2004. However, agriculture and fisheries ministers from the Council of the European Union endorsed the EU/Norway Agreement and set the total allowable catch (TAC) at 27,300 tons. Seafood sustainability guides, such as the Monterey Bay Aquarium's Seafood Watch, often recommend environmentally conscious customers not purchase Atlantic cod.
The stock of northeast Arctic cod was more than a million tons following World War II, but declined to a historic minimum of 118,000 tons in 1987. The catch reached a historic maximum of 1,343,000 tons in 1956, and bottomed out at 212,000 tons in 1990. Since 2000, the spawning stock has increased quite quickly, helped by low fishing pressure. However, there are worries about a decreased age at first spawning (often an early sign of stock collapse), combined with the level of discards and unreported catches. The total catch in 2003 was 521,949 tons, the major fishers being Norway (191,976 tons) and Russia (182,160 tons).
See also [edit]
References [edit]
This article incorporates CC-BY-2.0 text from the reference.[16]
- ^ J. Sobel (1996). "Gadus morhua". IUCN Red List of Threatened Species. Version 2.3. International Union for Conservation of Nature. Retrieved July 5, 2011.
- ^ Atlantic Cod. Seafood Portal.
- ^ C.Michael Hogan, (2011) Sea of the Hebrides. Eds. P. Saundry & C.J.Cleveland. Encyclopedia of Earth. National Council for Science and the Environment. Washington DC.
- ^ O’Brien, L., J. Burnett, and R. K. Mayo. (1993) Maturation of Nineteen Species of Finfish off the Northeast Coast of the United States, 1985-1990. NOAA Tech. Report. NMFS 113, 66 p.
- ^ a b ICES (2007), Arctic Fisheries Working Group Report, Section 03, Table 3.5, International Council for the Exploration of the Sea (accessed 2008/12/11)
- ^ a b c Kenneth T. Frank, Brian Petrie, Jae S. Choi, William C. Leggett (2005). "Trophic Cascades in a Formerly Cod-Dominated Ecosystem". Science 308 (5728): 1621–1623. doi:10.1126/science.1113075. PMID 15947186.
- ^ J. Sobel (1996). "Gadus morhua". IUCN Red List of Threatened Species. Version 2009.2. International Union for Conservation of Nature. Retrieved February 5, 2010.
- ^ K. M. Brander (1994). "The location and timing of cod spawning around the British Isles". ICES Journal of Marine Science 51 (1): 71–89. doi:10.1006/jmsc.1994.1007.
- ^ Kai Wieland, Astrid Jarre-Teichmann & Katarzyna Horbowa (2000). "Changes in the timing of spawning of Baltic cod: possible causes and implications for recruitment". ICES Journal of Marine Science 57 (2): 452–464. doi:10.1006/jmsc.1999.0522.
- ^ Scott, Beth E.; Marteinsdottir, Gudrun; Begg, Gavin A.; Wright, Peter J.; Kjesbu, Olav Sigurd (2005). "Effects of population size/age structure, condition and temporal dynamics of spawning on reproductive output in Atlantic cod (Gadus morhua)". Ecological Modelling 191 (3-4): 383–415. doi:10.1016/j.ecolmodel.2005.05.015.
- ^ J. A. Hutchings, T. D. Bishop, C. R. McGregor-Shaw (1999). "Spawning behaviour of Atlantic cod, Gadus morhua: evidence of mate competition and mate choice in a broadcast spawner". Canadian Journal of Fisheries and Aquatic Sciences 56 (1): 97–104. doi:10.1139/cjfas-56-1-97.
- ^ J. T. Nordeide; Folstad (2000). "Is cod lekking or a promiscuous group spawner?". Fish and Fisheries 1 (1): 90–93. doi:10.1046/j.1467-2979.2000.00005.x.
- ^ D. Bekkevold, M. M. Hansen & V. Loeschcke (2002). "Male reproductive competition in spawning aggregations of cod". Molecular Ecology 11 (1): 91–102. doi:10.1046/j.0962-1083.2001.01424.x. PMID 11903907.
- ^ O'Brien, L., J. Burnett, and R. K. Mayo. (1993) Maturation of Nineteen Species of Finfish off the Northeast Coast of the United States, 1985-1990. NOAA Tech. Report. NMFS 113, 66 p.
- ^ ICES (2007), Arctic Fisheries Working Group Report, Section 03, International Council for the Exploration of the Sea (accessed 2008/12/11)
- ^ a b c d e Perdiguero-Alonso D., Montero F. E., Raga J. A. & Kostadinova A. (2008). "Composition and structure of the parasite faunas of cod, Gadus morhua L. (Teleostei: Gadidae), in the North East Atlantic". Parasites & Vectors 2008, 1: 23. doi:10.1186/1756-3305-1-23
- ^ Gadus morhua (Linnaeus, 1758) FAO, Species Fact Sheet. Retrieved April 2012.
- ^ "N.L. funds cod fishery research on 15th anniversary of moratorium". CBC News. July 2, 2007.
- ^ Freedman, Bill. "Atlantic Cod and its fishery". Codfishes: Atlantic Cod and its fishery, 2008. 3 November 2008 Free Site Search Engine
- ^ Atlantic cod NOAA FishWatch. Retrieved 5 November 2012.
- ^ "Cod Fishermen’s Alarm Outlasts Reprieve on Catch Limits". The New York Times. 12 February 2012.
- ^ Arctic Fisheries Working Group of ICES, published in the ICES Report AFWG CM 2009, ACOM:2. The estimation method was standard VPA.
Unreviewed
Names and Taxonomy
Taxonomy
Comments: DNA data for western North Atlantic populations reveal weak population genetic structuring that may reflect the recent age of populations rather than extensive gene flow among populations (Pogson et al. 2001).
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