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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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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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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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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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Poll, M. (1945). Contribution à la connaissance de la faune ichtyologique du Bas-Escaut. Bull. Mus. royal d'Hist. Nat. Belg./Med. Kon. Natuurhist. Mus. Belg. 21(11): 1-32
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1641
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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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Leloup, E. (1951). Contributions à l'étude de la faune belge: 18. Observations sur des poissons marins en 1949. Med. K. Belg. Inst. Nat. Wet. 27(4): 1-12
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1661
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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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Janssens, J.G. (1984). Excursion to Sas van Goes on 25.08.84 [Excursie naar Sas van Goes op 25.08.84]. De Strandvlo 4(3): 62-64
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=141407
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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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Beyst, B. (2001). Epi- en hyperbenthische gemeenschappen van Belgische zandstranden [Epi- and hyperbenthic communities of Belgian sandy beaches]. PhD Thesis. Universiteit Gent. Instituut voor Dierkunde. Vakgroep morfologie, systematiek en ecologie: Gent, Belgium. 351 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=811
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Mees, J. (1994). Het hyperbenthos van ondiepe kustgebieden en estuaria: gemeenschapsstruktuur en biologie van de dominante soorten [The hyperbenthos of shallow coastal waters and estuaries: community structure and biology of the dominant species]. PhD Thesis. Universiteit Gent. Mariene Biologie. Instituut voor Dierkunde. Vakgroep Morfologie, Systematiek en Ecologie: Gent, Belgium. 212 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=815
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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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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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Borges, P.A.V., Costa, A., Cunha, R., Gabriel, R., Gonçalves, V., Martins, A.F., Melo, I., Parente, M., Raposeiro, P., Rodrigues, P., Santos, R.S., Silva, L., Vieira, P. & Vieira, V. (Eds.) (2010). A list of the terrestrial and marine biota from the Azores. Princípia, Oeiras, 432 pp.
http://www.marinespecies.org/ascidiacea/aphia.php?p=sourcedetails&id=149079
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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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Galil, B.; Goren, M.; Mienis, H. (2011). Checklist of marine species in Israel. Compiled in the framework of the EU FP7 PESI project.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=149096
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A.Boltachev & E. Karpova, IBSS NAS Ukraine
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=149025
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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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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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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Range Description
Anguilla anguilla is found in all European rivers draining to the Mediterranean, North and Baltic seas, in the Atlantic south to Canary Islands and parts of Mediterranean north Africa and Asia. It very rarely enters the White and Barents seas, but is recorded eastward to the Pechora River in northwest Russia. The species occurs in low abundance in the Black Sea where it migrates east to the Kuban drainage (occasional individuals reach the Volga drainage through canals), in northern Scandinavia and eastern Europe, but 'trap-and-transport' stocking is interfering with natural population numbers (W. Dekker pers. comm. 2007). Large parts of the population remain at sea particularly in the north western Atlantic and Mediterranean. It is also widely stocked in most inland waters of Europe.
The species is thought to breed in the Sargasso Sea in the West Central Atlantic, migrating across the Atlantic from Europe.
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Geographic Range
The geographic range of adult European eels includes the English Channel and coasts of the Mediterranean Sea and northern Atlantic Ocean from Iceland to Mauritania (Ringuet et al., 2002). Their range also encompasses the Baltic and North Seas, as well as all accessible continental or coastal hydrosystems (Ringuet et al., 2002). In the early spring months, European eels migrate to the Sargasso sea for breeding. Larvae are hatched from the Sargasso Sea and can also be found along the coast of Europe. Silver (juvenile) stage eels of Anguilla anguilla live in tributaries along the European coast.
Biogeographic Regions: palearctic (Native ); atlantic ocean (Native ); mediterranean sea (Native )
- Tsukamoto, K., I. Nakai, W. Tesch. 1998. Do all freshwater eels migrate?. Nature, 396: 635-636.
- Ringuet, S., F. Muto, C. Raymakers. 2002. Eels: Their Harvest and Trade in Europe and Asia. Traffic Bulletin, 19/2: 2-27.
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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Range
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Physical Description
Morphology
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Bauchot, M.-L. 1986 Anguillidae. p. 535-536. In P.J.P. Whitehead, M.-L. Bauchot, J.-C. Hureau, J. Nielsen and E. Tortonese (eds.) Fishes of the north-eastern Atlantic and the Mediterranean. volume 2. UNESCO, Paris. (Ref. 6125)
http://www.fishbase.org/references/FBRefSummary.php?id=6125&speccode=35
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Physical Description
The appearance of European eels varies greatly depending on life stage. As leptocephali, European eels are small, leaflike, and transparent (Deelder, 1970). After metamorphosing into the silver stage, European eels appear silvery in color with elongated dorsal and anal fins that are continuous with the caudal fin (Deelder, 1970). European eels lack pelvic fins (Deelder, 1970). Upon full sexual maturation, European eels develop enlarged eyes, lose their ability to feed, and turn green, yellow or brownish in color (Van Ginniken and Thillhart, 2000).
Female eels are generally substantially larger than males. The largest recorded mass of a female eel is 6.599 g (Dekker, van Os and van Willigen, 1998). The maximum published length of a European eel was 133 cm.
Range mass: 6,599 (high) g.
Range length: 133 (high) cm.
Other Physical Features: ectothermic ; heterothermic ; bilateral symmetry
Sexual Dimorphism: female larger
- Van Ginneken, V., G. Van Den Thillart. 2000. Physiology: Eel fat stores are enough to reach the Sargasso. Nature, 403: 156-157.
- Dekker, W., B. van Os, J. van Willigen. 1998. Minimal and maximal size of eel.. L'ANGUILLE EUROPENNE. 10E REUNION DU GROUPE DE TRAVAIL "ANGUILLE" EIFAC/ICES..
- Deelder, C. 1970. Synopsis of biological data of the eel Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop., 80: 68.
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Size
Max. size
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Castle, P.H.J. 1984 Anguillidae. p. 34-37. In J. Daget, J.-P. Gosse and D.F.E. Thys van den Audenaerde (eds.) Check-list of the freshwater fishes of Africa (CLOFFA). ORSTOM, Paris and MRAC, Tervuren. Vol. 1. (Ref. 3506)
http://www.fishbase.org/references/FBRefSummary.php?id=3506&speccode=1274
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Bobick, J.E. and M. Peffer 1993 Science and technology desk reference. Gale Research Inc. (Ref. 72468)
http://www.fishbase.org/references/FBRefSummary.php?id=72468&speccode=35
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Dekker, W., B. van Os and J. van Willigen 1998 Minimal and maximal size of eel. L'ANGUILLE EUROPEENNE. 10E REUNION DU GROUPE DE TRAVAIL "ANGUILLE" EIFAC/ICES.Bulletin Francais de Peche et Pecherie, Conseil superieur de la peche, Paris (France), 1998. (Ref. 39903)
http://www.fishbase.org/references/FBRefSummary.php?id=39903&speccode=35
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Diagnostic Description
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Bauchot, M.-L. 1986 Anguillidae. p. 535-536. In P.J.P. Whitehead, M.-L. Bauchot, J.-C. Hureau, J. Nielsen and E. Tortonese (eds.) Fishes of the north-eastern Atlantic and the Mediterranean. volume 2. UNESCO, Paris. (Ref. 6125)
http://www.fishbase.org/references/FBRefSummary.php?id=6125&speccode=35
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Ecology
Habitat
Seine River Demersal Habitat
This taxon is one of a number of demersal species in the Seine River system of Western Europe. Demersal river fish are found at the river bottom, feeding on benthos and zooplankton
The Marne and Yonne exhibit the greatest torrential flows, due to the percentage of their courses underlain by impermeable strata, in combination with the river gradients. Although the Loing manifests the highest percentage of impermeable strata of all the tributaries, its low gradient mitigates against torrential velocities. Thus the majority of the Seine and its tributaries exhibit a relaxed generally even flow rate.
Seine water pollutant loads of heavy metals, nutrients, sediment and bacteria are relatively high, especially influnced by wastewater and surface runoff from Paris and its suburbs. Parisian pollutant loadings are noted to be particularly high during periods of high rainfall, not only due to high runoff, but also from the inadequate sewage treatment facilities in periods of high combined wastewater/stormwater flow.
Heavy metal concentrations at Poses weir reveal the following levels: copper, 1.9 milligrams per liter; cadmium, 32 mg/l; and lead, 456 mg/l. Concentrations of zinc are also quite high, making the Seine Estuary one of the most highly contaminated estuaries in the world with respect especially to lead and cadmium. Significant amounts of toxic pollutants are also attached to sediments deposited in the Seine during the last two centuries, including mercury, nickel, chromium, toluene, DDT and a variety of herbicides and pesticides. Downriver from Paris, significant quantites of ammonium are discharged into the Seine from effluent of the Achères wastewater treatment plant.
There are a total of 37 fish species inhabiting the Seine, and another two taxa that are known to have been extirpated in modern times. Two of the largest aquatic fauna known to have lived in the Seine are now locally extinct: the 500 centimeter (cm) long sturgeon (Acipenser sturio) and the 83 cm long allis shad (Alosa alosa).
The largest extant native demersal (species living on or near the river bottom) taxa in the Seine are:
the 133 cm European eel (Anguilla anguilla);
the 150 cm northern pike (Esox lucius);
the 120 cm sea lamprey (Petromyzon marinus); and,
the 152 cm Burbot (Lota lota).
- C.Michael Hogan. 2012. ''Seine River. Encyclopedia of Earth, National Council for Science and the Environment, Washington DC ed. Peter Saundry; ed.in-chief C.M.Hogan
- Fishbase. 2010. Species in Seine
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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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Matallanas, J. 2005 A world overview of species of interest to fisheries. Chapter: Anguilla anguilla. Retrieved on 05 May 2005, from www.fao.org/figis/servlet/species?fid=2203. 4p. FIGIS Species Fact Sheets. Species Identification and Data Programme-SIDP, FAO-FIGIS (Ref. 54218)
http://www.fishbase.org/references/FBRefSummary.php?id=54218&speccode=35
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Habitat and Ecology
The species is found in all types of benthic habitats from small streams to shores of large rivers and lakes. Naturally it only occurs in water bodies that are connected to the sea; it is stocked elsewhere.
Biology:
The species is catadromous, living in fresh water but migrating to marine waters to breed. While its life in freshwaters are well understood, relatively little is known about its life history at sea. The spawning peaks at the beginning of March continuing until July, and the adults probably die after spawning. There are no concrete data about specific spawning, however, it is assumed that spawning takes place only in an elliptic zone, about 2,000 km wide in the Sargasso Sea, in the West Central Atlantic (about 26°N 60°W). The mechanisms by which leptocephali reach the European coasts are not also well understood. By the time the leptocephali reach the continental slope they are about 70 mm in size and metamorphose into glass-eels which are almost adult in appearance, but have a transparent body, and enter estuaries. These glass-eels are observed in the autumn on Portuguese coasts, and in winter and spring in the North Sea. The generation length of the species varies greatly and ranges from 2 to 50 years, and having a typical mean of 20 years with females being twice the size and age of males (W. Dekker pers. comm. 2007).
Systems
- Freshwater
- Marine
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Depending on the lifestage of the individual eel, European eels can be found in marine, freshwater, and brackish aquatic environments. Typically, the European eel is found in depths of 0-700 m, most often on the floor of the ocean or river in which it is living.
Range depth: 0 to 700 m.
Habitat Regions: saltwater or marine ; freshwater
Aquatic Biomes: benthic ; coastal ; brackish water
Other Habitat Features: estuarine
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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 210 samples.
Environmental ranges
Depth range (m): -9 - 615
Temperature range (°C): 3.141 - 21.403
Nitrate (umol/L): 0.194 - 17.847
Salinity (PPS): 6.114 - 38.613
Oxygen (ml/l): 2.113 - 8.276
Phosphate (umol/l): 0.035 - 1.740
Silicate (umol/l): 0.885 - 50.947
Graphical representation
Depth range (m): -9 - 615
Temperature range (°C): 3.141 - 21.403
Nitrate (umol/L): 0.194 - 17.847
Salinity (PPS): 6.114 - 38.613
Oxygen (ml/l): 2.113 - 8.276
Phosphate (umol/l): 0.035 - 1.740
Silicate (umol/l): 0.885 - 50.947
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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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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Trophic Strategy
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Food Habits
European eels have completely different diets during different life stages. No food contents have ever been discovered in the guts of leptocephali, therefore their diet is unknown (Fisheries Global Information System, 2005). Glass eels consume insect larvae, dead fish, and small crustaceans (Sinha and Jones, 1975). Adult eels have a fairly broad diet and eat freshwater, marine, or terrestrial fauna. Their primary food source is aquatic invertebrates, but they will eat essentially any food they can find-- even dead organisms (Sinha and Jones, 1975). European eels are reported to leap out of the water during the winter and feed on terrestrial invertebrates (Deedler, 1970).
Animal Foods: fish; eggs; carrion ; insects; mollusks; terrestrial worms; aquatic or marine worms; aquatic crustaceans; zooplankton
Other Foods: detritus
Primary Diet: carnivore (Insectivore , Eats non-insect arthropods, Molluscivore , Eats other marine invertebrates, Scavenger )
- Sinha, V., J. Jones. 1975. The European Freshwater Eel. Liverpool: Liverpool University Press.
- 2001. "Fisheries Global Information System" (On-line). Accessed December 01, 2005 at http://www.fao.org/figis/servlet/species?fid=2203.
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Associations
Animal / parasite / endoparasite
Acanthocephalus lucii endoparasitises anterior intestine of Anguilla anguilla
Animal / parasite / endoparasite
metacaria (diplostomula) of Diplostomum spathaceum endoparasitises eye (lens) of Anguilla anguilla
Animal / parasite / ectoparasite
Ergasilus gibbus ectoparasitises gill of Anguilla anguilla
Animal / parasite / endoparasite
Trypanosoma granulosum endoparasitises blood of Anguilla anguilla
Other: sole host/prey
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Ecosystem Roles
European eels are both a food source and a predator of organisms in their ecosystem. They are consumed by birds and large predatory fish (Deelder, 1970). European eels also act as a host for the nematode Aguillicola crassus which infects the swim bladders of European eels (Deelder, 1970). European eels distribute nutrients between marine and freshwater ecosystems because they migrate between those habitats (Deelder, 1970).
Commensal/Parasitic Species:
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Predation
European eels are preyed upon by larger eels and other fish and fish-consuming birds, such as cormorants (Phalacrocorax) and herons (Ardeidae) (Deelder, 1970). One defense mechanism employed by eels is that they hide under rocks and burrow in the sand, thus avoiding their predators. The coloring of eels at various life stagies (i.e. the transparency of leptocephali, the dark grey to green color of adults, etc.) also serves as camouflage.
Known Predators:
- herons (Ardeidae)
- cormorants (Phalacrocoracidae)
- predatory fish (Actinopterygii)
Anti-predator Adaptations: cryptic
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Known predators
Lutra lutra
Phalacrocorax carbo
Ardea cinerea
Sterna paradisaea
Platichthys flesus
Podocotyle staffordi
Derogenes varicus
Based on studies in:
Scotland (Estuarine)
This list may not be complete but is based on published studies.
- Hall SJ, Raffaelli D (1991) Food-web patterns: lessons from a species-rich web. J Anim Ecol 60:823842
- Huxham M, Beany S, Raffaelli D (1996) Do parasites reduce the chances of triangulation in a real food web? Oikos 76:284300
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Known prey organisms
Tanypus punctipennis
Blicca bjorkna
Acerina cernua
Crangon crangon
Nereis diversicolor
Neomysis integer
Corophium volutator
Gammarus
Jaera albifrons
Based on studies in:
Austria, Neusiedler Lake (Lake or pond)
Scotland (Estuarine)
This list may not be complete but is based on published studies.
- F. Schiemer, The benthic community of the open lake. In: Neusiedlersee: The Limnology of a Shallow Lake in Central Europe, H. L ffler, Ed. (Dr. W. Junk, The Hague, Netherlands, 1979), pp. 337-384, from p. 376.
- Hall SJ, Raffaelli D (1991) Food-web patterns: lessons from a species-rich web. J Anim Ecol 60:823842
- Huxham M, Beany S, Raffaelli D (1996) Do parasites reduce the chances of triangulation in a real food web? Oikos 76:284300
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Diseases and Parasites
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
http://www.fishbase.org/references/FBRefSummary.php?id=45634&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
http://www.fishbase.org/references/FBRefSummary.php?id=45634&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
http://www.fishbase.org/references/FBRefSummary.php?id=45634&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
http://www.fishbase.org/references/FBRefSummary.php?id=45634&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
http://www.fishbase.org/references/FBRefSummary.php?id=45634&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
http://www.fishbase.org/references/FBRefSummary.php?id=45634&speccode=35
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Horne, M.T. and A.C. Barnes 1999 Enteric redmouth disease (Yersinia ruckeri). p.455-477. In P.T.K. Woo and D.W. Bruno (eds.) Fish Diseases and Disorders, Vol. 3: Viral, Bacterial and Fungal Infections. CAB Int'l. (Ref. 48849)
http://www.fishbase.org/references/FBRefSummary.php?id=48849&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
http://www.fishbase.org/references/FBRefSummary.php?id=45634&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
http://www.fishbase.org/references/FBRefSummary.php?id=45634&speccode=35
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Lin, C.C., C.I. Liu and G.H. Kou 2001 Review of eel diseases reported by livestock disease control centers in central Taiwan. J. Taiwan Fish. Res. 9(1&2):69-71. (Ref. 45634)
http://www.fishbase.org/references/FBRefSummary.php?id=45634&speccode=35
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Life History and Behavior
Behavior
Communication and Perception
European eels sense the environment using their sense of taste. They have been shown to locate necessary amino acids via chemotaxis (Sola and Tongiorgi, 1998). European eels also utilize olfaction, most probably for homing purposes. There is little if any documentation of social communication between eels (Deelder, 1970).
Perception Channels: visual
- Sola, C., P. Tongiorgi. 1998. Behavioural responses of glass eels of Anguilla anguilla to non-protein amino acids. Journal of Fish Biology, 53/6: 1253.
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Life Cycle
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Deelder, C.L. 1984 Synopsis of biological data on the eel, Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop. (80, Rev. 1):73 p. (Ref. 172)
http://www.fishbase.org/references/FBRefSummary.php?id=172&speccode=35
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Development
European eels begin their life cycle as eggs on the bottom of the Sargasso Sea. They hatch as leptocephali, leaf-like larvae (Tsukamoto, Nakai and Tesch, 1998). After hatching, larvae spend a maximum of one year migrating to Europe, or occasionally North America, via ocean currents. The larvae will then metamorphose into 'glass eels,' the next stage of the life cycle, and enter estuarine areas. Male glass eels contineu to grow for approximately 6 to 12 years; females for 9 to 20 years (Deelder, 1970). After a final metamorphosis, European eels migrate back to the Sargasso Sea to spawn.
Development - Life Cycle: metamorphosis
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Life Expectancy
Lifespan/Longevity
The lifespan of European eels is dependent on maturation time because once eels mature and spawn, they die. European eels can spawn as early as 7 years old. The maximum reported age of a European eel in the wild is 85 years (Dekker, van Os and van Willigen, 1998).
Range lifespan
Status: wild: 85 (high) years.
Typical lifespan
Status: wild: 7 (low) years.
Average lifespan
Status: captivity: 55.0 years.
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Lifespan, longevity, and ageing
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Reproduction
Upon reaching sexual maturity, European eels migrate from freshwater streams back to the Sargasso Sea in order to spawn and die in the late winter months to the early summer months. European eel males release sperm into the water in which female European eels have already laid eggs, thereby fertilizing the eggs (Horie et al., 2004). Very little is known about the actual spawning mechanism, and time to hatching is variable.
Mating System: polygynandrous (promiscuous)
European eels spawn during the late winter to early spring months. There is little information on their reproduction, but since European eels are closely related to Japanese eels, Anguilla japonica, similar breeding patterns might be assumed. Female A. japonica can lay from 2,000,000 to 10,000,000 eggs, but die soon after spawning (Deelder, 1970). Eel larvae are independent from time of birth until time of death.
Breeding interval: European eels breed only once during their lifetime. Once spawning is complete, European eels die .
Breeding season: European eels spawn in late winter to early spring.
Range number of offspring: 2,000,000 to 10,000,000.
Range age at sexual or reproductive maturity (female): 9 to 20 years.
Range age at sexual or reproductive maturity (male): 6 to 12 years.
Key Reproductive Features: semelparous ; seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); sexual ; fertilization (External ); broadcast (group) spawning; oviparous
European eels invest a substantial amount of energy in reproduction, and die shortly thereafter (Deelder, 1970). Consequently, the only resource that female eels give to their offspring is enough food source to last the egg until hatching. After hatching, the larvae are completely independent and able to find food (Lecomte-Finiger, 1994).
Parental Investment: no parental involvement; pre-fertilization (Provisioning)
- Lecomte-Finiger, R. 1994. The Early Life of the European Eel. Nature, 370: 424-425.
- Okamura, A., H. Zhang, T. Utoh, A. Akazawa, Y. Yamada, N. Horie, N. Mikawa, S. Tanaka, H. Oka. 2004. Artificial hybrid between Anguilla anguilla and A. japonica. Journal of Fish Biology, 64/5: 1450.
- Deelder, C. 1970. Synopsis of biological data of the eel Anguilla anguilla (Linnaeus, 1758). FAO Fish. Synop., 80: 68.
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Evolution and Systematics
Functional Adaptations
Functional adaptation
European eels navigate during long migrations by being sensitive to many different types of stimuli.
"Those specimens that do complete their life cycle use many environmental cues to navigate during their migration. Not only are eels highly sensitive to olfactory stimuli, they also respond readily to small fluctuations in water movements, seismic activity, and even to the minute electrical fields generated by water currents." (Shuker 2001:74-75)
Learn more about this functional adaptation.
- Shuker, KPN. 2001. The Hidden Powers of Animals: Uncovering the Secrets of Nature. London: Marshall Editions Ltd. 240 p.
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Molecular Biology and Genetics
Molecular Biology
Barcode data: Anguilla anguilla
There are 11 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: Anguilla anguilla
Public Records: 21
Specimens with Barcodes: 31
Species With Barcodes: 1
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Conservation
Conservation Status
IUCN Red List Assessment
Red List Category
Red List Criteria
Version
Year Assessed
Assessor/s
Reviewer/s
Contributor/s
Justification
The species has undergone a sharp decline in recruitment, yield and stock, which will continue into the future.
The recruitment of glass eels has declined from 1980, and since 2000 is at an historical low at just 1-5% of the pre-1980 levels, showing a 95 to 99% decline. This recent decline in recruitment will translate into a future decline in adult stock, at least for the coming two decades (ICES 2006).
Yield and stock abundance have declined since the 1960s. As the recruitment rate is so low the population is continuing to decline as older eels disappear from the stock. According to the FAO global catch landings (which cannot be directly linked to population due to stocking and harvest effort, though scientific evidence supports this decline) show that in 2005 only 4,855 tonnes were caught, a decline of 76% since a harvest peak in 1968, 37 years earlier (three generations of the species is estimated to be 60 years).
Even though the exact cause of the decline in recruitment is not known the species has many threats. The level of harvest of the species according to the International Council for the Exploration of the Seas (2006) is currently unsustainable. A nematode parasite (Anguillicola crassus) from introduced eels from Japan is suspected to impact the ability of the eels to reach the spawning grounds. Dams (for hydropower) are also a threat to the species by blocking migration routes and by causing high mortality rates as downstream migrating eels are killed by turbines. Pollution, loss of wetlands and climate change are also potential threats to the species.
Although a reliable population decline in mature individuals is not known, it is inferred that there has been a decline of over 80% in the past three generations (60 years) based on the massive decline in recruitment (95% in 24 years) which is supported by the decline in catch landings of 76% between 1968 and 2005 (37 years). This decline is likely to continue. Full and immediate protection is required and ICES have recommended that a recovery plan be developed for the whole stock on an urgent basis.
Action has already been taken at the international level, but the impacts of this will not be detected for many years. In 2007, CITES listed the species in Appendix II (this came into force in March 2009) and will require exporting states to have an export permit which can only be issued if the export will not be detrimental to the survival of the species. Also the European Commission has issued a Regulation requiring all member states to produce eel management plans, amongst other measures. These management plans were required to be in place by July 2009 and have the objective to permit the escapement to the sea of at least 40% of the silver eel biomass [relative to the estimated stock levels in the absence of human influences].
History
- 2006Not Evaluated(IUCN 2006)
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European eel populations are not currently threatened.
US Federal List: no special status
CITES: no special status
IUCN Red List of Threatened Species: critically endangered
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Status
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Trends
Population
Since the early 1980s, a steady and almost continent wide decline of 90% has been observed in the recruitment of glass (juvenile) eels (Dekker 2003). According to an ICES and FAO report (2006) European Eel recruitment levels reached an historical low in 2001 of 1 to 2% of the pre-1980 level, this has not improved and is an indication that the reproduction is seriously impaired and that the stock is severely depleted. In recent years, no substantial recovery in recruitment has been observed (Dekker 2007). This recent decline in recruitment will translate into a future decline in adult stock, at least for the coming two decades (ICES 2006).
Yellow/silver eels:
Even though there is no analytical assessment of the state of the [continental] European Eel stock, all available information indicates that the stock is at an historical minimum in most of the distribution area and continues to decline (ICES and FAO 2006). Unfortunately, a total continental stock assessment cannot be made as it is hard to monitor, being scattered over millions of rivers, lakes, estuaries, etc. (Dekker 2000). However, even though catch effort can be variable and under reporting of landings is a serious problem in most European countries, trends in the reported catch data will to some extent reflect true changes in fishing yields. According to FAO global capture statistics (exploited at all stages of their freshwater life), capture peaked in 1968 with 20,278 tonnes, in 1975 this had dropped to 16,110 tonnes, in 1985 it was 12,665 tonnes, 1995 8,706 tonnes and the most recent available figure in 2005 was 5,059 tonnes a decline of 76% since the peak in 1968. This is supported by the possibly only long-term scientific data [from Lake Ijsselmeer in the Netherlands] where there has been a gradual decline since 1960 (Dekker 2004a). However, there is also evidence that in Norway catches seem to be stable over this period (ICES 2002).
The overall population is continuing to decline as the older eels disappear from the stock and recruitment rate is so low and declining. Noting the longevity of the species, and the extremely depleted state, restoration of the stock is expected to take several generations from 60 to 200 years depending on the protection level (Astrom and Dekker 2007). Temporary increases (over 10-15 years) in abundance following the implementation of protective measures thus do not guarantee ultimate recovery, if not severely protecting the stock (W. Dekker pers. comm.).
Population Trend
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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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The North Atlantic Oscillation (NAO) may have reduced larval survival and/or growth rate (Castonguay et al. 1994). However, Dekker (2004b) shows that the NAO index correlation is strong for growth rate but weak for glass eel numbers as in 2000 the NAO index returned to normal but recruitment still declined.
Overfishing for glass eels (mainly in France, Spain, Portugal and UK) and downstream migrating eels (silver eels) across Europe (W. Dekker pers. comm.) is also a threat to the species. The demand from Asia and Europe for glass eels is huge and the price is increasing (750 Euro per kilo in 2006 from around 100 Euro in 1990.). According to ICES (2006) Anguilla anguilla fisheries are currently not sustainable, and a recovery plan urgently needs to be developed for the whole stock.
There is also a parasite nematode (Anguillicola crassus), from introduced eels from Japan which is suspected to impact the ability of the European Eels to reach their spawning grounds.
Dams (for hydropower and water management) are also a threat to the species by blocking migration routes and also through causing high mortality rate as the downstream migrating eels are killed by turbines.
Climate change may be having an impact on the suspected breeding grounds (Sargasso Sea).
Increasing numbers of predators, in particular cormorants, across Europe may also have a negative impact on this species.
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Management
Conservation Actions
However, in 2007 two major multi-lateral bodies recognized the state of the European Eel and have acted upon it.
The European Council (EC) Regulation No 1100/2007 establishing measures for the recovery of the stock of European Eel was published in September 2007. The Regulation required, by 1 July 2009, all member states that contain natural habitats of the European Eel to establish eel management plans at a river basin scale. The objective of these plans was to permit the escapement to the sea of at least 40% of the silver eel biomass [relative to the estimated stock levels in the absence of human influences], through various measures including reducing commercial and recreational fisheries, restocking, measures to improve habitats and make rivers passable, transportation of silver eels to the sea and monitor eel status in each basin. The Regulation also requires that by 31 July 2013, 60% of eels less than 12 cm in length caught annually should be reserved for restocking [and not aquaculture], also that over a 5 year period starting from 1 July 2009 catches or fishing effort of eels in coastal and sea waters [i.e. beyond river basin plan] should be reduced by at least 50% [of average between 2004-2006], and that a control and monitoring system be set up by each member state.
The European Eel was listed in Appendix II of the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) in June 2007. The listing came into effect on 13 March 2009, after which time all Parties to the Convention will be required to issue permits for all exports of the species. An export permit may be issued only if the specimen was legally obtained and if the export will not be detrimental to the survival of the species. In the European Union, which includes 24 eel range States, CITES is implemented through Council Regulation 338/97 and Commission Regulation 865/2006 which require both import and export permits to be issued for species listed in Annex B of the Regulation (Annex B contains most CITES Appendix II species). In the case of specimens introduced from the sea, a certificate has to be issued by the Management Authority of the State into which the specimens are being brought, for species listed in Appendix I or II.
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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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Flower, S.S. 1935 Further notes on the duration of life in animals. I. Fishes: as determined by otolith and scale-readings and direct observations on living individuals. Proc. Zool. Soc. London 2:265-304. (Ref. 274)
http://www.fishbase.org/references/FBRefSummary.php?id=274&speccode=2066
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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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Economic Importance for Humans: Negative
European eels thrive on a diet of marine and freshwater fauna, so impact populations of other marine and freshwater organisms (Deelder, 1970). There are no direct adverse effects to humans.
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Economic Importance for Humans: Positive
European eels are a popular food source for humans, especially in Europe and Asia. The eels also feed on the eggs of predatory fish such as trout, which keep ecosystems from overpopulation (Deelder, 1970).
Positive Impacts: food ; controls pest population
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Wikipedia
European eel
The European eel, Anguilla anguilla,[1] is a species of eel, a snake-like, catadromous fish. They can reach (in exceptional cases) a length of 1.5 m (4 ft 11 in), but are normally much smaller, about 60–80 cm (2.0–2.6 ft), and rarely more than 1 m (3 ft 3 in).
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Life history[edit]
Much of the European eel’s life history was a mystery for centuries, as fishermen never caught anything they could identify as a young eel. Unlike many other migrating fish, eels begin their life cycle in the ocean and spend most of their lives in fresh water, returning to the ocean to spawn and then die. In the early 1900s, Danish researcher Johannes Schmidt identified the Sargasso Sea as the most likely spawning grounds for European eels.[2] The larvae (Leptocephalus) drift towards Europe in a three-hundred-day migration.[3] When approaching the European coast, the larvae metamorphose into a transparent larval stage called "glass eel", enter estuaries and start migrating upstream. After entering fresh water, the glass eels metamorphose into elvers, miniature versions of the adult eels. As the eel grows, it becomes known as a "yellow eel" due to the brownish-yellow color of their sides and belly. After 5–20 years in fresh water, the eels become sexually mature, their eyes grow larger, their flanks become silver and belly white in color. In this stage the eels are known as "silver eels", and they begin their migration back to the Sargasso sea to spawn.
Conservation status[edit]
The European Eel is a critically endangered species.[4] Since the 1970s, the numbers of eels reaching Europe is thought to have declined by around 90% (possibly even 98%). Contributing factors include overfishing, parasites such as Anguillicola crassus, barriers to migration such as hydroelectric plants, and natural changes in the North Atlantic oscillation, Gulf Stream and the North Atlantic drift. Recent work suggests that PCB pollution may be a factor in the decline.[5]
Eels have been important sources of food both as adults (including the famous jellied eels of East London) and as glass eels. Glass eel fishing using basket traps has been of significant economic value in many river estuaries on the western seaboard of Europe.
In captivity European eels can become very old.[6]
Sustainable consumption[edit]
In 2010, Greenpeace International has added the European eel to its seafood red list. "The Greenpeace International seafood red list is a list of fish that are commonly sold in supermarkets around the world, and which have a very high risk of being sourced from unsustainable fisheries."[7]
Decreasing population numbers and breeding projects[edit]
For quite some time, the population number of European eels has been falling. For this reason, a research project has been started by Innovatie Netwerk, led by Henk Huizing to see whether it is possible to breed European eels in captivity. The breeding of European eel is very difficult, since eel is generally only able to reproduce after having swum a distance of 6,500 kilometres (4,000 mi). In the project, this is being simulated by means of a hometrainer for the fish. Innovatie Netwerk has also started a breeding project, called InnoFisk Volendam.[8][9]
Commercial fisheries[edit]
| Detailed time series |
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Gallery[edit]
References[edit]
- ^ "Anguilla anguilla". Integrated Taxonomic Information System. Retrieved 11 March 2006.
- ^ Schmidt, J. (1912) Danish researches in the Atlantic and Mediterranean on the life-history of the Fresh-water Eel (Anguilla vulgaris, Turt.). Internationale Revue der gesamten Hydrobiologie und Hydrographie 5: 317-342.
- ^ "FAO Fisheries & Aquaculture Anguilla anguilla". Fao.org. 2004-01-01. Retrieved 2012-08-02.
- ^ The IUCN Red List of Threatened Species, 2008.
- ^ "PCBs are killing off eels". New Scientist 2452: 6. 2006.
- ^ (Swedish) Branteviksålen kan vara världens äldsta, 2008.
- ^ Greenpeace International Seafood Red list
- ^ EOAS magazine, september 2010
- ^ Innofisk Volendam breedign project
- ^ a b c Based on data sourced from the FishStat database, FAO.
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