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Overview
Brief Summary
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Biology
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Description
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Comprehensive Description
Description
- the umbones turn down, giving the basal line of the shell a concave appearance;
- the valves are higher and less angular;
- the mantle edges are darker, becoming blue or purple, and
- Mytilus galloprovincialis tends to grow larger (Tebble, 1976).
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Description
“Mytilus edulis, Linné, 1758. Plate 56, fig. 4.
Shell attaining sometimes a large size, oblong-oval or triangular, dilated behind, the beaks anterior and terminal, smooth. Beaks slightly uncinate, close together. Anterior end narrowed, pointed, and usually somewhat inflate, the dorsal margin ascending on the anterior half, the posterior part broadly rounded or almost straight. Posterior end regularly convex, the basal margin straight or more or less concave. Sculpture consisting of fine concentric growth-lines and very fine radiate striæ; under the beaks a small triangular area with prominent ribs corresponding with the hinge-teeth. Epidermis thin, dark olive-brown. Colour deep blackish-blue, sometimes whitish-yellow with brown at the anterior basal part. Interior bluish-white, black outside the pallial line, polished. Margins smooth and sharp. Hinge-plate narrow, oval with 3 or 4 teeth in each valve, which may be reduced to 2 or 1. Ligament external, long and strong, deep-seated. Adductor-scars 2, the anterior very small, behind the umbo; the posterior large, roundish, situate at the upper part of posterior end, and confluent with the long and narrow byssus retractor scar; the anterior retractor scar of the foot is small, oblong, on the dorsal side behind the beak. Pallial line simple. Byssus consisting of a round stalk, from which on all sides the threads of attachment are given off.
Diameter. – Ant.-post., 50 mm. to 120 mm.; dorso-ventral, 25 mm. to 67 mm.: thickness 17 mm. to 40 mm.
Anatomy. – Alex. Purdie, “Studies in Biology for New Zealand Students,” No. 3, 1887.
Hab. – Throughout New Zealand, but more common in the south. Auckland and Campbell Islands.
The species is abundant around the coasts of the North Atlantic, and in the Mediterranean; Strait of Magellan to St. Catharina, Brazil, and extending on the west coast of America to California; Falkland Islands; Kerguelen Island. It is not recorded from Tasmania and Australia.
Remarks. – Specimens from our subantarctic islands are of a very large size. The animal is used as food and for bait. These mussels, like those of other species, contain sometimes pearls of an inferior quality.
Fossil in the Pliocene and Pleistocene of Europe and northern parts of America, and in the Miocene and Pliocene of New Zealand.”
(Suter, 1913)
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Linnaeus, C. 1758. Systema naturae per regna tria naturae, secundum classes, ordines, genera, species cum characteribus, diferentiis, synonymis, locis. Holmiae [=Stockholm], I, 894 p.
http://invertebrates.si.edu/antiz/taxon_view.cfm?mode=bibliography&citation=1042
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Distribution
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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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Christie, H.; Jørgensen, N.M.; Norderhaug, K.M.; Waage-Nielsen, E. (2003). Species distribution and habitat exploitation of fauna associated with kelp (Laminaria hyperborea) along the Norwegian Coast. J. Mar. Biol. Ass. U.K. 83(4): 687-699
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1291
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Vandendriessche, S.; Degraer, S.; Vincx, M. (2003). Drijvende wieren als habitat voor macrofauna aan de Belgische kust [Floating seaweeds as habitat for macrofauna at the Belgian coast]. De Strandvlo 23(2): 50-57
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1670
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M'harzi, A. (1999). Phytoplankton community structuring in some areas of the North Sea. PhD Thesis. Vrije Universiteit Brussel: Brussel, Belgium. 221 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1107
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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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Leloup, E. (1950). Contributions à l'étude de la faune belge: 17. Recherches sur une moulière naturelle de la côte belge. Med. K. Belg. Inst. Nat. Wet. 26(30): 1-56.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1653
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Little, C.; Morritt, D.; Seaward, D.R.; Williams, G.A. (1989). Distribution of intertidal molluscs in lagoonal shingle (The Fleet, Dorset, U.K.). J. Conch., Lond. 33: 225-232
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1314
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Backeljau, T. (1986). Lijst van de recente mariene mollusken van België [List of the recent marine molluscs of Belgium]. Koninklijk Belgisch Instituut voor Natuurwetenschappen: Brussels, Belgium. 106 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2
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de Bruyne, R.H. (1991). Schelpen van de Nederlandse kust [Shells of the Dutch coast]. Jeugdbondsuitgeverij/KNNV Uitgeverij: Utrecht, The Netherlands. ISBN 90-5107-017-9. III, 165 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=705
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Cardigos, F.; Tempera, F.; Ávila, S.; Gonçalves, J.; Colaço, A.; Santos, R.S. (2006). Non-indigenous marine species of the Azores. Helgol. Mar. Res. 60(2): 160-169
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=9808
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Reise, K.; Olenin, S.; Thieltges, D.W. (2006). Are aliens threatening European aquatic coastal ecosystems?. Helgol. Mar. Res. 60(2): 77-83
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=9796
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Savini, D.; Occhipinti-Ambrogi, A. (2006). Consumption rates and prey preference of the invasive gastropod Rapana venosa in the Northern Adriatic Sea. Helgol. Mar. Res. 60(2): 153-159.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=9806
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Nehls, G.; Diederich, S.; Thieltges, D.W.; Strasser, M. (2006). Wadden Sea mussel beds invaded by oysters and slipper limpets: competition or climate control?. Helgol. Mar. Res. 60(2): 135-143.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=9804
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Trott, T.J. 2004. Cobscook Bay inventory: a historical checklist of marine invertebrates spanning 162 years. Northeastern Naturalist (Special Issue 2): 261 - 324.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=3072
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Gollasch, S.. 2006. Overview on introduced aquatic species in European navigational and adjacent waters. Helgoland Marine Research 60(2):84-89.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=84157
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Polk, Ph. (1976). Inventarisatie plankton: fauna en flora [Plankton inventory : fauna and flora], in: Nihoul, J.C.J.; De Coninck, L. (Ed.) (1976). Project Sea final report: 7. Inventory of fauna and flora. Project Sea final report, 7: pp. 233-311
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1590
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ILVO macrofauna data: macrofauna monitoring on the Belgian Part of the North Sea since 1979
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=132965
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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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De Pauw, N., 1969. Contribution à l'étude du plancton dans le port d'Ostende. Biol. Jb. 37 : 186-262.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=25970
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d'Udekem d'Acoz, C. (1990). Notes on some organisms collected between Wenduine and De Haan on 3 March 1990 [Notes sur quelques organismes recueillis entre Wenduine et De Haan le 3 mars 1990]. De Strandvlo 10(3): 74-78
http://www.marinespecies.org/ophiuroidea/aphia.php?p=sourcedetails&id=138631
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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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Lock, K.. 1996. Intertidale hyperbenthische gemeenschappen van zandstranden. (Intertidal hyperbenthic communities of sandy beaches.) B.Sc. Thesis, Universiteit Gent, Ghent, Belgium 95 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=100101
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Gofas, S.; Le Renard, J.; Bouchet, P. (2001). Mollusca, 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. 180-213
http://www.marinespecies.org/mollusca/aphia.php?p=sourcedetails&id=1364
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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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Billiau, R. (2002). Reuzenstranding van verse (levende) wijde mantels Aequipecten opercularis (L., 1758) te De Panne op 8 en 9 november 1999 [Mass stranding of fresh (living) Queen scallop Aequipecten opercularis (L., 1758) at De Panne on 8 and 9 November 1999]. De Strandvlo 22(3-4): 99-102
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1088
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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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Leloup, E. (1952). Contributions à l'étude de la faune belge: 19. Observation sur la crevette grise au large de la côte belge en 1949 [Contribution to the study on the Belgian fauna: 19. Observation on the brown shrimp along the Belgian coast in 1949]. Med. K. Belg. Inst. Nat. Wet. 18(1): 1-28
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1648
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Engledow, H.; Spanoghe, G.; Volckaert, A.; Coppejans, E.; Degraer, S.; Vincx, M.; Hoffmann, M. (2001). Onderzoek naar (1) de fysische karakterisatie en (2) de biodiversiteit van strandhoofden en andere harde constructies langs de Belgische kust: eindrapport van de onderhandse overeenkomst dd. 17.02.2000 i.o.v. de Afdeling Waterwegen Kust van het Ministerie van de Vlaamse Gemeenschap, Departement Leefmilieu en infrastructuur, Administratie Waterwegen en Zeewezen [Research on (1) the physical characterization and (2) the biodiversity of groins and other hard constructions along the Belgian coast: final report]. Rapport Instituut voor Natuurbehoud, 2001.20. Universiteit Gent/Instituut voor Natuurbehoud: Gent & Brussel, Belgium. 110 + annexes pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=756
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Põllumäe, A.; Kotta, I.; Kotta, J. (2006). Port biological sampling as a tool for monitoring invasive species in high-risk areas of bioinvasions, in: Ojaveer, H.; Kotta, J. (Ed.) (2006). Alien invasive species in the north-eastern Baltic Sea: population dynamics and ecological impacts. Estonian Marine Institute Report Series, 14: pp. 35-41
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=9789
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Leloup, E. (1942). Contributions à l'étude de la faune belge: 12. L'hydraire Campanularia johnstoni Alder et le mollusque Mytilus edulis Linné, épizoaires sur le crustacé Pandalus montagui Leach [Contributions to the study of the Belgian fauna: 12. The hydroid Campanularia johnstoni Alder and the mollusc]. Bull. Mus. royal d'Hist. Nat. Belg./Med. Kon. Natuurhist. Mus. Belg. 18(18): 1-4
http://www.marinespecies.org/mollusca/aphia.php?p=sourcedetails&id=1634
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Rappé, G. (1989). Haliclona xena De Weerdt, 1986 (Porifera, Desmospongiae), Petrobius maritimus (Leach) (Insecta, Thysanura) and some other exceptional observations on the eastern harbour jetty of Zeebrugge [Haliclona xena De Weerdt, 1986 (Porifera, Desmospongiae), Petrobius maritimus (Leach) (Insecta, Thysanura) en enkele andere bijzondere waarnemingen van de oostelijke strekdam van Zeebrugge]. De Strandvlo 9(4): 113-116
http://www.marinespecies.org/mollusca/aphia.php?p=sourcedetails&id=138705
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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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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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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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Koukouras, Athanasios. (2010). Check-list of marine species from Greece. Aristotle University of Thessaloniki. Assembled in the framework of the EU FP7 PESI project.
http://www.marinespecies.org/asteroidea/aphia.php?p=sourcedetails&id=142068
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Miller, Roberta. 2011. The St. Anne de Bellevue Arctic Biological Station Collection In Museum collection database, Fisheries and Oceans Canada digital collections, Maurice Lamontagne Institute, Quebec
http://www.marinespecies.org/asteroidea/aphia.php?p=sourcedetails&id=150285
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Mark, S., Provencher, L., Albert, E. et Nozères, C. 2010. Cadre de suivi écologique de la zone de protection marine Manicouagan (Québec) : bilan des connaissances et identification des composantes écologiques à suivre. Rapp. tech. can. sci. halieut. aquat. 2914 : xi + 121 p
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=150858
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Bossé, L., B. Sainte-Marie et J. Fournier (1996). Les invertébrés des fonds meubles et la biogéographie du fjord du Saguenay. Rapp. tech. can. sci. halieut. aquat. 2 132: vii + 45 p.
http://www.marinespecies.org/asteroidea/aphia.php?p=sourcedetails&id=153966
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Préfontaine, G. & P. Brunel. 1962. Liste d'invertébrés marins recueillis dans l'estuaire du Saint-Laurent de 1929 à 1934. Naturaliste Canadien, Quebec 89(8-9):237-263, fig. 1.
http://www.marinespecies.org/ascidiacea/aphia.php?p=sourcedetails&id=109070
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Spry, J.F. (1964). The sea shells of Dar es Salaam: Part 2: Pelecypoda (Bivalves). Tanganyika Notes and Records 63
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=5904
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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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Geographic Range
Mytilus edulis is found in coastal areas of the northern Atlantic Ocean, including North America, Europe, and the northern Palearctic. They are found from the White Sea in Russia to southern France, throughout the British Isles, with large commercial beds in the Wash, Morecambe Bay, Conway Bay and southwest England, north Wales, and west Scotland. In the west Atlantic, M. edulis occupies the southern Canadian Maritime provinces to North Carolina.
Biogeographic Regions: nearctic (Native ); atlantic ocean (Native ); pacific ocean (Introduced )
- FAO Inland Water Resources and Aquaculture Service (FIRI). 2006. "Fisheries Global Information System (FIGIS)" (On-line). Cultured Aquatic Species Information Programme - Mytilus edulis. Accessed December 12, 2006 at http://www.fao.org/figis/servlet/static?dom=culturespecies&xml=Mytilus_edulis.xml.
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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
United States
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
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Range
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Physical Description
Morphology
Physical Description
Mytilus edulis is characterized by a smooth inequilateral shell, usually purple, blue, or dark brown, which features concentric growth lines emanating from the hinge. The interior of the shell is pearl-white. Internally the mantle has a whitish/yellow color, with a posterior adductor scar significantly larger than its anterior adductor scar. Extending from the closed shell are fibrous brown byssal threads for attachment to a surface.
Range mass: 1.4 to 6.5 g.
Range length: 2 to 20 cm.
Average length: 5-10 cm.
Other Physical Features: ectothermic ; heterothermic ; bilateral symmetry
Sexual Dimorphism: female larger
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Ecology
Habitat
Mytilus edulis is eurythermal and are able to withstand freezing conditions for several months. Blue mussels are well acclimated to a 5 to 20 °C temperature range, with an upper sustained thermal tolerance limit of about 29 °C for adults. Blue mussels do not thrive in salinities of less than 15%, but can withstand wide environmental fluctuations. Their depth ranges from 5 to 10 meters. Usually, M. edulis is found in subtidal and intertidal beds on rocky shores, and remain permanently attached there. The range of Mytilus edulis is limited by the movement of drifting larval and juvenile stages.
Range depth: 1 to 10 m.
Habitat Regions: temperate ; polar ; saltwater or marine
Aquatic Biomes: coastal ; brackish water
Other Habitat Features: estuarine ; intertidal or littoral
- Tyler-Walters, H., R. Seed. 2006. "The Marine Life Information Network" (On-line). Accessed December 01, 2006 at http://www.marlin.ac.uk/species/Mytilusedulis.htm.
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Natural Geography in Shore Areas (NaGISA) database, compiled by Ann Knowlton.
http://www.marinespecies.org/arms/aphia.php?p=sourcedetails&id=145467
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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 276 samples.
Environmental ranges
Depth range (m): -3 - 408
Temperature range (°C): -1.363 - 23.436
Nitrate (umol/L): 0.660 - 18.830
Salinity (PPS): 6.095 - 36.284
Oxygen (ml/l): 2.113 - 8.544
Phosphate (umol/l): 0.048 - 1.740
Silicate (umol/l): 1.824 - 50.947
Graphical representation
Depth range (m): -3 - 408
Temperature range (°C): -1.363 - 23.436
Nitrate (umol/L): 0.660 - 18.830
Salinity (PPS): 6.095 - 36.284
Oxygen (ml/l): 2.113 - 8.544
Phosphate (umol/l): 0.048 - 1.740
Silicate (umol/l): 1.824 - 50.947
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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Trophic Strategy
Food Habits
The diet of Mytilus edulis consists of phytoplankton, dinoflagellates, small diatoms, zoospores, flagellates, other protozoans, various unicellular algae, and detritus filtered from the surrounding water. Blue mussels are suspension filter feeders and are considered scavengers, collecting anything in the water column that is small enough to ingest.
Animal Foods: eggs; zooplankton
Plant Foods: algae; phytoplankton
Other Foods: detritus ; microbes
Foraging Behavior: filter-feeding
Primary Diet: planktivore ; detritivore
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Associations
Ecosystem Roles
Mytilus edulis has a high tolerance for increased sediment levels and help to remove sediments from the water column. Large blue mussel beds provide habitat and prey for other animals and act as a substrate for algal attachment, increasing local diversity. Blue mussel larvae are an important food source for plantivorous animals as well.
Commensal/Parasitic Species:
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Predation
Blue mussels are most often found in large mussel beds, where they are somewhat protected from predation by virtue of their numbers. The shell of Mytilus edulis acts as a protective layer, though some predator species are able to crush the shell.
Some predators of M. edulis wait until the mussel is forced to open its valves to breathe. The predator then pushes the mussel's siphon into the gap, wedging the mussel open so it can be eaten.
Known Predators:
- flounders (Pleuronectiformes)
- sandpipers (Scolopacidae)
- gulls (Larus)
- crows (Corvus)
- dogwhelks (Nucella lapillus)
- common starfish (Asterias rubens)
- Strongylocentrotus droebachiensis
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Known predators
Thais lapillus
Leptasterias
Pisaster
Pycnopodia
Thais canaliculata
Tadorna tadorna
Somateria mollissima
Haematopus ostralegus
Calidris alpina
Arenaria interpres
Larus marinus
Sterna sandvicensis
Corvus corone
Ammodytes tobianus
Pholis gunnellus
Zoarces viviparus
Pomatoschistus minutus
Pomatoschistus microps
Pleuronectes platessa
Platichthys flesus
Crangon crangon
Himasthla elongata
Himasthla interrupta
Profilicollis botulus
Psilostomum brevicolle
Based on studies in:
USA: New England (Littoral, Rocky shore)
USA: Washington (Littoral, Rocky shore)
USA: Alaska, Torch Bay (Littoral, Rocky shore)
USA: Washington, Cape Flattery (Littoral, Rocky shore)
Scotland (Estuarine)
This list may not be complete but is based on published studies.
- B. A. Menge and J. P. Sutherland, Species diversity gradients: synthesis of the roles of predation, competition and temporal heterogeneity, Am. Nat. 110(973):351-369, from p. 355 (1976).
- B. A. Menge and J. P. Sutherland, Species diversity gradients: synthesis of the roles of predation, competition and temporal heterogeneity, Am. Nat. 110(973):351-369, from p. 360 (1976).
- R. T. Paine, Food webs: linkage, interaction strength and community infrastructure, J. Anim. Ecol. 49:667-685, from p. 670 (1980).
- 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
detritus
plankton
POM
Based on studies in:
USA: New England (Littoral, Rocky shore)
USA: Washington (Littoral, Rocky shore)
USA: Alaska, Torch Bay (Littoral, Rocky shore)
USA: Washington, Cape Flattery (Littoral, Rocky shore)
Scotland (Estuarine)
This list may not be complete but is based on published studies.
- B. A. Menge and J. P. Sutherland, Species diversity gradients: synthesis of the roles of predation, competition and temporal heterogeneity, Am. Nat. 110(973):351-369, from p. 355 (1976).
- B. A. Menge and J. P. Sutherland, Species diversity gradients: synthesis of the roles of predation, competition and temporal heterogeneity, Am. Nat. 110(973):351-369, from p. 360 (1976).
- R. T. Paine, Food webs: linkage, interaction strength and community infrastructure, J. Anim. Ecol. 49:667-685, from p. 670 (1980).
- 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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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
Blue mussels have statocysts to aid in geo-positioning and orientation. Blue mussels have chemoreceptors capable of detecting the release of gametes. These chemoreceptors also help juvenile blue mussels avoid settling temporarily on substrata near mature blue mussle, presumably to decrease competition for food.
Communication Channels: chemical
Perception Channels: tactile ; chemical
- Conservation Management Institute, 2001. "Fish and Wildlife Information Exchange (FWIE)" (On-line). Marine and Coastal Species Information System. Accessed December 12, 2006 at http://fwie.fw.vt.edu/WWW/macsis/lists/M060008.htm.
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Life Cycle
Development
After the egg is fertilized it turns into a ciliated trocophore larva. The trochophore larva then becomes a veliger, which persists 1 to 1.5 months. In this phase, the larva bears ciliated fan-like protrusions and filter feeds before becoming a juvenile and finding a primary settlement location. The primary settlement location is often located in openings in the substrata, or amongst bryozoans or other filamentous structures and often situated away from mature mussels, presumably to decrease competition. After weeks there, the juvenile has doubled in size and detaches to drift again and find a permanent substrate to which to attach. The young adult will attach to the sea floor with a byssus thread or, if such open substrate is not stable, may attach to another mussel, creating a mussel bed.
Development - Life Cycle: metamorphosis ; colonial growth ; indeterminate growth
- Nordsieck, R. 2006. "The Living World of Molluscs" (On-line). The Common Mussel (Mytilus edulis). Accessed December 12, 2006 at http://www.weichtiere.at/Mollusks/Muscheln/miesmuschel.html.
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Life Expectancy
Lifespan/Longevity
The lifespan of Mytilus edulis may vary considerably depending on attachment location. Settline in more exposed coastal areas make individuals significantly more vulnerable to predation, in large part avian. Quality and stability of the substrate also plays a role in the lifespan. Mussels that settle in exposed locations can experience mortality up to 98% per year. Drifting larval and juvenile stages suffer the highest mortality rates.
Range lifespan
Status: wild: 18 to 24 years.
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Reproduction
Mytilus edulis sexes are separate and gametes are shed into the water where fertilization occurs.
Mating System: polygynandrous (promiscuous)
Mytilus edulis spawns from April to September, depending on water temperature, currents, and other environmental factors. In most populations, resting gonads begin to develop from October to November, with gametogenesis occurring throughout winter so that gonads are mature in early spring. A partial spawning in spring is followed by rapid gametogenesis, with gonads maturing by early summer, resulting in a less intensive secondary spawning in late August or September. Larvae spawned in spring can take advantage of phytoplankton blooms. Occurrence of the secondary spawning is opportunistic, depending on favorable environmental conditions and food availability. Gametogenesis, spawning, and reproductive strategies vary with geographic location. An individual female can produce 5 to 8 million eggs, larger individuals may produce as many as 40 million eggs. In optimal conditions, larval development may be complete in less than 20 days but larval growth and metamorphosis between spring and early summer, at 10 °C, usually takes 1 month. Pediveligers can delay metamorphosis for up to 40 days at 10 °C or for up to 6 months in some cases.
Breeding interval: Reproductive output is influenced by temperature, food availability, and tidal exposure and can therefore vary from year to year and from place to place.
Breeding season: Blue mussels generally breed during the spring to late summer.
Range number of offspring: 5000000 to 40000000.
Average number of offspring: 7000000.
Range age at sexual or reproductive maturity (female): 1 to 2 years.
Range age at sexual or reproductive maturity (male): 1 to 2 years.
Key Reproductive Features: iteroparous ; seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); fertilization (External ); broadcast (group) spawning
There is no parental care after fertilization.
Parental Investment: no parental involvement; pre-fertilization (Provisioning, Protecting: Female)
- Nordsieck, R. 2006. "The Living World of Molluscs" (On-line). The Common Mussel (Mytilus edulis). Accessed December 12, 2006 at http://www.weichtiere.at/Mollusks/Muscheln/miesmuschel.html.
- Tyler-Walters, H., R. Seed. 2006. "The Marine Life Information Network" (On-line). Accessed December 01, 2006 at http://www.marlin.ac.uk/species/Mytilusedulis.htm.
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Evolution and Systematics
Functional Adaptations
Functional adaptation
The byssus threads of mollusks are strong anchors that can resist hydrodynamic forces because of mechanically distinct regions within each thread.
"One particular use of a collagenous rope gives a sense of the range of performance nature can get from this material--and of some of the peculiarities of applying data from standard analyses. As familiar to anyone who has poked around rocky, wave-swept shores, mussels don't dislodge easily. Each is attached to rocks by twenty to sixty stringy byssus threads of sufficient tenacity to resist extreme hydrodynamic forces. (Denny [1988] provides an especially good view of the origin of these forces.) At first glance, a collagenous material looks inappropriate for the mission. After all, low extensibility means that unless particularly well matched and faced with forces of invariant strength and direction, only some subset of threads will bear the load. Imagine hanging from a group of inextensible ropes each of slightly different length--having more than one will gain you nothing, since they'll break one by one instead of sharing the load.
A byssus thread contains two mechanically distinct regions, called, for their distance from the shell, proximal and distal. The material of both regions proves to be unusually extensible for collagens, which sounds right and proper. But then, according to Bell and Gosline (1996) things get more complex. The proximal region can be strained to a greater fraction of unloaded length, but it never achieves the breaking strength of the distal region, as you can see from figure 16.14a. So it looks as if their proximal regions take care of distributing the load among the threads. Not so. The distal region of threads happens to be two to four times longer and only half as wide. So a given force will stretch it quite far. Replotting the data as force against extension for a whole thread as a structure, as in figure 16.14b, shows a nice match. Even better, it shows how the distal thread yields (the horizontal portion of its curve) just short of the breaking force--an extension that will permit threads to reorient closer to the direction of the applied force and to share increasing loads among an increasing number of threads." (Vogel 2003:347)
Learn more about this functional adaptation.
- Steven Vogel. 2003. Comparative Biomechanics: Life's Physical World. Princeton: Princeton University Press. 580 p.
- Bell EC; Gosline JM. 1996. Mechanical design of mussel byssus: material yield enhances attachment strength. Journal of Experimental Biology. 199: 1005-1017.
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Functional adaptation
Secretions of several marine invertebrates may gain adhesive and cohesive qualities in part via phosphorylation of certain proteins.
"Protein phosphorylation is an important regulator of both cellular and extracellular events. Recently, protein phosphorylation has also emerged as an important process in biological adhesives. During the last decade, Herbert Waite and his group have indeed characterized several polyphosphoproteins from the adhesive secretions of two different marine organisms, mussels and tube-building worms. This suggests the possibility that polyphosphoproteins could be important components of several bioadhesives and may, therefore, be widely distributed throughout the animal kingdom…These findings bring to three the number of animal groups in which adhesive processes involve polyphosphoproteins and raise interesting questions about the convergent evolution of these adhesives.
"In the marine environment, attachment mechanisms developed by animals usually rely on highly viscous or solid adhesive secretions, which all contain specialized proteins. Functional convergences are noted among marine animals, particularly in terms of the type of adhesion used: permanent, temporary, or instantaneous. Although marine adhesive proteins from non-related organisms do not present any sequence homologies, molecular convergences have been recognized, and some adhesive motifs have been found to be shared by phylogenetically different animals. DOPA has long been known as one such motif. Now, another modified amino acid, phosphoserine (pSer), is emerging as an important motif in biological adhesives. Indeed, our findings bring the number of polyphosphoprotein-containing marine adhesives to three. The occurrence of high levels of pSer in adhesive systems from totally unrelated animals, which moreover use different types of adhesion, raise questions about the convergent evolution of these adhesives." (Flammang et al. 2009:447, 462-3)
Learn more about this functional adaptation.
- Flammang P; Lambert A; Bailly P; Hennebert E. 2009. Polyphosphoprotein-containing marine adhesives. The Journal of Adhesion. 85(8): 447 - 464.
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Functional adaptation
The byssal threads of mussels display both hardness and extensibility thanks to sacrificial cross-links in the outer cuticle.
"Sacrificial bonds and hidden length in structural molecules and composites have been found to greatly increase the fracture toughness of biomaterials by providing a reversible, molecular-scale energy-dissipation mechanism. This mechanism relies on the energy, of order 100 eV, needed to reduce entropy and increase enthalpy as molecular segments are stretched after being released by the breaking of weak bonds, called sacrificial bonds. This energy is relatively large compared to the energy needed to break the polymer backbone, of order a few eV. In many biological cases, the breaking of sacrificial bonds has been found to be reversible, thereby additionally providing a 'self-healing' property to the material." (Fantner 2006:1411)
"The extensible byssal threads of marine mussels are shielded from abrasion in wave-swept habitats by an outer cuticle that is largely proteinaceous and approximately fivefold harder than the thread core. Threads from several species exhibit granular cuticles containing a protein that is rich in the catecholic amino acid 3,4-dihydroxyphenylalanine (dopa) as well as inorganic ions, notably Fe3+. Granular cuticles exhibit a remarkable combination of high hardness and high extensibility. We explored byssus cuticle chemistry by means of in situ resonance Raman spectroscopy and demonstrated that the cuticle is a polymeric scaffold stabilized by catecholato-iron chelate complexes having an unusual clustered distribution. Consistent with byssal cuticle chemistry and mechanics, we present a model in which dense cross-linking in the granules provides hardness, whereas the less cross-linked matrix provides extensibility." (Harrington et al. 2010:216)
Learn more about this functional adaptation.
- Steven Vogel. 2003. Comparative Biomechanics: Life's Physical World. Princeton: Princeton University Press. 580 p.
- Weaver, James C.; Aizenberg, Joanna; Fantner, Georg E.; Kisailus, David; Woesz, Alexander; Allen, Peter; Fields, Kirk; Porter, Michael J.; Zok, Frank W.; Hansma, Paul K.; Fratzl, Peter; Morse, Daniel E. 2007. Hierarchical assembly of the siliceous skeletal lattice of the hexactinellid sponge Euplectella aspergillum. Journal of Structural Biology. 158(1): 93-106.
- Fantner, G. E.; Oroudjev, E.; Schitter, G.; Golde, L. S.; Thurner, P.; Finch, M. M.; Turner, P.; Gutsmann, T.; Morse, D. E.; Hansma, H. 2006. Sacrificial Bonds and Hidden Length: Unraveling Molecular Mesostructures in Tough Materials. Biophysical Journal. 90(4): 1411-1418.
- Harrington MJ; Masic A; Holten-Andersen N; Waite H; Fratzl P. 2010. Iron-clad fibers: A metal-based biological strategy for hard flexible coatings. Science. 328(5975): 216 - 220.
- 2010. How marine mussels grip rocks: iron atoms convey mussel fibers with a robust but stretchy covering. Science Daily [Internet],
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Functional adaptation
Byssus threads of the blue mussel attach to a wet, solid surface due to catechols on adhesive proteins that overcome the surface’s affinity for water molecules.
"Pounding waves are no match for the mighty mussel, that produces strong, flexible threads that cling to rocks…mussels secrete a unique amino acid called dihydroxyphenylalanine…Researchers have developed a new group of adhesives for wood products inspired by the ability of mussels to cling to rocks using thread-like tentacles. These threads are proteins that retain powerful adhesive properties even in water.” (ScienceDaily 2005)
Learn more about this functional adaptation.
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2005. Wood Glue Inspired by Mussels: Chemist's Glue Borrows Unique Amino Acid from Mollusk. Science Daily LLC.
http://www.sciencedaily.com/videos/2005/0601-wood_glue_inspired_by_mussels.htm. - Lee, Haeshin; Dellatore, Shara M.; Miller, William M.; Messersmith, Phillip B. 2007. Mussel-Inspired Surface Chemistry for Multifunctional Coatings. Science. 318(5849): 426-430.
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Molecular Biology and Genetics
Molecular Biology
Barcode data: Mytilus edulis
There are 242 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.
-- end --
Download FASTA File
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Statistics of barcoding coverage: Mytilus edulis
Public Records: 234
Specimens with Barcodes: 347
Species With Barcodes: 1
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Conservation
Conservation Status
Mytilus edulis is fairly common and is abundant in many coastal areas and has therefore not been placed on any conservation list or given any special status.
US Federal List: no special status
CITES: no special status
State of Michigan List: no special status
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National NatureServe Conservation Status
United States
Rounded National Status Rank: NNR - Unranked
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Status
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Threats
Management
Conservation
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Relevance to Humans and Ecosystems
Benefits
Economic Importance for Humans: Negative
There are no known adverse effects of Mytilus edulis on humans.
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Economic Importance for Humans: Positive
People harvest blue mussels as food and they are used in commercial aquaculture. Blue mussels are considered an important food source in some coastal areas and the shells are used in jewelry manufacturing. Blue mussels also help limit algae growth, which has become problematic in the Mediterranean Sea and elsewhere.
Positive Impacts: food ; research and education
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Wikipedia
Blue mussel
The blue mussel (Mytilus edulis), also known as the common mussel,[1] is a medium-sized edible marine bivalve mollusc in the family Mytilidae, the mussels. Blue mussels are subject to commercial use and intensive aquaculture.
Contents |
Systematics and distribution [edit]
The Mytilus edulis complex [edit]
Systematically blue mussels consist of a group of (at least) three closely related taxa of mussels, known as the Mytilus edulis complex. Collectively they occupy both coasts of the North Atlantic (including the Mediterranean) and of the North Pacific in temperate to polar waters, as well as coasts of similar nature in the Southern Hemisphere. The distribution of the component taxa has been recently modified as a result of human activity (invasive species). The taxa can hybridise with each other, if present at the same locality.
- Mytilus edulis sensu stricto: Native to the North Atlantic.
- Mytilus edulis platensis ( = Mytilus chilensis), the Chilean mussel: Temperate waters in the Southern Hemisphere.[2]
- Mytilus galloprovincialis, the Mediterranean mussel: Native in the Mediterranean, the Black Sea and Western Europe. Introduced in the temperate North Pacific, South Africa and elsewhere in the Southern Hemisphere. A distinct lineage native to the Southern Hemisphere also exists.
- Mytilus trossulus: North Pacific, northern parts of the North Atlantic, Baltic Sea.
Mytilus edulis, strict sense [edit]
The Atlantic blue mussel is native on the North American Atlantic coast, but is found intermixed with M. trossulus north of Maine. In Europe it is found from French Atlantic coast northwards to Novaya Zemlya and Iceland, but not in the Baltic Sea. In France and in the British Isles, it makes hybrid zones with M. galloprovincialis, and also is sometimes intermixed with M. trossulus.
A genetically distinct lineage of M. edulis is present in the Southern Hemisphere, and has been attributed to subspecies Mytilus edulis platensis. This includes the Chilean mussel.[2]
Habitat [edit]
Blue mussels are boreo-temperate invertebrates that live in intertidal areas attached to rocks and other hard substrates by strong (and somewhat elastic) thread-like structures called byssal threads, secreted by byssal glands located in the foot of the mussel.
Description [edit]
The shape of the shell is triangular and elongate with rounded edges. The shell is smooth with a sculpturing of fine concentric growth lines but no radiating ribs. The shells of this species are purple, blue or sometimes brown in color, occasionally with radial stripes. The outer surface of the shell is covered by the periostracum which as eroded, exposes the colored prismatic calcitic layer. Blue Mussels are semi-sessile, having the ability to detach and reattach to a surface allowing the mollusk to reposition itself relative to the water position.
Reproduction [edit]
Mussels have separate sexes. Once the sperm and eggs are fully developed they are released into the water column for fertilization. Although there are about 10,000 sperm per an egg,[3] large proportions of eggs deposited by blue mussel are never fertilized. As few as 1% of larvae that do mature ever reach adulthood, the majority are eaten by predators before completing metamorphosis.
The reproductive strategy seen in blue mussels is characteristic of planktotrophs, by minimizing nutrients in egg production to the bare minimum they are able to maximize the number of gametes produced. If the adult mussels are stressed during the beginning of gametogenesis, the process is terminated.[4] When stressed while fresh gametes are present, adult mussels reabsorb gametes. Larvae viability is also effected by the condition of parents: high water temperatures, pollutants and scarcity of food, during gamete production.[4] The reduction in viability is probable to the lack of lipid reserves distributed to the eggs.
Larval development [edit]
Larval development can last from 15 to 35 days depending environmental conditions including salinity and temperature, as well as location. Larvea originating from Connecticut mature normally at 15–20 °C, though at 15 °C normal development occurs at salinities between 15 and 35 ppt and 20 at 35 ppt at 20 °C.[5]
The first stage of development is the ciliated embryo, which in 24-hours for fertilization form the trochophore. At this point although mobile, it is still reliant on the yolk for nutrients. Characterized by a functional mouth and alimentary canal the veliger stage also has cilia which are used for filtering food as well as propulsion. A thin translucent shell is secreted by the shell gland forming the notable straight hinge of the prodissoconch I shell. The veliger continues to mature forming the prodissoconch II shell. In the end stage of veliger development photosensitive eye spots and elongated foot with a byssal gland are formed.
Once the pediveliger is fully developed, its foot extends and makes contact with substrate. The initial contact with the substrate is loose. If the substrate is suitable, the larva will metamorphoses into the juvenile form, plantigrade, and attach byssus threads. The mussel will remain in that state until reaching 1-1.5mm in length. This attachment is the prerequisite for the foundation for the blue mussel population. In sheltered environments large masses sometimes form beds which offer shelter and food for other invertebrates. Byssal thread are secreted by byssal glands located in the foot of the mussel, and are made up of polyphenolic proteins are proteins which serve as a bioadhesive.[6]
Aggregation [edit]
Blue mussels occasionally form clumps, or aggregates, of individuals when population density is low.The mussels attach to one another via collagenous protein strands called byssal threads. The aggregates are observed mostly in Mussel fields, which are short-lived populations of Mussels, usually exhibiting a clumped distribution pattern.[7] It is hypothesized that the mussels form these aggregates to increase reproductive success in low density populations.[8] This hypothesis, however, has yet to be conclusively proven. Alternative possible reasons for the behavior include resisting wave action and increasing water flow through the siphons of the mussel. The significance of the behavior is its relation to the formation of mussel beds from mussel fields. Mussel beds are persistent, dense mussel populations. Beds generally form from fields that persist long enough to establish a dense population.[7] Thus in areas where blue mussels are threatened, such as the Wadden Sea, it is of great importance to enhance the survival of mussel fields, of which mussel aggregates are the primary component.
Predators [edit]
Predation of blue mussels is greatest during the 3 weeks it spends as a planktonic larva. During this stage it is susceptible to jellyfish and fish larvae through adults. Once it metamorphoses the mussel is still restricted by predation, with smaller mussels with thinner, weaker shells most affected. Once the shells becomes stronger, blue mussels are preyed upon by sea stars such as Asterias vulgaris as well as by several species of sea gulls. Small mussels are also eaten by the dog whelk, Nucella lapillus.[9] The blue mussel is host to a wide range of parasites, but these parasites usually do not cause much damage.
Uses [edit]
Blue mussels are filter feeders and play a vital role in estuaries by removing bacteria and toxins.
Mytilus edulis is commonly harvested for food throughout the world, from both wild and farmed sources. Mussels are a staple of many seafood dishes in various cuisines including Spanish (especially Galician), Portuguese, French, Dutch, Belgian and Italian. They are also commonly used as lab animals. Blue mussels were also harvested by the indigenous peoples of North America.[10]
Gallery [edit]
Numerous empty blue mussel shells on a beach in Iceland
References [edit]
- ^ Paul Sterry (1997). Collins Complete Guide to British Wildlife. HarperCollins. ISBN 978-0-00-723683-1.
- ^ a b Borsa, P., Rolland, V., Daguin-Thiebaut, C. (2012). "Genetics and taxonomy of Chilean smooth-shelled mussels, Mytilus spp. (Bivalvia: Mytilidae)". Comptes Rendus Biologies 335: 51–61. Retrieved June 2012.
- ^ Thomas, Thomas R.J. (1979). "Fecundity and reproductive effort in the blue mussel, the sea urchin, and the snow crab from populations in Nova Scotia and Newfoundland". J. Fish. Res. Board Canada (36): 955–964.
- ^ a b Bayne, B.; Widdows, J.; Thompson, R. (1976). Marine mussels: their ecology and physiology. New York, NY: Cambridge University Press. pp. 261–291.
- ^ HRS-Brenko, M.; Calabrese, A. (1976). "The combined effects of salinity and temperature on larvae of the mussel Mytilus edulis". Marine Biology: 224–266.
- ^ Rzepecki, Leszek M.; Hansen, Karolyn M.; Waite, J. Herbert (August 1992). "Characterization of a Cystine-Rich Polyphenolic Protein Family from the Blue Mussel Mytilus edulis L.". Biological Bulletin 183 (1): 123–37. doi:10.2307/1542413. JSTOR 1542413.
- ^ a b Georg Nehls, Sophia Witte, Heike Büttger, Norbert Dankers, Jeroen Jansen, Gerald Millat, Mark Herlyn, Alexandra Markert, Per Sand Kristensen, Maarten Ruth, Christian Buschbaum and Achim Wehrmann, 2009. Beds of blue mussels and Pacific oysters. Thematic Report No. 11. In: Marencic, H. & Vlas, J. de (Eds.), 2009. Quality Status Report 2009. WaddenSea Ecosystem No. 25. Common Wadden Sea Secretariat, Trilateral Monitoring and Assessment Group, Wilhelmshaven, Germany.
- ^ DOWNING, J. and DOWNING, W. 1992. Spatial Aggregation, Precision, and Power in Surveys of Fresh-Water Mussel Populations. Can. J. Fish. Aquat. Sci. 49(5): 985-991. doi:10.1139/f92-110.
- ^ Petraitis, P. S. (1987). "Immobilization of the Predatory Gastropod , Nucella lapillus, by its prey, Mytilus edulis". Biol Bull. 172: 307-314.
- ^ http://books.google.com/books?id=fvuChpvgVZAC&pg=PA33&dq=%22Blue+mussel%22+native&hl=en&sa=X&ei=A7ovUbnWOsrK0wHdnoHQAw&ved=0CEsQ6AEwBQ#v=onepage&q=%22Blue%20mussel%22%20native&f=false
- Department of Marine Resources
- Gilbertson, Lance. (1999). Zoology Laboratory Manual (4th ed.), pp. 11.1-11.4. The McGraw-Hill Companies, Inc.
- Environmental Health Perspectives- Mercury-binding proteins from the marine mussel, Mytilus edulis.
- Fisheries and Oceans Canada - Blue mussel
- Bayne, B., Widdows, J., & Thompson, R. (1976). Physiological integrations. In B. B.L., & ed., Marine mussels: their ecology and physiology (pp. 261–291). New York: Cambridge University Press.
- HRS-Brenko, M., & A., C. (1969). The combined effects of salinity and temperature on larvae of the mussel Mytilus edulis. Marine Biology, 224-266.
- Newell, R. I. (1989). Species profiles: life histories and environmental requirements of coastal fishes and invertebrates (North and Mid-Atlantic)--blue mussel. U.S. Fish. Wildl. Serv. Biol. Rep. 82(11. 102 ). U.S. Army Corps of Engineers, TR El-82-4. 25 pp.
- Thompson, R. (1979). Fecundity and reproductive effort in the blue mussel, the sea urchin, and the snow crab from populations in Nova Scotia and Newfoundland. J. Fish. Res. Board Canada, 955-964.
Unreviewed
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