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Overview
Brief Summary
Biology
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Description
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Comprehensive Description
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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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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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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Hostens, K.; Mees, J. (1999). The mysid-feeding guild of demersal fishes in the brackish zone of the Westerschelde estuary. J. Fish Biol. 55: 704-719
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1145
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Vine, P. (1986). Red Sea Invertebrates. Immel Publishing, London. 224 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=5987
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Adema, J.P.H.M. (1991). De krabben van Nederland en Belgie (Crustacea, Decapoda, Brachyura) [The crabs of the Netherlands and Belgium (Crustacea, Decapoda, Brachyura)]. Nationaal Natuurhistorisch Museum: Leiden, The Netherlands. ISBN 90-73239-02-8. 244 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=51
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Annys, A. (1984). Verslag excursie naar Sas van Goes (Ned.) op 9 oktober 1983 [Report on the excursion to Sas van Goes (Netherlands), 9 October 1983]. De Strandvlo 4(1): 18-19
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=757
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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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Crosnier, A. (1962). Faune de Madagascar. XVI Crustaces Decapodes: Portunidae.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=5919
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Robinson, T.B.,Griffiths, C.L.,and Kruger, N. (2004). Distribution and status of marine invasive species in and bordering the West Coast National park. Koedoe 47 (1):79-87. Pretoria. ISSN 0075-6458
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=42339
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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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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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Charles H.J.M. Fransen
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=42308
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Emmerson W.D. A comparison between decapod Species common to both Mediterranean and Southern African Waters.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=42379
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Branch G.M., Griffiths C.L., Branch M.L. & Beckley L.E. (1994). Two Oceans. A guide to the marine life of Southern Africa. David Philip, Cape Town, 360 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=21781
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Raymond B.Manning & L. B. Holthuis (1981). West Africa Brachyuran Crabs (Crustacea: DECAPODA). Smithsonian Contributions to Zoology, Number 306, Smithsonian Institution Press. Washington, USA. 306-379pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=42414
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Robinson, T.B.,Griffiths, C.L., McQuaid, C.D. and Rius, M.(2005). Marine alien species of South Africa — status and impacts. African Journal of Marine Science 2005, 27(1): 297–306
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=42451
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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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Lock K., Beyst B. & Mees J. (1999). Circadiel patterns in the tidal plankton of a sandy beach in Zeebrugge (Belgium). Belgian Journal of Zoology, 129, 2, 339-352.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=17174
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d'Udekem d'Acoz, C. (1991). Reproduction in a population of shore crabs Carcinus maenas (Linnaeus, 1758) in the Southern North Sea. Belg. J. Zool. 121 (suppl. 1): 18
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=132999
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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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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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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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Asselberghs, M. (1989). Report on the beach excursion at Oostduinkerke on 4 November 1989 [Verslag van de strandwandeling te Oostduinkerke op 4 november 1989]. De Strandvlo 9(4): 121-123
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=138707
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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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De Maersschalck, V. (2004). An inventory of the macrofauna of the Sluice Dock at Oostende: contribution to an integrated management [Een inventarisatie van de macrofauna van de Spuikom te Oostende: bijdrage tot een geïntegreerd beheer]. MSc Thesis. Universiteit Gent, Vakgroep Biologie: Gent, Belgium. 71, tables, figures pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=133008
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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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Heip, C.H.R.; Herman, R.L.; Bisschop, G.; Govaere, J.C.R.; Holvoet, M.; van Damme, D.; Vanosmael, C.; Willems, K.R.; De Coninck, L.A.P. (1979). Benthic studies of the Southern Bight of the North Sea and its adjacent continental estuaries: Progress Report 1, in: (1979). Coordinated Research Actions Interuniversitary Actions Oceanology: symposium reports. pp. 133-163
http://www.marinespecies.org/ophiuroidea/aphia.php?p=sourcedetails&id=132916
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Türkay, M. (2001). Decapoda, 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. 284-292
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1392
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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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Leloup, E. (1941). Contributions à l'étude de la faune belge: 11. Les crustacés Décapodes Brachyoures de la côte belge [Contributions to the study of Belgian fauna: 11. The Decapoda Brachyura of the Belgian coast]. Bull. Mus. royal d'Hist. Nat. Belg./Med. Kon. Natuurhist. Mus. Belg. 17(11): 1-19
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1613
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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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d'Udekem d'Acoz, C. (1989). A note on the Crustacea Decapoda of the eastern harbour wall of Zeebrugge, and in particular on Processa edulis (Risso, 1816) [Note sur les Crustacés Décapodes de la jetée orientale du port de Zeebrugge et en particulier sur Processa edulis (Risso, 1816), Thoralus cranchii (Leach, 1817) et Pandalina brevirostris (Rathke, 1843)]. De Strandvlo 9(1): 13-20
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=138712
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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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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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Vanhaelen, M.-Th. (1990). Observations at Koksijde and Oostduinkerke after the heavy winter storms of 26-27 February and 1-2 March 1990 [Waarnemingen te Koksijde en Oostduinkerke na de zware winterstormen van 26-27 februari en 1-2 maart 1990]. De Strandvlo 10(4): 88-92
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=138623
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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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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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Lock, K.; Mees, J.; Vincx, M.; Goethals, P.L.M. (2011). Did global warming and alien invasions affect surf zone hyperbenthic communities on sandy beaches in Belgium? Hydrobiologia 664: 173-181, + suppl. mat.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=150292
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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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Lioris, D., Rucabado, J. 1998. Guide d'identification des Ressources Marines Vivantes du Maroc. Guide FAO d'identification des espèces pour les besoins de la pêche. Organisation des Nations Unies pour l'Alimentation et l'Agriculture : 263pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=164103
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Geographic Range
The green crab is native to the Atlantic Ocean off of the coast of Europe. Around the early eighteen hundreds the green crab was first seen on the Atlantic coast of North America. The crab can now be found from ranging from as far north as Nova Scotia and to the southern state of Virginia. In the late eighties, the crab mysteriously showed up in the San Francisco Bay area, and has since been spotted as far north as Oregon. This crab has also been found in such areas as far reaching as the continent of Australia.(Deegan, et al 1999, Holden 1997)
Biogeographic Regions: atlantic ocean (Native ); pacific ocean (Native )
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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National Distribution
Canada
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
United States
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
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Range
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Physical Description
Morphology
Physical Description
The name, green crab, can be deceiving. The color of this crab depends on the molting cycle the crab is undergoing. These colors can range from green to orange and even red in some cases. Green crabs are also visibly identifiable by the yellowish spots on the abdomen, which are also accompanied by five small spines also located on the front edge of the shell. The adult green crab only grows to about three inches in width and two inches in length. (Washington Dept 1997, Jaquette 1998)
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Ecology
Habitat
The green crab resides among tidal marshes, sandflats, and coasts with a rocky terrain. They tend to stay around these areas for protection from predators, and to be close to a readily available food supply.(Holden 1997, Deegan, et al 1999)
Aquatic Biomes: coastal
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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 63 samples.
Environmental ranges
Depth range (m): -3 - 113
Temperature range (°C): 8.938 - 12.348
Nitrate (umol/L): 2.283 - 16.868
Salinity (PPS): 22.343 - 35.363
Oxygen (ml/l): 6.069 - 7.118
Phosphate (umol/l): 0.312 - 0.890
Silicate (umol/l): 2.147 - 11.419
Graphical representation
Depth range (m): -3 - 113
Temperature range (°C): 8.938 - 12.348
Nitrate (umol/L): 2.283 - 16.868
Salinity (PPS): 22.343 - 35.363
Oxygen (ml/l): 6.069 - 7.118
Phosphate (umol/l): 0.312 - 0.890
Silicate (umol/l): 2.147 - 11.419
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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Trophic Strategy
Food Habits
The green crab enjoys a variety of different foods. These foods include clams, oysters, mussels, and other small crabs. The green crab is very dexterous and has many ways in which to open up the shellfish on which it feeds. The green crab is known as a very vicious carnivore that will consume anything it can get its claws on.(Holden 1997, Washington Dept. 1997)
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Associations
Animal / parasite / endoparasite
Portunion meanadis endoparasitises visceral cavity of Carcinus maenas
Animal / parasite / endoparasite
adult of Sacculina carcini endoparasitises body of Carcinus maenas
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Known predators
Conger conger
Trigla lucerna
Dicentrarchus labrax
Ciliata mustella
Based on studies in:
Portugal (Estuarine)
This list may not be complete but is based on published studies.
- L. Saldanha, Estudio Ambiental do Estuario do Tejo, Publ. no. 5(4) (CNA/Tejo, Lisbon, 1980).
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Known prey organisms
detritus
Mytilus galloprovincialis
Based on studies in:
Portugal (Estuarine)
This list may not be complete but is based on published studies.
- L. Saldanha, Estudio Ambiental do Estuario do Tejo, Publ. no. 5(4) (CNA/Tejo, Lisbon, 1980).
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Life History and Behavior
Reproduction
The mating process of the green crab begins with the seeking out of a recently molted female crab by a male green crab. The female lays eggs which she carries in a pouch underneath her abdomen where the male crab fertilizes them. The female green crab can lay as many as a hundred thousand eggs at one time. Following fertilization, the females then travel to deeper water to more stable water conditions where the eggs begin to develop. Once the eggs have developed into a larvae,or the zoea stage, the larvae then return to the surface waters for about two weeks. Once the larvae have entered the final stage of development or the megalopae stage, the young crabs travel to the coastal waters where they begin a molting cycle and life as a juvenile crab. In approximately three years the juvenile crab will become a fully developed crab and be able to mate and reproduce.(Bamber and Naylor 1997, Washington Dept. 1997)
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Molecular Biology and Genetics
Molecular Biology
Barcode data: Carcinus maenas
There are 102 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: Carcinus maenas
Public Records: 102
Specimens with Barcodes: 131
Species With Barcodes: 1
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Conservation
Conservation Status
No conservation of the green crab is currently under way.
US Federal List: no special status
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National NatureServe Conservation Status
Canada
Rounded National Status Rank: NNR - Unranked
United States
Rounded National Status Rank: NNR - Unranked
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Threats
Management
Conservation
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Relevance to Humans and Ecosystems
Benefits
Economic Importance for Humans: Negative
Due to the number of shell fish the green crab eats, and the rate at which it is done, the green crab is seen as a large threat to the many of the nations commercial shellfisheries. It is estimated that millions of dollars could be spent and are spent each year to try and thwart the green crabs from destroying a very important industry, and helping to maintain biodiversity in areas poplutlated by the green crab. The green crab also carries a parasitic worm that can infect birds that prey on the crabs. This can have a potentially devastating effect by throwing off the food chain, and on the ecosystem as a whole in these areas. (Washington Sea 1998, Washington Dept.1997, Jaquette 1998, Holden 1997)
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Economic Importance for Humans: Positive
The green crab serves no basic benefit to humans.
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Wikipedia
Carcinus maenas
- "Shore crab" redirects here. This may also be used for crabs in the superfamily Grapsoidea.
Carcinus maenas is a common littoral crab, and an important invasive species, listed among the 100 "world's worst alien invasive species".[2] It is native to the north-east Atlantic Ocean and Baltic Sea, but has colonised similar habitats in Australia, South Africa, South America and both Atlantic and Pacific coasts of North America. It grows to a carapace width of 90 millimetres (3.5 in), and feeds on a variety of molluscs, worms and small crustaceans, potentially impacting a number of fisheries. Its successful dispersion has occurred via a variety of mechanisms, such as on ships' hulls, packing materials, bivalves moved for aquaculture, and rafting.
C. maenas is known by different names around the world. In the British Isles, it is generally referred to simply as the shore crab. In North America and South Africa, it bears the name green crab or European green crab. In Australia and New Zealand, it is referred to as either the European green crab or European shore crab.
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Description [edit]
C. maenas has a carapace up to 60 millimetres (2.4 in) long and 90 mm (3.5 in) wide,[3] but can be larger outside its native range, reaching 101 mm (4.0 in) wide in British Columbia.[4] The carapace has five short teeth along the rim behind each eye, and three undulations between the eyes. The undulations, which protrude beyond the eyes, are the simplest means of distinguishing C. maenas from the closely related C. aestuarii, which can also be an invasive species. In C. aestuarii, the carapace lacks any bumps and extends forward beyond the eyes. Another characteristic for distinguishing the two species is the form of the first and second pleopods (collectively the gonopods), which are straight and parallel in C. aestuarii, but curve outwards in C. maenas.[3]
The colour of C. maenas varies greatly, from green to brown, grey or red. This variation has a genetic component, but is largely due to local environmental factors.[5] In particular, individuals which delay moulting become red–coloured rather than green. Red individuals are stronger and more aggressive, but are less tolerant of environmental stresses, such as low salinity or hypoxia.[6]
Native and introduced range [edit]
C. maenas is native to European and North African coasts as far as the Baltic Sea in the east, and Iceland and central Norway in the north, and is one of the most common crabs throughout much of its range. In the Mediterranean Sea, it is replaced by the closely related species Carcinus aestuarii.
C. maenas was first observed on the east coast of North America in Massachusetts in 1817, and may now be found from southern Virginia northwards; by 2007, this species had extended its range northwards to Placentia Bay, Newfoundland.[7] In 1989, the species was found in San Francisco Bay, California, on the Pacific coast of the United States. Until 1993, it was not able to extend its range, but reached Oregon in 1997, the state of Washington in 1998 and British Columbia in 1999,[8][9] thus extending its range by 750 kilometres (470 mi) in ten years.[10] By 2003, C. maenas had extended to South America with specimens discovered in Patagonia.[11]
In Australia, C. maenas was first reported "in the late 1800s",[12] in Port Phillip Bay, Victoria. It has since spread along the south-eastern and south-western seaboards, reaching New South Wales in 1971, South Australia in 1976 and Tasmania in 1993. One specimen was found in Western Australia in 1965, but there have been no further discoveries in the area since.[12]
C. maenas first reached South Africa in 1983, in the Table Docks area near Cape Town.[13] Since then, it has spread at least as far as Saldanha Bay in the north and Camps Bay in the south, over 100 kilometres (62 mi) apart.
There have been appearances of C. maenas recorded in Brazil, Panama, Hawaii, Madagascar, the Red Sea, Pakistan, Sri Lanka and Myanmar; however, these have not resulted in invasions, but remain isolated findings. Japan has been invaded by a related crab, either C. aestuarii or a hybrid of C. aestuarii and C. maenas.[14]
It is believed, based on the ecological conditions, that C. maenas could eventually extend its range to colonise the Pacific coast of North America from Baja California to Alaska.[8] Similar ecological conditions are to be found on many of the world's coasts, with the only large potential area not to have been invaded yet being New Zealand; the New Zealand government has taken action, including the release of a Marine Pest Guide[15] in an effort to prevent colonisation by C. maenas.
Ecology [edit]
C. maenas can live in all types of protected and semi-protected marine and estuarine habitats, including habitats with mud, sand, or rock substrates, submerged aquatic vegetation, and emergent marsh, although soft bottoms are preferred. C. maenas is euryhaline, meaning that it can tolerate a wide range of salinities (from 4 to 52 ‰), and survive in temperatures of 0 to 30 °C (32 to 86 °F).[16] The wide salinity range allows C. maenas to survive in the lower salinities found in estuaries. A molecular biological study using the COI gene found genetic differentiation between the North Sea and the Bay of Biscay, and even more strongly between the populations in Iceland and the Faroe Islands and those elsewhere. This suggests that C. maenas is unable to cross deeper water.[17]
Females can produce up to 185,000 eggs, and larvae develop offshore in several stages before their final moult to juvenile crabs in the intertidal zone.[18] Young crabs live among seaweeds and seagrasses, such as Posidonia oceanica, until they reach adulthood.[19]
C. maenas has the ability to disperse by a variety of mechanisms,[18] including ballast water, ships' hulls, packing materials (seaweeds) used to ship live marine organisms, bivalves moved for aquaculture, rafting, migration of crab larvae on ocean currents, and the movement of submerged aquatic vegetation for coastal zone management initiatives. Thresher et al.[12] found C. maenas dispersed in Australia mainly by rare long-distance events, possibly caused by human actions.
C. maenas is a predator, feeding on many organisms, particularly bivalve molluscs (such as clams, oysters, and mussels), polychaetes and small crustaceans.[20] They are primarily nocturnal, although activity also depends on the tide, and crabs can be active at any time of day.[21] In California, preferential predation of C. maenas on native clams (Nutricola spp.) resulted in the decline of the native clams and an increase of a previously introduced clam (the amethyst gem clam, Gemma gemma).[22] C. maenas has been implicated in the destruction of the soft-shell clam (Mya arenaria) fisheries on the east coast of the United States and Canada, and the reduction of populations of other commercially important bivalves (such as scallops, Argopecten irradians, and northern quahogs, Mercenaria mercenaria).[18] The prey of C. maenas includes the young of bivalves[23] and fish, although the effect of its predation on winter flounder, Pseudopleuronectes americanus is minimal.[24] C. maenas can, however, have substantial negative impacts on local commercial and recreational fisheries, by preying on the young of species, such as oysters and the Dungeness crab, or competing with them for resources.[25]
Control [edit]
Due to its potentially harmful effects on ecosystems, various efforts have been made to control introduced populations of C. maenas around the world. In Edgartown, Massachusetts, a bounty was levied in 1995 for catching C. maenas, to protect local shellfish, and 10 tons were caught.[26]
There is evidence that the native blue crab in eastern North America, Callinectes sapidus, is able to control populations of C. maenas; numbers of the two species are negatively correlated, and C. maenas is not found in the Chesapeake Bay, where Callinectes sapidus is most frequent.[27] On the west coast of North America, C. maenas appears to be limited to upper estuarine habitats, in part because of predation by native rock crabs (Romaleon antennarium and Cancer productus) and competition for shelter with a native shore crab, Hemigrapsus oregonensis.[28] Host specificity testing has recently been conducted on Sacculina carcini, a parasitic barnacle, as a potential biological control agent of C. maenas.[29] In the laboratory, Sacculina settled on, infected, and killed native California crabs, including the Dungeness crab, Metacarcinus magister (formerly Cancer magister), and the shore crabs Hemigrapsus nudus, Hemigrapsus oregonensis and Pachygrapsus crassipes. Dungeness crabs were the most vulnerable of the tested native species to settlement and infection by the parasite. Although Sacculina did not mature in any of the native crabs, developing reproductive sacs were observed inside a few Metacarcinus magister and Hemigrapsus oregonensis. Any potential benefits of using Sacculina to control C. maenas on the west coast of North America would need to be weighed against these potential non-target impacts.[29]
Fishery [edit]
C. maenas is fished on a small scale in the north-east Atlantic Ocean, with approximately 1200 tonnes being caught annually, mostly in France and the United Kingdom. In the northwest Atlantic, C. maenas was the subject of fishery in the 1960s, and again since 1996, with up to 86 tonnes being caught annually.[30]
Taxonomic history [edit]
Carcinus maenas was first given a binomial name, Cancer maenas, by Carl Linnaeus in his 1758 10th edition of Systema Naturae.[31] An earlier description was published by Georg Eberhard Rumphius in his 1705 work De Amboinsche Rariteitkamer, calling the species Cancer marinus sulcatus, but this predates the starting point for zoological nomenclature.[31] A number of later synonyms have also been published:[31]
| External identifiers for Carcinus maenas | |
|---|---|
| Encyclopedia of Life | 128502 |
| ITIS | 98734 |
| NCBI | 6759 |
| WoRMS | 107381 |
| Also found in: Wikispecies, ADW, MarLIN | |
- Monoculus taurus Slabber, 1778
- Cancer granarius Herbst, 1783
- Cancer viridis Herbst, 1783
- Cancer pygmaeus Fabricius, 1787
- Cancer rhomboidalis Montagu, 1804
- Cancer granulatus Nicholls, 1943
- Megalopa montagui Leach, 1817
- Portunus menoides Rafinesque-Schmaltz, 1817
- Portunus carcinoides Kinahan, 1857
The lectotype chosen for the species came from Marstrand, Sweden, but it is assumed to have been lost.[31] In 1814, writing for The Edinburgh Encyclopaedia, William Elford Leach erected a new genus, Carcinus to hold this species alone (making it the type species of the genus, by monotypy).[31] In 1847, Nardo described a distinct subspecies occurring in the Mediterranean Sea, which is now recognised as a distinct species, Carcinus aestuarii.[1]
Unreviewed
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