Invasion History

First Non-native North American Tidal Record: 1992
First Non-native West Coast Tidal Record: 1992
First Non-native East/Gulf Coast Tidal Record:

General Invasion History:

Mytilus edulis has long been treated as a single species, naturally distributed through the temperate regions of the Northern and Southern Hemispheres. However, taxonomists have identified geographical subspecies or full species, based on subtle morphological features (McDonald et al. 1991). The use of molecular techniques, initially amino-acid electrophoresis, and later DNA assays, has enabled biologists to define the ranges of the three major species of the complex, M. edulis, described by Linneaus from Sweden; M. galloprovincialis (Lamarck 1819), described from the Mediterranean; and M. trossulus (Gould 1850), described from Oregon. These techniques have also enabled researchers to document cryptic invasions and hybridization among members of the M. edulis complex (McDonald et al. 1991; Heath et al. 1995; Hilbish et al. 2000; Rawson et al. 2001; Shields et al. 2008; Shields et al. 2010).

Mytilus edulis, as currently defined, is native to the North Atlantic from Newfoundland, Iceland, northern Norway, and the White Sea, south to Cape Hatteras, North Carolina (NC) and the Bay of Biscay, at the French-Spanish border (Hutchins 1947; McDonald et al. 1991; Hilbush et al. 2000; Jones et al. 2008). In 2004, a small, isolated population was discovered in Svalbard (78N), apparently recently transported by the West Spitsbergen Current. This mussel had been absent on Svalbard for at least 1000 years (Berge et al. 2005). At the northern and Baltic borders, M. edulis co-occurs and hybridizes with M. trossulus, the high-latitude Atlantic-Pacific-Baltic species (McDonald et al. 1991; Hilbush et al. 2000; Rawson et al. 2001; Smietanka et al. 2004.). Where the two species co-occur, M. trossulus ranges further into brackish water, apparently based on greater larval tolerance to low salinity (Qiu et al. 2002).  In the east Atlantic, at its sorthern border in Portugal, it hybridizes with M. galloprovincialis (McDonald et al. 1991; Hilbush et al. 2000). In the west Atlantic, the traditional limit for Mytilus edulis has been Cape Hatteras, a major biogeographical boundary (Hutchins 1947), but occasional settlement has been seen as far south as Beaufort, NC, facilitated by upwellings of cool water (Wells and Gray 1960). Jones et al. (2009) did temperature tolerance experiments that suggest that survival at Beaufort and Oregon Inlet would be poor, and predict that the southern limit of M. edulis is shifting northward. Mytilus edulis has been introduced to British Columbia, in aquaculture operations (Heath et al. 1995; Shields et al. 2008; Shields et al. 2010), and to Chile, Australia, and New Zealand by ballast water, fouling, or aquaculture (Westfall and Gardner 2010). Most specimens identified during genetic surveys have been hybrids, either with native M. trossulus, with the presumably native Southern Hemisphere genotype of M. galloprovincialis (in Chile, Australia, and New Zealand), or the introduced Northern Hemisphere form of M. galloprovincialis (Heath et al. 1995; Shields et al. 2008; Shields et al. 2010; Westfall and Gardner 2010). However, a small percentage of Mytilus surveyed in British Columbia were identified as purebred M. edulis (Shields et al. 2010). Purebred M. edulis have been identified from the Atlantic coast of Argentina, the Falkland Islands, and southern Chile (McDonald et al. 1991; Oyarzun et al. 2016). Oyarzun et al. (2016) consider the southwest Atlantic populations as native, but we treat them as cryptogenic.

North American Invasion History:

Invasion History on the West Coast:

Early (pre-1990s) references to 'M. edulis' on the West Coast mostly refer to the native M. trossulus, although introductions of varieties or subspecies of the widely defined species were frequently suspected (Carlton 1979). Attempts at cultivating M. trossulus in Canada have been unsuccessful, because of its low meat yield, fragile shells, and in British Columbia high, mortality in culture (Heath et al. 1995; Rawson 2001). Importation of M. edulis was suggested as a solution to these problems (Jamieson 1989, cited by Heath et al. 1995). Mytilus edulis was imported from Prince Edward Island in 1992, raised for one generation in closed systems, and the F2 generation was stocked in a mussel farm in Genoa Bay, Vancouver Island. Mussels derived from this stock are/were being raised in at least four aquaculture operations in the Strait of Georgia (Centre for Shellfish Research, Vancouver Island University, Genotypes of 'alien mussels' and hybrids with M. trossulus were detected in British Columbia waters by Heath et al. (1995), although they could not distinguish between M. edulis and M. galloprovincialis. Shields et al. (2008) found that 8 of 292 animals sampled at Ladysmith, Vancouver Island, in 2006 were M. galloprovincialis X M. edulis hybrids, although no purebred animals were found. Using a different locus, on mussels sampled in 2006 at Ladysmith, 2% of animals at Ladysmith were purebred M. edulis, 2% were M. edulis X M. trossulus, and 4% were M. edulis X M. galloprovincialis (Shields et al. 2010). Additional M. trossulus X M. edulis hybrids were found on floats in Burrard Inlet, Vancouver Harbour in 2004 (Richoux et al. 2006). While these numbers are quite small, they suggest that M. edulis genotypes are likely to persist in the population.

Invasion History Elsewhere in the World:

Mytilus edulis has been introduced to several locations in the Southern Hemisphere, where they have hybridized with a presumably native form of M. galloprovincialis, which probably colonized the region in prehistoric times (Hilbish et al. 2000; Westfall et al. 2010), and with the more recently introduced M. galloprovincialis, bearing Northern Hemisphere genotypes (Westfall et al. 2010). Purebred M. edulis have been found in the southwest Atlantic, in Argentina, the Falkland Islands, and southern Chile (McDonald et al. 1991; Oyarzun et al. 2016). A high frequency (15-95%) of M. edulis was found in the eastern portion of the Strait of Magellan (Oyarzun et al. 2016). Purebred M. edulis have not yet been found in the Southern Hemisphere, but hybrid mussels with M. edulis markers have been found in bays in Chile, Australia (Port Phillip Bay and Tasmania), and at several sites in New Zealand, including the relatively isolated Auckland Islands, located southeast of the main islands. These mussels were sampled in 1994-2010 (Westfall et al. 2010), but the dates of introduction of M. edulis to these regions are not known. It is likely that shipping (both fouling and ballast water) and aquaculture have transported M. edulis to the Southern Hemisphere. In Chile, mussel aquaculture is especially important, while in the case of the Auckland Islands, 19th century whaling ships are a likely vector, since travel to these islands (now a conservation reserve) has been restricted in recent decades (Westfall et al. 2010). However, a recent analysis using Single Nucleotide Polymorphisms (SNPs) indicates that the 'edulis-like' genotypes represent native cryptic species, M. platensis in the Southwest Atlantic, M. planulatus, and M. aoteanus in islands south of New Zealand. Mytilus spp. in the Falkland Islands and Kerguelen were a mixture of M. platensis and M. chilensis. In this view, invasions of Northern Hemisphere Mytilus are much less extensive than reported in earlier papers (Zbawicka et al. 2019).


Mytilus edulis has a smooth shell which is roughly shaped like an elongate triangle, with the beak forming the apex. The anterior margin is straight, while the posterior margin is broadly rounded. The surface is marked by concentric growth lines. The exterior color is black to bluish-black, or brown, while the interior is white, with a violet margin, and a distinct muscle scar. The shell can reach a length (height) of 100 mm (Abbott 1974; Morris 1975; Gosner 1978). Like other mussels, M. edulis clings to hard surfaces (rocks, logs, structures) by a cluster of byssus threads.

Mytilus edulis is part of the M. edulis species complex, which includes M. galloprovincialis, M. trossulus, and possibly other species (e.g. M. chilensis, M. desolationis) whose distinctness is disputed (Westfall and Gardner 2010). Mytilus edulis tends to have a longer hinge plate and adductor muscle scar than either M. galloprovincialis or M. trossulus. However, overlap is considerable. The species are best distinguished morphologically by statistical analysis of multiple measurements (McDonald et al. 1991) or by molecular methods (McDonald et al. 1991; Heath et al. 1995; Shields et al. 2008; Westfall and Gardner 201; Zbawicka et al. 2019).

Larvae of M. edulis are described by Chanley and Andrews (1971). Late veligers are roughly egg-shaped, with a prominent eye-spot. Settlement occurs at 215-305 μm (Chanley and Andrews 1971). To our knowledge, larvae of M. edulis cannot be distinguished visually from those of M. galloprovincialis or M. trossulus.


Taxonomic Tree

Kingdom:   Animalia
Phylum:   Mollusca
Class:   Bivalvia
Subclass:   Pteriomorphia
Order:   Mytiloida
Family:   Mytilidae
Genus:   Mytilus
Species:   edulis


Potentially Misidentified Species

Mytilus aoteanus
Mytilus aoteanus (Powell 1958) was described from the Campbell and Auckland Islands. It had been treated as synonym of M. planulatus (Huber, in Appletans et al. 2019), but Zbawicka et al. (2019) found that it was genetically distinct.

Mytilus californianus
Mytilus californianus, native to the northeast Pacific, ranges from northern Mexico to Alaska. It is not a member of the M. edulis complex and can be easily distinguished by the radial ribs on its shell (McDonald et al. 1991).

Mytilus chilensis
Mytilus chilensis, described from the southeast Pacific, may be synonymous with the southern hemisphere genotype of M. galloprovincialis (McDonald et al. 1991; Westfall and Gardner 2010; Oyarzun et al. 2016). 

Mytilus desolationis
Mytilus desolationis, described from the sub-Antarctic island of Kerguelen, may be a distinct species or a hybrid, displaying affinities both to M. edulis and presumably native southern Hemisphere form of M. galloprovincialis (McDonald et al. 1991; Westfall and Gardner 2010).

Mytilus galloprovincialis
Mytilus galloprovincialis, the Mediterranean Mussel, is native to the Mediterranean Sea and the warmer waters of the European Atlantic, ranging north to the Atlantic shores of Ireland and Scotland. (McDonald et al. 1991, Hilbish 2000).

Mytilus trossulus
Mytilus trossulus, the Bay Mussel, is native to the North Atlantic and North Pacific, ranging north to Alaska, Siberia, and Labrador. In European waters, it is primarily found in the Baltic Sea (McDonald et al. 1991, Hilbish et al. 2000).   



Mytilus edulis has separate sexes and individuals mature at one year of age or less. This species has a prolonged spawning season, and in some habitats spawns year round (Seed 1969). Fertilized eggs develop into a planktonic trochophore larva, then into a shelled veliger. The larvae settle at 215-305 μm (Chanley and Andrews 1971). Larvae of Mytilus edulis can settle and metamorphose on a wide variety of surfaces, including rock, wood and vegetation. Initially, juveniles can be quite mobile, using their byssus threads to move up and down, and attaching to drifting substrates such as vegetation. As they grow, they are attracted to other mussels. Extensive beds develop on rocky surfaces, but also on soft sediments, in which mussels are connected to each other by byssus threads, creating a complex habitat (Bertness 1999; Buschbaum et al. 2009). Mussels are strong-filter feeders, and create substantial currents as they pump in water to ingest phytoplankton and other suspended material. They deposit the uneaten material as pseudofeces, creating deposits of silt around and within the mussel bed (Bertness 1999; Buschbaum et al. 2009).

Blue Mussels are characteristic of the shallow subtidal and intertidal zone, and can be subject to sharp changes in temperature when exposed to the air, and changes in salinity due to rainfall and river flow. Adult M. edulis can tolerate salinities of 10 PSU, but require at least 20 PSU for successful larval development (Hutchins 1947; Qiu et al. 2002; Jones et al. 2009). In experiments simulating trasport in ship fouling, 60-70% survived exposure to freshwater, for up to 14 days.  Freshwater survival was much, o.5 to 60% at 15-25 °C (Riley et ql. 2022).


phytoplankton, detritus


crabs, snails, fishes, birds, humans


barnacles, tunicates, bryozoans, seaweeds

Trophic Status:

Suspension Feeder



General HabitatGrass BedNone
General HabitatCoarse Woody DebrisNone
General HabitatOyster ReefNone
General HabitatMarinas & DocksNone
General HabitatRockyNone
General HabitatVessel HullNone
Salinity RangeMesohaline5-18 PSU
Salinity RangePolyhaline18-30 PSU
Salinity RangeEuhaline30-40 PSU
Tidal RangeSubtidalNone
Tidal RangeLow IntertidalNone
Tidal RangeMid IntertidalNone
Tidal RangeHigh IntertidalNone
Vertical HabitatEpibenthicNone

Life History

Tolerances and Life History Parameters

Minimum Temperature (ºC)-1.8Based on geographical range, occurrence in areas with sea ice
Maximum Temperature (ºC)35Water temperature, experimental, Jones et al. 2009.
Minimum Salinity (‰)10Experimental, Qiu et al. 2002.. In simulated voyages, using animals from the Netherlands, M. edulis had a high tolerance at 10.5-36 PSU (van der Gaag et al. 2016), with 1052 days for 100% mortality.
Maximum Salinity (‰)35Typical Atlantic Ocean salinity, probably tolerates higher salinities.
Minimum Reproductive Temperature16Onset of spawning, Gulf of St. Lawrence, Myrand et al. 2000
Maximum Reproductive Temperature12Larval development was unsuccessful at 6 C, but was completed at 12 C (Sprung 1984)
Minimum Reproductive Salinity20Experimental, development of eggs and larvae, Qiu et al. 2002
Maximum Reproductive Salinity35Typical Atlantic Ocean salinity, probably tolerates higher salinities
Minimum Duration20Lab, 18 C, Sprung 1984
Maximum Duration30Lab, 12 C, Sprung 1984
Minimum Length (mm)9based on field growth data, England, and spawning at 1 year of age (Seed 1969)
Maximum Length (mm)100Maximum adult length, Lippson and Lippson 1997
Broad Temperature RangeNoneCold temperate-Warm temperate
Broad Salinity RangeNoneMesohaline-Euhaline

General Impacts

In its native range, Mytilus edulis is ecologically and economically important, as a major ecosystem engineer, a major component of coastal food webs, and an important food resource (Bertness 1999; Buschbaum et al. 2009; Shields et al. 2010; Centre for Shellfish Research, Vancouver Island University, undated). However, as far as we know, M. edulis has become established in wild habitats, mostly as a hybrid with a low genotypic frequency, with native mussels (M. trossulus and the Southern Hemisphere genotype of M. galloprovincialis), or with introduced M. galloprovincialis (Shields et al. 2008; Shields et al. 2010; Westfall and Gardner 2010).

Economic Impacts

Fisheries- Mytilus edulis are being extensively cultured in open waters in The Strait of Georgia, British Columbia, where they are considered superior to the native M. trossulus, having higher meat yields, less fragile shells, and reduced likelihood of summer mortality (Rawson 2001; Centre for Shellfish Research, Vancouver Island University, undated). So far, purebred M. edulis have been found in the wild only at one location, and the frequency of hybrids is low, so the effect on 'natural' mussel populations appears to be small (Richoux et al. 2006; Shields et al. 2008; Shields et al. 2010).

Regional Impacts

NEP-IIIAlaskan panhandle to N. of Puget SoundEconomic ImpactFisheries
Mytilus edulis is actively cultured in open water on a large scale in British Columbia waters (Shields et al. 2008; Shields et al. 2010).

Regional Distribution Map

Bioregion Region Name Year Invasion Status Population Status
NEP-III Alaskan panhandle to N. of Puget Sound 1992 Def Unk
NA-S3 None 0 Native Estab
NA-S2 None 0 Native Estab
NA-ET1 Gulf of St. Lawrence to Bay of Fundy 0 Native Estab
NA-ET2 Bay of Fundy to Cape Cod 0 Native Estab
NA-ET3 Cape Cod to Cape Hatteras 0 Native Estab
AR-III None 0 Native Estab
B-II None 0 Native Estab
NEA-II None 0 Native Estab
NEA-III None 0 Native Estab
NEA-IV None 0 Native Estab
NEA-V None 0 Native Estab
AR-IV None 0 Native Estab
AR-V None 0 Native Estab
NZ-IV None 2009 Def Unk
AUS-VIII None 2009 Def Unk
AUS-IX None 2009 Def Unk
SEP-B None 2009 Crypto Unk
NZ-VIII None 2009 Def Unk
B-I None 0 Native Estab
B-III None 0 Native Estab
B-VII None 0 Native Estab
B-X None 0 Native Estab
AUS-X None 2009 Def Unk
B-VI None 0 Native Estab
NEA-VI None 1965 Def Failed
CAR-VII Cape Hatteras to Mid-East Florida 0 Native Unk
SEP-A' None 1988 Crypto Estab
SA-I None 1988 Crypto Estab

Occurrence Map

OCC_ID Author Year Date Locality Status Latitude Longitude


Abbott, R. Tucker (1974) American Seashells, Van Nostrand Reinhold, New York. Pp. <missing location>

Arzul, Isabelle and 10 authors (2011) Can the protozoan Bonamia ostreae infect larvae of flat oysters Ostrea edulis?, Veterinary Parasitology 179: 69-76

Ballasteros, M.; Madrenas, E.; Pontes, M. 2022 OPK Opisthobranquis- Doris pseudoargus (Von Rapp, 1827).

Barroso, Cristiane Xerez; Rabay, Soraya Guimarães; Matthews-Cascon, Helena (2018) Mollusks on recruitment panels placed in an offshore harbor in tropical northeastern Brazil , Arquivos de ciencias do mar 51(1): 65-74

Berge, Jørgen; Johnsen, Geir; Nilsen, Frank; Gulliksen, Bjørn; Slagstad, Dag (2005) Ocean temperature oscillations enable reappearance of blue mussels Mytilus edulis in Svalbard after a 1000 year absence, Marine Ecology Progress Series 303: 167-175

Bertness, Mark D. (1999) <missing title>, Sinauer Associates, Sunderland MA. Pp. 417

Boisset, Fernando; Ferrer-Gallego, P. Pablo (2015) Typification of the marine siphonous green algae Caulerpa prolifera (Bryopsidales,Chlorophyta), Phytotaxa 221(2): 148–156

Buschbaum, Christian and 8 authors (2009) Mytilid mussels: global habitat engineers in coastal sediments, Helgoland Marine Research Published online: <missing location>

Carlton, James T. (1979) History, biogeography, and ecology of the introduced marine and estuarine invertebrates of the Pacific Coast of North America., Ph.D. dissertation, University of California, Davis. Pp. 1-904

Chainho, Paula and 20 additional authors (2015) Non-indigenous species in Portuguese coastal areas, lagoons, estuaries, and islands, Estuarine, Coastal and Shelf Science <missing volume>: <missing location>

Chanley, Paul; Andrews, J. D. (1971) Aids for identification of bivalve larvae of Virginia, Malacologia 11(1): 45-119

Dean, T.A.; Hurd, L. E. (1980) Development in an estuarine fouling community: the influence of early colonists on later arrivals, Oecologia (Berl) 46: 295-301

Dijkstra, Jennifer A.; Simkanin, Christina (2016) Intraspecific response of colonial ascidians to variable salinity stress in an era of global change, Marine Ecology Progress Series 551: 215-225,

Durr, Simone; Wahl, Martin (2004) Isolated and combined impacts of the blue mussels Mytilus edulis and barnacles, Balanus improvius, on structure and diversity of a fouling community., Journal of Experimental Marine Biology and Ecology 306: 181-195

Gosner, Kenneth L. (1978) A field guide to the Atlantic seashore., In: (Eds.) . , Boston. Pp. <missing location>

Heath, David D..; Rawson, Paul D.; Hilbish, Thomas J. (1995) PCR-based nuclear markers identify alien blue mussel (Mytilus spp.) genotypes on the west coast of Canada, Canadian Journal of Fisheries and Aquatic Science 52: 2621-2627

Hilbish, T. J.; Mullinax, A.; Dolven, S. I.; Meyer, A.; Koehn, R. K.; Rawson, P. D. (2000) Origin of the antitropical distribution pattern in marine mussels (Mytilus spp.): Routes and timing of transequatorial migration, Marine Biology 136: 69-77

Hutchins, Louis W. (1947) The bases for temperature zonation in geographical distribution, Ecological Monographs 17(3): 325-335

Jones, Sierra J.; Mieszkowska, Nova; Wethey, David S. (2009) Linking thermal tolerances and biogeography: Mytilus edulis (L.) at its southern limit on the east coast of the United States, Biological Bulletin 217: 73-85

Joyce, Patrick W. S.; Smyth, David M.; Dick . Jaimie T. A. ; Kregting, Louise T. (2021) Coexistence of the native mussel, Mytilus edulis, and the invasive Pacific oyster,Crassostrea (Magallana) gigas, does not affect their growth or mortality, but reduces condition of both species, Hydrobiolgia 848: 1859-1871

Kijewski, T. and 5 authors (2011) Distribution of Mytilus taxa in European waters as inferred from molecular markers, Journal of Sea Research 65: 224-234

Lippson, Alice Jane; Lippson, Robert L. (1997) <missing title>, Johns Hopkins University Press, Baltimore. Pp. <missing location>

McDonald, J. H.; Seed, R.; Koehn, R. K. (1991) Allozymes and morphometric characters of three species of Mytilus in the Northern and Southern Hemispheres., Marine Biology 111(3): 323-334

Morris, Percy A. (1975) A field guide to shells of the Atlantic, Houghton-Mifflin, Boston. Pp. <missing location>

Myrand, Bruno; Guderley, Helga; Himmelman, John H. (2000) Reproduction and summer mortality of blue mussels Mytilus edulis in the Magdalen Islands, southern Gulf of St. Lawrence, Marine Ecology Progress Series 197: 193-207

Newell, Roger I. E.; Hilbish, Thomas J.; Koehn, Richard K.; Newell, Christine J. (1982) Temporal variation in the reproductive cycle of Mytilus edulis l. (Bivalvia, Mytilidae) from localities on the East Coast of the United States, Biological Bulletin 162: 299-310

Oyarzun, Pablo A.; Toro, Jorge E.; Canete, Juan I.; Gardner, Jonathan P. (2016) Bioinvasion threatens the genetic integrity of native diversity and a natural hybrid zone: smooth-shelled blue mussels (Mytilus spp.) in the Strait of Magellan, Biological Journal of the Linnean Society 117: 574-585

Qiu, Jian-Wen;Tremblay, Réjean; Bourget, Edwin (2002) Ontogenetic changes in hyposaline tolerance n the mussels Mytilus edulis and M. trossulus implications for distribution, Marine Ecology Progress Series 228: 143-152

Rawson, Paul D.; Hayhurst, Susan. Vanscoyoc, Brook (2001) Species composition of blue mussel populations in the northwestern Gulf of Maine, Journal of Shellfish Research 20(1): 31-38

Richoux, N. B.; Levings, C. D.; Lu, L.; Piercey, G. E. (2006) Preliminary survey of indigenous, non-indigenous and cryptogenic benthic invertebrates in Burrard Inlet, Vancover, British Columbia, Canadian Data Report of Fisheries and Aquatic Sciences 1183: 1-20

Riley, Cyrena; Drolet, David; Goldsmit, Hill, Jesica Jaclyn M.; Howland, Kimberly L.; Lavoie, Marie-France; Kenzie, Cynthia H.; Simard, Nathalie; M (2022) Experimental analysis of survival and recovery of ship fouling musseld during transit between marine and freshwaters, Frontiers in Marine Science 8(808007): Published online

Sarver, S. K.; Foltz, D. W. (1993) Genetic population structure of a species' complex of blue mussels (Mytilus spp.), Marine Biology 117: 105-112

Seed, R. (1969) The ecology of Mytilus edulis l. (Lamellibranchiata) on exposed rocky shores II. growth and mortality, Oecologia 3: 317-350

Shields, J. L.; Heath, J. W.; Heath, D. D. (2010) Marine landscape shapes hybrid zone in a broadcast spawning bivalve: introgression and genetic structure in Canadian west coast Mytilus, Marine Ecology Progress Series 399: 211-223

Shields, Jody L.; Barnes, Penny; Heath, Daniel D. (2008) Growth and survival differences among native, introduced and hybrid blue mussels (Mytilus spp.): genotype, environment and interaction effects., Marine Biology 154: 919-928

Smietanka, B.; Zbawicka, M.; Wolowicz, M.; Wenne, R. (2004) Mitochondrial DNA lineages in the European populations of mussels (Mytilus spp.), Marine Biology 146: 79-92

Soors, Jan; Faasse, Marco; Stevens, Maarten; Verbessem, Ingrid; De Regge, Nico;Van den Bergh, Ericia (2010) New crustacean invaders in the Schelde estuary (Belgium), Belgian Journal of Zoology 140: 3-10

Sorte, Cascade J. B.; Jones, Sierra J.; Miller, Luke P. (2013) Geographic variation in temperature tolerance as an indicator of potential population responses to climate change, Journal of Experimental Marine Biology and Ecology 400: 209-217

Sprung, Martin (1984) Physiological energetics of mussel larvae (Mytilus edulis). I. Shell growth and biomass, Marine Biology 17: 283-293

Wells, Harry W.; Gray, I. E. (1960) The seasonal occurrence of Mytilus edulis on the Carolina coast as a result of transport around Cape Hatteras, Biological Bulletin 119(3): 550-559

Westfall, Kristen M.; Gardner, Jonathan P. A. (2010) Genetic diversity of Southern hemisphere blue mussels (Bivalvia: Mytilidae) and the identification of non-indigenous taxa, Biological Journal of the Linnean Society 101: 898-909

White, C. ;Snodgrass, J. (1988) <missing title>, Office of Natural Resources Management, Brevard County, Titusville FL. Pp. 12 pp.

Wolff, W. J. (1973) The estuary as a habitat: An analysis of data on the soft-bottom macrofauna of the estuarine area of the rivers Rhine, Meuse, and Scheldt, Zoologische Verhandelingen 126: 4-242