Back to 
Animals
Back to 
Mytilidae
Back to Alphabetized Species List

Back to Completed Reports List

 

Species Name:      Perna viridis
Common Name:      (Asian Green Mussel)

 

I.  TAXONOMY

Kingdom Phylum/Division: Class: Order: Family: Genus:
Animalia Mollusca Bivalvia Lamellibranchia Mytilidae Perna



The non-native Asian green mussel, Perna viridis. Photo courtesy SERTC, Photograpger Susan Thornton-DeVictor.

  

Asian green mussels can attach to hard surfaces in large numbers by means of protenaceous byssal threads. Photo courtesy USCG, Photograpger Buck Albert.

Species Name: 
Perna viridis Linnaeus, 1758

Common Name(s):
Asian Green Mussel, Green-Lipped Mussel

Species Description:
The Asian green mussel, Perna viridis, is a large (> 80 mm) bivalve, with a smooth, elongate shell typical of several mytilids (but see below). It has visible concentric growth rings and a ventral margin that is distinctly concave on one side. The characteristic green coloration comes from the periostrocum, the proteinaceous outer layer of the shell. It is uniformly bright green in juveniles, but dulls to brown with green margins in mature individuals. The inner surfaces of the valves are smooth and iridescent blue to bluish-green in color. A prominent, kidney-shaped retractor muscle scar is present, but the species lacks anterior adductor muscles. Close examination of the beak (i.e., where the two valves hinge together) reveals a pair of hinge teeth on the left valve that interlock with a single hinge tooth on the right valve (DeVictor and Knott undated, NIMPIS 2002, Rajagopal et al. 2005).

As is typical of most members of the family, P. viridis attaches to hard surfaces by means of proteinaceous byssal threads.


Potentially Misidentified Species:
At least 12 different mytilid mussels have been documented within the IRL region. The most commonly encountered of these are readily distinguishable from P. viridis. The scorched mussel (Brachidontes exustus), ribbed mussel (Geukensia demissa), and hooked mussel (Ischadium recurvum) all exhibit prominent radial ribs that are lacking in P. viridis, while the horsemussels (Modiolus spp.) are smaller and possess a shell that is brown on the outside and whitish inside and is partially covered by a mossy periostracum in living specimens (UF/IFAS Green Mussel Homepage). The non-native charru mussel (Mytella charruana) is also readily differentiated from P. viridis; its shell is mostly dark brown to black and exhibits a wavy dark pattern on a lighter background.

Within the genus Perna, karyotypeing (counting chromosomes) reveals that P. viridis possesses 30 chromosomes while congeners such as the brown mussel the brown mussel (P. perna) only have 28 (Ahmed 1974).


II.  HABITAT AND DISTRIBUTION 

Regional Occurrence:
Green mussels are coastal bivalves, typically occurring at depths of less than 10 m, and shown to be tolerant of a wide range of turbidity and pollution (Power 2004).

The native range of the Asian green mussel broadly encompasses the Asia-Pacific and Indo-Pacific regions. The known introduced range of the species is extensive and includes portions of coastal Australia, Japan, the Caribbean, and North and South America (Benson et al. 2002; NIMPIS 2002).

Atlantic and Caribbean occurrences of P. viridis have been reported from Trinidad and Tobago, Jamaica, and Venezuela (Agard et al. 1992, Rylander et al 1996, Benson et al. 2002, Buddo et al. 2003). In the southeastern U.S., Perna viridis has been reported from coastal Georgia and from both Florida coasts (Power et al 2004).

IRL Distribution:
Although the first Florida east coast reports of Perna virdis date back to 2002 from approximately St. Augustine south toward Ponce Inlet, the first positive identification of the organism from the IRL system proper only occurred in 2006. This initial discovery of green mussels was in Mosquito Lagoon within the boundaries of Canaveral National Seashore near the historic Eldora State House. This area is also the epicenter of IRL occurrence for the charru mussel (Mytella charruana). Since the initial discovery, findings of small numbers of new animals have been slow but steady and the number of green mussels thus far found remains lower than the numbers for charru mussels (Dr. Linda Walters, personal communication).


III. LIFE HISTORY AND POPULATION BIOLOGY

Age, Size, Lifespan:
Green mussels are large, with shells typically reaching 80-100 mm in length and occasionally growing larger than 160 mm (Rajagopal et al. 2005). They live for approximately three years (Power et al 2004).

In parts of their native range, rapid growth rates of up to 6-10 mm per month have been reported. In Tampa Bay where the species has been introduced, even more rapid growth rates of 4-5 mm per week have been reported (Power 2004).

Abundance:
Baker et al. (2002) report Tampa Bay intertidal densities of Perna viridis attaining peaks ranging between 3,675 and 4,117 individuals per square meter at three study locations. The authors report significantly higher densities of 9,000-12,000 individuals per square meter when they found several layers of mussels on pilings at the mouth of the Little Manatee River.

Reproduction:
Reproduction is sexual, sexes are separate, and fertilization is external. Onset of sexual maturity is rapid, occurring at 2-3 months of age in parts of the animal's native range and in as little as 1-2 months in parts of its non-native tange, e.g., Tampa Bay (Power 2004).

Male and female green mussels release gametes directly into the water column. As with many marine bivalves, the presence of gametes in the water can trigger other individuals to release gametes, thereby synchronizing spawning to a degree. Salinity reductions (i.e., such as those often experienced in estuarine environments particularly in the wet seasons) can also elicit spawning in P. viridis (Stephen and Shetty 1981). Within their native Pacific range, spawning peaks coincide with the monsoon seasons, although the species is known to be capable of reproducing year-round in some locations (Sivalingam 1977, Stephen and Shetty 1981, Walter 1982).

Embryology:
Within eight hours of fertilization, Perna viridis larvae enter a ciliated, free-swimming stage known as the trochophore stage. Eight to twelve hours later the larvae have reached a stage known as the veliger stage which is characterized by the presence of a shell and a ciliated membrane or skirt called the velum. Metamorphosis and settlement to the benthic habit typically occur within 8-12 days to as many as 20 days. Settlement-stage individuals are capable of secreting byssal threads (Tan 1975, Siddall 1980, Manoj Nair and Appukuttan 2003).


IV.  PHYSICAL TOLERANCES

Temperature:
Green mussels occur in environments whose temperatures range from 10-35ºC and exhibit optimal response at temperatures between 26ºC and 32ºC (Power 2004). Although the reported native thermal range of the green mussel is broad, reduced temperatures have been demonstrated to significantly negatively impact growth rates (Chatterji et al. 1984).

Manipulative studies by Manoj Nair and Appukuttan (2003) confirm the thermal optimum for Perna viridis resides very close to the upper lethal limits of the species; optimum larval development, growth and survival occurred at 31ºC, but total mortality was reported after 24 h exposure at 33ºC and 35ºC.

Salinity:
The green mussel is euryhaline, able to tolerate both hypersaline conditions (80 ppt) and reduced salinities, e.g., 12 ppt (Sivalingam 1977, Chatterji et al. 1984, Morton, 1987). An optimal salinity range has been reported as 27-33 ppt (Power 2004).


V.  COMMUNITY ECOLOGY

Trophic Mode:
Like other mussels, Perna viridis is a cilliary-mucus suspension feeder. Firmly attached to a substrate, immobile mussels use their incurrent siphon to draw in food-laden water that is then carried by ciliary action to the branchial chamber. Water is discharged through the excurrent siphon while appropriately sized food particles are funneled by the labial palps into the mouth for ingestion and digestion.

Associated Species:
The likely nature of the association between green mussels and co-occurring fouling organisms will be as spatial and/or food resource competitors.


VI. INVASION INFORMATION

Invasion History:
Several aspects of the life history of Perna viridis are responsible for its success as an invasive animal. These include broad temperature, salinity, turbidity, and pollution tolerances, rapid growth and onset of maturity, and broadcast dispersal of planktonic larvae.

The first reported Caribbean appearance of the species dates to the 1990s in Trinidad (Agard et al. 1992, Power et al. 2004). Rylander et al. (1996) suggest that current-mediated larval dispersal from this population resulted in successive introductions in Venezuela. Green mussels have also been reported in Jamaican waters (Benson et al. 2002, Buddo et al. 2003).

The first occurrence of P. viridis in U.S. coastal waters apparently occurred as a result of accidental release into Tampa Bay on the Gulf coast of Florida in 1999 (Ingrao et al. 2001, Benson et al. 2002). The most likely pathway for this invasion has been identified as larval release in ballast water (Power et al. 2004). Current-facilitated dispersal of larvae originating from in situ reproduction of the Tampa Bay population has subsequently led to southward range expansion along western peninsular Florida to Boca Grande outside of Charlotte Harbor (Benson et al. 2002, Power et al. 2004).

A subsequent Florida occurrence of P. viridis was reported near St. Augustine on the northeast coast in 2002. The most likely vector for accidental introduction in this case is overland transport between Florida coasts, perhaps occuirring on or in recreational or fishing boats or possibly gear that was not cleaned properly (Power et al. 2004).

The green mussel population introduced to St. Augustine waters is the likely source of larvae that dispersed northward via currents along the Atlantic cost to Jacksonville and then into Georgia. As of 2003 the Atlantic distribution of this invasive species had been extended northward through the entirety of coastal Georgia. This represents the northernmost U.S. occurrence of the species (Power et al 2004).

In 2006, small numbers of P. viridis began to be uncovered within Mosquito Lagoon within a couple miles of Ponce Inlet (Linda Walters, pers. comm.). These individuals also likely originated from the previously detected St. Augustine population.

Potential to Compete With Natives:
Juvenile settlement densities of several thousand individuals per square meter in Tampa Bay suggest Perna viridis is a formidable spatial competitor (Power 2004). Large non-native green mussel populations may also represent a significant source of competition for planktonic food resources.

Baker and Benson (2002) report that oyster reefs composed of native eastern oysters (Crassostrea virginica) have been displaced by invading green mussels in Tampa Bay.

Possible Economic Consequences of Invasion:
Although economically important fisheries and aquaculture industries based green mussels exist within their native range, utilization as a food resource in areas into which they have been introduced is uncommon. Consumption of introduced green mussels taken from polluted waters is discouraged as they are known to accumulate some toxic substances.

Green mussels are common nuisance organisms fouling manmade structures such as intake and outfall pipes, buoys, bridges, pilings, and seawalls. Power et al. (2004) suggest the species may eventually become the marine equivalent of the highly invasive freshwater Asian zebra mussel (Dreissena polymorpha). Zebra mussels currently occur in more than 40% of inland US waterways and their partial-control in this country cost nearly $1 billion over a span of 15 years.


VII.  REFERENCES

Agard J., Kishore R., and B. Bayne. 1992. Perna viridis (Linnaeus, 1758): First record of the Indo-Pacific green mussel (Mollusca: Bivalvia) In the Caribbean. Caribbean Marine Studies 3:59-60.

Ahmed M. 1974. Chromosomes of two species of the marine mussel Perna (Mytilidae:Pelecypoda). Bol. Inst. Oceanogr. Univ. Oriente 13:17-22.

Baker S.M., Baker P., Benson A., Nunez J., Phlips E., and J. Williams. 2002. Biopollution by the green mussel, Perna viridis, in the southeastern United States. 2002 Progress Report. EPA Grant Number: R828898.

Benson A.J., Marelli D.C., Frischer M.E., Danforth J.M., and J.D. Williams. 2002. Establishment of the green mussel, Perna viridis (Linnaeus 1758), (Mollusca: Mytilidae) on the west coast of Florida. Paper presented at the Eleventh International Conference on Aquatic Invasive Species, February 25 to March 1, 2002, Alexandria VA.

Buddo D. St. A., Steele, R.D., and E.R. D'Oyen. 2003. Distribution of the invasive Indo-Pacific green mussel, Perna viridis, in Kingston Harbour, Jamaica. Bulletin of Marine Science 73:433-441.

Chatterji A., Ansari Z.A., Ingole B.S., and A.H Parulekar. 1984. Growth of the green mussel Perna viridis L., in a sea water circulating system. Aquaculture 40:47-55.

DeVictor and Knott. Undated. The Asian green mussel: Recent introduction to the South Atlantic Bight. South Carolina Department of natural Resources Species of the Month Fact Sheet.

Ingrao D.A., Mikklesen P.M., and D.W. Hicks. 2001. Another introduced marine mollusk in the Gulf of Mexico: the Indo-Pacific green mussel, Perna viridis, in Tampa Bay, Florida. Journal of Shellfish Research 20:13-19.

Manoj N.R., and K.K. Appukuttan. 2003. Effect of temperature on the development, growth, survival and settlement of green mussel Perna viridis (Linnaeus, 1758). Aquaculture Research 34:1037-1045.

Morton B. 1987. The functional morphology of the organs of the mantle cavity of Perna viridis (Linnaeus, 1758) (Bivalvia:Mytilacea). American Malacological Bulletin 5:159-164.

NIMPIS. 2002. Perna viridis species summary. CSIRO National Introduced Marine Pest Information System (Hewitt C.L., Martin R.B., Sliwa C., McEnnulty, F.R., Murphy, N.E., Jones T. and S. Cooper Eds). Available online.

Power A.J., Walker R.L., Payne K., and D. Hurley. 2004. First occurrence of the nonindigenous green mussel, Perna viridis in coastal Georgia, United States. Journal of Shellfish Research 23:741-744.

Rajagopal S., Venugopalan V.P., van der Velde G, and H.A. Jenner. 2006. Greening of the coasts: a review of the Perna viridis success story. Aquatic Ecology. 40:273-297.

Rylander K., Perez J., and J.A. Gomez. 1996. Status of the green mussel, Perna viridis (Linnaeus, 1758) (Mollusca: Mytilidae), In North-eastern Venezuela. Caribbean Marine Studies 5:86-87.

Siddall S.E. 1980. A clarification of the genus Perna (Mytilidae). Bulletin Of Marine Science 30:858-870.

Sivalingam P.M. 1977. Aquaculture of the green mussel, Mytilus viridis Linnaeus, in Malaysia. Aquaculture 11:297-312.

Stephen D., and H.P.C. Shetty. 1981. Induction of spawning in four species of bivalves of the Indian coastal waters. Aquaculture 25:153-159.

Tan W.H. 1975. Egg and larval development in the green mussel, Mytilus viridis Linnaeus. The Veliger 18:151-155.

Walter C. 1982. Reproduction and growth in the tropical mussel Perna viridis. (Bivalvia: Mytilidae). Kalikasan, Philippine Journal Of Biology 11:83-97.

Report by:  J. Masterson, Smithsonian Marine Station
Submit additional information, photos or comments to:
irl_webmaster@si.edu
Page last updated: October 4, 2007