Arcuatula senhousia

Arcuatula senhousia, commonly known as the Asian date mussel, Asian mussel or bag mussel, is a small saltwater mussel, a marine bivalve mollusk species in the family Mytilidae, the mussels. Other common names for this species include: the Japanese mussel, Senhouse's mussel, the green mussel (a name also applied to Perna viridis), and the green bagmussel. It is harvested for human consumption in China.

For the Asian green mussel, see Perna viridis.

Arcuatula senhousia
Exterior of left valve of an Asian date mussel
Scientific classification
Kingdom: Animalia
Phylum: Mollusca
Class: Bivalvia
Order: Mytilida
Family: Mytilidae
Genus: Arcuatula
Species:
A. senhousia
Binomial name
Arcuatula senhousia
(Benson), 1842)
Synonyms[1]
  • Modiola aquarius Grabau & King, 1928
  • Modiola bellardiana Tapparone Canefri, 1874
  • Modiola senhousia Benson, 1842
  • Musculista senhousia (Benson, 1842)
  • Musculus senhousia (Benson in Cantor, 1842)

This mussel is native to the Pacific Ocean from Siberia to Singapore, but it has also been accidentally introduced and become an invasive species in numerous other areas worldwide. It can live in the intertidal or shallow subtidal zones. In California the species has been recorded in densities of up to 150,000 individuals per square meter. It grows quickly and lives only about 2 years. It prefers soft substrates and surrounds its shell in a dense mass of byssus.

One of several negative impacts of this invasive species is that it has a detrimental effect on eelgrass.

Description

This species is differentiated from other mussels by its relatively small size and inflated shape, as well as by the greenish colour of its outer periostracal layer. The shell has radiating reddish lines on its posterior surfaces, small internal teeth on the dorsal edge posterior to the ligament, and small ribs anterior to the umbones. It can grow up to 30 mm in length.[2][3] It is also known for its relatively fast growth and has a maximum lifetime of about two years.[4]

Distribution

Interior of left valve of Asian date mussel

Arcuatula senhousia is native to the Pacific Ocean, inhabiting coastal areas from Siberia and the Kuril Islands south to Singapore. The mussel has become an invasive species in California, the Mediterranean, Australia, and New Zealand.[3] It was introduced to the Western coast of the United States sometime in the early 20th century with shipments of Japanese oysters. In 1983, large specimens of the species were collected in the Swan River estuary in Western Australia. The mussel has been present in Auckland harbour since 1980, and specimens have also been reported at Tamar estuary in Tasmania.[2][3] Invasion of the aforementioned locales is thought to have been achieved in a variety of manners: the mussels were transported on the hulls of ships, in water-intake chambers and the ducts of ships, as planktonic larvae carried in the ballast water of bulk-cargo vessels, in association with intentionally introduced oysters, and by Lessepsian migration through the Suez Canal.[3][4]

Ecology

Habitat

The Asian date mussel is generally found in sheltered mud or other soft substrates up to twenty metres below the surface of the water.[2] In China and Japan, where it is native, the mussels are found in intertidal zones with densities up to 2500 individuals per square metre. In Australia, as an invasive species, they are found from 0.5 to 4 metres below the surface of the water in slightly higher densities.[3]

Along the Western coast of North America, however, the species generally reaches densities of 5000 to 10,000 individuals per square metre and has been recorded at densities of up to 150,000 individuals per square metre in Mission Bay in San Diego, California, USA. The mussel is most abundant in the summer and early autumn.[4] In the Swan River estuary in Western Australia, the mussel population has a high mortality rate in the late autumn and early winter. This may be the result of a decrease in water salinity from increased rainfall.[3]

Behavior

Arcuatula senhousia uses byssal threads to form a sort of cocoon around itself. The cocoon may be necessary for protection due to the relatively thin shells of the species, as well as to assist in the stabilization of the individuals within the sediment. The cocoons of the individuals can intertwine to form a mat that tends to trap other shells, sediment, algae, and detritus on its surface.[4]

Predators

Predators of the Asian date mussel vary depending on the native fauna of the area. In the Swan River estuary of Western Australia, for example, predation occurs mainly by boring carnivorous gastropods such as Nassarius burchardi or Bedeva paivae, which drill through the mussel's thin shell.[3] In Mission Bay in San Diego, however, the mussel's main predators include the yellowfin croaker, spotfin croaker, sargo, willet, and the marbled godwit (three fish and two bird species respectively). Other less significant predators include carnivorous gastropods (especially Pteropurpura festiva), crustaceans, echinoderms, fish, and diving ducks.[4] Recent research has emphasized the importance of the predation of Arcuatula senhousia by native fauna as a means of reducing the negative effects of the invasive species on ecosystems.

Asian date mussels also face predation by humans. The mussel is gathered as food in China, as food for domestic organisms in Japan, Thailand, and India, as well as bait for fishing throughout Asia. There are currently no commercial or recreational uses for the mussel in the invaded areas. It has been suggested that harvesting the species might help reduce the effects of their invasion; however, there are a number of detrimental effects associated with benthic harvesting.[4]

Impact on invaded ecosystems

Research has shown that the Asian date mussel can have a variety of effects on various ecosystems. In the Swan River estuary in Western Australia, for example, the presence of mats of Arcuatula senhousia has caused an increase in the biomass of benthic macro-organisms in general.[3]

In Mission Bay in San Diego, California, USA, the increasing abundance of Asian date mussels has caused a decrease in species richness and abundance of the native Solen rostriformis as well as the complete disappearance of the native [Chione fluctifraga]]. The Asian date mussel has also become one hundred times more abundant than any native bivalves. Two other native species have appeared in the bay, however: Macoma nasuta and Chione undatella. Laboratory experiments using these species show that the growth and survival of the surface-dwelling and suspension-feeding species of the Chione genus decrease dramatically in areas where the Asian date mussel is abundant. Populations of the deeper-dwelling and deposit-feeding Macoma nasuta are not significantly affected, however, by the invasion of the mussel.[5]

Similar occurrences have been observed at Sacca di Goro, a brackish lagoon in the Po River Delta of the Northern Adriatic Sea in Italy, which the Asian date mussel invaded in the early 1990s. Researchers there have found that growth and survival of suspension feeders has significantly decreased following the arrival of the Asian date mussel. There has also been a concomitant increase in the abundance of detritivores and herbivores.[6]

Laboratory research has also shown that deeper-dwelling species are less affected by the invasion of the Asian date mussel. Mussel mats have no significant effect on the mortality of deeper-dwelling clam species such as Tapes decussatus and Ruditapes philippinarum.[7]

Competition with native species is the primary cause of concern in areas of New Zealand where the Asian date mussel has invaded. There are significantly fewer macrofaunal invertebrates and there has been an eightfold decrease in the abundance of infaunal bivalves. Scientists suggest, however, that the adverse environmental effects of the mussel in New Zealand will be localized and short-lived.[8]

Arcuatula senhousia shares its habitat with eelgrass (Zostera marina) in many of the areas in which it has invaded. The presence of the mussel has been shown to affect rhizome growth in the eelgrass. This decreases the ability of established patches to spread. The Asian date mussel had the most detrimental effect on rhizome growth in areas where the eelgrass was sparse and patchy. This is a cause of concern for conservationists because beds of eelgrass are already degraded and sparse as a result of anthropogenic forces. The presence of Arcuatula senhousia can only worsen the situation.[9]

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References

  1. Markus Huber; Bruce Marshall (2016). "Arcuatula senhousia (Benson, 1842)". World Register of Marine Species. Retrieved 2 March 2017.
  2. Edgar, Graham J. Australian Marine Life: The Plants and Animals of Temperate Waters. Victoria: Reed, 1997.
  3. Slack-Smith, S.M., A. Brearley. "Musculista senhousia (Benson, 1842); a mussel recently introduced into the Swan River estuary, Western Australia." Records of the Western Australian Museum. 13.2 (1987): 225-230.
  4. Crooks, Jeffrey A. "Predators of the invasive mussel Musculista senhousia (Mollusca: Mytilidae)." Pacific Science. 56.1 (2002): 49-57.
  5. Crooks, Jeffrey A. "Assessing invader roles within changing ecosystems: Historical and experimental perspectives on an exotic mussel in an urbanized lagoon." Biological Invasions. 3.1 (2001): 23-36.
  6. Mistri, M., R. Rossi, and E.A. Fano. "The spread of an alien bivalve (Musculista senhousia) in the Sacca di Goro Lagoon (Adriatic Sea, Italy)." Journal of Molluscan Studies. 70.3 (2004): 257-261.
  7. Mistri, Michele. "Effect of Musculista senhousia mats on clam mortality and growth: much ado about nothing?" Aquaculture. 241.1-4 (2004): 207-218.
  8. Creese, Robert, Simon Hooker, Sharon De Luca, and Yvette Wharton. "Ecology and environmental impact of Musculista senhousia (Mollusca: Bivalvia: Mytilidae) in Tamaki Estuary, Auckland, New Zealand." New Zealand Journal of Marine and Freshwater Research. 31.2 (1997): 225-236.
  9. Reusch, Thorsten B.H. and Susan L. Williams. "Variable responses of native eelgrass Zostera marina to a non-indigenous bivalve Musculista senhousia." Oecologia. 113.3 (1998): 428-441.
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