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Species
Musculista senhousia (Benson, 1842)
IUCN
NCBI
EOL Text
Ciclo reproductivo
M. senhousia es una especie dioica, alcanza la madurez sexual aproximadamente a los 9 meses de edad. La fecundación es externa, y el desarrollo de las larvas es planctónico abarcando un período de 14 a 55 días (NIMPIS, 2002; Cohen, 2005). En el hemisferio norte se reproduce durante el verano, las larvas son mas abundantes durante el otoño y al inicio del invierno (NIMPIS, 2002).
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Años
Musculista senhousia vive hasta 2 años (Cohen, 2005).
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4.5 Reproducción
Es una especie que tiene una amplia emisión en el desove, ya que la fertilización ocurre en la columna de agua. Las larvas están a la deriva en el plancton durante 14-55 días. Aunque que es capaz de asentarse en superficies duras como la mayoría de los mejillones, esta especie prefiere asentarse gregariamente en sustratos suaves. Estos mejillones se entierran en el sedimento, dejando solo la parte trasera de la concha de fuera y secretan hilos fibrosos que se adhieren a las partículas de sedimento, creando una especie de nido o bolsa alrededor de sí mismos, llamado tapete bisal (Cohen, 2005).
Factores ambientales que fomentan la reproducción
Los requerimientos mínimos para la reproducción son temperaturas de al menos 22.5°C y salinidades menores a 30ppt (Inoue and Yamamuro, 2000). En condiciones mayores a 28°C y 30 ppt, se reduce la reproducción (Sgro et al., 2002).
Edad de primera reproducción
Musculista senhousia crece rápidamente y puede alcanzar el tamaño adulto en sólo nueve meses (Northern Territory Government. sin fecha).
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Rights holder/Author | CONABIO |
Source | No source database. |
The following is a representative barcode sequence, the centroid of all available sequences for this species.
There are 25 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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Barcode of Life Data Systems (BOLDS) Stats
Public Records: 25
Specimens with Barcodes: 32
Species With Barcodes: 1
1.8 Usos de la especie
Musculista senhousia se ha utilizado como carnada para peces y como alimento para camarones y cangrejos en granjas de cultivo en Japón, y como alimento en China, incluso ha habido intentos de cultivarlos (Cohen, 2005).
Alimento
Se consume la carne, la grasa, la sangre, y los despojos (completos, cortados, frescos, congelados, enlatados, curados, procesados o ahumados) (ISC, 2011).
License | http://creativecommons.org/licenses/by-nc-sa/2.5/ |
Rights holder/Author | CONABIO |
Source | No source database. |
6.1.3 Económico
A pesar de que la asfixia y muerte de almejas en cultivos en China y Japón se le ha atribuido a los efectos de M. senhousia (Cohen, 2005), los estudios de Mistri (2004 a,b) no muestran un efecto negativo significativo en el crecimiento ni en la mortalidad de dos especies de almejas cultivadas (Tapes decussatus y Ruditapes phillipinarum) causado por los tapetes bisales de M. senhousia en el Adriático (ISC, 2011).
6.1.2 Ecológico
M. senhousia es un invasor exitoso en muchas partes del mundo, capaz de producir efectos interespecíficos y de alterar el hábitat (Mistri et al., 2004). En algunas zonas ha formado grandes tapetes a lo largo del lecho marino en zonas resguardadas de poca profundidad, alcanzando densidades de 3300 individuos por m2. Tales eventos pueden alterar significativamente la biota local y el sustrato debido a la competencia por alimento y espacio (GWA, 2005) y pueden tener un impacto adverso en la biodiversidad a través de la exclusión de otras especies. La tasa a la cual este ensamblaje de M. senhousia filtra el oxígeno y el alimento del agua, acelera la tasa de conversión de sedimento suspendido a material depositado y puede alterar rápidamente la estabilidad del sustrato. La introducción de este tipo de organismos pueden resultar en la introducción de especies asociadas y/o parásitos y enfermedades (GWA, 2005).
La colonización exitosa de M. senhousia da lugar a efectos dinámicos a nivel trófico y béntico. M. senhousia remueve un gran volumen de material orgánico que está suspendido en la columna de agua mientras se alimenta, y subsecuentemente deposita el material filtrado en el fondo en forma de heces y pseudoheces. El depósito de grandes cantidades de material orgánico resulta en la alteración de la calidad nutricional de los sedimentos y en la disminución de la capa que marca la transición entre condiciones químicamente oxidativas y condiciones químicamente reductoras (RPD redox potential discontinuity),que a su vez tiene el potencial de afectar a la fauna residente, suprimiendo su crecimiento y afectando su supervivencia, haciendo el medioambiente en el tapete bisal inadecuado para los adultos o larvas de otras especies (Mistri et al., 2004).
Se ha reportado en zonas de la Bahía de San Diego, que M. senhousi impide el crecimiento de rizomas y la propagación vegetativa de algunas especies de pastos marinos debido a la acumulación de metabolitos tóxicos como el sulfuro (Reusch y Williams, 1998), mientras que en Australia occidental ha provocado cambios en los sedimentos arenosos volviéndolos fangosos (GWA, 2005).
Dada la naturaleza efímera de los tapetes bisales de M. senhousia, los efectos en el hábitat son probablemente de corta duración. A pesar de que el fango anóxico acumulado en los sedimentos puede persistir por algún tiempo después de la muerte de los mejillones, eventualmente será arrastrado por las corrientes marinas (Creese et al., 1997).
6.1.1 A flora y fauna nativa
M. senhousia es una especie dominante en comunidades bentónicas y se ha observado que es capaz de excluir a especies nativas (Cohen, 2005; NIMPIS, 2002; Crooks, 2006). Se ha observado que la superficie formada por las estructuras de las esteras hechas por M. senhousia favorece la abundancia de anfípodos y gusanos poliquetos, en contraste, la abundancia de otros bivalvos es afectada negativamente, posiblemente a causa de la competencia por alimento (Reusch, 1998; Mistri, 2002; NIMPIS, 2002; Cohen, 2005; Crooks, 2001)
License | http://creativecommons.org/licenses/by-nc-sa/2.5/ |
Rights holder/Author | CONABIO |
Source | No source database. |
- For the Asian Green Mussel, see Perna viridis.
The Asian mussel, scientific name Musculista senhousia, (commonly known as the Asian date 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.
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.
Contents
Description[edit]
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. [1][2] It is also known for its relatively fast growth and has a maximum lifetime of about two years.[3]
Distribution[edit]
Musculista 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.[2] 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.[1][2] 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.[2][3]
Ecology[edit]
Habitat[edit]
The Asian mussel is generally found in sheltered mud or other soft substrates up to twenty metres below the surface of the water.[1] In China and Japan, the native mussel is found in intertidal zones with densities up to 2500 individuals per square metre. In Australia, the invasive species is found from 0.5 to 4 metres below the surface of the water in slightly higher densities.[2]
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.[3] 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.[2]
Behavior[edit]
Musculista 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.[3]
Predators[edit]
Predators of the Asian 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.[2] 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.[3] Recent research has emphasized the importance of the predation of Musculista senhousia by native fauna as a means of reducing the negative effects of the invasive species on ecosystems.
Asian 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.[3]
Impact on invaded ecosystems[edit]
Research has shown that the Asian 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 Musculista senhousia has caused an increase in the biomass of benthic macro-organisms in general.[2]
In Mission Bay in San Diego, California, USA, the increasing abundance of Asian 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 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 mussel is abundant. Populations of the deeper-dwelling and deposit-feeding Macoma nasuta are not significantly affected, however, by the invasion of the mussel.[4]
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 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 mussel. There has also been a concomitant increase in the abundance of detritivores and herbivores.[5]
Laboratory research has also shown that deeper-dwelling species are less affected by the invasion of the Asian mussel. Mussel mats have no significant effect on the mortality of deeper-dwelling clam species such as Tapes decussatus and Ruditapes philippinarum.[6]
Competition with native species is the primary cause of concern in areas of New Zealand where the Asian 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.[7]
Musculista 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 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 Musculista senhousia can only worsen the situation.[8]
References[edit]
- ^ a b c Edgar, Graham J. Australian Marine Life: The Plants and Animals of Temperate Waters. Victoria: Reed, 1997.
- ^ a b c d e f g h 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.
- ^ a b c d e f Crooks, Jeffrey A. "Predators of the invasive mussel Musculista senhousia (Mollusca: Mytilidae)." Pacific Science. 56.1 (2002): 49-57.
- ^ 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.
- ^ 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.
- ^ Mistri, Michele. "Effect of Musculista senhousia mats on clam mortality and growth: much ado about nothing?" Aquaculture. 241.1-4 (2004): 207-218.
- ^ 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.
- ^ 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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Source | http://en.wikipedia.org/w/index.php?title=Asian_mussel&oldid=653691809 |
1.1 Descripción de la especie
Tiene valvas lisas, delgadas de color verde olivo a café, con líneas radiales oscuras (NIMPIS, 2002).
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Depth range based on 87 specimens in 1 taxon.
Environmental ranges
Depth range (m): 0.8 - 224
Graphical representation
Depth range (m): 0.8 - 224
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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Rights holder/Author | Ocean Biogeographic Information System |
Source | http://www.iobis.org/mapper/?taxon_id=474046 |