BIOTIC Species Information for Macoma balthica
| |||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Researched by | Lizzie Tyler | Data supplied by | University of Sheffield | ||||||||||||
Refereed by | This information is not refereed. | ||||||||||||||
Taxonomy | |||||||||||||||
Scientific name | Macoma balthica | Common name | Baltic tellin | ||||||||||||
MCS Code | W2029 | Recent Synonyms | None | ||||||||||||
Phylum | Mollusca | Subphylum | |||||||||||||
Superclass | Class | Pelecypoda | |||||||||||||
Subclass | Order | Veneroida | |||||||||||||
Suborder | Family | Tellinidae | |||||||||||||
Genus | Macoma | Species | balthica | ||||||||||||
Subspecies | |||||||||||||||
Additional Information | |||||||||||||||
Taxonomy References | Hayward et al., 1996, Hayward & Ryland, 1995b, Fish & Fish, 1996, | ||||||||||||||
General Biology | |||||||||||||||
Growth form | Bivalved |
Feeding method | Passive suspension feeder Active suspension feeder Surface deposit feeder Sub-surface deposit feeder |
||||||||||||
Mobility/Movement | Crawler Burrower |
Environmental position | Infaunal |
||||||||||||
Typical food types | Diatoms, deposited plankton, suspended phytoplankton & detritus. | Habit | Burrow dwelling | ||||||||||||
Bioturbator | Flexibility | None (< 10 degrees) | |||||||||||||
Fragility | Intermediate | Size | Small(1-2cm) | ||||||||||||
Height | Insufficient information | Growth Rate | 3 mm/year | ||||||||||||
Adult dispersal potential | 100-1000m | Dependency | Independent | ||||||||||||
Sociability | Solitary | ||||||||||||||
Toxic/Poisonous? | No | ||||||||||||||
General Biology Additional Information | Abundance Stephen (1929) reported typical abundances of Macoma balthica from the Firth of Forth to be 0-89/m² and maximum abundance to be 288/m². Ratcliffe et al. (1981) reported adult densities in the Humber Estuary, UK, between 5,000/m² and 40,000/m² depending on time since a successful spatfall. Bonsdorff et al. (1995) reported juvenile density in the Baltic Sea following settlement to be 300,000/m² decreasing to a stable adult density of 1,000/m². Size at maturity Caddy (1967) reported Macoma balthica from the River Thames reaching maturity in their 2nd year at a size of 5-6mm, whereas in the Netherlands, first year animals larger than 4mm had developed gonads during the spawning season (Lammens, 1967). Lavoie (1970) (cited in Gilbert, 1978) reported that a population of Macoma balthica from a French estuary did not achieve sexual maturity until their second year at a mean length of 3.57mm. Given that the growth rate varies significantly between populations, Gilbert (1978) suggested that Macoma balthica may mature in its 2nd year of life regardless of size or during its first year if a certain size is achieved. Harvey & Vincent (1989), however, consider that sexual maturity is a function of size rather than age in Macoma balthica, maturation occurring when the shell reaches 6mm with corresponding ages of individuals from the same population varying between 10 and 22 months. Growth rate Gilbert (1973) reported mean annual growth rate of Macoma balthica to be 3.3mm/yr with an average length of 18-20mm for fully grown individuals. However, other studies show considerable variations in growth patterns in relation to habitat and depth. McLusky & Allan (1976) reported the maximum growth rate of Macoma balthica in the laboratory to be 1mm over an 8 month period for 5-7mm long animals maintained at 15°C and 25psu. Toxicity Macoma balthica is not normally considered to be toxic but may transfer toxicants through the food chain to predators. Macoma balthica was implicated in the Mersey bird kill in the late 1970's, owing to bioconcentration of alklyC-lead residues (Bull et al., 1983). |
||||||||||||||
Biology References | Fish & Fish, 1996, Bonsdorff, 1984, Harvey & Vincent, 1989, McLusky & Allan, 1976, Brafield & Newell, 1961, Clay, 1967(b), Stephen, 1929, Gilbert, 1973, Gilbert, 1978, Caddy, 1967, Lammens, 1967, Ratcliffe et al., 1981, Bonsdorff et al., 1995, Tebble, 1976, Bull et al., 1983, Hayward & Ryland, 1990, Julie Bremner, unpub data, | ||||||||||||||
Distribution and Habitat | |||||||||||||||
Distribution in Britain & Ireland | Common in estuarine environments around the British Isles, with the exception of the south coast. | ||||||||||||||
Global distribution | Macoma balthica has an extensive geographic range that reaches from temperate to arctic coastal waters in both the North Atlantic and North Pacific oceans. | ||||||||||||||
Biogeographic range | Not researched | Depth range | |||||||||||||
Migratory | Non-migratory / Resident | ||||||||||||||
Distribution Additional Information | Studies have indicated that eastern and western North Atlantic populations of Macoma balthica are morphologically and genetically different from one another, and that they may have diverged as sibling species (Meehan & Carlton, 1988). Depth preferences Macoma balthica occurs in a wide depth range between the mid shore and 190m but is most abundant at moderate depths on muddy and sandy bottoms (Olafsson, 1986). However, in British waters Macoma balthica is mainly an intertidal species. Local distribution Macoma balthica is a resident species but because of near-surface habitat preference, populations may be subject to tidal re-location and scouring. Also observations of propulsion stimulus to scallops may assist in local relocation (Langston, W.J., pers. comm.) |
||||||||||||||
Substratum preferences | Mud Muddy sand Sandy mud |
Physiographic preferences | Ria / Voe Estuary Enclosed coast / Embayment |
||||||||||||
Biological zone | Upper Eulittoral Mid Eulittoral Lower Eulittoral |
Wave exposure | Sheltered Very Sheltered Extremely Sheltered |
||||||||||||
Tidal stream strength/Water flow | Moderately Strong (1-3 kn) Weak (<1 kn) |
Salinity | Variable (18-40 psu) Reduced (18-30 psu) Low (<18 psu) |
||||||||||||
Habitat Preferences Additional Information | |||||||||||||||
Distribution References | Hayward et al., 1996, Hayward & Ryland, 1995b, Fish & Fish, 1996, Clay, 1967(b), Meehan & Carlton, 1988, Olafsson, 1986, Ratcliffe et al., 1981, Bonsdorff et al., 1995, Tebble, 1976, Picton & Costello, 1998, JNCC, 1999, Bruce et al., 1963, Hayward & Ryland, 1990, Julie Bremner, unpub data, | ||||||||||||||
Reproduction/Life History | |||||||||||||||
Reproductive type | Gonochoristic |
Developmental mechanism | Planktotrophic |
||||||||||||
Reproductive Season | Spring and autumn | Reproductive Location | Insufficient information | ||||||||||||
Reproductive frequency | Annual episodic | Regeneration potential | No | ||||||||||||
Life span | 6-10 years | Age at reproductive maturity | |||||||||||||
Generation time | 1-2 years | Fecundity | 30000 | ||||||||||||
Egg/propagule size | Fertilization type | Insufficient information | |||||||||||||
|
|||||||||||||||
Reproduction Preferences Additional Information | Life span Gilbert (1973) reviewed longevity records of Macoma balthica. Life span is typically 5-10 years but may be as long as 30 years in populations from deep, cold water. The data presented suggest that maximum size and growth rate decrease and longevity increases with increasing latitude and associated cooler temperatures. Age at maturity Caddy (1967) reported Macoma balthica from the River Thames reaching maturity in their 2nd year at a size of 5-6mm, whereas in the Netherlands, first year animals larger than 4mm had developed gonads during the spawning season (Lammens, 1967). Lavoie (1970) (cited in Gilbert, 1978) reported that a population of Macoma balthica from a French estuary did not achieve sexual maturity until their second year at a mean length of 3.57mm. Given that the growth rate varies significantly between populations, Gilbert (1978) suggested that Macoma balthica may mature in its 2nd year of life regardless of size or during its first year if a certain size is achieved. Harvey & Vincent (1989), however, consider that sexual maturity is a function of size rather than age in Macoma balthica, maturation occurring when the shell reaches 6mm with corresponding ages of individuals from the same population varying between 10 and 22 months. Gametogenesis and spawning Caddy (1967) studied gametogenesis and spawning in a population of Macoma balthica from the Thames Estuary, UK. The primary gonad passed through a male phase, maturation being achieved in the 2nd year of life. Gametogenesis was associated with a system of follicle cells which broke down as the gametes approached maturity. The arrangement of the follicle cells was characteristic of the sex. In the female, gametocytes were peripheral to the follicle cells, while in the male they were interstitial. Spermatogenesis proceeded most rapidly in the centre of the follicle, resulting in a gradient of spermatogenic stages of increasing maturity from the periphery to the centre. Spawning occurred principally in the spring and to a lesser extent in the autumn. Several spawnings were identified within a season, but repeated cycles of gametogenesis were absent. Ejection of eggs occurred from the exhalant siphon and continued for 40 minutes with brief spawning bursts at 3 minute intervals. Eggs were expelled at considerable speed to a height in the water column of approximately 8cm and settled out of suspension slowly. Females of approximately 17mm shell length were estimated to have expelled between 10,000 and 50,000 eggs. |
||||||||||||||
Reproduction References | Fish & Fish, 1996, Harvey & Vincent, 1989, Gilbert, 1973, Gilbert, 1978, Caddy, 1967, Lammens, 1967, Ratcliffe et al., 1981, Bonsdorff et al., 1995, Eckert, 2003, Julie Bremner, unpub data, |