BIOTIC Species Information for Laminaria hyperborea
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Researched by | Dr Harvey Tyler-Walters | Data supplied by | MarLIN | ||||||||||||
Refereed by | Dr Joanna Jones | ||||||||||||||
Taxonomy | |||||||||||||||
Scientific name | Laminaria hyperborea | Common name | Tangle or cuvie | ||||||||||||
MCS Code | ZR351 | Recent Synonyms | None | ||||||||||||
Phylum | Chromophycota | Subphylum | |||||||||||||
Superclass | Class | Phaeophyceae | |||||||||||||
Subclass | Order | Laminariales | |||||||||||||
Suborder | Family | Laminariaceae | |||||||||||||
Genus | Laminaria | Species | hyperborea | ||||||||||||
Subspecies | |||||||||||||||
Additional Information | Other common names include, redware, cuvy, sea rod, mayweed or Slat mara. The new blade grows below the older from November onwards. The old blade is shed in spring and early summer. Blade and stipe vary with exposure and current. In sheltered conditions the blade has few or no digits and the stipe becomes thin but in exposed conditions the blade is deeply digitate and the stipe becomes thick. The stipe is usually up to 1m long but stipes up to 3m long have been recorded (Parke unpublished, cited in Kain, 1971a). | ||||||||||||||
Taxonomy References | Howson & Picton, 1997, Guiry, 2000, Lüning, 1990, | ||||||||||||||
General Biology | |||||||||||||||
Growth form | Forest Straplike / Ribbonlike Foliose |
Feeding method | Photoautotroph |
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Mobility/Movement | Permanent attachment |
Environmental position | Epilithic Epifloral |
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Typical food types | Not relevant | Habit | Attached | ||||||||||||
Bioturbator | Not relevant | Flexibility | High (>45 degrees) | ||||||||||||
Fragility | Robust | Size | Large(>50cm) | ||||||||||||
Height | Growth Rate | 0.94 cm/day | |||||||||||||
Adult dispersal potential | None | Dependency | Independent | ||||||||||||
Sociability | Solitary | ||||||||||||||
Toxic/Poisonous? | No | ||||||||||||||
General Biology Additional Information | The adult plant exhibits no gender but the gametophytes are dioecious. The approximate size of male and female gametophytes are given. Growth |
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Biology References | Lüning, 1990, Birkett et al., 1998b, Kain, 1979, Jones & Kain, 1967, Kain et al., 1975, Wilkinson, 1995, Sjøtun et al., 1996, Sjøtun & Fredriksen, 1995, | ||||||||||||||
Distribution and Habitat | |||||||||||||||
Distribution in Britain & Ireland | Found on most coasts of Britain and Ireland. Scarce along the south east coast of Britain due to a lack of suitable substrata. | ||||||||||||||
Global distribution | Restricted to the north east Atlantic from the northern coast of Iceland, north to the Russian coast near Murmansk and south to Cape Mondego, mid-Portugal including Norway, Faroes, northern France and northern Spain but absent from the Bay of Biscay. | ||||||||||||||
Biogeographic range | Not researched | Depth range | Extreme low water to 47m although usually to ca 30m | ||||||||||||
Migratory | Non-migratory / Resident | ||||||||||||||
Distribution Additional Information | Laminaria hyperborea is not found in areas influenced by sediment (e.g. sand) scour. Laminaria hyperborea is absent is areas of extreme wave action or currents (e.g. surge gullies) since the stiff stipe is likely to snap or holdfasts tear off. It is also absent from sheltered areas. The upper limit of its distribution may be depressed by wave action, e.g. in St Kilda its upper limit is several metres below MLWS (Birkett et al., 1998b). High irradiances (comparable to direct sunlight) reduce photosynthesis in Laminaria hyperborea, which may explain its absence from intertidal rock pools, where it is replaced by %Laminaria digitata% (Kain et al., 1975). The lower limit of Laminaria hyperborea is determined by light penetration except in the presence of grazing e.g. by Echinus in the Isle of Man (Jones & Kain, 1967; Kain et al. 1974). The lower limit for Laminarians is generally considered to be about 1 percent of surface irradiance (Luning, 1990; Birkett et al., 1998b). | ||||||||||||||
Substratum preferences | Bedrock Large to very large boulders Cobbles Pebbles Artificial (e.g. metal/wood/concrete) |
Physiographic preferences | Open coast Strait / sound Ria / Voe Enclosed coast / Embayment |
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Biological zone | Upper Infralittoral Lower Infralittoral |
Wave exposure | Very Exposed Exposed Moderately Exposed |
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Tidal stream strength/Water flow | Moderately Strong (1-3 kn) Weak (<1 kn) |
Salinity | Full (30-40 psu) |
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Habitat Preferences Additional Information | |||||||||||||||
Distribution References | Lüning, 1990, Norton, 1985, Birkett et al., 1998b, JNCC, 1999, Picton & Costello, 1998, Jones & Kain, 1967, Kain et al., 1975, Erwin et al., 1990, Hardy & Guiry, 2003, | ||||||||||||||
Reproduction/Life History | |||||||||||||||
Reproductive type | Vegetative Gonochoristic |
Developmental mechanism | Spores (sexual / asexual) |
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Reproductive Season | September to April | Reproductive Location | |||||||||||||
Reproductive frequency | Annual protracted | Regeneration potential | No | ||||||||||||
Life span | 11-20 years | Age at reproductive maturity | 3-5 years | ||||||||||||
Generation time | 3-5 years | Fecundity | In excess of 1,000,000 | ||||||||||||
Egg/propagule size | Zoospores ca 5µm across | Fertilization type | External | ||||||||||||
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Reproduction Preferences Additional Information |
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Reproduction References | Lüning, 1990, Birkett et al., 1998b, Lein et al., 1991, Kain, 1979, Dieck, 1993, Guiry & Blunden, 1991, Norton, 1992, Lüning, 1980, Lüning & Müller, 1978, Kain, 1975b, Sjøtun et al., 1993, |