Description of biotope or habitat type
Laminaria saccharina with foliose red seaweeds and ascidians on sheltered tide-swept infralittoral rock
Physical habitat description
|Salinity||Full (30-35 ppt), Variable (18-35 ppt)|
|Wave exposure||Sheltered, Very sheltered, Extremely sheltered|
|Tidal streams||Strong (3-6 kn), Moderately strong (1-3 kn)|
|Substratum||Boulders, bedrock and gravel|
|Depth Band||0-5 m|
Download comparative physical and biological data. The comparative tables enable a rapid comparison of the species composition and principal physical characteristics between a given set of biotopes.
- Records used to define the biotope (core records)
- Other records assigned to this biotope, marked as 'certain'
- Other records assigned to this biotope, marked as 'uncertain'
- Predicted extent of the level 3 (for sublittoral rock & deep sea) or 4 (for sublittoral sediment) habitat
Sheltered, tide-swept rock in south-western Britain tends to be restricted to estuarine conditions, where variable salinity and increased turbidity have a significant effect on the biota. Due to the turbidity of the water, the infralittoral zone is restricted to very shallow depths. Unlike the tide-swept channels in sealochs, which support a mixed kelp canopy, the rock in these estuaries is characterised by Laminaria saccharina alone, occurring in relatively low abundance (Frequent). The brown alga Desmarestia ligulata can occur in this biotope, though never dense, along with the non-native brown seaweed Sargassum muticum. Beneath the sparse kelp, cobbles and boulders, often surrounded by sediment, are encrusted by fauna and often a dense turf of red seaweed. The foliose red seaweeds associated with this biotope include Callophyllis laciniata, Nitophyllum punctatum, Kallymenia reniformis, Gracilaria gracilis, Gymnogongrus crenulatus, Hypoglossum hypoglossoides, Rhodophyllis divaricata, Chylocladia verticillata, Cryptopleura ramosa and Erythroglossum laciniatum as well as the filamentous Ceramium nodulosum and Pterothamnion plumula. Green seaweeds Ulva lactuca, Bryopsis plumosa and Cladophora spp. may be locally abundant. The dominating faunal species vary from site to site but include sponges such as Halichondria panicea, Esperiopsis fucorum, Dysidea fragilis and Hymeniacidon perleve as well as ascidians, particularly Dendrodoa grossularia and Morchellium argus, which can cover the rocks. Also present is the anthozoan Anemonia viridis, the barnacle Balanus crenatus and the tube-building polychaete Pomatoceros triqueter. The hydroid Plumularia setacea can cover rocks and seaweed fronds Of the range of solitary ascidians found in the north-west, only Ascidiella aspersa tends also to be present in these south-western inlets. There is also a general absence of echinoderms. Where there is vertical rock present, it tends to support more fauna, including barnacles Balanus crenatus, the ascidians Clavelina lepadiformis and Botryllus schlosseri and sometines the featherstar Antedon bifida. Where soft rock allows, such as the limestone in Plymouth Sound, rock-boring organisms such as Polydora sp. may be locally abundant. Sheltered, tide-swept rock is generally restricted to the narrows or tidal rapids of marine inlets. The clear tide-swept waters of Scottish sealochs are significantly different to the marine inlets of south-west Britain. This biotope deals with the latter.
This biotope generally occurs on rocky outcrops interspersed by sediment areas. Where the rock extends into deeper water, beyond the limit of kelp, sponges and ascidians tend to dominate these sheltered, tide-swept circalittoral sites (CuSpH); also Alcyonium digitatum with sponges and Nemertesia antennina (ByErSp).
|Taxon||Relative importance of taxon for defining this community (%)||Typical abundance - SACFOR scale||% of core records where taxon was recorded|
|Halichondria panicea||3||Occasional||41-60 %|
|Hymeniacidon perleve||3||Frequent||41-60 %|
|Dysidea fragilis||1||Occasional||21-40 %|
|Plumularia setacea||2||Occasional||21-40 %|
|Anemonia viridis||1||Occasional||21-40 %|
|Pomatoceros triqueter||2||Occasional||21-40 %|
|Balanus crenatus||2||Occasional||21-40 %|
|Morchellium argus||1||Frequent||21-40 %|
|Dendrodoa grossularia||4||Abundant||41-60 %|
|Rhodophyllis divaricata||3||Occasional||41-60 %|
|Callophyllis laciniata||2||Occasional||21-40 %|
|Kallymenia reniformis||2||Occasional||21-40 %|
|Gracilaria gracilis||1||Occasional||21-40 %|
|Chylocladia verticillata||1||Rare||21-40 %|
|Ceramium nodulosum||4||Frequent||41-60 %|
|Pterothamnion plumula||1||Occasional||21-40 %|
|Cryptopleura ramosa||3||Frequent||21-40 %|
|Hypoglossum hypoglossoides||3||Occasional||41-60 %|
|Nitophyllum punctatum||3||Occasional||41-60 %|
|Desmarestia ligulata||1||Rare||21-40 %|
|Laminaria saccharina||23||Frequent||81-100 %|
|Sargassum muticum||2||Occasional||21-40 %|
|Ulva lactuca||5||Frequent||41-60 %|
|Bryopsis plumosa||1||Occasional||21-40 %|
Similar biotopes or habitat types
Not applicable or unknown.
Classification history of this biotope or habitat type
|97.06||Lsac.T (in part)|