Sabellaria spinulosa

Researched ByLizzie TylerData Supplied ByUniversity of Sheffield
Refereed byThis information is not refereed.
Taxonomy
Scientific nameSabellaria spinulosaCommon nameRoss worm
MCS CodeP1117Recent SynonymsNone
PhylumAnnelidaSubphylum
SuperclassClassPolychaeta
SubclassOrderTerebellida
SuborderFamilySabellariidae
GenusSabellariaSpeciesspinulosa
Subspecies  
Additional InformationAt low densities, the tubes are attached to the substratum along the entire length but at greater densities competition for space results in the tubes overlapping and may cause the tubes to be built outwards, away from the substratum.
Taxonomy References Howson & Picton, 1997, Hayward & Ryland, 1995b, English Nature, 1998
General Biology
Growth formTubicolous, Vermiform segmentedFeeding methodPassive suspension feeder, Active suspension feeder
Mobility/MovementPermanent attachmentEnvironmental positionEpifaunal
Typical food typesPhytoplanktonHabitTubiculous
BioturbatorNot relevantFlexibilityNone (< 10 degrees)
FragilityIntermediateSizeSmall-medium(3-10cm)
Height2-3 cmGrowth RateField unresearched
Adult dispersal potentialNoneDependencyIndependent
SociabilityGregarious
Toxic/Poisonous?No
Additional InformationCan be found in very high densities, for example when forming a reef. Typically found in lower densities as a crust or as individuals. At the Bristol Channel location studied by George & Warwick (1986), densities in excess of 4,000/m² for loosely aggregated Sabellaria spinulosa were recorded whilst the area sampled by Hiscock & Rostron (unpublished) on a level hard substratum had a single layer crust with 9,561 individual Sabellaria spinulosa in 1.4m². There has been considerable concern about decline in Sabellaria spinulosa reefs and shrimp fisheries have been implicated in the decline. However, Vorberg (2000) could find no damage caused after experiments with shrimp trawls in the Wadden Sea and suggests that declines might be more associated with changing patterns of currents perhaps associated with construction, dredging and dumping.
Biology References Hayward & Ryland, 1995b, English Nature, 1998, George & Warwick, 1985, Vorberg, 2000, Holt et al., 1998, Hayward & Ryland, 1995b, Heidi Tillin, unpub data, Julie Bremner, unpub data, Rees & Dare, 1993
Distribution and Habitat
Distribution in Britain & IrelandAll British and Irish coasts
Global distributionArctic, North Sea, Channel, Atlantic
Biogeographic rangeNot researchedDepth range
MigratoryNon-migratory / Resident
Distribution Additional InformationNone entered
Substratum preferencesBedrock, Large to very large boulders, Small boulders, CobblesPhysiographic preferencesOpen coast, Offshore seabed
Biological zoneUpper Infralittoral, Lower InfralittoralWave exposureVery Exposed, Exposed, Moderately Exposed
Tidal stream strength/Water flowStrong (3-6 kn), Moderately Strong (1-3 kn)Salinity
Habitat Additional InformationOften settles on Pecten maximus and Buccinum undatum and occasionally on Chlamys opercularis. Has strong settlement preference for tubes or sites currently or previously used by the species.
AMBI Group (Borja et al., 2000)I 
Distribution References Hayward & Ryland, 1995b, Hayward et al., 1996, Holt et al., 1998, Hayward & Ryland, 1995b, Julie Bremner, unpub data
Reproduction/Life History
Reproductive typeGonochoristic Developmental mechanismPlanktotrophic
Reproductive SeasonJanuary to MarchReproductive LocationInsufficient information
Reproductive frequencyAnnual protracted Regeneration potentialNo
Life span3-5 yearsAge at reproductive maturity
Generation timeInsufficient informationFecundity100,000 to 1 million eggs
Egg/propagule sizeFertilization typeInsufficient information
Larvae/Juveniles
Larval/Juvenile dispersal potential>10kmLarval settlement periodMarch
Duration of larval stage1-2 months  
Additional InformationWilson (1970b) stated that the larvae spend between six weeks and two months in the plankton. Reproductive seasonality is unclear but George & Warwick (1985) and Wilson (1970) have both reported larval settlement in March in the Bristol Channel and Plymouth areas respectively. Wilson (1970) found a spawning period from January to March in Plymouth. Possibly has similar lifespan to Sabellaria alveolata (up to 9 years). Fecundity and recruitment may be variable (Holt et al., 1998) but may be similar to Sabellaria alveolata.
Reproduction References Wilson, 1970(b), George & Warwick, 1985, Holt et al., 1998, Heidi Tillin, unpub data, Julie Bremner, unpub data, Gruet & Lassus, 1983, Giangrande, 1997