A catworm (Nephtys hombergii)

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Summary

Description

Nephtys hombergii is a relatively thin, smooth, segmented (90-200) worm up to 10-20 cm in length. Its head is small with four small antennae. It has a prominent, papillated proboscis which it uses to dig in to the sediment. Its body is rectangular when viewed in cross section but, may appear flattened (when viewed from above) owing to bristled lobes (parapods) that extend sidewards from the body. Typically it is a pearly white colour and chaetae (bristles on parapods) are golden. A long single tail-filament trails from its rear end. Nephtys hombergii is an active worm that demonstrates the characteristic swimming motion (a rapid lateral wriggling, starting from the rear and increasing in amplitude towards the head) of the Nephtyidae.

Recorded distribution in Britain and Ireland

Found throughout Britain and Ireland.

Global distribution

Found from the northern Atlantic, from such areas as the Barents Sea, the Baltic and the North Sea, to the Mediterranean. Nephtys hombergii has been reported from as far south as South Africa.

Habitat

Nephtys hombergii lives infaunally in muddy sand in the intertidal and shallow sublittoral. It may also be found amongst gravel, rocks, and occasionally in Zostera beds.

Depth range

-

Identifying features

  • Body with 90-200 segments; 10-20 cm in length and relatively thin.
  • Smooth front and back, white in colour with a pearly iridescence.
  • Body markedly rectangular in cross section.
  • Head small, sometimes with small, visible eyes.
  • No posterior chaetae (bristles) sharply bent.
  • Branchial cirri shorter than gills.

Additional information

The different species of Nephtys are difficult to identify, requiring detailed examination of the parapodia and chaetae. Reference to Rainer (1991) is recommended. Two other Nephtys species have previously been synonymous with Nephtys hombergii. Nephtys assimilis and Nephtys kersivalensis are now recognized as separate species as described in Rainer (1989) and Rainer (1991). Consequently, some records of the geographical distribution of Nephtys hombergii should be viewed with caution (Olive & Morgan, 1991).

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Biology review

Taxonomy

LevelScientific nameCommon name
PhylumAnnelida
ClassPolychaeta
OrderPhyllodocida
FamilyNephtyidae
GenusNephtys
AuthoritySavigny in Lamarck, 1818
Recent Synonyms

Biology

ParameterData
Typical abundanceSee additional information
Male size range10-20 cm
Male size at maturity
Female size rangeMedium(11-20 cm)
Female size at maturity
Growth formVermiform segmented
Growth rate
Body flexibilityHigh (greater than 45 degrees)
MobilityBurrower, Mobile
Characteristic feeding methodPredator, Scavenger
Diet/food sourceCarnivore
Typically feeds onMolluscs, crustaceans & other polychaetes.
SociabilitySolitary
Environmental positionInfaunal
DependencyNo information found.
SupportsNo information
Is the species harmful?No

Biology information

Abundance. Clay (1967f) lists densities of Nephtys hombergii reported by various authors from locations in the British Isles, which range from 570 per m² in the Tamar Estuary to 2 per m² at a location on the Northumbrian coast.

Mobility. Nephtys hombergii excavates no permanent burrow, but continually changes course in the sediment in the hunt for food, so that a maze of temporary burrows is made, marked only by a mucilage lining. These tunnels are located 5 to 15 cm beneath the surface (Linke, 1939; Holme, 1949). The sampling technique of Vader (1964) showed that the worm can move very quickly through the substratum, downwards on the ebb tide and up again on the flood tide (Clay, 1967f). Nephtys hombergii is also capable of swimming short distances with an undulatory movement.

Nutrition. Adults of the species are carnivorous and capture prey with their eversible, papillated proboscis.

Habitat preferences

ParameterData
Physiographic preferencesOpen coast, Estuary, Enclosed coast or Embayment
Biological zone preferencesLower eulittoral, Mid eulittoral, Sublittoral fringe
Substratum / habitat preferencesCoarse clean sand, Fine clean sand, Muddy sand, Sandy mud
Tidal strength preferencesNo information
Wave exposure preferencesExtremely sheltered, Moderately exposed, Sheltered, Very sheltered
Salinity preferencesReduced (18-30 psu), Variable (18-40 psu)
Depth range
Other preferencesNo text entered
Migration PatternNon-migratory or resident

Habitat Information

Maximum densities of Nephtys hombergii tend to occur in the lower part of the intertidal that is also occupied by Arenicola marina (Clark & Haderlie, 1960; Clark et al., 1962) but has been collected from dredge hauls at various depths. On some shores the intertidal zonation of Nephtys hombergii is probably determined by the type of substratum found at various levels (Clark & Haderlie, 1960). Although the species may colonize a variety of substrata, Nephtys hombergii may be found in higher densities in muddy environments and this tends to isolate it from Nephtys cirrosa, which is characteristic of cleaner, fairly coarse sand. High densities of Nephtys hombergii were found in substrata of 0.3% particles >0.25mm and 5.8% <0.125mm in diameter but the worm tolerated up to 3.8% 0.25mm and 2.2-15.9% <0.125mm (Clark et al.,1962).

Nephtys species penetrate into the mouths of estuaries and estuarine lagoons until the salinity falls below 20 psu, but Nephtys hombergii occasionally extends into waters with a salinity <18 psu (Barnes, 1994). Clark & Haderlie (1960) found Nephtys hombergii in the Bristol Channel at salinities between 15.9 psu and 25.1 psu.

Life history

Adult characteristics

ParameterData
Reproductive typeGonochoristic (dioecious)
Reproductive frequency Annual protracted
Fecundity (number of eggs)No information
Generation time2-3 years
Age at maturity2 years
SeasonSee additional information
Life span2-5 years

Larval characteristics

ParameterData
Larval/propagule type-
Larval/juvenile development Lecithotrophic
Duration of larval stage1-2 months
Larval dispersal potential No information
Larval settlement periodInsufficient information

Life history information

Spawning. Sexes are separate. Nephtys hombergii remains in the sediment during spawning and eggs and sperm are released on to the surface of the sediment during low tide. Bentley (1989) gives an ultrastructural description of oogenesis in Nephtys hombergii. Mean size of oocytes was reported to be between 140 and 160 µm in Arcachon Bay, France, 200 µm in Southampton Water and between 100 to 140 µm on the Northumbrian coast (Mathivat-Lallier & Cazeau, 1991; Oyenenkan, 1986). The animals spawn via the anus. Histological examination by Bentley et al. (1984) revealed the development of a cleft in the central part of the gut in the prepygidial segment which serves to deliver the mature gametes to the anus for spawning. This system is developed only in mature worms of both sexes. Bentley et al. (1984) suggested that this represents the normal pathway for the discharge of gametes in the Nephtyidae, which lack functional coelomoducts. A spawning hormone (SH) released from the supraoesophageal ganglion brings about spawning in mature individuals (Olive, 1976; Olive & Bentley, 1980). Nephtys hombergii is a broadcast spawner, so it is advantageous that the spawning of a given individual coincides with that of several others of the same species. In addition to endocrine control, environmental factors, such as temperature, day-length, and tidal or lunar cycles, have been implicated in the timing of spawning of the Nephtyidae, in particular the spring tide phase of the lunar cycle (Bentley et al., 1984).

Developmental mechanism. The planktonic cycle of Nephtys hombergii was described by Cazaux (1970), who defined five stages: two trochophore stages (2-3 days) and three metatrochophore stages. The first trochophore stage is lecithotrophic and successive four other stages are planktotrophic. The pelagic life cycle of Nephtys hombergii lasts seven to eight weeks at the end of which larvae metamorphose into benthic juveniles. Newly metamorphosed juveniles have an average width of 0.2 mm and eight or nine segments (Mathivat-Lallier & Cazaux, 1991).

Reproductive cycle. Observation of the reproductive patterns of the Nephtyidae suggests that they are related to environmental conditions in central parts of the range of each species, marginal populations of some species exhibit occasional reproductive failures, e.g. Nephtys cirrosa, whose reproductive physiology is not sufficiently well adapted to conditions experienced in the northern limit of its range (Olive & Morgan, 1991). In the British Isles Nephtys hombergii has been observed to spawn in May and June in northern Britain, sometimes successfully but also unsuccessfully, to be followed by a period of oosorption (internal breakdown of gametes) overlapping with the subsequent cycle of gamete production. Olive & Morgan (1991) found reproductive failure in this species difficult to explain, as distribution records inferred Nephtys hombergii to be in the centre of its range in northeast England. They suggested for the relatively long-lived Nephtys hombergii that spawning failure could be part of an adaptive response in which adult survivorship is maintained at the expense of reproductive output (see Lewis et al., 1962; Grémare & Olive, 1986). The endocrine system of Nephtys hombergii (see Bentley & Pacey, 1992) is able to control spawning by failing to secrete gonadotrophic hormone (GH), withdrawing GH secretion during the vitellogenic phase, or failing to secrete spawning hormone. Such endocrine responses may result from the receipt of inappropriate environmental signals from the soma (Bentley & Pacey, 1992). Olive et al. (1985) suggested that when energy levels of the soma fall below some critical level (which may reduce survival chances of the individual) then reproductive failure through GH withdrawal may result.

In the Tyne Estuary spawning of Nephtys hombergii occurred in May and September, whilst in Southampton Water the species spawned throughout the year with peaks in July and November (Wilson, 1936; Oyenekan, 1986). In Århus Bay, Denmark, Nephtys hombergii spawned in August and September, but a decrease in the number of individuals bearing gametes in May and June suggested that at least part of the population spawned in early summer (Fallesen & Jørgensen, 1991).

Sensitivity reviewHow is sensitivity assessed?

Physical pressures

Use / to open/close text displayed

 IntoleranceRecoverabilitySensitivityEvidence / Confidence
Substratum loss [Show more]

Substratum loss

Benchmark. All of the substratum occupied by the species or biotope under consideration is removed. A single event is assumed for sensitivity assessment. Once the activity or event has stopped (or between regular events) suitable substratum remains or is deposited. Species or community recovery assumes that the substratum within the habitat preferences of the original species or community is present. Further details

Evidence

Nephtys hombergii lives infaunally so a considerable proportion of a population within an area would be removed with the sediment. However, the species is a rapid burrower and is able to swim using an undulatory movement, so some may escape the factor if the disturbance is detected in sufficient time. Intolerance has been assessed to be intermediate. Recoverability has been assessed to be very high as recolonization would occur via adult migration and larval settlement. Dittman et al. (1999) observed that Nephtys hombergii was amongst the macrofauna that colonized experimentally disturbed tidal flats within two weeks of the disturbance that caused defaunation of the sediment.
Intermediate Very high Low High
Smothering [Show more]

Smothering

Benchmark. All of the population of a species or an area of a biotope is smothered by sediment to a depth of 5 cm above the substratum for one month. Impermeable materials, such as concrete, oil, or tar, are likely to have a greater effect. Further details.

Evidence

Nephtys hombergii is an active polychaete that uses its eversible proboscis to dig rapidly through the sediment. Vader (1964) observed that the worm relocates throughout the tidal cycle (see general adult biology). It is unlikely therefore, that Nephtys hombergii would be adversely affected by additional sediment of a texture consistent with that of the habitat. At the benchmark level an assessment of not sensitive has been made.
It is likely that viscous or impermeable materials would prevent the polychaete coming to the surface to seek food, but as it hunts infaunally and is mobile and therefore may be able to travel sufficient distance beneath impermeable materials in avoidance and therefore may survive for a period of one month.
Tolerant Not relevant Not sensitive High
Increase in suspended sediment [Show more]

Increase in suspended sediment

Benchmark. An arbitrary short-term, acute change in background suspended sediment concentration e.g., a change of 100 mg/l for one month. The resultant light attenuation effects are addressed under turbidity, and the effects of rapid settling out of suspended sediment are addressed under smothering. Further details

Evidence

Nephtys hombergii lives infaunally and is a predatory species feeding on molluscs, crustaceans and other polychaetes. Increased suspended sediment would not interfere with its feeding. An assessment of not sensitive has been made.
Tolerant Not relevant Not sensitive Low
Decrease in suspended sediment [Show more]

Decrease in suspended sediment

Benchmark. An arbitrary short-term, acute change in background suspended sediment concentration e.g., a change of 100 mg/l for one month. The resultant light attenuation effects are addressed under turbidity, and the effects of rapid settling out of suspended sediment are addressed under smothering. Further details

Evidence

Nephtys hombergii lives infaunally and is a predatory species feeding on molluscs, crustaceans and other polychaetes. Decreased suspended sediment would not interfere with its ability to feed. An assessment of not relevant has been made.
Not relevant Not relevant Not relevant High
Desiccation [Show more]

Desiccation

  1. A normally subtidal, demersal or pelagic species including intertidal migratory or under-boulder species is continuously exposed to air and sunshine for one hour.
  2. A normally intertidal species or community is exposed to a change in desiccation equivalent to a change in position of one vertical biological zone on the shore, e.g., from upper eulittoral to the mid eulittoral or from sublittoral fringe to lower eulittoral for a period of one year. Further details.

Evidence

The infaunal habit of Nephtys hombergii and its ability to burrow relatively rapidly through, and into the substratum are likely to aid the species in its avoidance of increased desiccation in the intertidal zone. Specimens at the uppermost of their distribution in the intertidal zone may become stressed by desiccation if the substratum begins to dry but Nephtys hombergii is sufficiently mobile to relocate to damper substrata. For instance, Vader (1964) observed that the worm relocates throughout the tidal cycle (see general adult biology). An assessment of not relevant has been made.
Not relevant Not relevant Not relevant High
Increase in emergence regime [Show more]

Increase in emergence regime

Benchmark. A one hour change in the time covered or not covered by the sea for a period of one year. Further details

Evidence

An increase in emergence regime is also likely to cause a decline in the abundance of polychaetes at the uppermost edge of their distribution in the intertidal zone, as they would experience drying of the substratum. Nephtys hombergii is sufficiently mobile to rapidly burrow and seek damper substrates. For instance, Vader (1964) observed that the worm relocates throughout the tidal cycle (see general adult biology). Consequently, an intolerance assessment of not relevant has been made as the species is protected from the factor by its habit.
Not relevant Not relevant Not relevant Low
Decrease in emergence regime [Show more]

Decrease in emergence regime

Benchmark. A one hour change in the time covered or not covered by the sea for a period of one year. Further details

Evidence

When the substratum is immersed Nephtys hombergii comes to the surface to feed, but also hunts within the substratum at other times. A longer immersion time may mean that Nephtys hombergii spends longer at the surface where it would be prone to predation by demersal fish. However, as such hunting is part of the polychaetes normal behaviour, effects of a decrease in emergence are unlikely to have a significant effect on the populations viability and intolerance has been assessed to be low. Recoverability has been assessed to be very high as recolonization of the substratum would occur via adult migration and larval settlement. Dittman et al. (1999) observed that Nephtys hombergii was amongst the macrofauna that colonized experimentally disturbed tidal flats within two weeks of the disturbance that caused defaunation of the sediment.
Low Very high Very Low Low
Increase in water flow rate [Show more]

Increase in water flow rate

A change of two categories in water flow rate (view glossary) for 1 year, for example, from moderately strong (1-3 knots) to very weak (negligible). Further details

Evidence

Nephtys hombergii lives within the sediment but may surface during periods of immersion to hunt on the surface where it would experience surface currents, but its size and growth form mean that it would not protrude above the substratum and therefore is unlikely to be swept away. Furthermore, if the polychaete finds conditions intolerable at the surface it may cease to emerge and only hunt infaunal prey. The locations where Nephtys hombergii is typically found have low rates of water flow, which favour the deposition of finer sediments. Increased water flow over a period of one year may cause erosion of the finer fractions of the sediment. Although Nephtys hombergii may inhabit a variety of substrata, it is reported to occur in highest densities in muddier sediments (see adult distribution) and consequently other species of Nephtyidae e.g. Nephtys cirrosa, that favour coarser cleaner sands may become dominant in the habitat. Nephtys hombergii may suffer reduced viability as a result of changes in its habitat and competition. Intolerance has been assessed to be low. Recoverability has been assessed to be very high as recolonization of the substratum would occur via adult migration and larval settlement. Dittman et al. (1999) observed that Nephtys hombergii was amongst the macrofauna that colonized experimentally disturbed tidal flats within two weeks of the disturbance that caused defaunation of the sediment.
Low Very high Very Low Low
Decrease in water flow rate [Show more]

Decrease in water flow rate

A change of two categories in water flow rate (view glossary) for 1 year, for example, from moderately strong (1-3 knots) to very weak (negligible). Further details

Evidence

Nephtys hombergii may be found in and amongst a variety of substrata, but has been recorded in higher abundance in muddy sands in locations with relatively low water flow. As a consequence of decreased water flow, over a period of one year, the habitat in which Nephtys hombergii lives is likely to accumulate additional sediment but would probably remain within the habitat preferences of the species. It is also unlikely that the behaviour of the polychaete would change. An assessment of tolerant has been made.
Tolerant Not relevant Not sensitive Low
Increase in temperature [Show more]

Increase in temperature

  1. A short-term, acute change in temperature; e.g., a 5°C change in the temperature range for three consecutive days. This definition includes ‘short-term’ thermal discharges.
  2. A long-term, chronic change in temperature; e.g. a 2°C change in the temperature range for a year. This definition includes ‘long term’ thermal discharges.

For intertidal species or communities, the range of temperatures includes the air temperature regime for that species or community. Further details

Evidence

By virtue of its burrowing habit and of its preference for the sublittoral and lower part of the littoral, Nephtys hombergii seems able to withstand extremes of temperature (Clay, 1967f). The species is found to the south of the British Isles (Mediterranean and Atlantic coasts in the southern hemisphere), so is likely to tolerate a long-term increase of 2°C. Emery & Stevensen (1957) found that the polychaete could withstand summer temperatures of 30-35°C so may also be able to tolerate a short-term acute increase in temperature. In addition, the species environmental position and mobility probably protects it from the factor. Therefore, an assessment of tolerant has been recorded.
Tolerant Not relevant Not sensitive High
Decrease in temperature [Show more]

Decrease in temperature

  1. A short-term, acute change in temperature; e.g., a 5°C change in the temperature range for three consecutive days. This definition includes ‘short-term’ thermal discharges.
  2. A long-term, chronic change in temperature; e.g. a 2°C change in the temperature range for a year. This definition includes ‘long term’ thermal discharges.

For intertidal species or communities, the range of temperatures includes the air temperature regime for that species or community. Further details

Evidence

Nephtys hombergii by virtue of its burrowing habit and of its preference for the sublittoral and lower part of the littoral seems able to withstand extremes of temperature (Clay, 1967f). The species is found to the north of the British Isles so is apparently tolerant of average temperatures lower than those it experiences in the British Isles. Raymont (1955) commented that Nephtys hombergii did not appear to suffer on the Argyleshire coast during the severe winter of 1946, as the polychaetes habitat was at low water level and beneath the sediment, it was unaffected by the intertidal freezing. Crisp (1964) also found no evidence that the polychaete was affected by the severe winter of 1962-63 on the north Wales coast. In addition, the species environmental position and mobility probably protects it from the factor. Therefore, an assessment of tolerant has been recorded.
Tolerant Not relevant Not sensitive High
Increase in turbidity [Show more]

Increase in turbidity

  1. A short-term, acute change; e.g., two categories of the water clarity scale (see glossary) for one month, such as from medium to extreme turbidity.
  2. A long-term, chronic change; e.g., one category of the water clarity scale (see glossary) for one year, such as from low to medium turbidity. Further details

Evidence

Nephtys hombergii lives infaunally between a depth of 5 and 15 cm where light is not transmitted. An increase in turbidity is unlikely to have a detectable effect on the viability of the species and an assessment of not relevant has been made.
Not relevant Not relevant Not relevant Not relevant
Decrease in turbidity [Show more]

Decrease in turbidity

  1. A short-term, acute change; e.g., two categories of the water clarity scale (see glossary) for one month, such as from medium to extreme turbidity.
  2. A long-term, chronic change; e.g., one category of the water clarity scale (see glossary) for one year, such as from low to medium turbidity. Further details

Evidence

Nephtys hombergii lives infaunally between a depth of 5 and 15 cm where light is not transmitted. A decrease in turbidity is unlikely to have a detectable effect on the viability of the species and an assessment of not relevant has been made.
Not relevant Not relevant Not relevant Not relevant
Increase in wave exposure [Show more]

Increase in wave exposure

A change of two ranks on the wave exposure scale (view glossary) e.g., from Exposed to Extremely exposed for a period of one year. Further details

Evidence

Nephtys hombergii lives infaunally but may sometimes partially emerge to seek and capture food but does not present a significant surface area to wave action to sustain physical damage. Clark & Haderlie (1960) and Clark, Alder & McIntyre (1962) suggested that strong wave action limited the distribution of Nephtys hombergii. Increased wave action for the duration of one year may begin to change the nature of the substratum that the polychaete inhabits and its distribution may consequently alter. Therefore, an intolerance of intermediate has been recorded. On return to prior conditions recoverability may be very high as recolonization of the substratum would occur via adult migration as well as larval settlement. For instance, Dittman et al. (1999) observed that Nephtys hombergii was amongst the macrofauna that colonized experimentally disturbed tidal flats within two weeks of the disturbance that caused defaunation of the sediment.
Intermediate Very high Low Moderate
Decrease in wave exposure [Show more]

Decrease in wave exposure

A change of two ranks on the wave exposure scale (view glossary) e.g., from Exposed to Extremely exposed for a period of one year. Further details

Evidence

Clark & Haderlie (1960) and Clark, Alder & McIntyre (1962) suggested that strong wave action limited the distribution of Nephtys hombergii, so it may be inferred that decreased wave exposure would not be detrimental to the species so an intolerance assessment of tolerant has been suggested.
Tolerant Not relevant Not sensitive
Noise [Show more]

Noise

  1. Underwater noise levels e.g., the regular passing of a 30-metre trawler at 100 metres or a working cutter-suction transfer dredge at 100 metres for one month during important feeding or breeding periods.
  2. Atmospheric noise levels e.g., the regular passing of a Boeing 737 passenger jet 300 metres overhead for one month during important feeding or breeding periods. Further details

Evidence

Nephtys hombergii would probably detect vibration caused by noise, but noise at the benchmark level is unlikely to have a detectable effect on the viability of the species and an assessment of tolerant has been suggested.
Tolerant Not relevant Not sensitive Low
Visual presence [Show more]

Visual presence

Benchmark. The continuous presence for one month of moving objects not naturally found in the marine environment (e.g., boats, machinery, and humans) within the visual envelope of the species or community under consideration. Further details

Evidence

Nephtyidae possess primitive photoreceptors (Clark, 1956) and are unlikely to have the acuity to visually detect objects moving about on the surface of the overlying water. An assessment of not sensitive has been suggested.
Tolerant Not relevant Not sensitive Moderate
Abrasion & physical disturbance [Show more]

Abrasion & physical disturbance

Benchmark. Force equivalent to a standard scallop dredge landing on or being dragged across the organism. A single event is assumed for assessment. This factor includes mechanical interference, crushing, physical blows against, or rubbing and erosion of the organism or habitat of interest. Where trampling is relevant, the evidence and trampling intensity will be reported in the rationale. Further details.

Evidence

Nephtys hombergii lives in sediment between a depth of 5-15 cm and is therefore protected from most sources of abrasion and physical disturbance caused by surface action. However, it is likely to be damaged by any activity (e.g. anchors, or scallop dredging) that penetrates the sediment. Although the species is relatively mobile within the sediment intolerance has been assessed to be intermediate, as some individuals would probably be damaged. Recovery has been assessed to be very high, as re-population would occur initially relatively rapidly via adult migration and later by larval recruitment.
Intermediate Very high Low Low
Displacement [Show more]

Displacement

Benchmark. Removal of the organism from the substratum and displacement from its original position onto a suitable substratum. A single event is assumed for assessment. Further details

Evidence

If displaced Nephtys hombergii would be able to bury itself back into the substratum using its eversible proboscis (see general adult biology). It has been assessed to be not sensitive to displacement.
Tolerant Immediate Not sensitive High

Chemical pressures

Use [show more] / [show less] to open/close text displayed

 IntoleranceRecoverabilitySensitivityEvidence / Confidence
Synthetic compound contamination [Show more]

Synthetic compound contamination

Sensitivity is assessed against the available evidence for the effects of contaminants on the species (or closely related species at low confidence) or community of interest. For example:

  • evidence of mass mortality of a population of the species or community of interest (either short or long term) in response to a contaminant will be ranked as high sensitivity;
  • evidence of reduced abundance, or extent of a population of the species or community of interest (either short or long term) in response to a contaminant will be ranked as intermediate sensitivity;
  • evidence of sub-lethal effects or reduced reproductive potential of a population of the species or community of interest will be assessed as low sensitivity.

The evidence used is stated in the rationale. Where the assessment can be based on a known activity then this is stated. The tolerance to contaminants of species of interest will be included in the rationale when available; together with relevant supporting material. Further details.

Evidence

No evidence concerning the specific effects of chemical contaminants on Nephtys hombergii was found. Boon et al. (1985) reported that Nephtys species in the North Sea accumulated organochlorines but, based on total sediment analyses, organochlorine concentrations in Nephtys species were not correlated with the concentrations in the (type of) sediment which they inhabited. Specific effects of synthetic chemicals have been reported for other species of polychaete. Exposure of Hediste diversicolor and Arenicola marina to Ivermecten resulted in significant mortality (see MarLIN reviews; Collier & Pinn, 1998). Beaumont et al. (1989) investigated the effects of tri-butyl tin (TBT) on benthic organisms. At concentrations of 1-3 µg/l there was no significant effect on the abundance of Hediste diversicolor or Cirratulus cirratus after 9 weeks in a microcosm. However, no juvenile polychaetes were retrieved from the substratum suggesting that TBT had an effect on the larval and/or juvenile stages of these polychaetes. Bryan & Gibbs (1991) reported that Arenicola costata larvae were unaffected by 168 hr exposure to 2000 ng TBT/ l seawater and were probably relatively tolerant, however in another study, Scoloplos armiger exhibited a dose related decline in numbers when exposed to TBT paint particles in the sediment. Intolerance has been assessed to be intermediate owing to the fact that different chemicals are likely to have different modes of action and effect on different species of polychaete. Nephtys hombergii may demonstrate similar sensitivities as the species mentioned above but little evidence was found. Recoverability has been assessed to be high as recolonization is likely via adult migration and larval settlement.
Intermediate High Low Low
Heavy metal contamination [Show more]

Heavy metal contamination

Evidence

Nephtys hombergii is recorded in Restronguet Creek, a branch of the Fal Estuary system which is heavily contaminated with metals. Concentrations of dissolved Zn typically range from 100-2000 µ g/l, Cu from 10-100 µg/l and Cd from 0.25-5.0 µg/l. The sediments of Restronguet Creek are also highly contaminated, the levels of Cu, Zn, As and Sn being in the order of 1500-3500 µg/g (Bryan & Gibbs, 1983). Analyses of organisms from Restronguet Creek revealed that some species contained abnormally high concentrations of heavy metals. Nephtys hombergii from the middle and lower reaches of the creek contained appreciably higher concentrations of Cu (2227 µg/g dry wt), Fe and Zn than comparable specimens of Hediste diversicolor (as Nereis diversicolor). However, amongst polychaetes within the creek, there was evidence that some metals were regulated. In Nephtys hombergii the head end of the worm became blackened and x-ray microanalysis by Bryan & Gibbs (1983) indicated that this was caused by the deposition of copper sulphide in the body wall. In the same study, Bryan & Gibbs (1983) presented evidence that Nephtys hombergii from Restronguet Creek possessed increased tolerance to copper contamination. Specimens from the Tamar Estuary had a 96 h LC50 of 250 µg/l, whilst those from Restronguet Creek had a 96 h LC50 of 700 µg/l (35 psu; 13°C). Bryan & Gibbs (1983) suggested that since the area had been heavily contaminated with metals for > 200 years, there had been adequate time for metal-resistant populations to develop especially for relatively mobile species. An intolerance assessment of intermediate has been suggested as it is likely that given time populations of the species may become tolerant of heavy metal pollution, but that in the short term acute exposure of heavy metals may be deleterious to populations not previously exposed. Recoverability has been assessed to be high as recolonization is likely via adult migration and larval settlement.
Intermediate High Low Moderate
Hydrocarbon contamination [Show more]

Hydrocarbon contamination

Evidence

The 1969 West Falmouth Spill of Grade 2 diesel fuel, documented by Sanders (1978), illustrates the effects of hydrocarbons in a sheltered habitat with a soft mud/sand substrata (Suchanek, 1993). The entire benthic fauna was eradicated immediately following the spill and remobilization of oil that continued for a period >1 year after the spill contributed to much greater impact upon the habitat than that caused by the initial spill. Effects are likely to be prolonged as hydrocarbons incorporated within the sediment by bioturbation will remain for a long time owing to slow degradation under anoxic conditions. Oil covering the surface and within the sediment would prevent oxygen transport to the infauna and promote anoxia as the infauna utilise oxygen during respiration. Although Nephtys hombergii is relatively tolerant of hypoxia and periods of anoxia (see oxygenation), a prolonged absence of oxygen would probably result in the death of it and other infauna. McLusky (1982) found that petrochemical effluents, including organic solvents and ammonium salts, released from a point source to an estuarine intertidal mudflat of the Forth Estuary, Scotland, caused severe pollution in the immediate vicinity. Beyond 500 m distance the effluent contributed to an enrichment of the fauna in terms of abundance and biomass similar to that reported by Pearson & Rosenberg (1978) for organic pollution; Nephtys hombergii was found in the area with maximum abundance of species and highest total biomass at 500 m from the discharge. Intolerance has been assessed to be high as it seems likely that significant hydrocarbon contamination would kill affected populations of the species. On return to prior conditions recoverability has been assessed to be high as recolonization is likely via adult migration and larval settlement.
High High Moderate Moderate
Radionuclide contamination [Show more]

Radionuclide contamination

Evidence

Insufficient
information.
No information Not relevant No information Not relevant
Changes in nutrient levels [Show more]

Changes in nutrient levels

Evidence

Nephtys hombergii is unlikely to be directly affected by nutrient enrichment as growth is not dependent on nutrient availability. However, symptoms of eutrophication (when nutrient input may exceeds the assimilative capacity of the environment) include hypoxia, to which Nephtys hombergii may be intolerant over long episodes (see oxygenation below) but has been found tolerant of over short episodes. At the benchmark level an intolerance assessment of low has been suggested as in the long term species viability may be affected. Effects of deoxygenation are considered separately. Recoverability has been assessed to be very high. Dittman et al. (1999) observed that Nephtys hombergii was amongst the macrofauna that colonized experimentally disturbed tidal flats within two weeks of the disturbance that caused defaunation of the sediment.
Low Very high Very Low Moderate
Increase in salinity [Show more]

Increase in salinity

  1. A short-term, acute change; e.g., a change of two categories from the MNCR salinity scale for one week (view glossary) such as from full to reduced.
  2. A long-term, chronic change; e.g., a change of one category from the MNCR salinity scale for one year (view glossary) such as from reduced to low. Further details.

Evidence

Nephtys hombergii is considered to be a brackish water species (Barnes, 1994) but where the species occurs in open coastal locations the species would have to tolerate salinities of 25 psu and above. Within a few months of the closure of a dam across the Krammer-Volkerak estuary in the Netherlands, Wolff (1971) observed that species with pelagic larvae or a free-swimming phase, expanded rapidly with a concomitant increase of salinity to 9-15 psu everywhere. Prior to the closure of the dam the estuary demonstrated characteristics of a typical 'salt-wedge' estuary with a salinity gradient from 0.3 to 15 psu. Hence, Nephtys hombergii is likely to survive increases in salinity within estuarine environments and intolerance has been assessed to be low. In fully saline locations Nephtys hombergii may still be found but, may be competitively inferior to other species of Nephtyidae (e.g. Nephtys ciliata and Nephtys hystricis) and occur in lower densities. On return to optimal conditions recoverability is likely to be very high as recolonization via adult migration is likely to be rapid.
Low Very high Very Low Moderate
Decrease in salinity [Show more]

Decrease in salinity

  1. A short-term, acute change; e.g., a change of two categories from the MNCR salinity scale for one week (view glossary) such as from full to reduced.
  2. A long-term, chronic change; e.g., a change of one category from the MNCR salinity scale for one year (view glossary) such as from reduced to low. Further details.

Evidence

Nephtys hombergii is considered to be a brackish water species, and has been reported to extend in to estuarine locations where salinity is less than 18 psu (Barnes, 1994). Clark & Haderlie (1960) found Nephtys hombergii in the Bristol Channel at salinities between 15.9 psu and 25.1 psu. If the salinity were to become intolerable to the polychaete it is likely that as a mobile species, able to both swim and burrow, Nephtys hombergii would avoid the change in salinity by moving away and localized densities would decline. The species is unlikely to be killed by the decrease in salinity and intolerance has been assessed to be low. Recoverability has been assessed to be very high as recolonization would occur via adult migration and larval recruitment within the year.
Low Very high Very Low Moderate
Changes in oxygenation [Show more]

Changes in oxygenation

Benchmark.  Exposure to a dissolved oxygen concentration of 2 mg/l for one week. Further details.

Evidence

Nephtys hombergii is a free-living, burrowing predator in marine sediments in which it has to survive periods of severe hypoxia and sulphide exposure, while at the same time maintaining agility in order to feed on other invertebrates. Nephtys hombergii has adapted to such conditions by utilising several strategies. Arndt & Schiedek (1997) found Nephtys hombergii to have a remarkably high content of phosphagen (phosphoglycocyamine), which is the primary energy source during periods of environmental stress. With increasing hypoxia, energy is also provided via anaerobic glycolysis, with strombine as the main end-product. Energy production via the succinate pathway becomes important only under severe hypoxia, suggesting a biphasic response to low oxygen conditions which probably is related to the polychaete's mode of life. The presence of sulphide resulted in a higher anaerobic energy flux and a more pronounced energy production via glycolysis than in anoxia alone. Nevertheless, after sulphide exposure under anaerobic conditions of <24 h, Arndt & Schiedek (1997) observed Nephtys hombergii to recover completely. Although Nephtys hombergii appears to be well adapted to a habitat with short-term fluctuations in oxygen and appearance of hydrogen sulphide, its high energy demand as a predator renders it likely to limit its survival in an environment with longer lasting anoxia and concomitant sulphide exposure. For instance, Fallesen & Jørgensen (1991) recorded Nephtys hombergii in localities in Århus Bay, Denmark, where oxygen concentrations were permanently or regularly low, but in the late summer of 1982 a severe oxygen deficiency killed populations of Nephtys species (Nephtys hombergii and Nephtys ciliata) in the lower part of the bay. However, Nephtys hombergii recolonized the affected area by the end of autumn the same year. Alheit (1978) reported a LC50 at 8°C of 23 days for Nephtys hombergii maintained under anaerobic conditions. Such evidence suggests that Nephtys hombergii would be tolerant of short episodes of oxygen deficiency and at the benchmark duration of one week Nephtys hombergii is unlikely to be adversely affected by hypoxic conditions and would revive on return to oxygenated sediment. At the benchmark level an assessment of not sensitive has been suggested.
Tolerant Not relevant Not sensitive High

Biological pressures

Use [show more] / [show less] to open/close text displayed

 IntoleranceRecoverabilitySensitivityEvidence / Confidence
Introduction of microbial pathogens/parasites [Show more]

Introduction of microbial pathogens/parasites

Benchmark. Sensitivity can only be assessed relative to a known, named disease, likely to cause partial loss of a species population or community. Further details.

Evidence

Insufficient
information
No information Not relevant No information Not relevant
Introduction of non-native species [Show more]

Introduction of non-native species

Sensitivity assessed against the likely effect of the introduction of alien or non-native species in Britain or Ireland. Further details.

Evidence

No alien species are currently known to affect the viability of this species.
Tolerant Not relevant Not sensitive Not relevant
Extraction of this species [Show more]

Extraction of this species

Benchmark. Extraction removes 50% of the species or community from the area under consideration. Sensitivity will be assessed as 'intermediate'. The habitat remains intact or recovers rapidly. Any effects of the extraction process on the habitat itself are addressed under other factors, e.g. displacement, abrasion and physical disturbance, and substratum loss. Further details.

Evidence

Nephtys hombergii is known as a 'catworm' amongst anglers who may dig sediments on a relatively small scale to obtain the species for fishing bait. Intolerance has been assessed to be intermediate as a proportion of the population would be removed. Recovery of Nephtys hombergii has been assessed to be very high as re-population would occur initially relatively rapidly via adult migration and later by larval recruitment.
Intermediate Very high Low Low
Extraction of other species [Show more]

Extraction of other species

Benchmark. A species that is a required host or prey for the species under consideration (and assuming that no alternative host exists) or a keystone species in a biotope is removed. Any effects of the extraction process on the habitat itself are addressed under other factors, e.g. displacement, abrasion and physical disturbance, and substratum loss. Further details.

Evidence

Commercially exploitable species such as Cerastoderma edule occur in the same habitat as Nephtys species. Shellfish of marketable size can be harvested both in the intertidal and subtidal more rapidly and efficiently using mechanical methods such as tractor-powered harvesters and suction dredgers than by traditional methods. Hydraulic suction dredgers operate by fluidising the sand using water jets and then lifting the sediment and infauna into a revolving drum for sorting. The tractor-towed dredge utilises a blade between 70 -100 cm wide that penetrates to a depth of between 20-40 cm. Sediment is sorted through a rotating drum cage (Hall & Harding, 1997). Such machinery adversely impacts on non-target infaunal species as they are sucked or displaced from the sediment and sustain damage as 'by-catch'. For instance, Ferns et al. (2000) recorded significant losses of common infaunal polychaetes from areas of intertidal muddy sand sediment worked with a tractor-towed cockle harvester: 31 % of the polychaete Scoloplos armiger (initial density of 120 m²) and 83 % of Pygospio elegans (initial density 1850 m²) were removed and bird feeding activity increased on harvested areas as gulls and waders took advantage of invertebrates made available. Intolerance of Nephtys hombergii has been assessed to be high as mortalities would occur. In the study by Ferns et al. (2000) the population of Pygospio elegans remained depleted for more than 100 days after harvesting, whilst those of Nephtys hombergii, Scoloplos armiger and Bathyporeia spp. were depleted for over 50 days. Recovery of Nephtys hombergii has been assessed to be very high as re-population would occur initially relatively rapidly via adult migration and later by larval recruitment.
High Very high Low High

Additional information

None entered

Importance review

Policy/legislation

- no data -

Status

Non-native

ParameterData
Native-
Origin-
Date Arrived-

Importance information

Large specimens of the Nephtyidae family are called 'catworms' and used as bait by fishermen.
A negative relationship between the abundance of the predatory polychaete Nephtys hombergii and values of biomass and rate of increase in two of its prey species, the polychaetes Scoloplos armiger and Heteromastus filiformis, were found by Beukema (1987) in long-term data from tidal flats in the western-most part of the Wadden Sea. Beukema (1987) observed that values for prey biomass tended to decline at high Nephtys hombergii biomass, whereas they tended to increase at lower levels of Nephtys hombergii biomass. Beukema (1987) considered these results to corroborate that Nephtys hombergii is an important infaunal predator in the Wadden Sea. Schubert & Reise (1986) also reported similar evidence and concluded Nephtys hombergii to be an important intermediate predator in the Wadden Sea.

Bibliography

  1. Alheit, J., 1978. Distribution of the polychaete genus Nephtys: a stratified random sampling survey. Kieler Meeresforschungen, 4, 61-67.

  2. Arndt, C. & Schiedek, D., 1997. Nephtys hombergii, a free living predator in marine sediments: energy production under environmental stress. Marine Biology, 129, 643-540.

  3. Barnes, R.S.K., 1994. The brackish-water fauna of northwestern Europe. Cambridge: Cambridge University Press.

  4. Beaumont, A.R., Newman, P.B., Mills, D.K., Waldock, M.J., Miller, D. & Waite, M.E., 1989. Sandy-substrate microcosm studies on tributyl tin (TBT) toxicity to marine organisms. Scientia Marina, 53, 737-743.

  5. Bentley, M.G. & Pacey, A.A., 1992. Physiological and environmental control of reproduction in polychaetes. Oceanography and Marine Biology: an Annual Review, 30, 443-481.

  6. Bentley, M.G., 1989. An ultrastructural study of oogenesis in the polychaete Nephtys hombergii Savigny. Helgolander Meeresuntersuchungen, 43, 157-169.

  7. Bentley, M.G., Olive, P.J.W., Garwood, P.R. & Wright, N.H., 1984. The spawning and spawning mechanism of Nephtys caeca (Fabricius, 1780) and Nephtys hombergii Savigny, 1818 (Annelida: Polychaeta). Sarsia, 69, 63-68.

  8. Beukema, J.J., 1987. Influence of the predatory polychaete Nephtys hombergii on the abundance of other polychaetes. Marine Ecology Progress Series, 40, 95-107.

  9. Boon, J.P., Zantvoort, M.B., Govaert, M.J.M.A. & Duinker, J.C ., 1985. Organochlorines in benthic polychaetes (Nephtys spp.) and sediments from the southern North Sea. Identification of individual PCB components. Netherlands Journal of Sea Research, 19, 93-109.

  10. Bryan, G.W. & Gibbs, P.E., 1983. Heavy metals from the Fal estuary, Cornwall: a study of long-term contamination by mining waste and its effects on estuarine organisms. Plymouth: Marine Biological Association of the United Kingdom. [Occasional Publication, no. 2.]

  11. Bryan, G.W. & Gibbs, P.E., 1991. Impact of low concentrations of tributyltin (TBT) on marine organisms: a review. In: Metal ecotoxicology: concepts and applications (ed. M.C. Newman & A.W. McIntosh), pp. 323-361. Boston: Lewis Publishers Inc.

  12. Cazeau, C., 1970. Recherches sur l'écologie et le developpement larvaire des Polychétes d'Arcachon. , These de Doctorat es Sciences, Bordeaux, 295, 1-395.

  13. Clark, R.B. & Haderlie, E.C., 1960. The distribution of Nephtys cirrosa and Nephtys hombergii of the south western coasts of England and Wales. Journal of Animal Ecology, 29, 117-147.

  14. Clark, R.B., Alder, R.R. & McIntyre, A.D., 1962. The distribution of Nephtys on the Scottish coast. Journal of Animal Ecology, 31, 359-372.

  15. Clay, E., 1967f. Literature survey of the common fauna of estuaries, 6. Nephtys hombergii Lamarck. Imperial Chemical Industries Limited, Brixham Laboratory, PVM45/B/379.

  16. Collier, L.M. & Pinn, E.H., 1998. An assessment of the acute impact of the sea lice treatment Ivermectin on a benthic community. Journal of Experimental Marine Biology and Ecology, 230 (1), 131-147. DOI https://doi.org/10.1016/s0022-0981(98)00081-1

  17. Crisp, D.J. (ed.), 1964. The effects of the severe winter of 1962-63 on marine life in Britain. Journal of Animal Ecology, 33, 165-210.

  18. Dittmann, S., Günther, C-P. & Schleier, U., 1999. Recolonization of tidal flats after disturbance. In The Wadden Sea ecosystem: stability, properties and mechanisms (ed. S. Dittmann), pp.175-192. Berlin: Springer-Verlag.

  19. Emery, K.O., Stevenson, R.E., Hedgepeth, J.W., 1957. Estuaries and lagoons. In Treatise on marine ecology and paleoecology. vol. 1. Ecology, (ed. J.W. Hedgpeth), Geological Society of America, Memoir 67, pp. 673-750. Waverley Press, Baltimore, Mayland.

  20. Fallesen, G. & Jørgensen, H.M., 1991. Distribution of Nephtys hombergii and Nephtys ciliata (Polychaeta: Nephtyidae) in Århus Bay, Denmark, with emphasis on the severe oxygen deficiency. Ophelia, Supplement 5, 443-450.

  21. Fauchald, K., 1963. Nephtyidae (Polychaeta) from Norwegian waters. Sarsia, 13, 1-32.

  22. Ferns, P.N., Rostron, D.M. & Siman, H.Y., 2000. Effects of mechanical cockle harvesting on intertidal communities. Journal of Applied Ecology, 37, 464-474.

  23. Fish, J.D. & Fish, S., 1996. A student's guide to the seashore. Cambridge: Cambridge University Press.

  24. Grémare, A. & Olive, P.J.W., 1986. A preliminary study of fecundity and reproductive strategies. International Journal of Invertebrate Reproduction and Development, 9, 1-16.

  25. Hayward, P., Nelson-Smith, T. & Shields, C. 1996. Collins pocket guide. Sea shore of Britain and northern Europe. London: HarperCollins.

  26. Hayward, P.J. & Ryland, J.S. (ed.) 1995b. Handbook of the marine fauna of North-West Europe. Oxford: Oxford University Press.

  27. Holme, N.A., 1949. The fauna of sand and mud banks near the mouth of the Exe Estuary. Journal of the Marine Biological Association of the United Kingdom, 28, 189-237.

  28. Lewis, J.R., Bowman, R.S., Kendall, M.A. & Williamson, P., 1982. Some geographical components in population dynamics: possibilities and realities in some littoral species. Netherlands Journal of Sea Research, 16, 18-28.

  29. Linke, O., 1939. Die Biota des Jadebusenwatts. Helgolander Wissenschaftliche Meeresuntersuchungen, 1, 201-348.

  30. Mathivat-Lallier, M.H. & Cazaux, C., 1991. Life-history of Nephtys hombergii in Arcachon Bay. Estuarine and Coastal Marine Science, 32, 1-9.

  31. McLusky, D.S., 1982. The impact of petrochemical effluent on the fauna of an intertidal estuarine mudflat. Estuarine, Coastal and Shelf Science, 14 (5), 489-499. DOI https://doi.org/10.1016/S0302-3524(82)80072-8

  32. Olive, P.J.W. & Bentley, M.G., 1980. Hormonal control of oogenesis, ovulation and spawning in the annual reproductive cycle of the polychaete, Nephtys hombergii Savigny (Nephtyidae). International Journal of Invertebrate Reproduction and Development, 2, 205-221.

  33. Olive, P.J.W. & Morgan, P.J., 1991. The reproductive cycles of four British intertidal Nephtys species in relation to their geographical distribution (Polychaeta: Nephtyidae). Ophelia, Supplement 5, 351-361.

  34. Olive, P.J.W., 1976. Preliminary evidence for a previously un-described spawning hormone in Nephtys hombergii (Polychaeta: Nephtyidae). General and Comparative Endocrinology, 28, 454-460.

  35. Oyenekan, J.A., 1986. Population dynamics and secondary production of Nephtys hombergii (Polychaeta: Nephtyidae). Marine Biology, 93, 217-223.

  36. Rainer, S.F., 1989. Redescription of Nephtys assimilis and Nephtys kersivalensis (Polychaeta: Phyllodocida) and a key to Nephtys from northern Europe. Journal of the Marine Biological Association of the United Kingdom, 45, 875-889.

  37. Rainer, S.F., 1990. The genus Nephtys (Polychaeta: Phyllodocida) of northern Europe: redescription of N. hystricis and N. incisa. Journal of Natural History, 24, 361-372.

  38. Rainer, S.F., 1991. The genus Nephtys (Polychaeta: Phyllodocida) of northern Europe: a review of species, including the description of N. pulchra sp. n. and a key to the Nephtyidae. Helgolander Meeresuntersuchungen, 45, 65-96.

  39. Raymont, J.E.G., 1955. The fauna of an intertidal mud flat. Deep Sea Research, Supplement 3, 178-203.

  40. Sanders, H.L., 1978. Florida oil spill impact on the Buzzards Bay benthic fauna: West Falmouth. Journal of the Fisheries Board of Canada, 35 (5), 717-730.

  41. Schubert, A. & Reise, K., 1987. Predatory effects of Nephtys hombergii on other polychaetes in tidal flat sediments. Marine Ecology Progress Series, 34, 117-124.

  42. Suchanek, T.H., 1993. Oil impacts on marine invertebrate populations and communities. American Zoologist, 33, 510-523. DOI https://doi.org/10.1093/icb/33.6.510

  43. Vader, W.J.M., 1964. A preliminary investigation in to the reactions of the infauna of the tidal flats to tidal fluctuations in water level. Netherlands Journal of Sea Research, 2, 189-222.

  44. Wolff, W.J., 1971b. Changes in intertidal benthos communities after an increase in salinity. Thalassia Jugoslavica, 7, 429-434.

Datasets

  1. Bristol Regional Environmental Records Centre, 2017. BRERC species records recorded over 15 years ago. Occurrence dataset: https://doi.org/10.15468/h1ln5p accessed via GBIF.org on 2018-09-25.

  2. Centre for Environmental Data and Recording, 2018. Ulster Museum Marine Surveys of Northern Ireland Coastal Waters. Occurrence dataset https://www.nmni.com/CEDaR/CEDaR-Centre-for-Environmental-Data-and-Recording.aspx accessed via NBNAtlas.org on 2018-09-25.

  3. Environmental Records Information Centre North East, 2018. ERIC NE Combined dataset to 2017. Occurrence dataset: http://www.ericnortheast.org.ukl accessed via NBNAtlas.org on 2018-09-38

  4. Kent Wildlife Trust, 2018. Kent Wildlife Trust Shoresearch Intertidal Survey 2004 onwards. Occurrence dataset: https://www.kentwildlifetrust.org.uk/ accessed via NBNAtlas.org on 2018-10-01.

  5. Merseyside BioBank., 2018. Merseyside BioBank (unverified). Occurrence dataset: https://doi.org/10.15468/iou2ld accessed via GBIF.org on 2018-10-01.

  6. National Trust, 2017. National Trust Species Records. Occurrence dataset: https://doi.org/10.15468/opc6g1 accessed via GBIF.org on 2018-10-01.

  7. NBN (National Biodiversity Network) Atlas. Available from: https://www.nbnatlas.org.

  8. North East Scotland Biological Records Centre, 2017. NE Scotland other invertebrate records 1800-2010. Occurrence dataset: https://doi.org/10.15468/ifjfxz accessed via GBIF.org on 2018-10-01.

  9. OBIS (Ocean Biodiversity Information System),  2025. Global map of species distribution using gridded data. Available from: Ocean Biogeographic Information System. www.iobis.org. Accessed: 2025-05-31

  10. South East Wales Biodiversity Records Centre, 2018. SEWBReC Worms (South East Wales). Occurrence dataset: https://doi.org/10.15468/5vh0w8 accessed via GBIF.org on 2018-10-02.

  11. South East Wales Biodiversity Records Centre, 2018. Dr Mary Gillham Archive Project. Occurance dataset: http://www.sewbrec.org.uk/ accessed via NBNAtlas.org on 2018-10-02

Citation

This review can be cited as:

Budd, G.C. & Hughes, J.R. 2005. Nephtys hombergii A catworm. In Tyler-Walters H. Marine Life Information Network: Biology and Sensitivity Key Information Reviews, [on-line]. Plymouth: Marine Biological Association of the United Kingdom. [cited 31-05-2025]. Available from: https://marlin.ac.uk/species/detail/1710

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Last Updated: 26/10/2005