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You are viewing an archived site. The Chesapeake Bay Introduced Species Database project ended in 2020 and the database is no longer receiving updates. Learn more…
Image of Ficopomatus enigmaticus

Ficopomatus enigmaticus

Annelids-Polychaetes

serpulid tubeworm

Image Credit: Ruiz laboratory

Description Taxonomy Invasion History Ecology Impacts References

Description

Taxonomy of this species is confused in the literature prior to the revision by ten Hove and Weerdenburg (1978). Many papers referring to F. enigmaticus are actually describing F. uschakovi.


Taxonomy

Kingdom Phylum Class Order Family Genus
Animalia Annelida Polychaeta Canalipalpata Serpulidae Ficopomatus

Synonyms

Merceriella enigmatica

Invasion History

Chesapeake Bay Status

First Record Population Range Introduction Residency Source Region Native Region Vectors
1994 Established Unknown Introduced Regular Resident Unknown-Marine Unknown-Marine Shipping(Ballast Water,Fouling Community), Fisheries(Oysters-accidental)

History of Spread

The place of origin of the tubeworm Ficopomatus enigmaticus remains unclear. It has been speculated that it came from a subtropical to temperate area such as southern Australia. Most authors rule out Fauvel's (Fauvel 1923) hypothesized Indian/Indonesian origin, but no one knows for certain. It first appeared more or less simultaneously in Australia, CA, Spain, France (Fauvel 1923); England in the the 1920's, and since has been recorded in most major harbors in northern Europe and the Mediterranean, New Zealand (Read and Gordon 1921), South America (Obenat and Pezzani 1991), South Africa, Hawaii and Japan (Ten Hove and van Weedenburg 1978 , Asakura 1992). It has been suggested that it was brought to Europe in ships during World War I (ten Hove and Weerdenburg 1978).

Ficopomatus enigmaticus first appeared in North America in 1921 in Lake Merritt, a lagoon of San Francisco Bay, and has since spread to many locations in that Bay (Carlton 1979). This worm may have been found on a boat at Corpus Christi TX in 1951 (Hartman 1952), and has been since found in the same locality on riprap by Andrew Cohen in TX in 1995 (McCann and Carlton in prep.). It occurs in several Gulf Coast bays from Tampa Bay (FL) to Corphus Christi (Ruiz et al., unpublished data; U.S. National Museum of Natural History 2007). On the Atlantic Coast of the United States, it was found on settling plates in Barnegat Bay in 1976 (Hoagland and Turner 1980) and appears to be established there, although at low densities (Shafto and Loveland 1984). In 1979, it was collected on the FL Atlantic Coast, in the Banana River, Indian River Lagoon (Fofonoff, unpublished data). Ficopomatus enigmaticus has also been collected in the East River, Brunswick GA (USGS Nonindigenous Species Program 2007), and Charleston Harbor (Ruiz et al. unpublished data) In the fall of 1994, F. enigmaticus was found on settling plates in Scott Creek and Norfolk Harbor, Norfolk VA. In 1995, it was also found in Baltimore and the Severn River (McCann et al. in prep.; Ruiz et al. unpublished data). History References - Carlton 1979; Fauvel 1923; Hartman 1952; Hoagland and Turner; 1980; McCann et al in prep.; Obenat and Pezzani 1991; Read and Gordon 1991; Ruiz et al. unpublished data; Shafto and Loveland 1984; ten Hove and Weerdenburg 1978; Zibrowius 1992

Invasion Comments

Ecology

Environmental Tolerances

For SurvivalFor Reproduction
Minimum Maximum Minimum Maximum
Temperature (ºC) 0.0 30.0 10.0 18.0
Salinity (‰) 1.0 55.0
Oxygen
pH 10.0000000000 8.0000000000
Salinity Range meso-poly

Age and Growth

Male Female
Minimum Adult Size (mm)
Typical Adult Size (mm) 44.0 44.0
Maximum Adult Size (mm) 20.0 20.0
Maximum Longevity (yrs) 8.0 8.0
Typical Longevity (yrs 6.0 6.0

Reproduction

Start Peak End
Reproductive Season
Typical Number of Young
Per Reproductive Event
Sexuality Mode(s)
Mode(s) of Asexual
Reproduction
Fertilization Type(s)
More than One Reproduction
Event per Year
Reproductive Startegy
Egg/Seed Form

Impacts

Economic Impacts in Chesapeake Bay

The tubeworm Ficopomatus enigmaticus is too rare and local in Chesapeake Bay to cause important economic impacts as a fouling organism at the present time (Ruiz et al. unpublished data).

References- Ruiz et al. unpublished data


Economic Impacts Outside of Chesapeake Bay

In a number of estuaries around the world, the tubeworm Ficopomatus enigmaticus is a major fouling organism, covering man-made surfaces with thick layers of calcareous tubes. It created fouling problems on boats, pilings and pontoons in New Zealand (Read and Gordon 1991), and frequently blocks lock gates and other structures used to control flow in estuaries (Nelson-Smith 1971; Zibrouwius 1994).

References- Nelson-Smith 1971; Read and Gordon 1991; Zibrouwius 1994


Ecological Impacts on Chesapeake Native Species

In Chesapeake Bay fouling communites examined so far, the tubeworm Ficopomatus enigmaticus does not appear to reach abundances sufficient to greatly affect populations of native species (Ruiz et al. unpublished data).

However, in many brackish and hypersaline areas around the world, this worm has formed large reef-like colonies, greatly affecting estuarine habitats. These calcareous masses can be 1-3 m across, reaching to within a few centimeters of the water's surface, reducing circulation, providing a substrate for algal growth, and affecting planktonic and benthic communities through filtering of suspended particles (Bianchi and Morri 1996; Cohen and Carlton 1995; Thomas and Thorp 1994).

References- Bianchi and Morri 1996; Cohen and Carlton 1995; ; Ruiz et al. unpublished data; Thomas and Thorp 1994


Ecological Impacts on Other Chesapeake Non-Native Species

In Chesapeake Bay fouling communites examined so far, Ficopomatus enigmaticus does not appear to reach abundances sufficient to greatly affect populations of exotic species (Ruiz et al. unpublished data).

However, in many brackish and hypersaline areas around the world, this worm has reached high abundances, forming large reef-like colonies, greatly affecting estuarine habitats, and potentially affecting introduced as well as native species. In European waters (Italy, England), such introduced species as Cordylophora caspia and Balanus improvisus used F. enigmaticus reefs as a substrate (Bianchi and Morri 1996; Cohen and Carlton 1995; Thomas and Thorp 1994).

References- Bianchi and Morri 1996; Cohen and Carlton 1995; Thomas and Thorp 1994; Ruiz et al. unpublished data


References

Bianchi, Carlo N.; Morri, Carla (1996) Ficopomatus 'reefs' in Po river delta (northern Adriatic): their constructional dynamics, biology, and influences on the brackish water biota., Pubblicazioni della Stazione Zoologica di Napoli I: Marine Ecology 17: 51-66

Carlton, James T. (1979) History, biogeography, and ecology of the introduced marine and estuarine invertebrates of the Pacific Coast of North America, , Davis. Pp. 1-904

Cohen, Andrew N.; Carlton, James T. (1995) Nonindigenous aquatic species in a United States estuary: a case study of the biological invasions of the San Francisco Bay and Delta, , Washington DC, Silver Spring MD.. Pp.

Davies, B. R.; Stuart, V.; Villiers, M. de (1989) The filtration activity of a serpuid polychaete population (Ficopomatus enigmaticus) and its effects on water quality in a coastal marina., Estuarine Coastal and Shelf Science 29: 613-620

Dixon, D.R. (1981) Reproductive biology of the serpulid Ficopomatus (Mercierella) enigmaticus in the Thames Estuary, S.E. England, Journal of the Marine Biological Association of the United Kingdom 61: 805-815

Fauvel, Pierre (1953) Annelides Polychetes de la Croisiere du 'President Theodore Tissier aux Antilles (1951)., Bulletin de lInstitut Oceanographique, Monaco 1033: 1-23

Hartman, O. (1951) The littoral marine annelids of the Gulf of Mexico, Publications of the Institute of Marine Science 2: 7-124

Hoagland, K. E.; Turner, R. D. (1980) Range extensions of teredinids (shipworms) and polychaetes in the vicinity of a temperate-zone nuclear generating station., Marine Biology 58: 55-64

Loveland, Robert E.; Shafto, Sylvia S. (1984) Fouling Organisms, In: Kennish, Michael J., and Lutz, Richard A.(Eds.) Ecology of Barnegat Bay, New Jersey.. , Berlin. Pp. 226-20

Nelson-Smith, Anthony (1971) Annelids as fouling organisms., In: Gareth Jones, E. B. and Eltringham, S. K.(Eds.) Marine Borers, Fungi, and Fouling Organisms of Wood.. , Paris. Pp. 171-184

Obenat, S. M.; Pezzani, S. E. (1994) Life cycle and population structure of the polychaete Ficopomatus enigmaticus in Mar Chiquita coastal lagoon, Argentina, Estuaries 17: 263-270

Read, Geoffrey B.; Gordon, Dennis P. (1991) Adventive occurrence of the fouling serpulid Ficopomatus enigmatus (Polychaeta) in New Zealand, New Zealand Journal of Marine and Freshwater Research 25: 269-274

Schwindt, Evangel; Bortolus, Alejandro; Iribarne, Oscar Osvaldo (2001) Invasion of a reef-builder polychaete: direct and indirect impacts on the native benthic community structure, Biological Invasions 3: 137-149

Ten Hove, H. A.; Weerdenburg, J. C. A. (1978) A generic revision of the brackish-water serpulid Ficopomatus Southern 1921 (Polychaeta : Serpulinae) including Mercierella Fauvel 1923, Sphaeropomatus Treadwell 1934, Mercierellopsis Rioja 1945 and Neopomatus Pillai 196, Biological Bulletin 154: 96-120

Thomas, Nigel S.; Thorp, Clifford H. (1994) Cyclical changes in the fauna associated with tube aggregates of Ficopomatus enigmaticus (Fauvel), Memoires du Museum Nationale d'Histoire Naturelle 162: 575-584

2002-2021 Invertebrate Zoology Collections Database.

2003-2024 Nonindigenous Aquatic Species Database. Gainesville, FL. http://nas.er.usgs.gov

Zibrowius, Helmut (1991) Ongoing modification of the Mediterranean marine fauna and flora by the establishment of exotic species., Mesogee 51: 83-107

Zibrowius, Helmut (1994) Introduced invertebrates: Examples of success and nuisance in the European Atlantic and the Mediterranean., , Brussels. Pp. 44-65


Direct questions and comments to chesnemo@si.edu.

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