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Species
Rapana venosa (Valenciennes, 1846)
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Rapana venosa is native to marine and estuarine waters of the western Pacific, from the Sea of Japan, Yellow Sea, East China Sea and Bohai Sea (Richerson 2006). It is now also established in many other parts of the world, where it is generally viewed as an invasive species with the potential to have a seriously negative impact.
According to Culha et al. (2009) and references therein: Rapana venosa became established in the Black Sea in the 1930s and 1940s and spread over the coasts of the Caucasus, the Crimea, and the Azov Sea over a period of 10 years. It expanded its distribution toward the Turkish and Bulgarian coasts of the Black Sea and the coasts of Romania during 1959-1972. It has also been reported from the southeastern coast of South America and from the Red Sea and many localities in the Adriatic Sea since the 1980s. It was presumably introduced into these areas accidentally by ships.
The first specimen in North America was collected by members of the Virginia Institute of Marine Science Trawl Survey Group in August 1998 in Hampton Roads, Virginia (Harding and Mann 1999). Harding and Mann (2005) documented three range extensions of Rapana venosa in Chesapeake Bay, Virginia. These extensions into Tangier Sound, the mid James River estuary, and to Cape Henry at the Bay mouth extended respectively, the northern, western, and southeastern boundaries of the known occupied range in Virginia waters. Salinity and tidal circulation mediate the distribution of adults and larvae of this animal. During dry years (e.g., 2001 and 2002) adult R. venosa may move up-estuary in western tributaries like the James River, given increased salinity and available habitat and food resources. Declines in salinities (or return to normal salinities) will either kill the whelks in the upriver habitats or force a return to downstream habitats (Harding and Mann 2005). The species is now widely distributed in Chesapeake Bay, which harbors what is still the only known breeding population in North America (Harding et al. 2008).
Gilberto et al. (2006) studied a recently established population of Rapana venosa in the Rio de la Plata estuary along the southeastern coast of South America (Uruguay/Argentina).
License | http://creativecommons.org/licenses/by-nc/3.0/ |
Rights holder/Author | Shapiro, Leo, Shapiro, Leo, EOL Rapid Response Team |
Source | http://eolspecies.lifedesks.org/pages/15884 |
Rapana venosa is a large predatory marine snail that is native to marine and estuarine waters of the western Pacific, from the Sea of Japan, Yellow Sea, East China Sea and Bohai Sea (Richerson 2006). It is now also established in many other parts of the world, where it is generally viewed as an invasive species with the potential to have a seriously negative impact.
In the Black Sea, Rapana venosa occurs down to 30 m in depth in areas with sandy bottoms, as well as in rocky and muddy habitats (Culha et al. 2009). Harding and Mann (1999) report that in the lower Chesapeake Bay (USA), Rapana venosa inhabits subtidal hard bottom habitats, where it can feed, mate, and move while completely burrowed. Rapana venosa is ecologically flexible, able to tolerate low salinity, low oxygen, and significantly polluted water (Gilberto et al. 2006; Culha et al. 2009). It feeds at night and is often found in locations that are hard to sample, making early detection of newly established populations difficult (Harding et al. 2007).
Working with animals from the Chesapeake Bay region (Virginia, USA), Harding et al. (2007) found significant differences in predation strategies and prey species consumed between the introduced veined Rapana venosa and the smaller, native Atlantic oyster drills (Urosalpinx cinerea). As Rapana venosa becomes more prevalent, these differences could result in considerable disruption of the trophic structure (feeding relationships among species) of Chesapeake Bay.
License | http://creativecommons.org/licenses/by-nc/3.0/ |
Rights holder/Author | Shapiro, Leo, Shapiro, Leo, EOL Rapid Response Team |
Source | http://eolspecies.lifedesks.org/pages/15884 |
Rapana venosa is a large predatory marine snail that has recently become established in a number of areas outside its native range, raising concerns about potentially serious ecological and economic impacts as it expands into new regions.
License | http://creativecommons.org/licenses/by-nc/3.0/ |
Rights holder/Author | Shapiro, Leo, Shapiro, Leo, EOL Rapid Response Team |
Source | http://eolspecies.lifedesks.org/pages/15884 |
Depth range based on 2 specimens in 1 taxon.
Environmental ranges
Depth range (m): 19 - 20
Graphical representation
Depth range (m): 19 - 20
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
License | http://creativecommons.org/publicdomain/mark/1.0/ |
Rights holder/Author | Ocean Biogeographic Information System |
Source | http://www.iobis.org/mapper/?taxon_id=502756 |
In the Black Sea, Rapana venosa occurs down to 30 m in depth in areas with sandy bottoms, as well as in rocky and muddy habitats (Culha et al. 2009).
Harding and Mann (1999) report that in the lower Chesapeake Bay (USA), Rapana venosa inhabits subtidal hard bottom habitats, where it can feed, mate, and move while completely burrowed.
License | http://creativecommons.org/licenses/by-nc/3.0/ |
Rights holder/Author | Shapiro, Leo, Shapiro, Leo, EOL Rapid Response Team |
Source | http://eolspecies.lifedesks.org/pages/15884 |
Both shipping activities and natural dispersion from the nearest population in France (Quiberon, Brittany) are possible modes of introduction of R. venosa to the Dutch part of the North Sea and the Southern North Sea.
License | http://creativecommons.org/licenses/by/4.0/ |
Rights holder/Author | This work is licensed under a Creative Commons Attribution-Share Alike 4.0 License |
Source | http://www.marinespecies.org/aphia.php?p=taxdetails&id=140416 |
Harding et al. (2009) reported significant mortality of Rapana venosa during a bloom of the dinoflagellate Alexandrium monilatum in the lower York River, Virginia (USA) in September 2007. The whelks stopped feeding as dissolved oxygen and chlorophyll concentrations increased with the development of the bloom. Harding et al. noted that whelk mortality was preceded by external signs of stress including reduced ventilation, inability to attach to hard substrates, periodic pumping of the opercular plate, and increased mucus production over a period of 24-48 hours prior to death. High concentrations of goniodimum A (a toxin produced by A. monilatum) were observed in bivalves attached to the shells of R. venosa. Mortality of R. venosa was 100%. Mortality of oysters (Crassostrea virginica) and northern quahog clams (Mercenaria mercenaria) in the same flow-through system was 0%. The symptoms displayed by the R. venosas in the 24-48 hours prior to death were indicative of paralysis and followed a timecourse similar to that documented for some other molluscs exposed to toxic A. monilatum.
Savini et al. (2002) suggested that the introduction of Rapana venosa to Chesapeake Bay (U.S.A.) offers cause for both ecological and economic concern. Adult Rapana venosa are large predatory gastropods that consume bivalves including commercially valuable species such as hard clams (Mercenaria mercenaria). Laboratory feeding experiments were used to estimate daily consumption rates of two sizes of whelks feeding on two size classes of hard clams. Large R. venosa (shell length, SL > 101 mm) are capable of consuming up to 2.7 g wet weight of clam tissue daily, equivalent to 0.8% of their body weight. Small whelks (60-100 mm SL) ingest an average of 3.6% of their body weight per day.
Very large striped hermit crabs (Clibinarius vittatus) have begun to use shells of the exotic Rapana venosa as shelters (Harding and Mann 1999).
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Rights holder/Author | Shapiro, Leo, Shapiro, Leo, EOL Rapid Response Team |
Source | http://eolspecies.lifedesks.org/pages/15884 |
Rapana venosa is ecologically flexible, able to tolerate low salinity, low oxygen, and significantly polluted water (Gilberto et al. 2006; Culha et al. 2009). It feeds at night and is often found in locations that are difficult to sample, making early detection of newly established populations difficult (Harding et al. 2007).
Harding et al. (2007) studied predation signatures of Rapana venosa, such as distinctive bore holes in prey shell remains (only R. venosa individuals too small to grasp and manipulate prey leave visible predation signatures). These signs could provide a powerful surveillance tool, allowing early detection of smaller, pre-reproductive animals than is possible by simply waiting for their appearance as fishing bycatch (R. venosa are likely to be caught by fishermen only once a population is well established and significant numbers of larger animals are present).
License | http://creativecommons.org/licenses/by-nc/3.0/ |
Rights holder/Author | Shapiro, Leo, Shapiro, Leo, EOL Rapid Response Team |
Source | http://eolspecies.lifedesks.org/pages/15884 |
Culha et al. 2009: Moves between warmer deep waters in winter and coastal regions in summer.
License | http://creativecommons.org/licenses/by-nc/3.0/ |
Rights holder/Author | Shapiro, Leo, Shapiro, Leo, EOL Rapid Response Team |
Source | http://eolspecies.lifedesks.org/pages/15884 |
12-18 years (Harding et al. 2007)
10-15 years (Harding et al. 2008)
License | http://creativecommons.org/licenses/by-nc/3.0/ |
Rights holder/Author | Shapiro, Leo, Shapiro, Leo, EOL Rapid Response Team |
Source | http://eolspecies.lifedesks.org/pages/15884 |