Invasion History
First Non-native North American Tidal Record: 1877First Non-native West Coast Tidal Record: 1915
First Non-native East/Gulf Coast Tidal Record: 1877
General Invasion History:
The precise origin of Styela plicata is unknown. The type specimen was described from a ship in the Delaware River, Philadelphia, Pennsylvania in 1823 (Van Name 1912). It was apparently well established south of Cape Hatteras by the late 19th and early 20th centuries before regular collecting began. It is believed to have been introduced to the Mediterranean, probably centuries ago (Monniot, in Food and Agricultural Organization 2000). James T. Carlton considers the species introduced to the Northwest Atlantic, based on the general diversity of this genus in the Pacific (Carlton and Rucklelshaus 1997; Carlton, pers. comm.). Genetic analysis by de Barros et al. (2009) suggested the Northwest Pacific as the probable native region. However, another study (Pineda et al. 2011) found the highest genetic diversity in the Western Atlantic, although the authors could not definitely identify a native region. The cladistic history of the genus Styela does support a Northwest Pacific ancestry of S. plicata, since it is distinct both from an Eastern Atlantic clade of warm-shallow water Styela, and cold deep-water forms (e.g. S. rustica (Carlton et al., in prep.)). Pineda et al's (2011) genetic analysis is consistent with historical data that suggests that transport of S. plicata began very early, and was very frequent, blurring genetic distinctions among native and introduced populations.
North American Invasion History:
Invasion History on the West Coast:
In the Northeast Pacific, Styela plicata was first collected in San Diego Bay in 1915 and ranges north to Santa Barbara, California (Lambert and Lambert 1998; Nichols et al. 2023). To the south, it has been reported from Baja California, Mexico, being collected in Ensenada in 2000 (Lambert and Lambert 2003) and Bahia San Quintin in 2005 (Rodriguez and Ibarra-Obando 2008).
Invasion History on the East Coast:
The type specimen for Styela plicata was described from a ship in the Delaware River, Philadelphia, Pennsylvania in 1823 (Van Name 1912; 1945). However, because this specimen was reported from a vessel hull and not as present in the surrounding environment, we do not consider this record to be its date of introduction. It was also collected in 1880 on Blackfish Bank, off Charleston, South Carolina (USNM 6960, U.S. National Museum of Natural History 2007). The long-established range of S. plicata along the Western Atlantic is from Cape Lookout, North Carolina (USNM 14790, U.S. National Museum of Natural History 2007) to Padre Island, Texas (USNM 14424, U.S. National Museum of Natural History 2007), and south through the Caribbean to Venezuela (Van Name 1945; USNM 14481, U.S. National Museum of Natural History 2007). Recently, however, S. plicata has been collected north of Cape Hatteras, in Lynnhaven Bay, Virginia Beach, at the mouth of Chesapeake Bay (Ruiz et al., unpublished data), in Chincoteague Bay, Virginia (in 1999, O'Beirn et al. 2004, on oyster-culture floats), and in the Mystic River, Long Island Sound (one specimen in 2001, but not yet established in Long Island Sound as of 2011; J.T. Carlton personal communication). Howver, by 2023, thousands of individuals ranging from juveniles to adults were found attached to many different substrates in the Mystic River Estuary in Mystic, Connecticut. The population is being monitored to determine if it has survived the winter of 2022-2023. (James T. Carlton, perosnal communication 2023)..
Invasion History on the Gulf Coast:
A specimen of Styela plicata was collected from Padre Island, Texas (USNM 14424, U.S. National Museum of Natural History 2007) and Cedar Key, Florida in 1877 (USNM 940, U.S. National Museum of Natural History 2007). This tunicate is established and abundant on the Gulf Coast from Florida through Texas (Van Name 1921; Van Name 1945; Ruiz et al., unpublished data).
Invasion History Elsewhere in the World:
The long-established range of Styela plicata along the Western Atlantic is from Cape Lookout, North Carolina (USNM 14790, U.S. National Museum of Natural History 2007) to Padre Island, Texas (USNM 14424, U.S. National Museum of Natural History 2007), and south through the Caribbean to Venezuela (Van Name 1945; USNM 14481, U.S. National Museum of Natural History 2007). In 1884, S. plicata was reported from St. Thomas, US Virgin Islands/Caribbean Sea (USNM 6916, U.S. National Museum of Natural History 2007), and from Bermuda in 1882 (USNM 2769, U.S. National Museum of Natural History 2007) suggesting that it was established and widespread in warm waters of the Western Atlantic by the late 19th century.
Styela plicata was collected from Panama in 1973 (USNM 19744, US National Museum of Natural History 2007). Nearly a century before, in 1883, it was collected from Rio de Janeiro state, Brazil (Trautstedt 1883, cited by da Rocha and Kremer 2005), It ranges south to Uruguay (Orensanz et al. 2002), but in Bahia, northern Brazil, it was known only from 'one individual' (da Rocha and Kremer 2005).
Styela plicata is considered introduced to the Mediterranean: ['This species is not native to the Mediterranean, but was introduced centuries ago. It is present in all warm-temperate and tropical regions, especially in zones of human activity.'] (C. F. Monniot, in Food and Agricultural Organization 2000). It was collected from Naples (Traustedt 1877, cited by Kott 1985) and Trieste, Italy (Heller 1877, cited by Kott 1998). Outside the Mediterranean, it has been collected from Dakar, Senegal (Monniot 1969).
In the Northwest Pacific, S. plicata ranges from Hong Kong (Huang 2001) to Mutsu Bay, at the north end of Honshu, Japan (Oka 1935, cited by Nishikawa 1991). Within the Indian Ocean, it has been collected from Vizhinjam, India, on the Arabian Sea (Abdul and Sivakumar 2007), Somalia (in 1964, USNM 18297, U.S. National Museum of Natural History 2007), and the Gulf of Suez (in 1927, Monniot 2002). These scattered records could represent introductions.
In the Southwest Pacific, S. plicata was first collected at Port Jackson, near Sydney, Australia (Heller 1878, cited by Kott 1985). Its range runs from the mouth of the Calliope River, Queensland to Port Phillip Bay (in 1963, Millar 1966, cited by Keough and Ross 1999), and west to Cockburn Sound and the Perth area (Hartmeyer and Michaelsen 1928, cited by Kott 1985). Within this range, it is strongly associated with harbors and artificial structures (Kott 1985; Keough and Ross 1999). A genetic survey indicates high diversity in Australian populations, with significant genetic structure in more southern latitudes, but no structure in tropical latitudes (David et al. 2010). In New Zealand, it has been reported at several locations on the North Island, including Auckland Harbour and Hauraki Gulf (in 1957, Cranfield et al. 1998), Gulf Harbour Marina (Inglis et al. 2005), and Taranaki (Inglis et al. 2006).
Description
Styela plicata is a solitary tunicate, variable in shape, but roughly oval. It is fixed to the substrate by the posterior end of its body, usually without roots or stalks. Its tunic is firm and thick, slightly translucent, with deep, irregular, longitudinal furrows, and horizontal creases that form large, irregularly rounded lumps. Its total body length can reach 90 mm. The oral siphon is terminal, and the atrial siphon is a little behind it – both siphons are short, with square apertures with rounded humps on each side. The color of the tunic is whitish with brown or black stripes radiating from the siphons (Van Name 1945; Kott 1985; Nishikawa 1991; Gretchen Lambert, personal communication 2012).
Taxonomy
Taxonomic Tree
Kingdom: | Animalia | |
Phylum: | Chordata | |
Subphylum: | Tunicata | |
Class: | Ascidiacea | |
Order: | Stolidobranchia | |
Family: | Styelidae | |
Genus: | Styela | |
Species: | plicata |
Synonyms
Styela gyrosa (Heller, 1883)
Styela pinguis (Herdman, 1899)
Tethyum plicatum (Hartmeyer, 1909)
Ascidia cuvieri (Delle Chiaje, 1841)
Ascidia patata (Costa, 1844)
Ascidia phusca (Delle Chiaje, 1828)
Phallusia sulcata (Delle Chiaje, 1841)
Potentially Misidentified Species
New species intorduced to Caribbean Panama and Venezuela, of unkknown origin (de Barros and da Rocha 2021).
Styela panamensis
New species, native to Caribbean Panama. Records of S. plicata from Bocas del Toro, Panama, may refer to S. panamensis.
Ecology
General:
Life History- A solitary tunicate is ovoid, elongate or vase-like in shape, with two openings or siphons. Most solitary tunicates attach to substrates by their side or base, but some attach with a conspicuous stalk. They are sessile filter feeders with two siphons, an oral and an atrial siphon. Water is pumped in through the oral siphon, where phytoplankton and detritus is filtered by the gills, and passed on mucus strings to the stomach and intestines. Waste is then expelled in the outgoing atrial water.
Solitary ascidians are hermaphroditic, meaning that both eggs and sperm are released to the atrial chamber. Eggs may be self-fertilized or fertilized by sperm from nearby animals, but many species have a partial block to self-fertilization. Depending on the species, eggs may be externally or internally fertilized. In external fertilizers, eggs and sperm are released through the atrial siphon into the surrounding water column were fertilization takes place. In internal fertilizers, eggs are brooded and fertilized within the atrial chamber and then released into the water column upon hatching. Fertilized eggs hatch into a tadpole larva with a muscular tail, notochord, eyespots, and a set of adhesive papillae. The lecithotrophic (non-feeding, yolk-dependent) larva swims briefly before settlement. Swimming periods are usually less than a day and some larvae settle immediately after release, but the larval period can be longer at lower temperatures. Once settled, the tail is absorbed, the gill basket expands, and the tunicate begins to feed by filtering (Barnes 1983).
Food:
Phytoplankton
Trophic Status:
Suspension Feeder
SusFedHabitats
General Habitat | Marinas & Docks | None |
General Habitat | Oyster Reef | None |
General Habitat | Vessel Hull | None |
General Habitat | Canals | None |
General Habitat | Mangroves | None |
General Habitat | Rocky | None |
General Habitat | Salt-brackish marsh | None |
Salinity Range | Polyhaline | 18-30 PSU |
Salinity Range | Euhaline | 30-40 PSU |
Tidal Range | Subtidal | None |
Vertical Habitat | Epibenthic | None |
Life History
Tolerances and Life History Parameters
Maximum Temperature (ºC) | 30.2 | Field, US East & West Coast marinas (Lord et al. 2015) |
Minimum Salinity (‰) | 17.5 | Experimental- This was tested experimentally with animals at Santa Barbara CA. Only '75% seawater' (26 ppt), '50% seawater' (18ppt), and '110% seawater' (38.5 ppt) were used (Sims 1984). |
Maximum Salinity (‰) | 40 | Field salinity (Shark Bay, Western Australia) (Wyatt et al. 2005) |
Minimum Reproductive Temperature | 18 | Experimental- Lowest temperature tested for embryonic development and metamorphosis (Thiyagarajan and Qian 2003). |
Maximum Reproductive Temperature | 30 | Experimental- Highest temperature tested for embryonic development and metamorphosis. Only 30% of larvae successfully completed development (Thiyagarajan and Qian 2003). |
Minimum Reproductive Salinity | 30 | Experimental- Development was observed at 22, 26, 30, and 34 ppt. Embryonic development was unsuccessful at 22 and 26 ppt (Thiyagarajan and Qian 2003). |
Maximum Reproductive Salinity | 34 | Experimental- Highest salinity tested (Thiyagarajan and Qian 2003). |
Minimum Duration | 0 | Larvae can attach immediately after hatching (Thiyagarajan and Qian 2003). |
Maximum Duration | 2 | Larvae prevented from settling (Thiyagarajan and Qian 2003). |
Maximum Length (mm) | 90 | Van Name 1945 |
Broad Temperature Range | None | Warm temperate-Tropical |
Broad Salinity Range | None | Polyhaline-Euhaline |
General Impacts
Economic Impacts
Fisheries: Styela plicata is known to foul cultured bivalves, interfering with their growth in Brazil, Hong Kong, Japan, and Spain (da Rocha et al. 2009).
Ecological Impacts
Competition: Styela plicata has been a dominant fouling organism in southern California harbors since 1960 (Lambert and Lambert 1998). It dominates fouling communities from Ensenada, Mexico to Santa Barbara (Lambert and Lambert 2003). It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes from southern California harbors (Lambert and Lambert 1998). Styela plicata was one of the dominant fouling organisms on fouling plates at Beaufort, North Carolina. It invaded plates initially dominated by other species and created 'monopolies,' for up to four months (Sutherland and Karlson 1977). Settled juveniles of Styela plicata inhibited settlement of the native Microcosmus squamiger (from Brisbane, Australia), in a laboratory experiment (Ruis et al. 2009). The mechanism was not clear, but could involve competition for food or allelopathy (inhibitory chemicals).
Fisheries: Styela plicata is known to foul cultured bivalves, interfering with their growth in Brazil, Hong Kong, Japan, and Spain (da Rocha et al. 2009). On the positive side, S. plicata is extensively cultured on long lines in Korea and Japan (Lambert et al. 2016).
Regional Impacts
NEP-VI | Pt. Conception to Southern Baja California | Ecological Impact | Competition | ||
Styela plicata has been the dominant marina fouling organism in southern California harbors since 1960 (Lambert and Lambert 1998). It dominates fouling communities from Ensenada, Mexico to Santa Barbara (Lambert and Lambert 2003). It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
P020 | San Diego Bay | Ecological Impact | Competition | ||
Styela plicata has been the dominant marina fouling organism in southern California harbors since 1960 (Lambert and Lambert 1998). It produced large monospecific patches in several locations during serveral years in San Diego Bay (Lambert and Lambert 2003). It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
P030 | Mission Bay | Ecological Impact | Competition | ||
Styela plicata has been the dominant marina fouling organism in southern California harbors since 1960 (Lambert and Lambert 1998). It produced large monospecific patches in several locations during serval years in San Diego Bay (Lambert and Lambert 2003). It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
P023 | _CDA_P023 (San Louis Rey-Escondido) | Ecological Impact | Competition | ||
Styela plicata has been the dominant marina fouling organism in southern California harbors since 1960 (Lambert and Lambert 1998). It produced large monospecific patches in Oceanside Harbor (Lambert and Lambert 2003). It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
P027 | _CDA_P027 (Aliso-San Onofre) | Ecological Impact | Competition | ||
It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
P040 | Newport Bay | Ecological Impact | Competition | ||
It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
P050 | San Pedro Bay | Ecological Impact | Competition | ||
It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
P060 | Santa Monica Bay | Ecological Impact | Competition | ||
It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
P062 | _CDA_P062 (Calleguas) | Ecological Impact | Competition | ||
It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
P064 | _CDA_P064 (Ventura) | Ecological Impact | Competition | ||
It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
P065 | _CDA_P065 (Santa Barbara Channel) | Ecological Impact | Competition | ||
It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
CAR-VII | Cape Hatteras to Mid-East Florida | Ecological Impact | Competition | ||
Styela plicata was one of the dominant fouling organisms on fouling plates at Beaufort, North Carolina. It invaded plates initially dominated by other species and created 'monopolies'; for up to four months (Sutherland and Karlson 1977). | |||||
S030 | Bogue Sound | Ecological Impact | Competition | ||
Styela plicata was one of the dominant fouling organisms on fouling plates at Beaufort, North Carolina. It invaded plates intially dominated by other species and created 'monopolies; which lasted for up to four months (Sutherland and Karlson 1977). | |||||
MED-II | None | Ecological Impact | Competition | ||
Fouling cultured bivalves in the Ebro Delta, Spain (Perera et al. 1990, cited by da Rocha et al. 2009). | |||||
MED-II | None | Economic Impact | Fisheries | ||
Fouling cultured bivalves in the Ebro Delta, Spain (Perera et al. 1990, cited by da Rocha et al. 2009). | |||||
NWP-2 | None | Ecological Impact | Competition | ||
Fouls cultured bivalves in Hong Kong (Huang 2003, cited by da Rocha et al. 2009). | |||||
NWP-2 | None | Economic Impact | Fisheries | ||
Fouls cultured bivalves in Hong Kong (Huang 2003, cited by da Rocha et al. 2009). | |||||
SA-II | None | Ecological Impact | Competition | ||
Fouls cultured oysters (Crassostrea gigas) and mussels (Perna perna) in farms in Santa Catarina, Brazil (da Rocha et al. 2009). | |||||
SA-II | None | Economic Impact | Fisheries | ||
Fouls cultured oysters (Crassostrea gigas) and mussels (Perna perna) in farms in Santa Catarina, Brazil (da Rocha et al. 2009). | |||||
NWP-3b | None | Ecological Impact | Competition | ||
Fouls cultured oysters (Crassostrea gigas) in Hiroshima Bay (Arakawa 1990, cited by da Rocha et al. 2009). | |||||
NWP-3b | None | Economic Impact | Fisheries | ||
Fouls cultured oysters (Crassostrea gigas) in Hiroshima Bay (Arakawa 1990, cited by da Rocha et al. 2009). | |||||
AUS-XII | None | Ecological Impact | Competition | ||
Settled juveniles of Styela plicata inhibited settlement of the native Microcosmus squamiger (from Brisbane, Australia), in a laboratory experiment. The mechanism was not clear, but could involve competition for food or allelopathy (inhibitory chemicals; Rius et al. 2009). | |||||
CA | California | Ecological Impact | Competition | ||
Styela plicata has been the dominant marina fouling organism in southern California harbors since 1960 (Lambert and Lambert 1998). It produced large monospecific patches in several locations during serveral years in San Diego Bay (Lambert and Lambert 2003). It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998)., It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998)., Styela plicata has been the dominant marina fouling organism in southern California harbors since 1960 (Lambert and Lambert 1998). It produced large monospecific patches in several locations during serval years in San Diego Bay (Lambert and Lambert 2003). It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998)., Styela plicata has been the dominant marina fouling organism in southern California harbors since 1960 (Lambert and Lambert 1998). It produced large monospecific patches in Oceanside Harbor (Lambert and Lambert 2003). It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998)., It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998)., It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998)., It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998)., It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998)., It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998)., It and other introduced ascidians have replaced the native species Pyura haustor and Ascidia ceratodes in southern California harbors (Lambert and Lambert 1998). | |||||
NC | North Carolina | Ecological Impact | Competition | ||
Styela plicata was one of the dominant fouling organisms on fouling plates at Beaufort, North Carolina. It invaded plates intially dominated by other species and created 'monopolies; which lasted for up to four months (Sutherland and Karlson 1977). |
Regional Distribution Map
Bioregion | Region Name | Year | Invasion Status | Population Status |
---|---|---|---|---|
NWP-3a | None | 1965 | Crypogenic | Established |
NWP-2 | None | 0 | Crypogenic | Established |
AUS-III | None | 2002 | Non-native | Established |
AUS-IV | None | 1928 | Non-native | Established |
AUS-VI | None | 1972 | Non-native | Established |
AUS-VII | None | 1952 | Non-native | Established |
AUS-VIII | None | 1963 | Non-native | Established |
AUS-X | None | 1878 | Non-native | Established |
AUS-XII | None | 1972 | Non-native | Established |
NA-ET4 | Bermuda | 1882 | Non-native | Established |
NWP-3b | None | 1894 | Crypogenic | Established |
CAR-VII | Cape Hatteras to Mid-East Florida | 1880 | Non-native | Established |
CAR-I | Northern Yucatan, Gulf of Mexico, Florida Straits, to Middle Eastern Florida | 1877 | Non-native | Established |
NEP-VI | Pt. Conception to Southern Baja California | 1915 | Non-native | Established |
NEP-V | Northern California to Mid Channel Islands | 2003 | Non-native | Unknown |
CAR-V | None | 1955 | Non-native | Established |
CAR-II | None | 1981 | Non-native | Established |
CAR-IV | None | 1884 | Non-native | Established |
SA-II | None | 1883 | Non-native | Established |
NZ-IV | None | 1948 | Non-native | Established |
WA-I | None | 1969 | Non-native | Established |
MED-I | None | 0 | Non-native | Established |
MED-II | None | 0 | Non-native | Established |
MED-III | None | 1877 | Non-native | Established |
MED-IV | None | 0 | Non-native | Established |
MED-VI | None | 0 | Non-native | Established |
MED-V | None | 0 | Non-native | Established |
MED-VII | None | 1877 | Non-native | Established |
SEP-H | None | 1973 | Non-native | Unknown |
CAR-III | None | 1971 | Non-native | Unknown |
NA-ET3 | Cape Cod to Cape Hatteras | 2002 | Non-native | Established |
AUS-V | None | 0 | Non-native | Established |
RS-3 | None | 0 | Crypogenic | Established |
P020 | San Diego Bay | 1915 | Non-native | Established |
P050 | San Pedro Bay | 1960 | Non-native | Established |
S180 | St. Johns River | 1940 | Non-native | Established |
G130 | Pensacola Bay | 1957 | Non-native | Established |
G070 | Tampa Bay | 1947 | Non-native | Established |
S190 | Indian River | 1977 | Non-native | Established |
M130 | Chesapeake Bay | 2002 | Non-native | Established |
G310 | Corpus Christi Bay | 1938 | Non-native | Established |
SA-III | None | 2002 | Non-native | Established |
CIO-I | None | 0 | Crypogenic | Established |
P030 | Mission Bay | 1966 | Non-native | Established |
P023 | _CDA_P023 (San Louis Rey-Escondido) | 1995 | Non-native | Established |
P027 | _CDA_P027 (Aliso-San Onofre) | 1994 | Non-native | Established |
P040 | Newport Bay | 1966 | Non-native | Established |
P060 | Santa Monica Bay | 1970 | Non-native | Established |
P062 | _CDA_P062 (Calleguas) | 1994 | Non-native | Established |
P064 | _CDA_P064 (Ventura) | 1994 | Non-native | Established |
P065 | _CDA_P065 (Santa Barbara Channel) | 1970 | Non-native | Established |
P080 | Monterey Bay | 2003 | Non-native | Unknown |
M090 | Delaware Bay | 1823 | Non-native | Failed |
M040 | Long Island Sound | 2001 | Non-native | Established |
S050 | Cape Fear River | 1885 | Non-native | Established |
S030 | Bogue Sound | 1895 | Non-native | Established |
S020 | Pamlico Sound | 1961 | Non-native | Established |
M120 | Chincoteague Bay | 1999 | Non-native | Established |
S080 | Charleston Harbor | 1880 | Non-native | Established |
S056 | _CDA_S056 (Northeast Cape Fear) | 1919 | Non-native | Established |
S100 | St. Helena Sound | 1960 | Non-native | Established |
S140 | St. Catherines/Sapelo Sounds | 1971 | Non-native | Established |
G030 | North Ten Thousand Islands | 1884 | Non-native | Established |
G080 | Suwannee River | 1877 | Non-native | Established |
G086 | _CDA_G086 (Econfina-Steinhatchee) | 1901 | Non-native | Established |
G050 | Charlotte Harbor | 1901 | Non-native | Established |
G074 | _CDA_G074 (Crystal-Pithlachascotee) | 1887 | Non-native | Established |
G060 | Sarasota Bay | 1910 | Non-native | Established |
S200 | Biscayne Bay | 1946 | Non-native | Established |
G120 | Choctawhatchee Bay | 1947 | Non-native | Established |
G100 | Apalachicola Bay | 1929 | Non-native | Established |
G078 | _CDA_G078 (Waccasassa) | 1983 | Non-native | Established |
G020 | South Ten Thousand Islands | 1982 | Non-native | Established |
G110 | St. Andrew Bay | 1993 | Non-native | Established |
G210 | Terrebonne/Timbalier Bays | 1938 | Non-native | Established |
G240 | Calcasieu Lake | 1993 | Non-native | Established |
G220 | Atchafalaya/Vermilion Bays | 1978 | Non-native | Established |
G330 | Lower Laguna Madre | 1962 | Non-native | Established |
G270 | Brazos River | 1956 | Non-native | Established |
NWP-4a | None | 1935 | Crypogenic | Established |
EA-II | None | 0 | Crypogenic | Established |
AUS-II | None | 1985 | Non-native | Established |
EA-III | None | 0 | Crypogenic | Established |
WA-V | None | 1951 | Non-native | Established |
S045 | _CDA_S045 (New) | 2009 | Non-native | Established |
NEA-V | None | 1989 | Non-native | Established |
WA-IV | None | 2009 | Non-native | Established |
NEA-VI | None | 2010 | Non-native | Established |
PAN_PAC | Panama Pacific Coast | 1973 | Non-native | Unknown |
PAN_CAR | Panama Caribbean Coast | 1971 | Non-native | Established |
S040 | New River | 2014 | Non-native | Established |
NA-ET2 | Bay of Fundy to Cape Cod | 2022 | Non-native | Unknown |
N100 | Casco Bay | 2021 | Non-native | Unknown |
Occurrence Map
OCC_ID | Author | Year | Date | Locality | Status | Latitude | Longitude |
---|---|---|---|---|---|---|---|
4604 | USNM 19744 | 1973 | 1973-04-15 | Whorehouse Reef | Non-native | 8.8333 | -79.2500 |
4605 | Lambert and Lambert 2003 | 2000 | 2000-08-01 | Ensenada | Non-native | 31.8667 | -116.6167 |
4607 | Abbott and Johnson 1972 | 1960 | 1960-01-01 | Long Beach | Non-native | 33.7497 | -118.1172 |
4608 | Carlton 1979 | 1970 | 1970-01-01 | Santa Barbara | Non-native | 34.4072 | -119.6887 |
4611 | Ruiz et al. unpublished data | 2003 | 2002-08-01 | Lynnhaven, Virginia Beach | Non-native | 36.8888 | -76.0760 |
4612 | U.S. National Museum of Natural History 2007 | 1885 | 1885-10-20 | Cape Fear, SE Of | Non-native | 33.6333 | -77.6000 |
4613 | U.S. National Museum of Natural History 2007 | 1895 | 1895-07-01 | Beaufort | Non-native | 34.7182 | -76.6638 |
4614 | O'Beirn et al. 2004 | 1999 | 1999-06-15 | Chincoteague Island | Non-native | 37.9132 | -75.3888 |
4615 | U.S. National Museum of Natural History 2007 | 1880 | 1880-03-01 | Blackfish Bank, off Charleston | Non-native | 32.7766 | -79.9309 |
4616 | U.S. National Museum of Natural History 2007 | 1980 | 1980-01-29 | off Georgia | Non-native | 31.3983 | -80.8850 |
4617 | U.S. National Museum of Natural History 2007 | 1884 | 1884-05-01 | Marco Island | Non-native | 25.9412 | -81.7184 |
4618 | U.S. National Museum of Natural History 2007 | 1877 | 1877-02-01 | Cedar Key | Non-native | 29.1580 | -83.0465 |
4619 | U.S. National Museum of Natural History 200 | 1902 | 1902-02-13 | Key West | Non-native | 24.5546 | -81.7915 |
4620 | U.S. National Museum of Natural History 2007 | 1940 | 1940-04-17 | Jacksonville, East Of | Non-native | 30.4500 | -81.3000 |
4621 | Weiss 1948 | 1946 | 1946-05-01 | Tahiti Beach, Coral Gables | Non-native | 25.6982 | -80.2467 |
4622 | U.S. National Museum of Natural History 2007 | 1910 | 1910-01-01 | Sarasota Bay | Non-native | 27.3506 | -82.5720 |
4623 | U.S. National Museum of Natural History 2007 | 1901 | 1901-01-01 | Charlotte Harbor | Non-native | 26.7756 | -82.1422 |
4624 | U.S. National Museum of Natural History 2007 | 1947 | 1947-06-03 | Fort Walton Beach | Non-native | 30.4058 | -86.6188 |
4625 | U.S. National Museum of Natural History 2007 | 1929 | 2029-10-11 | Port St. Joe | Non-native | 29.8119 | -85.3030 |
4626 | Rosana da Rocha, personal communication, 2005 | 2005 | 2005-08-25 | Cape Canaveral Coast Guard Station | Non-native | 28.4058 | -80.6048 |
4627 | Mook 1983 | 1977 | 1977-01-01 | St. Lucie Inlet | Non-native | 27.1662 | -80.1567 |
4628 | U.S. National Museum of Natural History 2007 | 1880 | 1880-01-01 | Hamilton | Non-native | 32.2881 | -64.7911 |
4629 | U.S. National Museum of Natural History 2007 | 1938 | 1938-03-18 | Racoon Point, South Of | Non-native | 28.6083 | -90.9167 |
4630 | U.S. National Museum of Natural History 2007 | 1993 | 1993-10-30 | Near Cameron | Non-native | 29.1894 | -93.7000 |
4631 | U.S. National Museum of Natural History 2007 | 1978 | 1978-09-05 | Eugene Island Lease Area, | Non-native | 28.1672 | -91.4942 |
4632 | U.S. National Museum of Natural History 2007 | 1993 | 1993-01-01 | South Of Caillou Bay | Non-native | 28.2403 | -91.7000 |
4633 | U.S. National Museum of Natural History 2007 | 1938 | 1938-04-20 | Corpus Christi | Non-native | 27.7667 | -96.8583 |
4634 | U.S. National Museum of Natural History 2007 | 1962 | 1962-09-26 | Padre Island, East Of | Non-native | 26.4000 | -96.6417 |
4635 | U.S. National Museum of Natural History 2007 | 1956 | 1956-05-06 | Freeport, South Of | Non-native | 27.7000 | -95.1000 |
4636 | U.S. National Museum of Natural History 2007 | 1993 | 1993-10-26 | Texas, Gulf of Mexico | Non-native | 28.0000 | -94.0919 |
4637 | U.S. National Museum of Natural History 2007 | 1884 | 1884-01-01 | St. Thomas | Non-native | 18.3533 | -64.9365 |
4638 | U.S. National Museum of Natural History 2007 | 1925 | 1925-10-29 | Sao Francisco Island | Non-native | -26.5000 | -48.5000 |
4639 | U.S. National Museum of Natural History 2007 | 1935 | 1935-05-01 | Port Inhauma | Non-native | -22.7431 | -43.1328 |
4640 | da Rocha and Kremer 2005 | 2004 | 2004-03-11 | Ilha do Mel | Non-native | -25.5500 | -48.3000 |
4642 | da Rocha and Kremer 2005 | 1883 | 1883-01-01 | Rio de Janeiro | Non-native | -22.9000 | -43.2333 |
4643 | Orensanz et al. 2002 | 2002 | 2002-01-01 | La Paloma | Non-native | -34.6500 | -54.1500 |
4644 | Oka 1935, cited by Nishikawa 1991 | 1935 | 1935-01-01 | Mutsu Bay, Sea of Japan | Crypogenic | 41.0800 | 140.8378 |
4645 | Nishikawa 1991 | 1991 | 1991-01-01 | Tsukumo Bay | Crypogenic | 37.3333 | 137.0000 |
4646 | Nishikawa 1991 | 1991 | 1991-01-01 | Wakasa Bay | Crypogenic | 35.7500 | 135.6667 |
4647 | Nishikawa 1991 | 1894 | 1894-01-01 | Tokyo Bay | Crypogenic | 35.4169 | 139.7836 |
4648 | Nishikawa 1991 | 1991 | 1991-01-01 | Ise Bay | Crypogenic | 34.7167 | 136.7167 |
4649 | Nishikawa 1991 | 1973 | 1973-01-01 | Usa, Shikoku | Crypogenic | 33.4500 | 133.4500 |
4650 | Nishikawa 1991 | 1960 | 1960-01-01 | Ariake Sea | Crypogenic | 33.1333 | 130.1333 |
4651 | Nishikawa 1991 | 1991 | 1991-01-01 | Kagoshima Bay | Crypogenic | 31.4167 | 130.6333 |
4652 | Rho and Lee 1991 | 1991 | 1981-05-26 | Pusan | Crypogenic | 35.1183 | 129.0383 |
4653 | Rho and Lee 1991 | 1986 | 1986-12-27 | Samchonpo | Crypogenic | 34.9330 | 128.0670 |
4654 | Rho 1995 | 1994 | 1994-01-01 | Chopto, Chindo Islands | Crypogenic | 34.3844 | 126.2986 |
4655 | Huang 2001 | None | 9999-01-01 | Xiamen | Crypogenic | 24.4600 | 118.0789 |
4656 | Huang 2001 | None | 9999-01-01 | Hong Kong | Crypogenic | 22.2833 | 114.1500 |
4657 | Chengxing 1995 | None | 9999-01-01 | Luouyang Bay | Crypogenic | 26.4856 | 119.5492 |
4658 | U.S. National Museum of Natural History 2007 | 1971 | 1971-04-20 | None | Non-native | 9.3736 | -79.9533 |
4659 | U.S. National Museum of Natural History 2007 | 1978 | 1978-01-16 | Turpialito, | Non-native | 10.4667 | -64.1667 |
4660 | U.S. National Museum of Natural History 2007 | 1956 | 1956-03-26 | Woodbridge Bay | Non-native | 15.3167 | -61.4000 |
4661 | U.S. National Museum of Natural History 2007 | 1937 | 1937-03-29 | San Juan Harbor' | Non-native | 18.5000 | -66.0000 |
4662 | U.S. National Museum of Natural History 2007 | 1956 | 1956-03-16 | Carriacou Island | Non-native | 12.5000 | -61.4500 |
4663 | U.S. National Museum of Natural History 2007 | 1975 | 1975-01-01 | 3 Mile Off Brighton | Non-native | -37.9167 | 145.0000 |
4664 | U.S. National Museum of Natural History 2007 | 1983 | 1983-06-01 | Isla Margarita | Non-native | 11.0000 | -64.0000 |
4665 | U.S. National Museum of Natural History 2007 | 1955 | 1955-05-25 | Andros Island, 19 Mile SW Of Hawk Creek | Non-native | 24.7375 | -78.8111 |
4666 | U.S. National Museum of Natural History 2007 | 1973 | 1973-05-23 | Sidi Bou Said | Non-native | 36.8711 | 10.3503 |
4667 | U.S. National Museum of Natural History 2007 | 1964 | 1964-12-16 | South Hafun Bay, Indian Ocean | Crypogenic | 9.7000 | 51.0000 |
4668 | U.S. National Museum of Natural History 2007 | 1981 | 1981-03-01 | Twin Cays | Non-native | 16.8167 | -88.1000 |
4669 | Heller 1877 (cited by Kott 1998) | 1877 | 1877-01-01 | Trieste | Non-native | 45.6486 | 13.7800 |
4670 | Goodbody 2003 | None | 9999-01-01 | Kingston | Non-native | 17.9333 | -76.8500 |
4671 | da Rocha et al. 2005 | 2003 | 2003-08-12 | Isla Colon | Non-native | 9.4000 | -82.2833 |
4672 | Heller 1878, cited by Kott 1985 | 1878 | 1878-01-01 | Port Jackson | Non-native | -33.8500 | 151.2500 |
4673 | Herdmann 1899, cited by Kott 1985 | 1899 | 1899-01-01 | Port Stephen | Non-native | -32.7000 | 152.0833 |
4674 | Kott 1975, cited by Kott 1985 | 1975 | 1975-01-01 | None | Non-native | -35.2167 | 138.2500 |
4675 | Kott 1972, cited by Kott 1985 | 1972 | 1972-01-01 | Great Australian Bight | Non-native | -35.0000 | 130.0000 |
4676 | Kott 1985 | 1985 | 1985-01-01 | Monte Bello Islands | Non-native | -20.4667 | 115.5167 |
4677 | Hartmeyer and Michaelsen 1928, cited by Kott 1985 | 1928 | 1928-01-01 | Cockburn Sound | Non-native | -32.1667 | 115.7333 |
4678 | Kott 1985 | 1985 | 1985-01-01 | Perth Area | Non-native | -32.0500 | 115.7500 |
4679 | Kott 1985 | 1985 | 1985-01-01 | Indian Ocean | Non-native | -33.3333 | 115.6333 |
4680 | Wyatt et al. 2005 | 2001 | 2001-01-01 | Carnavon | Non-native | -25.5000 | 113.5000 |
4681 | Kott 1985 | 1985 | 1985-01-01 | Spencer Gulf | Non-native | -34.5000 | 136.9167 |
4682 | Kott 1985 | 1985 | 1985-01-01 | Moreton Bay | Non-native | -27.2500 | 153.2500 |
4684 | Kott 1985 | 1985 | 1985-01-01 | Mouth of Calliope River | Non-native | -23.8333 | 151.2167 |
4685 | Cranfield et al. 1998 | 1948 | 1948-01-01 | Auckland (North Island) | Non-native | -36.8333 | 174.8333 |
4686 | Brewin 1957, cited by Cranfield et al. 1998 | 1957 | 1957-01-01 | North Island | Non-native | -36.3333 | 175.0833 |
4688 | Naranjo et al. 1996 | 1998 | 1998-01-01 | Algeciras | Non-native | 36.1275 | -5.4539 |
4689 | Fiala-Médioni 1978 | 1978 | 1978-01-01 | Banyuls-sur-Mer | Non-native | 42.4833 | 3.1333 |
4690 | Clausade 1969 | 1969 | 1969-01-01 | Marseile | Non-native | 43.3000 | 5.4000 |
4691 | Peres 1957 | 1957 | 1957-01-01 | Majorca, Balearic Islands | Non-native | 39.5000 | 3.0000 |
4692 | Relini 1964 | 1964 | 1964-01-01 | Genoa/ | Non-native | 44.4167 | 8.9500 |
4693 | Chimenez et al. 1985 | 1976 | 1985-01-01 | Ischia | Non-native | 40.7167 | 13.9000 |
4694 | Tursi and Matarrese 1981 | 1976 | 1976-01-01 | Taranto | Non-native | 40.4761 | 17.2297 |
4695 | Traustedt 1877 | 1877 | 1877-01-01 | Naples | Non-native | 40.7167 | 14.1667 |
4696 | Tursi et al. 1979 | 1979 | 1979-01-01 | Bari | Non-native | 41.1333 | 16.8500 |
4697 | Antoniadou and Chintiroglou 2007 | 1997 | 1997-01-01 | Chalkidiki Peninsula | Non-native | 40.4167 | 23.4500 |
4698 | Sedra and Khalil 1971 | 1971 | 1971-01-01 | Alexandria | Non-native | 31.1981 | 29.9192 |
4699 | Agius et al. 1977 | 1976 | 1976-01-01 | Marsaxlokk Bay | Non-native | 35.8200 | 14.5456 |
4700 | Dinclasna and Ober 2004 | 2004 | 2004-01-01 | Izmir | Non-native | 38.4333 | 27.1167 |
4701 | Monniot 2002 | 1927 | 1927-01-01 | Gulf of Suez | Crypogenic | 28.0000 | 34.0000 |
4702 | Monniot 1969 | 1969 | 1969-01-01 | Dakar | Non-native | 14.6661 | -17.4367 |
5923 | Rodriguez et al. 2008 | 2005 | 2005-12-01 | Bahia San Quintin | Non-native | 30.4500 | -116.0000 |
6820 | Millar 1951, cited by de Barros et al. 2009 | 1951 | 1951-01-01 | Durban | Non-native | -29.8500 | 31.0333 |
6821 | Rius et al. 2010 | 2009 | 2009-01-01 | Knysna Marina | Non-native | -34.0547 | 23.0628 |
6934 | Pineda et al. 2012 | 2009 | 2009-07-01 | UNC Wilmington docks, Wilmington | Non-native | 34.1400 | -77.8622 |
767446 | Ruiz et al., 2015 | 2013 | 2013-07-23 | Marina Village, Mission Bay, CA, California, USA | Non-native | 32.7605 | -117.2364 |
767515 | Ruiz et al., 2015 | 2013 | 2013-08-01 | Hyatt Resort Marina, Mission Bay, CA, California, USA | Non-native | 32.7634 | -117.2397 |
767531 | Ruiz et al., 2015 | 2013 | 2013-08-03 | Mission Bay Sport Center, Mission Bay, CA, California, USA | Non-native | 32.7857 | -117.2495 |
767543 | Ruiz et al., 2015 | 2013 | 2013-07-30 | Hilton Resort Docks, Mission Bay, CA, California, USA | Non-native | 32.7791 | -117.2128 |
767672 | Ruiz et al., 2015 | 2013 | 2013-07-16 | Naval Base Point Loma, San Diego Bay, CA, California, USA | Non-native | 32.6886 | -117.2343 |
767722 | Ruiz et al., 2015 | 2013 | 2013-07-21 | Cabrillo Isle Marina, San Diego Bay, CA, California, USA | Non-native | 32.7272 | -117.1995 |
767793 | Ruiz et al., 2015 | 2013 | 2013-07-28 | Marriott Marquis and Marina, San Diego Bay, CA, California, USA | Non-native | 32.7059 | -117.1655 |
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