Invasion History

First Non-native North American Tidal Record: 1901
First Non-native West Coast Tidal Record: 1901
First Non-native East/Gulf Coast Tidal Record:

General Invasion History:

Crepidula plana is native from the southern Gulf of St. Lawrence, Canada to St. Catherine's Sound, Georgia (Bousfield 1960; Abbott 1974; Morris 1975). The southern limits of its range are unclear, because of the presence of two similar flat slippersnails, C. depressa and C. atrasolea, which range from North Carolina into the Gulf of Mexico (Collin 2000). Crepidula plana was introduced to the West Coast by 1898, with Eastern Oysters (Crassostrea virginica) planted in San Francisco Bay, California (Carlton 1979; Cohen and Carlton 1995; Miller 2000). They have subsequently been introduced to Willapa Bay and Puget Sound, Washington (Carlton 1979; Wonham and Carlton 2005).

North American Invasion History:

Invasion History on the West Coast:

Crepidula plana was first reported from San Francisco Bay, California (CA) by Doe (1901, cited by Carlton 1979). It was overlooked for many decades, due to confusion with the native C. perforans and C. nummaria, and its tendency to occupy cryptic habitats. This slippershell was found in 1972 at Coyote Point, in South San Francisco Bay, on the insides of shells of the introduced Busycotypus canaliculatus (Channeled Whelk) inhabited by the native Hairy Hermit Crab (Pagurus hirsutiusculus) (Carlton 1979). Museum collections indicate that it is widespread, in San Pablo Bay, and the Central and South Bays (California Academy of Sciences 2013).

In 1946, C. plana was found in Willapa Bay, Washington (Smith 1946; Hanna 1966, cited by Carlton 1979). It was present in the Bay at Nahcotta in 1977 (Carlton 1979), but was not mentioned in a 2001 survey (Cohen et al. 2001). Coe (1949, cited by Carlton 1979) reported C. plana from Puget Sound, but we have not found recent records of its occurrence. It is not included in a list of Puget Sound Crepidula species by Holm (2006).


Description

Crepidula plana is a limpet-like marine snail, with an oval, very flat shell. The apex is usually in the center of the shell, but is sometimes turned to one side. The shape of the shell varies with substrate, and can be slightly curved or even concave, according to the surface to which it's attached. The shell has an interior shelf-like deck, covering about 1/2 of the aperture, giving it an appearance like a wide, flat boat. If the shell has a concave curve the deck may be slightly convex. The edge of the deck is sinuous. On the interior side, is a shelf or deck, which covers about half the length of the shell. The outer surface is wrinkled by prominent concentric growth lines. The shell and the foot are white and the interior is highly polished, sometimes iridescent. The adult shell may reach 30-38 mm in length. Description from: Abbott 1974, Morris 1975, Gosner 1978, Collin 2000, and McLean in Carlton 2007.

Crepidula plana settles and grows on hard surfaces, including rocks and manmade structures, but it is often found on the shells of dead or living mollusks, shells inhabited by hermit crabs, or the undersides of living horseshoe crabs. Slippersnails are protandrous hermaphrodites, first maturing as a male, while the oldest individuals are females. This slipper shell rarely forms stacks, but mature males gather near large females and mate for varying periods of time. The timing and the size at which the sex-change takes place, varies greatly, according to whether the animals are solitary or associated with a female (Coe 1938; Gould 1949).

Crepidula 'plana' had been considered a single species, ranging from the Gulf of St. Lawrence to the Gulf of Mexico, but closer examination of the life history of different populations indicates that three species occur on the East and Gulf Coast. Crepidula plana, described from New Jersey, ranges from Canada to around Cape Hatteras, North Carolina. It has planktotrophic development. Crepidula depressa, ranging from North Carolina to Texas, also has planktotrophic larvae, but differs in the morphology of the female genital papilla, the structure of the protoconch, size at hatching, and features of the radula. Crepidula atrasolea, found from North Carolina to Sanibel Island, Florida has a black foot, differing radular features, and direct development (Collin 2000). Several additional species, similar to C. plana, occur in Brazil (Simone 2006).


Taxonomy

Taxonomic Tree

Kingdom:   Animalia
Phylum:   Mollusca
Class:   Gastropoda
Order:   Neotaenioglossa
Family:   Calyptraeidae
Genus:   Crepidula
Species:   plana

Synonyms

Crepidula lamina (H. C. Lea, 1843)
Crepidula rhyssema (Olsson & Harbison, 1953)
Crepidula riisei (Dunker, 1852)
Crepidula unguiformis (Lamarck, 1822)

Potentially Misidentified Species

Crepidula atrasolea
Formerly considered conspecific, identified by molecular methods. Ranges from Cape Hatteras, North Carolina to Sanibel, on Florida's Gulf Coast (Collin 2001).

Crepidula depressa
Formerly considered conspecific, identified by molecular methods (Collin 2001). Ranges from Cape Hatteras, North Carolina to Port Aransas, Texas (Collin 2001).

Crepidula nummaria
NE Pacific open-coast native, has a thick, brown periostracum, and is usually oval in shape  (McLean, in Carlton 2007).

Crepidula perforans
Native to the NE Pacific open-coast. Has a variable shape, being long and thin in pholad burrows, concave on hermit crab shells, or flat and white under rocks (McLean, in Carlton 2007).

Ecology

General:

Crepidula plana is a common Atlantic filter-feeding marine gastropod with a limpet-like body. It lives attached to a solid substrate, but this can often be live or empty mollusk shells (Abbott 1974; Gosner 1978). Crepidula plana is a protandric hermaphrodite, maturing first as a male. It often does not become fully functional unless in the presence of a female. When a solitary male does mature at about 8-12 mm in length, the male phase is brief. Younger snails, before maturation, often crawl on top of a larger animal, which may also be immature or in transition from male to female. The formation of such a mated pair speeds maturation of the upper animal as a male and the lower one as a female. In mated pairs, the male phase is prolonged and males may reach ~15 mm before the transition to female, while solitary males may start the transition around 10 mm. Crepidula plana does not form the large stacks characteristic of C. fornicata or C. onyx. Individuals can show great variability in the rate of growth, and the timing and occurrence of sexual maturity and transitions (Coe 1938; Gould 1949). Eggs are laid in capsules on the forward edge of the foot. Eggs take about 17 days to hatch at 18.5°C and hatch into swimming, planktotrophic veligers. The veligers settle after 11-72 days at 12-29°C as juveniles 0.97 - 1.10 mm long (Collin 2003b). At low temperatures (12°C) development can be prolonged to 72 days (Pechenik and Lima 1984).

Crepidula plana is most common at salinities of 20-30 PSU and inhabits shallow estuaries with a wide temperature range (Verrill and Smith 1873; Wass 1972; Leathem and Maurer 1975). It can grow on a wide range of substrates, including rock, plastic floats, buoys, and shells of dead or live mollusks (including Eastern Oysters, Crassostrea virginica) and other hard-shelled organisms (Verrill and Smith 1873; Abbott 1974; McGee and Targett 1989; Lippson and Lippson 1997). Other substrate examples include dead shells of large gastropods such as Busycotypus canaliculatus (Channeled Whelk), the undersides of horseshoe crabs (Limulus polyphemus), in bottles, cans, and other debris, and on floats and buoys. In San Francisco Bay, C. plana was found on hermit crab-inhabited shells of B. canaliculatus and on Macoma nasuta shells (Carlton 1979). Crepidula plana is a filter feeder, trapping phytoplankton and detritus in strings of mucus on its gills, which are conveyed to its mouth (Henry et al. 2010).

Food:

Phytoplankton

Trophic Status:

Suspension Feeder

SusFed

Habitats

General HabitatCoarse Woody DebrisNone
General HabitatOyster ReefNone
General HabitatMarinas & DocksNone
General HabitatRockyNone
General HabitatUnstructured BottomNone
Salinity RangePolyhaline18-30 PSU
Salinity RangeEuhaline30-40 PSU
Tidal RangeSubtidalNone
Tidal RangeLow IntertidalNone
Vertical HabitatEpibenthicNone


Tolerances and Life History Parameters

Maximum Depth (m)38(Abbott 19735 Morris 1975; Gosner 1978;
Minimum Salinity (‰)15Field, rare below 20 (Leathem and Maurer 1975)
Maximum Salinity (‰)35Normal marine sainity, probably tolerates higher
Minimum Reproductive Temperature12Experimental, lowest tested (Lima and Pechenik 1985)
Maximum Reproductive Temperature29Experimental, highest tested (Lima and Pechenik 1985)
Minimum Reproductive Salinity14.5Experimental, 70% survival of larvae, 0% at 8 ppt (Zimmerman and Pechenik 1991)
Maximum Reproductive Salinity35Normal marine salinity, probably tolerates higher
Minimum Duration11Experimental, 29 ppt, 29 C, time to first metamorphosis (Zimmerman and Pechenik 1991)
Maximum Duration72Experimental, 29 ppt, 12 C, Lima and Pechenik 1985
Minimum Length (mm)8Males can mature at 8-10 mm, and begin functioning as females at 17-22 mm (Coe 1938).

General Impacts

No ecological impacts have been reported for Crepidula plana on the West Coast of North America.

Regional Distribution Map

Bioregion Region Name Year Invasion Status Population Status
P050 San Pedro Bay 2011 Non-native Unknown
NEP-VI Pt. Conception to Southern Baja California 2011 Non-native Unknown
NEP-IV Puget Sound to Northern California 1937 Non-native Established
NEP-V Northern California to Mid Channel Islands 1901 Non-native Established
P090 San Francisco Bay 1901 Non-native Established

Occurrence Map

OCC_ID Author Year Date Locality Status Latitude Longitude
697256 Cohen et al. 2005 (SF Bay Area RAS) 2004 2004-05-27 Pete's Harbor, San Francisco Bay Non-native 37.5006 -122.2242
698011 Cohen et al. 2005 (SF Bay Area RAS) 2004 2004-05-24 Fruitvale Bridge, San Francisco Bay Non-native 37.7690 -122.2296
698618 Cohen et al. 2005 (SF Bay Area RAS) 2004 2004-05-27 Coyote Point Marina, San Francisco Bay Non-native 37.5907 -122.3180
701302 Doe 1901, cited in Carlton 1979 1901 San Francisco Bay [Bay Farm Island?] Non-native 37.8494 -122.3681
703252 Introduced Species Study 2010 2010-06-12 China Camp Non-native 38.0025 -122.4617
703825 Introduced Species Study 2011 2011-04-20 Fuel Depot Non-native 33.7440 -118.2358
704614 Introduced Species Study 2010 2010-06-01 Sierra Point Marina Non-native 37.6740 -122.3792
760250 Packard 1918a, 1918b 1913 Central San Francisco Bay Non-native 37.8595 -122.3884
760251 Packard 1918a, 1918b 1913 South San Francisco Bay Non-native 37.5457 -122.1645
760252 California Academy of Sciences Invertebrate Zoology Collections Database 1922 1922-08-28 Dumbarton Bridge Non-native 37.5058 -122.1180
760253 Carlton 1979 1951 1951-11-03 Suisun Bay Non-native 38.0713 -122.0581
760254 Carlton 1979 1951 1951-11-03 San Pablo Bay Non-native 38.0600 -122.3900
760255 Carlton 1979 1967 Lake Merritt Non-native 37.8025 -122.2578
760256 Wicksten 1978; Carlton 1979 1972 1972-03-25 Coyote Point Non-native 37.5922 -122.3210
775478 Ruiz et al., 2022 2014 2014-09-08 San Francisco Marina, San Francisco Bay, California, USA Non-native 37.8078 -122.4354
775479 Ruiz et al., 2022 2014 2014-09-17 Oyster Point Marina, San Francisco Bay, California, USA Non-native 37.6639 -122.3758
775480 Ruiz et al., 2022 2014 2014-09-18 Oakland Yacht Club, San Francisco Bay, California, USA Non-native 37.7835 -122.2630
819021 Ruiz GM and JB Geller (2015) 2012 San Leandro None 37.6580 -122.2217
819022 Ruiz GM and JB Geller (2015) 2012 Redwood City None 37.5574 -122.1755
819023 Ruiz GM and JB Geller (2015) 2012 Coyote Point None 37.5987 -122.3252
819024 Ruiz GM and JB Geller (2015) 2012 None None
819025 Ruiz GM and JB Geller (2015) 2012 Corte Madera None 37.9309 -122.4819
819026 Ruiz GM and JB Geller (2015) 2012 Oyster Point None 37.6805 -122.3731
819027 Ruiz GM and JB Geller (2015) 2012 Richardson Bay None 37.8788 -122.4759
819028 Ruiz GM and JB Geller (2015) 2012 Emeryville None 37.8596 -122.3152
819029 Ruiz GM and JB Geller (2015) 2012 Ballena Isle None 37.7643 -122.2978
819607 Ruiz GM and JB Geller (2015) 2013 Emeryville None 37.8602 -122.3000
819608 Ruiz GM and JB Geller (2015) 2013 Corte Madera None 37.9364 -122.4833
819609 Ruiz GM and JB Geller (2015) 2013 Richardson bay None 37.8737 -122.4667
819610 Ruiz GM and JB Geller (2015) 2013 None None
819611 Ruiz GM and JB Geller (2015) 2013 Ballena isle None 37.7578 -122.2500
819612 Ruiz GM and JB Geller (2015) 2013 Oyster Point None 37.6788 -122.3667
819613 Ruiz GM and JB Geller (2015) 2013 Redwood city None 37.5588 -122.2000
819614 Ruiz GM and JB Geller (2015) 2013 Coyote Point None 37.5926 -122.2667
819615 Ruiz GM and JB Geller (2015) 2013 San Leandro None 37.6602 -122.2167
819763 Ruiz GM and JB Geller (2018) 2014 Oyster Point None 37.6937 -122.3689
819764 Ruiz GM and JB Geller (2018) 2014 SF marina None 37.8075 -122.4347
819765 Ruiz GM and JB Geller (2018) 2014 Hayward None 37.6485 -122.2184
819766 Ruiz GM and JB Geller (2018) 2014 Ballena Isle None 37.7583 -122.2841
819767 Ruiz GM and JB Geller (2018) 2014 San Mateo None 37.5938 -122.3036
819768 Ruiz GM and JB Geller (2018) 2014 San Bruno None 37.6479 -122.3662
819769 Ruiz GM and JB Geller (2018) 2014 Richmond None 37.9187 -122.3919
819770 Ruiz GM and JB Geller (2018) 2014 Albany None 37.8877 -122.3247
819771 Ruiz GM and JB Geller (2018) 2014 San Quentin None 37.9372 -122.4787
819772 Ruiz GM and JB Geller (2018) 2014 Richardson bay None 37.8715 -122.4790
819973 Ruiz GM and JB Geller (2018) 2015 Oakland None 37.7056 -122.2473
819974 Ruiz GM and JB Geller (2018) 2015 Ballena Isle None 37.7588 -122.2834
819975 Ruiz GM and JB Geller (2018) 2015 SF marina None 37.8074 -122.4345
819976 Ruiz GM and JB Geller (2018) 2015 Richardson bay None 37.8705 -122.4797
819977 Ruiz GM and JB Geller (2018) 2015 Smithsonian None 37.8981 -122.4623
819978 Ruiz GM and JB Geller (2018) 2015 Hunters Point None 37.7088 -122.3691
819979 Ruiz GM and JB Geller (2018) 2015 Oyster Point None 37.6747 -122.3753
819980 Ruiz GM and JB Geller (2018) 2015 Union City None 37.5865 -122.1743
819981 Ruiz GM and JB Geller (2018) 2015 Albany None 37.8879 -122.3245
819982 Ruiz GM and JB Geller (2018) 2015 San Lorenzo None 37.6480 -122.2159
820193 Ruiz GM and JB Geller (2018) 2016 SF marina None 37.8071 -122.4345
820194 Ruiz GM and JB Geller (2018) 2016 Bay Farm None 37.7237 -122.2632
820195 Ruiz GM and JB Geller (2018) 2016 Brisbane None 37.6560 -122.3697
820196 Ruiz GM and JB Geller (2018) 2016 Mission Bay None 37.7553 -122.3790
820197 Ruiz GM and JB Geller (2018) 2016 Albany None 37.8773 -122.3241
820198 Ruiz GM and JB Geller (2018) 2016 El Cerrito None 37.8885 -122.3367
820199 Ruiz GM and JB Geller (2018) 2016 Richardson bay None 37.8669 -122.4751
820200 Ruiz GM and JB Geller (2018) 2016 Paradise Cay None 37.9044 -122.4684
820201 Ruiz GM and JB Geller (2018) 2016 Oyster Point None 37.6688 -122.3741
820202 Ruiz GM and JB Geller (2018) 2016 Ballena Isle None 37.7516 -122.2878

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