Species Profile: Bay Scallop, Argopecten Irradians
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Argopecten irradians Adult 2cm (from Goode 1884) Common Name: bay scallop Recreational: Bay scallops are sometimes collected Scientific Name: Argopecten irradians by hand picking while wading in seagrass beds. In Other Common Names: Atlantic bay scallop, peigne Florida waters of the Gulf of Mexico, recreational baie de /'At/antique (French), peine caletero atlantico harvest is common from Steinhatchee north and west {Spanish) (Fischer 1978). to Panama City (Arnold pers. comm.). However, Classification (Turgeon et al. 1988) recreational harvest elsewhere in the Gulf of Mexico is Phylum: Mollusca not especially common because of the bay scallop's Class: Bivalvia relatively low abundance. In Florida, the recreational Order: Ostreoida seasons extends from July 1 to September 10, from Family: Pectinidae Suwannee River southward (Arnold pers. comm.). The bag limit is two gallons of whole bay scallops in the Value shell, or one pint of meat, per day per person, or ten Commercial: Bay scallops are harvested commer gallons of whole scallops per day per boat (Arnold pers. cially by dredging, dip netting, raking, and hand picking comm.). In Texas, they may be taken year-round in {Peters 1978). Reported U.S. 1992 bay scallop land waters approved by the Texas Department of Health. ings were161.5 metric tons (mt), with a dollar value of $2.1 million (NMFS 1993). This an important commer Indicator of Environmental Stress: Filler feeders such cial species along the U.S. Atlantic coast, with fisheries as bay scallops often ingest and accumulate resus in Massachusetts, Rhode Island, New York, North pended detritus and organic matter from polluted ar Carolina, and the Gulf coast of Florida (Heffernan et al. eas. This species has been used to test the effects of 1988, MacKenzie 1989, Rhodes 1991). Landings for pollutants from the petroleum industry (Hamilton et al. 1992 totaled 58.5 mt in the Gulf of Mexico (Newlin 1981 ). Mortality of juvenile bay scallops has been 1993). However, the commercial scallop fishery in demonstrated in the laboratory in the presence of Florida has been closed since 1995 (Arnold pers. heavy metals (Nelson et al. 1976). comm.). There is no apparent commercial fishery for this species in the remaining Gulf coastal states be Ecological: The bay scallop is an important part of the cause of their relatively low abundance, but their high estuarine food web through its conversion of phy value and the available market has sparked consider toplankton and detritus into available biomass for sec able interest in maricultural production (Hall 1984, ond order consumers. Rhodes 1991 ). There are few commercial scallop mariculture ventures currently in operation, but hatch Range ery technology is well developed and research is in Overall: The range of this species extends along the progress (Hall 1984, Crenshaw et al. 1991, Rhodes western Atlantic from Cape Cod into the Gulfof Mexico, 1991, Walker et al. 1991 ). and down to Colombia (Turner and Hanks 1960, Sastry 1962, Fischer 1978, Peters 1978, Robert 1978, Faye! al. 1983). Areas of abundance as determined from 13 Bay scallop, continued commercial landings are coastal areas of Massachu Table 5.01. Relative abundance of bay scallop in 31 setts, Rhode Island, New York, North Carolina, and the Gulf of Mexico estuaries (from Volume /). gulf coast of Florida (Heffernan et al. 1988, Rhodes ,esaae 1991 ). Estuarv A s J L E In the United States, Argopecten irradlans is consid Florida Bay ✓ ✓ ✓ ✓ ✓ ered to include three subspecies: A. i. irradians, rang Ten Thousand Islands ✓ ✓ ✓ ✓ ✓ ing from Cape Cod to New Jersey; A. i. concentricus, New Jersey to the Chandeleur Islands, east of the Caloosahatchee River ✓ ✓ ✓ ✓ ✓ Mississippi River; and A. i. amplicostatus, Galveston Charlotte Harbor ✓ ✓ ✓ ✓ ✓ Bay to Tuxapan, Veracruz, Mexico (Andrews 1981, Tampa Bay ✓ ✓ ✓ ✓ ✓ Fay et al. 1983). Suwannee River Within Study Area: Along the Florida Gulf coast, bay Apalachee Bay 0 0 0 0 0 scallops are most abundant from Pepperfish Keys, south of Steinhatchee, north and westward to St. Apalachicola Bay ✓ ✓ ✓ ✓ ✓ Andrew Bay (Arnold pers. comm.). Populations are St. Andrew Bay 0 0 0 0 0 scattered in the northwestern Gulf, but become more Choctawhatchee Bay common In the western Gulf. In Texas, the bay scallop is most abundant in bays of the southern coast where Pensacola Bay ✓ ✓ ✓ ✓ ✓ the salinities are generally higher and seagrass mead Perdido Bay ows are extensive. The subspecies Argopecten Mobile Bay irradians concentricus ranges from Key West, Florida to the Chandeleur Islands of Louisiana (Broom 1976). Mississippi Sound 0 0 0 0 0 Argopecten irradians amp/icostatus ranges from Lake Borgne Galveston, Texas to the Laguna Madre (Broom 1976, Lake Pontchartrain Andrews 1981) (Table 5.01). Breton/Chandeleur Sounds ✓ ✓ ✓ ✓ ✓ Life Mode Mississippi River Fertilized eggs are demersal (Belding 1910). Early Barataria Bay larval stages are pelagic and planktonic. Late larval stages are epibenthic. Juveniles up to 20-30 mm in Terrebonneffimbalier Bays length attach to a surface suspended off the bottom by Atchafalaya/Verrnilion Bays byssal threads (Sastry 1965). Adults and juveniles >30 Calcasieu Lake mm in length are epibenthic, sometimes motile, and gregarious (Belding 191 O, Gutsell 1930, Marshall 1947, Sabine Lake Sastry 1962, Robert 1978, Peters 1978, Fonseca et al. Galveston Bay ✓ ✓ ✓ ✓ ✓ 1984). Brazos River Habitat Matagorda Bay ✓ ✓ ✓ ✓ ✓ Type:All life stages are estuarine, and marine in San Antonio Bay ✓ ✓ ✓ ✓ ✓ nearshore waters, occurring in high salinity (euhaline to polyhaline) waters. Bay scallops are typically sub Aransas Bay ✓ ✓ ✓ ✓ ✓ tidal, but may be exposed during especially low tides Corpus Christi Bay ✓ ✓ ✓ ✓ ✓ (Rhodes 1991). Collections have been recorded at Laguna Madre ✓ ✓ ✓ ✓ ✓ depths from Oto 10 m and a maximum of 18 m. They are most abundant in waters from 0.3 to 0.6 m at low Baffin Bay tide (Marshall 1960, Sastry 1962, Thayer and Stuart A s J L E 1974, Peters 1978, Robert 1978, Fay et al. 1983, Fonseca et al. 1984). Larvae inhabit the water column Relative abundance: Life stage: while searching for a settlement site (Sastry 1965). At Highly abundant A· Adults settlement the young scallop attaches epifaunally to a Abundant S - Spawning adults surface suspended off the bottom (rock, seagrass, algae, rope) by means of byssal threads (Belding 0 Common J - Juveniles 1910). At 20 to 30 mm in length the juvenile scallop ✓ Rare L - Larvae settles to the bottom, beginning a demersal existence blank Not present E • Eggs that continues through the adult stage (Castagna 1975). 14 Bay scallop, continued Substrate: Late larval/early juvenile stages use vari salinities on scallop behavior indicated that at salinities ous substrates for attachment, including oyster shells, of 16%0 and temperatures of 1 0° to 15°C the animals rope, algae, seagrass, and submerged macrophytes became inactive, and at 20° to 25°C reduced activity (Gutsell 1930, Marshall 1947, Marshall 1960, Thayer occurredat22%oand 18%o(Duggan 1973). Mortality of and Stuart 1974, Fay et al. 1983). Seagrasses, such scallops has been demonstrated in the laboratory at as eel grass (Zostera marina) and shoal grass (Halodule salinities of 10%o and less over a range of temperatures wrightit), appear to be the preferred settling site given (Mercaldo and Rhodes 1982). the abundance that is often associated with seagrass habitats (Belding 191 o, Gutsell 1930, Sastry 1962, Dissolved Oxygen: Oxygen resting requirements of 70 Thayer and Stuart 1974, Castiglione pers. comm.). ml/kg/hour at 20° have been reported (Van Dam 1954). However, if seagrass density is too great, current Critical dissolved oxygen (DO) concentrations for this velocity is reduced and bay scallop abundance may species may be related to individual size and ambient decline (MacKenzie 1989). Scallops can settle and water temperature (Voyer 1992). survive in areas lacking seagrass (Marshall 1947, Marshall 1960), but individuals <10 mm generally Other: Turbidities greater than 500 ppm may interfere cannot tolerate silty substrates (Castagna 1975), and with normal growth and reproduction (Fay et al. 1983). burial can occur in muddy substrates (Tettelbach et al. Water currents can displace scallops from their"home" 1990). Smith et al. (1988) have demonstrated that habitat, and current velocity can have effects on growth transplanted seagrass does not serve as a highest related to food availability (Moore and Marshall 1967, quality habitat, due to greater losses from predation Kirby-Smith 1972, Rhodes 1991 ). An optimal amount and/or transport as compared to a natural seagrass of current is necessary to maintain high concentrations site. of suspended food and remove waste materials rapidly (Kirby-Smith 1972). Physical/Chemical Characteristics: Temperature: Eggs and larvae are stenothermal, with Movements and Migrations: Egg and early larval 15 to 20°c required for early development. Optimal stages may be transported by tidal currents. Late larval embryonic development occurs from 20 to 25° and stages are capable of swimming by use of the ciliated best larval growth from 25 to 30°C (T ettlebach and velum and crawling with the foot (Gutsell 1930, Sastry Rhodes 1981 ). Wright et al. (1983, 1984) found larvae 1965, Hall 1984). Juvenile and adult scallops are subjected to temperatures below the spawning tem capable of swimming via propulsion created by the perature experienced a cold-shock which resulted in clapping of the two valves (Belding 1910, Gutsell 1930, higher mortalities. Juveniles and adults are euryther Moore and Marshall 1967). This ability apparently mal, and Connecticut bay scallops are reportedly able serves to maintain position in grassbeds and avoid to tolerate temperatures as low as -6.6°C for short competitors and predators (Peterson et al. 1982, Win periods (Marshall 1960). Throughout their range they ter and Hamilton 1985). The extent of late juvenile and occur in areas where summer maximum water tem adult movements is unclear. There are, however, peratures do not exceed 32°C (Sastry 1965, Barber some reports of scallops migrating in mass (Roessler and Blake 1983}.