Ecological Considerations in Oyster Bottom Culture

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Maine State Library Maine State Documents Coastal Resource Center Bar Harbor, Maine 6-1976 Ecological Considerations in Oyster Bottom Culture Walter S. Foster Coastal Resource Center, Inc. Follow this and additional works at: http://digitalmaine.com/coastal_resource_center_publications Recommended Citation Foster, Walter S. and Coastal Resource Center, Inc., "Ecological Considerations in Oyster Bottom Culture" (1976). Coastal Resource Center. 1. http://digitalmaine.com/coastal_resource_center_publications/1 This Text is brought to you for free and open access by the Bar Harbor, Maine at Maine State Documents. It has been accepted for inclusion in Coastal Resource Center by an authorized administrator of Maine State Documents. For more information, please contact statedocs@maine.gov.

Ecological Considerations in Oyster Bottom Culture by Walter S. Foster Research Bulletin No. 37 n

Prepared for the Coastal Resource Center Bar Harbor, Maine June 1976 Cover by: Carolyn Foster

A Review of Difficulties to be Anticipated in Oyster Bottom Culture in Maine, Based on Experiences in New England, Maritime Canada and Northern Europe. Study Performed for Coastal Resource Center Bar Harbor, Maine by Walter S. Foster

INTRODUCTION Some acquaintance with the oyster cultivation practices in southern New England, Canadian Maritimes ^nd northern Europe may be useful to those considering the culture of the European flat oyster, Ostrea edulis, on the bottom of bays in Maine. The object here is to make one aware of the oyster's relationship to its environment so that one may anticipate and recognize potential problems and take remedial action before they become serious. This review does not attempt to describe basic oyster culture methods, these may be found elsewhere (1,2,3,7,9). Oyster bottom culture, distinct from a wild fishery or simply hunting, has several phases in common wherever it is practiced: seed procurement (the acquisition of small oysters to grow into a marketable product), planting, and harvesting. Additional steps may be necessary in different areas, for example: selection of the culture area; preparation of the bottom prior to planting; i predator removal and predator control by other means; planting or transplanting into areas for a selected shell growth rate, shell shape, meat condition (color, flavor, or plumpness), or depuration (self-cleansing of bacteria from oysters transferred to clean water from polluted water); transplanting to break up clumps of oysters that have grown together or to lift them from accumulated sil t. This review does not include? the seed acquisition and harvesting phases of oyster culture. Oyster culture practices differ greatly with geographic region, species, chronology, mechanical capability and economy. This review is largely an extraction from reports of practices in the eastern American oyster, Crassostrea virginica, industries of

Maritime Canada and New England and the flat oyster industries of northern Europe. THE FISHERIES Present practices in the Maritimes and New England typically involve only the spreading of seed oysters on the private grant in spring and harvesting the following fall. A planter in these fisheries may buy three-year old oysters in April and plant them at 400 to 500 bushels per acre. He harvests them from September, five months later, through to the following April so that all are harvested in time for the next planting. A gross increment in volume may be expected on good grounds by this method. J. C. Medcof (7) distinguishes between "maturing," as in the above fishery and "rearing," which involves growing seed of about 1 1/2 to 2 1/2 inches up to nearly market size, the three-year old oysters planted in the above described fishery. THE OYSTER BED ENVIRONMENT When oyster culture is initiated in an area, characteristics of growth and meat condition at different times in the year will have to be determined for parts of the bottoms available. Virtually constant attention should be given to the cultured crop for maximum yield and production of a good quality oyster. In 1900 (9) English oyster growers were said to spend three days a week cultivating their oysters and three days harvesting them. Generally speaking, shallow grounds are warmer and produce more rapid growth and thin shells; deeper beds produce slower growth, deeper, more desirably shaped shell and better meats. -2-

H. A. Cole (2) gave this guide, "A useful indication of the characteristics of the locality can often be obtained by examining mussels collected at low water or by dredging. If the younger mussels are well grown and well fished, it is highly probable that oysters, feeding in a similar manner, will do well." Oyster mortalities can be expected if siltation or suspended silt is abundant, or water temperatures remain near zero degrees centigrade for extended periods or salinity is lowered. Great losses in Britain, France and the Netherlands have been attributed to conditions of temperature and salinity that are common on the Maine coast. Unfortunately, the precise factors responsible for winter mortalities in Europe are not known. Survival of the Dutch strain of flat oysters has been good in Maine estuaries at one to three meters depth at mean low water. Silt and fresh water, the combination of factors frequently cited as responsible for winter mortalities, can be avoided by careful site selection. Twenty-five parts per thousand should be the minimum salinity expected in prospective culture waters. Cole (2) points out that the presence of ascidians, slipper limpets, whelks, starfish or hermit crabs collectively indicates water of salinity which is suitable for Ostrea edulis as well. The flat oyster is less capable of dealing with silt than the eastern American oyster. Silt accumulated during the winter, which oyster growers considered normal, was found to be the cause of winter mortalities of seed eastern American oysters on the Connecticut shore. This was remedied by transplanting the seed early in the spring before water temperatures rose to a level at which metabolic activity in the silted seed increased to a point where they smothered. -3-

"Suitable bottoms are those of stiff mud," according to Cole (2), "sandy mud, fine gravel, or gravel and mud, or of shell with some sand or mud. Clean sand, loose gravel or rocky bottoms are unsuitable. In sand the oysters quickly become bedded and may be Very soft mud can be utilized only with difficulty on the shore and hardly at all where it is not uncovered, since dredging is barely possible on such grounds without burying large quantities of the oysters left behind." BIOLOGICAL ASSOCIATES Some other factors in bottom culture involve reaction to flora and fauna which may be predacious, competitive or which otherwise adversely affect the product. Disease diagnosis and treatment is beyond the scope of this review but for a brief mention of shell disease. Shell disease is believed to be caused by a fungus, Ostracoblabe implexa (5), producing white clear-centered "warts" inside the shell; at a later state, large olive-colored horny patches occur. When the disease reaches the adductor muscle attachment, the oyster cannot remain closed, weakens and dies. Large areas of oyster- producing grounds have been infected by the disease. It is believed to be a resident of shells of dead mollusks. Where vast areas of recently dead shells cover submerged grounds, the potential exists for proliferation of the disease. Since at least four days of water temperatures above 19 C (66 F) are believed necessary to transmit the disease (4), it should not be a problem in eastern Maine. Shell disease has been found in Canadian Maritime Ostrea edulis cultures. smothered during gales, while on rocky bottoms dredging is impossible. -4-

Shell disease infection can be destroyed by dipping the shells in solutions of organic mercury (7) which could make the oysters unfit for human consumption for an unknown period of time. PROBLEM FLORA Eel-grass reduces circulation and water exchange, consequently slowing oyster growth. Cape Cod and Maritime beds that have becomd overgrown with eel-grass have been those where hand tongs have been the methods of cultivation. It may be that routine use of drags or dredges would prevent the establishment of eel-grass on active oyster beds. Toothed harrows and mechanical harvesters or the type used in clam harvesting have been used to reclaim beds from eel-grass infestation. Soft ground and eel-grass have been remedied by covering the bottom with plastic sheets, tar paper or with gravel or shell to a thickness of six inches (7). Such modifications today could involve the various agencies having jurisdiction for environmental quality and use of the subtidal areas. An alga, Codium fragile, present in Boothbay Harbor commonly attaches to oysters grown in shallow water. It is so abundant in waters south of Cape Cod that considerable effort must be made to free oysters of it before they can be sold. Shell perforating algae seem common in Maine scallops from shallow beds. Shells so infected are weakened and discolored. Although shell perforating algae have been found in oysters (3) they have not had a significant impact in oyster growing areas. Species of these algae likely to be found in Maine oysters include Endocladia testarum and Gomontia polyrhiza. -5-

PROBLEM FAUNA Organisms troublesome to oysters cultured on the bottom as the practice is anticipated in Maine, will be found subtidally. The primary predator is the starfish or fivefinger, Asterias forbesii, A. vulgaris. Starfish do not travel far or fast under their own power: exceptional (7). 20 yards in summer is normal, 200 yards is They have been seen drifting with tidal currents (3). Feeding is minimal below 5 C, i.e. January to April. The size of eastern oysters overwhelmed is approximately two thirds the diameter of the starfish. Bedding size oysters, 1 1/2-2 1/2 inches, should survive attacks of starfish of the size most commonly found in shallow bays. If a bed and some area around the planted area is cleaned before planting, there should be little incursion of starfish of significant size. Young starfish settle on the bottom from their planktonic stage in mid-summer at a time when young mussels have settled from their planktonic stage. Since the mussels are a severe problem to the oyster grower, it is well to let the young starfish consume the newly set mussels. As the starfish grow and consume larger mussels as they too grow during the summer, they reach a size at the end of the summer at which they may become a threat to bedded oysters. Starfish diminish in numbers as the summer passes. Starfish predators are sunstars, Solaster; toad crabs, Hyas, possibly other crabs and tautogs. If starfish become a threat they may be killed by spreading lime at 500 to 1,000 pounds or up to a ton per acre. The lime kills the starfish but does not harm fish or oysters. Or starfish may be collected by means of large, cotton, dredge-like mops constructed for this purpose. Starfish collected may be dried on the shore, immersed in fresh water, -6-

hot water or brine to kill them (4,7). Of the several snails on the Maine coast that can bore small holes thorugh the shells of other mollusks and kill them, only the oyster drill, Urosalpinx, appears to be a potentially serious predator. It occurs the length of the Maine coast. Its distribution is patchy even within the bays where it is present. It may be possible to avoid drills by carefully selecting the planting sites (7). They are more apt to be found on hard clean bottoms than silty, muddy bottoms. They may travel 25 feet in one day (3). The drill is the most dangerous and most widely distributed of all oyster predators in Europe (3). From Cape Cod south, two- thirds or more of the newly set oysters in a year may commonly be destroyed by the drills. Drills may be trapped by placing nine-inch square tiles covered with barnacles in the culture area. The barnacle-covered tiles may be lifted every day or two by means of an eye cemented in the center. J. C. Hammond, a Cape Cod oyster grower, has caught as many as 450 drills on one tile. Mussels may be added to oyster beds if some predators become too numerous. This is one practice on Cape Cod where channeled whelks, Busycon canaliculaturn, are a problem. The whelk may be a threat in western Maine waters. A very small, quarter inch, conically shaped snail, Odostomia, may be locally abundant. Several of those may perch at the edge of the oyster's shell and nibble away at the edge of the oyster's mantle or soft parts. The effect is to weaken the oyster, stunt growth and change shell shape (3,4,6). -7-

The green crab is a serious predator of small oysters in Europe; it also eats blue mussels and clams. in western Maine, sporadic in eastern Maine. It is very abundant If oysters are small and mussels are few, the crabs may be a problem. One to two inch oysters have survived well in subtidal areas where crabs are numerous and where, in the intertidal areas of the same cove, green crabs have been a significant predator. In France, culture areas are fenced to keep out the crabs and crab traps inside the fences catch those that have passed the fence. A half inch long flat worm, Stylochus ellipticus, present on Maine s coast is known to prey on young oysters. Other members of the genus have occasionally been reported to destroy 30 to 40 percent of cultured oysters in regions of Puget Sound and Florida. Yellow boring sponges, Cliona, have rarely been a serious threat to oyster industries. They make small holes in the shell of live shellfish as well as in dead shell. A shell riddled with boring sponge holes is difficult to open properly. The sponge discolors the meat inside the shell; and if infected shells are shipped or stored, the oysters quickly spoil and contaminate other oysters. Infested oysters may be dipped in brine; dead shells harboring the sponge sould be dredged and removed from the culture areas. A small ciliated marine worm that lives on and in the shells of oysters makes small holes in the shell and causes unsightly black "blisters" to form on the inside. This blister worm, Polydora, is more common on soft bottoms than hard bottoms. Flat oysters in Roothbay Harbor are commonly riddled with holes made by -8-

these worms. If oysters are transplanted to hard bottoms, growers report that the conditions can be remedied in about a year. Several organisms may attach to oyster shells and by their presence and abundance inhibit growth and reduce marketability or increase the cost of preparation for market. Barnacles and sea graps, Molgula, and Botryllus may be only a seasonal problem or may require some attention to remove them from the oysters. Dredging grounds so infested with a dredge whose blade is wound with barbed-wire is said (7) to kill these animals by damaging the shell. Blue mussels setting among oysters bind them together with their elastic fibers and compete with them for food and space. Heavy infestations of mussels will smother and kill quantities of oysters. Oysters cannot be cultivated where mussels are abundant (7). Another competitor for space and food is the slipper limpet or boat shell, Crepidula. These have become so numerous on some neglected beds that they smother the oysters, as the blue mussels do, with the sediment they deposit. They are a serious pest in Britain. They are not prominent in accounts of Maritime oyster practices and are seldom a nuisance to oyster growers in New England and Chesapeake Bay. They are common in Maine, but may not be numerous enough to pose a threat. Mussels and slipper limpets are preferred by starfish to oysters. Salvage of oyster beds infested with mussels and slipper limpets may be accomplished by dredging. In southern New England, hydraulic dredges are used to remove all loose material from oyster beds prior to planting; predators are killed and dumped in deep water. Polyethylene sheeting may be used to smother mussels and -9-

other competitors. This is an extremely unwieldly operation if attempted under water. In summary Maine is between two areas with considerable historical experience in bottom oyster culture. The significant predators of one area in some cases have never been a problem in the other. In addition, the oyster we are considering has different requirements from the oyster cultured in the Maritimes and southern New England. Oyster bottom culture in Maine, particularly culture of the flat oyster, is a new experience; but forewarned, one may more quickly and effectively respond to threatening situations. -10-

In addition to the specific references cited, much of the material contained here was derived from conversations with Mr. Ken Campbell, Prince Edward Island Department of Fisheries; Mr. Warren Landers, National Marine Fisheries Service, Milford, Connecticut; Mr. Roy E. Drinnan, Cape Breton Development Corporation; Dr. J. Carl Medcof, Fisheries Research Board of Canada, retired; Mr. J. Richard Nelson, Long Island Oyster Farms; Mr. Richard C. Nelson, Cotuit Oyster Company; Mr. J. C. Hammond, Chatham, Massachusetts. -11-

SELECTED REFERENCES 1. Bailey, Robert S. 1958. Let's be oyster farmers. Educational Series No. 8. Virginia Institute of Marine Science, Gloucester Point, Virginia. 72 pages. 2. Cole, H. A. 1956. Oyster cultivation in Britain, a manual of current practice. Her Majesty's Stationery Office, London. 43 pages. 3. Galtsoff, Paul S. 1964. The American oyster, Crassostrea virginica Gmelin. U.S. Department of Commerce, Fishery Bulletin 64. 480 pages. 4. Hancock, D. A. 1974. Oyster pests and their control. Laboratory Leaflet No. 19. Fisheries Laboratory, Burnham on Crouch, Essex. 30 pages. 5. Key, D. and D. J. Alderman. 1974. A bibliography of diseases of commercial bivalves (supplementary to Sinderman 1968), with annotations upon recent European work. Fisheries Laboratory Technical Report Series No. 11. Fisheries Laboratory, Loestoft, Suffolk. 35 pages. 6. Larsen, Peter F. 1975. A preliminary checklist, with annotations, of potential associates of the American oyster, Crassostrea virginica, in New England. Publication No. 9. TRIGOM Publications, South Portland, Maine. 42 pages. 7. Medcof, J. C. 1961. Oyster farming in the Maritimes. Bulletin No. 131. Fisheries and Marine Service, Environment Canada. 158 pages. 8. Perkins, Lee F. and Peter F. Larsen 1975. A preliminary checklist of the invertebrate marine and estuarine invertebrates of Maine. TRIGOM Publication No. 10. TRIGOM Publications, South Portland, Maine. 37 pages. 9. Yonge, C. M. 1960. Oysters. Collins, London. 209 pages. -12-