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Marine Bivalve Mollusks asReservoirs of Viral Finfish Pathogens:
Significance to Marine and Anadromous Finfish Aquaculture
THEODORE R. MEYERS
Introduction
Epidemiologists have long knownthat bivalve mollusks are capable ofharboring disease agents significant tohuman health. The mollusks accomplish this phenomenon by filterfeeding, whereby seawater is pumpedin through the gills which entraplarger planktonic food organismswithin the cilia and mucus of therespiratory epithelium (Purchon,1977). As a result, these mollusks alsotake in smaller incidental particles including bacteria and viruses suspended in ambient seawater or adsorbedonto the surfaces of organic and inorganic solids.
Consequently, human pathogensincluding coliform and Vibrio speciesof bacteria as well as polio andhepatitis viruses have been detected inbivalve species from clean and organically polluted waters (Ross, 1956;Mitchell et aI., 1966; Hamblet et al.,1967; Liu et aI., 1967; Lovelace et aI.,1968; Kampelmacher et al., 1972;Ayres, 1975; Thompson and Vanderzant, 1976). Disease outbreaks causedby some of these agents have occurredin the human populace following in-
ABSTRACT-Filter-feeding bivalvemollusks can bioaccumulate variousdisease agents significant in the management ofpublic health. Recent evidence hasindicated that marine bivalves can harborviruses that are virulent for salmonidspecies. Examples offinfish viruses occurring in shellfISh tissues and those that havepotential of occurring are presented.
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gestion of poorly cooked or rawshellfish from contaminated areas(Mason and McLean, 1962; Liu et aI.,1967; Sakazaki, 1969.
Recent evidence has shown thatmarine shellfish are potential reservoirs for certain finfish pathogensthrough the same bioaccumulationprocess of filter feeding. This information has some significance whenconsidering finfish disease epizootiology in both marine andfreshwater finfish rearing systemshaving bivalve mollusks directly in thewater supply or immediately downstream. Any epizootic occurringwithin a finfish population can resultin the release of high concentrationsof the pathogen into ambient waterfrom dead or dying fish. As an example, infectious hematopoietic necrosisvirus (IHNV) in hatchery effluentsduring acute disease outbreaks hasbeen reported at levels as high as 400p.f.u./ml (Leong and Turner, 1979).
Recorded epizootics in feral finfishpopulations, though uncommonwhen fish are normally dispersed,become more evident when fish areconcentrated in smaller areas as occurs during periods of spawning or
Participation of shellfish in theepizootiology of endemic and/or exoticfinfISh diseases is possible and should beconsidered for future management offishhealth. To reduce potential introductionsoffinfISh disease agents which may be incidental in shellfish tissues, certification ofbivalve stocks is advised before movementinto new waters.
smolt outmigration. As much as 1,600p.f.u./ml of IHNV has been reportedin fresh water near spawning sockeyesalmon, Oncorhynchus nerka,(Mulcahy et aI., 1983). Nearbyshellfish beds filtering water contaminated by diseased finfish, wouldbe capable of entrapping the causativedisease agent. Filter feeding shellfishcan accumulate viruses and bacteriawithin their tissues at much higherconcentrations than present in surrounding seatwater (Mitchell et aI.,1966).
The actual concentration in thetissues is dependent upon: The rate atwhich bivalves pump water throughthe gills; the concentration andphysical characteristics of the microbein the ambient seawater; and seawatertemperature, salinity, and turbidity(Galtsoff, 1964; Hamblet et aI., 1967;Liu et aI., 1967). Eventually, incidental contaminants are depurated or expelled from the tissues back into theseawater. This virus or contaminantloss occurs over a period of time andis called the depuration rate. This rateis enhanced by exposure of theshellfish to waters free of the contaminant and is proportional to the degreeof tissue contamination.
Other factors influencing thedepuration rate are the same as thosedescribed for bioaccumulation (Liu etaI., 1967). Consequently, depuration
Theodore R. Meyers is Assistant Professor ofFisheries, School of Fisheries and Science,University of Alaska, Juneau, 11120 GlacierHighway, Juneau, AI( 99801. Views or opinionsexpressed or implied are those of the author anddo not necessarily reflect the position of the National Marine Fisheries Service, NOAA.
Marine Fisheries Review
and bioaccumulation rates for a givencontaminant vary among species ofbivalve and within a species depending upon animal size and environmental parameters influencing animalphysiology. Hard clams, Mercenariamercenaria can depurate human poliovirus type I within 96 hours if placedin clean seawater at l3-15°C (Liu etaI., 1967). However, after 40-60 daysthe European flat oyster, Ostreaedulis, still cannot completelydepurate certain strains of molluscanlPN viruses, some of which arepathogenic to finfish (Hill and Alderman, 1977; Hill et aI., 1982).
Whether a depurated disease agentremains infectious for its natural hostdepends upon its stability within theenvironment outside normal hosttissues. It is highly probable that bedsof filter feeding shellfish contaminated with a stable, viable finfishpathogen could disseminate waterborne infectious particles to other finfish hosts during depuration.
The following discussion presentsexamples of finfish pathogens actually isolated from bivalve mollusks andothers which have potential for bioaccumulation in shellfish tissues. Theseagents are all viruses which can infectsalmonid fishes and at least one centrarchid species. However, other finfish species may also be susceptible tosome of these viral agents. There arebacterial agents (Vibrio sp., etc.) common to bivalve tissues which arepathogenic for both finfish and othershellfish, but these will not be included herein (Tubiash et aI., 1965, 1970;Lovelace et aI., 1968; DiSalvo et aI.,1978; Leibovitz, 1978; Garland et aI.,1983).
Viral Finfish PathogensIsolated From Bivalves
13pz Reovirus
A new serotype of reovirus wasisolated from juvenile Americanoysters, Crassostrea virginica, held inrearing facilities of two differentLong Island, N.Y., shellfish hatcheries (Meyers, 1979; Meyers andHirai, 1980). The virus, designated as
46(3)
13pz, is very stable, remaining viablein both seawater or oyster tissues forlonger than 60 days (Meyers, 1980). Itdoes not replicate in oyster tissues butis infectious for various fish cell linesand for at least two finfish species.
The virus produces a 44 percentmortality in bluegill, Lepomismacrochirus, fingerlings causingsevere necrotic hepatitis (Meyers,1980). It also produces chronic selflimiting granulomatous hepatitis andoccasional pancreatitis in adult andfingerling rainbow trout, Salmogairdneri (Meyers, 1983). Thus, forrainbow trout, 13pz is weakly virulentfor the age classes tested, but its effecton sac fry or on other salmonidspecies has not been examined. Insalmonid aquaculture, this virus maynot be significant as a primarypathogen but would contribute toundesirable stress and lowered hostresistance to other biological or environmental pressures affecting fishsurvival.
JOV-l
A second reovirus-like agent, labeled JOV-l, has been isolated fromJapanese oysters, C. gigas, reared in aJapanese hatchery (Nagabayashi andMori I). Little information is yetavailable, but apparently the virus isinfectious for lO-week-old rainbowtrout, producing a 40 percent mortality in infected fish. Fifteen-week-oldtrout are reported refractory toclinical disease.
IPN MoUuscabirnaviruses
Infectious pancreatic necrosis virus(IPNV) was first islated from brooktrout, Salvelinus jontinalis (Snieszkoet aI., 1957), and has traditionallycaused disease in juvenile salmonids.However, other nonsalmonid strainsof lPNV have recently been isolatedfrom many other freshwater andmarine finfish species as reviewed byHill (1982). Many of these newisolates are not responsible for clinical
'Nagabayashi T., and S. Mori. 1983. XVI Annual Meeting of the Society for InvertebratePathology, Cornell Univ., Ithaca, N.Y. Unpub!. abstr.
disease in their respective hosts andare variable in their infectivity andvirulence for rainbow trout (Hill,1982). Included among these nonsalmonid IPN viruses are strainswhich have been isolated from severalspecies of marine bivalves, two speciesof gastropod, and one decapodcrustacean (Hill, 1976a, b; Hill,1982). Such isolates are nearly allbiochemically, biophysically, andserologically (three exceptions represent different serotypes) indistinguishable from reference strains ofIPNV in fish. At least eight of theseshellfish isolates are pathogenic inrainbow trout fry producing typicalclinical signs of IPN disease and frymortality (Hill, 1982). Definitiveevidence is still lacking to substantiatewhether such molluscan IPN virusescan replicate in shellfish tissues or aremerely bioaccumualted contaminants.Regardless of this final determination, the confirmed pathogenicity ofthese viruses for rainbow trout andtheir prolonged stability in shellfishtissues (~50 days; Hill and Alderman, 1977) make them significantdisease agents to be considered in themanagement of anadromous salmonid health.
Viral Finfish PathogensHaving Potential To
Occur in Bivalves
There are other viral finfishpathogens which have prolongedviability within the natural environment and could potentially accumulate in nearby mollusk tissues ifreleased from clinically diseased orcarrier fish.
CSV
The chum salmon virus (CSV) isanother recently discovered reovirussimilar in many respects to the 13pzagent. However, CSV is a differentvirus (WintonZ
) which was isolated
'Winton, J. R. 1984. Department ofMicrobiology, Oregon State University MarineScience Center, Newport, Oreg. Unpub!. data.
15
from spawning chum salmon, Oncorhynchus keta, caught in Japan.This virus can infect chum, chinook,0. tshawytscha; and kokanee, 0.nerka, salmon fingerlings, producinga self-limiting necrotic hepatitis (Winton et al., 1981). As with the 13p2agent, CSV remains viable for monthsoutside fish host cells. Thus, it couldpotentially accumulate in filterfeeding bivalve reservoirs near diseased fish hosts. This virus could besignificant in salmonid husbandry if itcaused similar host debilitation asdiscussed for the 13P2 agent.
IHNV
Infectious hematopoietic necrosisvirus (IHNV) is an extremely virulentpathogen of juvenile salmonids inwestern North America. Consequently, this rhabdovirus is particularly important to Pacific salmon, Oncorhynchus spp., and steelhead, S. gairdneri,husbandry in the Pacific Northwestand Alaska (Grischkowsky, 1981;Groberg et al., 1982, Groberg, 1983;Rohovec, 1983). Whether IHNVcould accumuJate in filter feedingmollusks is speculative, but physicallyand biologically possible.
It is clear that IHN virus can remain infectious for several months infreshwater rivers (Wedemeyer et al.,1978; Mulcahy et al., 1983), and recent laboratory studies indicate detectable levels of virus after 27 and 22days in estuarine and saltwaters,respectively (Toranzo and Hetrick1982). It becomes conceivable thathigh concentrations of IHNV shed byinfected spawning salmon or outmigrating clinically diseased smoltscould accumulate in marine bivalvemollusks located directly below shortstream systems. Shellfish could thenparticipate in waterborne transmission of the virus for a period of timeduring the depuration process.Although considerable dilution ofvirus concentrations would be involved, evidence suggests that low levelsof infectious particles may be sufficient for transmission of the disease(Mulcahy et aI., 1983).
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Salmonid IPNPiscibirnaviruses
Although infectious for salmonids,IPN molluscan birnaviruses are lessvirulent than the true salmonidstrains. However, these true salmonidstrains are also capable of survivingfor long periods of time in fresh,estuarine, and saltwaters (Ahne, 1982;Wedemeyer et al., 1978; Toranzo andHetrick, 1982). Consequently, theyare stable enough in the environmentto make possible their bioaccumulation and later dissemination by filterfeeding mollusks.
Conclusions
Marine bivalve mollusks are unavoidable in estuarine and salt waterswhich may be used in the rearing ofanadromous fishes or which may bedirectly downstream of freshwater eggand fry facilities operating on shortwatersheds. No less abundant are themany freshwater species of filterfeeding clams and mussels whichpopulate certain stream and lake bottoms around the world. The established occurrence of certain viral finfishpathogens in common species ofmarine bivalve mollusks indicates thatshellfish could serve two roles in theepizootiology of these disease agents,and possibly others: 1) Shellfish maybe seasonal reservoirs for someendemic finfish pathogens originatingfrom finfish epizootics and/or fromsubclinically diseased "carrier fish"; 2)shellfish could introduce exotic finfishdiseases when transported to otherwaters for commercial or experimental purposes from areas where suchagents may be endemic.
In terms of practical fisherymanagement, there is little that couldbe done about involvement of marinebivalve mollusks in endemic finfishdisease epizootiology. However, realization of their potential as diseasereservoirs would add a new dimensionto the future investigation of certainfinfish disease outbreaks.
Conversely, there are obvious prophylactic measures for reducing thepossible dissemination of exotic finfish diseases by shellfish introductions
into "new" waters. Specific invertebrate diseases, particularly those affecting commercially importantmarine bivalve mollusks, are becoming increasingly important regardingtheir geographic containment andcontrol. This concept is emphasizedby a growing recognition for the importance of health certification of imported and exported shellfish species(Rosenfield and Kern, 1978; Elston,1981; Elston3). Consequently, if certification procedures are exercised forshellfish pathogens, some additionaleffort made in screening mollusktissues for incidental viral finfishpathogens would provide significantprotection against the introduction ofthese agents by movement of shellfishstocks.
Literature Cited
Ahne, w. 1982. Comparative studies on thestability of four fish-pathogenic viruses(VHSV, PFR, SVCV, IPNV). Zentralbl. Vet.Med. B 29:457-476.
Ayres, P. A. 1975. The quantitative bacteriology of some commercial bivalve shellfishentering British markets. J. Hyg., Cam.74:431-440.
DiSalvo, L. H., J. Blecka, and R. Zebal. 1978.Vibrio anguillarum and larval mortality in aCalifornia coastal shellfish hatchery. Appl.Environ. Microbiol. 35:219-221.
Elston, R. 1981. Discussion of shellfish certification issues. Aquaculture 7(4): 28-33.
Galtsoff, P. S. 1964. The American oyster,Crassoslrea virginica Gmelin. U.S. Fish.Wildl. Serv., Fish. Bull. 64:1-4.
Garland, C. D., G. V. Nash, C. E. Sumner,and T. A. McMeekin. 1983. Bacterialpathogens of oyster larvae (Crassoslrea gigas)in a Tasmanian hatchery. Aust. J. Mar.Freshwater Res. 34:483-487.
Grischkowsky, R. S. 1981. Infectious hematopoietic necrosis virus. In R. A. Dieterich(editor), Alaskan wildlife diseases, p.339-348. Univ. Alaska, Fairbanks.
Groberg, W. J., J r. 1983. The status of viralfish diseases in the Columbia River Basin.Proc. Viral Dis. Salmonid Fish ColumbiaRiver Basin Workshop. Bonneville PowerAdmin., Portland, Oreg.
____, R. P. Hedrick, and J. L. Fryer.1982. Viral diseases of salmonid fish inOregon. In B. R. Melteff and R. A. Neve(editors), Proc. North Pac. Aquaculture
3Elston, R. Pathology and health certificationcriteria of the Japanese scallop, Palinopeclenyessoensis: A case history and model approach.Manuscr. Battelle, Pacific Northwest Division,Marine Research Laboratory, 439 West SequimBay Rd., Sequim, WA 98382.
Marine Fisheries Review
Symp., Alaska Sea Grant Rep. 82-2, p.345-357.
Hamblet, F. E., W. F. Hill, Jr., E. W. Akin,and W. H. Benton. 1%7. Effect of turbidityon the rate of accumulation and eliminationof poliovirus type I by the eastern oyster(Crassostrea virginica). In Proc. Gulf S. Atl.Shellfish Sanit. Res. Conf., N.H.S., p. 13-23.
Hill, B. J. 1976a. Properties of a virusisolated from the bivalve mollusc Tel/inatenuis (da Costa). In L. A. Page (editor),Wildlife diseases, p. 445-452. Plenum Press,N.Y.
____. 1976b. Molluscan viruses: Theiroccurrence, culture and relationships. InProc. 1st Int. Colloq. Invertebr. PathoI. , p.25-29. Kingston, Ont.
_-,-__.1982. Infectious pancreatic necrosisvirus and its virulence. In R. J. Roberts(editor), Microbial diseases of fish, p. 91-114.Academic Press, N.Y.
-----:::-:-__, and D. J. Alderman. 1977.Observations on the experimental infection ofOstrea edu/is with two molluscan viruses.Haliotis 8:297-299.
_---,--,-__, K. Way, and D. J. Alderman.1982. Further investigations into thepathogenicity of lPN-like viruses for oysters.In Proc. III Int. Colloq. Invertebr. Pathol.,p.273-274.
Kampelmacher, E. H., L. M. vanNoorleJansen, D. A. Mossel, and F. J. Groen. 1972.A survey of the occurrence of Vibrioparahaemo/yticus and V. a/gino/yticus onmussels and oysters and in estuarine waters inthe Netherlands. J. Appl. Bacteriol.35:431-438.
Leibovitz, L. 1978. A study of vibriosis ata Long Island shellfish hatchery. New YorkSea Grant Reprint Series. NYSG-PR-79-Q2.N.Y. Sea Grant Inst., Albany.
Leong, J., and S. Turner. 1979. Isolation ofwaterborne infectious hematopoietic necrosisvirus. Fish Health News 8:vi-viii.
46(3)
Liu, O. c., H. R. Seraichekas, and B. L.Murphy. 1%7. Viral depuration of the northern quahaug. Appl. Microbiol. 15:307-315.
Lovelace, T. E., H. Tubiash, and R. R.Colwell. 1968. Quantitative and qualitativecommensal bacterial flora of Crassostreavirginica in Chesapeake Bay. Proc. Natl.Shellfish. Assoc. 58:82-87.
Mason, J. 0., and W. R. McLean. 1962.Infectious hepatitis traced to the consumptionof raw oysters. Am. J. Hyg. 75:90-111.
Meyers, T. R. 1979. A reo-like virus isolatedfrom juvenile American oysters (Crassostreavirginica). J. Gen. Virol. 43:203-212.
_---::-__. 1980. Experimental pathogenicityof reovirus I3p, for juvenile Americanoysters Crassostrea virginica (Gmelin) andbluegill fingerlings Lepomis macrochirus(Rafinesque). J. Fish Dis. 3:187-201.
_-----:----;-_. 1983. Serological and histopathological responses of rainbow trout,Sa/mo gairdneri Richardson, to experimentalinfection with the I3p, reovirus. J. Fish Dis.6:277-292.
____, and K. Hirai. 1980. Morphology ofa reo-like virus from juvenile Americanoysters (Crassostrea virginica). J. Gen. Virol.46:249-253.
Mitchell, J. R., M. W. Presnell, E. W. Akin,J. M. Cummins, and O. C. Liu. 1966. Accumulation and elimination of poliovirus bythe eastern oyster. Am. J. Epidemiol.86:40-50.
Mulcahy, D., R. J. Pascho, and C. K. Jenes.1983. Detection of infectious haematopoieticnecrosis virus in river water and demonstration of waterborne transmission. J. Fish Dis.6:321-330.
Purchon, R. D. 1977. The biology of themollusca, 2nd ed. Pergamon Press, Oxf., 596p.
Rohovec, J. S. 1983. Current fish disease control policies affecting the Columbia RiverBasin. Proc. Viral Dis. Salmonid Fish Col-
umbia River Basin Workshop. BonnevillePower Admin., Portland, Oreg.
Rosenfield, A., and F. G. Kern. 1978.Molluscan imports and the potential for introduction of disease oganisms. In R. Mann(editor), Exotic species in mariculture, p.165-183. MIT Press, Cam., Mass.
Ross, B. 1956. Hepatitis epidemic conveyed byoysters. Sven. Larkartidn 53:989-1003.
Sakazaki, R. 1969. Halophilic Vibrio infections.In H. Riemann (editor), Food-borne infections and intoxications, p. 115. Acad. Press,N.Y.
Snieszko, S. F., E. M. Wood, and W. T.Yasutake. 1957. Infectious pancreaticnecrosis in trout. Am. Med. Assoc. Arch.PathoI. 63:229-233.
Thompson, C. A., and C. Vanderzant. 1976.Relationship of Vibrio parahemo/yticus inoysters, water and sediment, andbacteriological and environmental indices. J.Food Sci. 41:117-122.
Toranzo, A. E., and F. M. Hetrick. 1982. Comparative stability of two salmonid viruses andpoliovirus in fresh, estuarine and marinewaters. J. Fish Dis. 5:223-231.
Tubiash, H. S., P. E. Chanley, and E. Leifson.1965. Bacillary necrosis, a disease of larvaland juvenile bivalve molluscs. J. Bacteriol.90: 1036-1044.
-c::-::-:-:---:-' R. R. Colwell, and R. Sakazaki.1970. Marine vibrios associated with bacillarynecrosis, a disease of larval and juvenilebivalve mollusks. J. Bacteriol. 103:271-272.
Wedemeyer, G. A., N. C. Nelson, and C. A.Smith. 1978. Survival of the salmonid virusesinfectious hematopoietic necrosis (IHNV)and infectious pancreatic necrosis (IPNV) inozonated, chlorinated and untreated water. J.Fish Res. Board Can. 35:875-879.
Winton, J. R., C. N. Lannon, J. L. Fryer,and T. Kimura. 1981. Isolation of a newreovirus from chum salmon in Japan. FishPathol. 15: 155-162.
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