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Glycogen Concentration in the Mantle Tissue of Freshwater Mussels (Bivalvia : Unionidae) During Starvation and Controlled Feeding PDF

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Preview Glycogen Concentration in the Mantle Tissue of Freshwater Mussels (Bivalvia : Unionidae) During Starvation and Controlled Feeding

Glycogen concentration in the mantle tissue of freshwater mussels (Bivalvia: Unionidae) during starvation and controlled feeding Matthew A. Patterson1, Bruce C. Parker1, and Richard J. Neves2 1 DepartmentofBiology, VirginiaPolytechnic InstituteandState University,Blacksburg,Virginia24061,U. S. A. 2VirginiaCooperativeFish andWildlifeResearch Unit, DepartmentofFisheriesandWildlifeSciences, VirginiaPolytechnic Institute and StateUniversity, Blacksburg, Virginia 24061, U. S. A. Abstract: The effects ofcontrolled feeding versus starvation during quarantine on mantle tissue glycogen concentration (represented as milligrams glycogenpergramofmantletissue±SD)oftwofreshwatermussel species were compared. Starvedindividuals were notprovided with supplemental food duringquarantine,whilefedspecimenswereprovidedwith 105algalcells/ml,twiceperday. InitialmeanglycogenlevelsforAmblema plicata (Say, 1817) (9.4±2.4mg/g)andQuadrula pustulosa (I.Lea, 1831)(7.9± 1.8mg/g)collectedfromOhioRiverMile(ORM) 175.5inJuly 1997 were notsignificantly different(p>0.3) frommean glycogen levels ofA.plicata (8.1 ±4.2 mg/g) and Q.pustulosa (6.2±2.9 mg/g) collected fromthe same site inJuly 1996. Initialglycogenconcentrationsofquarantinedmussels, therefore, weresimilarinboththestarvedandfedgroups. Aftersevendaysoffeedinginquarantine, meanglycogenlevelsofA.plicata (12.3±2.3mg/g)andQ.pustulosa (7.1 ±3.7 mg/g)didnotchangesignificantly(p>0.1)relativetowild-caughtspeci- mens,andweresignificantlylarger(p<0.05)thanmeanglycogenlevelsofstarvedindividuals(3.6± 1.8mg/gand3.5±2.3 mg/g,respectively). Similarly, meanglycogenlevelsofA.plicata and Q.pustulosa after 14days(8.1 ±3.3 mg/gand7.7±3.3mg/g, respectively)and30days(9.9±4.8 mg/gand 8.4± 2.7 mg/g,respectively)offeeding weresignificantly larger(p<0.01)than meanglycogen levels ofstarvedspecimens after 14days (3.27± 1.74mg/gand 5.37 +3.06 mg/g, respectively) and 30 days (1.2 ± 0.5 mg/g and 1.9 ± 1.4 mg/g, respectively). Adequate feedingofunionids in quarantine is essential to maintainanimalsinaconditionthatwillincreasethelikelihoodofsurvivalfollowingrelocation. Key Words: glycogen, zebramussels,OhioRiver,quarantine,Dreissenidae Relocation has been used widely as a management relocation. tool to re-establish or assist in the recovery of declining Condition, as defined by Mann (1978: 490), is the populations ofterrestrial and aquatic organisms (Griffith et "ability ofan animal to withstand an adverse environmental al, 1989; Cope and Waller, 1995). In response to recent stress, be this physical, chemical or biological." Glycogen declines in the unionid fauna of North America (Williams is the primary energy store in bivalves (Bayne, 1976; et al, 1993), relocation is being tested as a management Gabbott, 1983), and the relative amount ofglycogen stored technique to (1) re-introduce extirpated populations, (2) in bivalve tissues is considered a good indicator of body remove unionids from project construction zones, (3) aug- condition (Galtsoff, 1964; Walne, 1970). Significant reduc- ment populations to increase genetic diversity, and (4) sal- tions in unionid glycogen stores prior to and during reloca- vage unionids from zebra mussel-infested areas (Cope and tion, therefore, could greatly reduce their ability to cope Waller, 1995). The ultimate goal ofany relocation projectis with natural stressors present in the new environment. to establish a self-sustaining population ofthe target organ- Collection, handling, aerial exposure, abrupt tem- ism, and several authors have developed a list of factors perature changes, holding, and transport ofunionids during that should extend population persistence after relocation, relocation can result in varying degrees ofstress, depending including (1) the presence of suitable habitat and refugia, on the length ofexposure, that can in turn adversely affect (2) the release of large founder groups with high genetic body condition (Cope and Waller, 1995). Relocation of diversity, (3) low levels of competition, and (4) high rates unionids to avoid the adverse effects ofbridge construction, of population growth (Griffith et al, 1989; Cope and for example, could have little or no effect on condition if Waller, 1995). Little attention, however, has been given to individual specimens are removed from their natural habitat the biochemical andphysiological condition ofan organism for short time periods (several hours or days). The presence priortorelocation and its influence on survival and the abil- of zebra mussels, however, has been shown to cause ity to develop reproductively viable populations after decreased glycogen reserves in unionids (Haag et al., AmericanMalacologicalBulletin,Vol. 15(1)(1999):47-50 47 48 AMER. MALAC. BULL. 15(1) (1999) 1993). In addition, zebra mussel-infested unionids presently tures of N. oleoabundans were grown in Bold's Basal require a 30-day quarantine period to ensure that zebra Medium (Nichols, 1973) under continuous cool white fluo- mussel adults andjuveniles are removed prior to relocation rescent light (photon flux: 60-100 uE/m2/s) at 20°C. Stock (J. Clayton, pers. comm.). In addition to the stress ofrelo- cultures were then transferred to the quarantine facility and cation, unionids can experience nutritive stress in quaran- used to inoculate a 20 1 carboy containing Fritz F2 algal tine because little or no information exists on their nutri- medium (Fritz Aquaculture, Mesquite, Texas). When cell tional requirements (Gatenby et al., 1997). Under laborato- densities in the carboy reached 106 cells/ml, 7 1 aliquots ry or hatchery conditions, bivalve energy stores have been were used to inoculate three 250 1 algal culture tanks shown to decline without proper feeding (Calvin, 1931; (Aquatic Ecosystems, Inc., Apopka, Florida), thatalso were Pora etai, 1969; Bayne and Thompson, 1970; Gabbott and fertilized with Fritz F2 algal medium, aerated, and placed Walker, 1971), and recent studies reveal that unionid glyco- outside the quarantine facility in direct sunlight. Culture gen stores can decline as much as 80% after only 30 days tanks were placed outside because algal cultures continual- of starvation in quarantine (Patterson et al., 1997). ly failed inside the quarantine facility, possibly due to Consequently, the development of a feeding regime for insufficient light or high water temperatures. Algal cell mussels held in quarantine could be a critical link in the densities in the 250 1 culture tanks reached 106 cells/ml in success of future relocation projects. The objectives ofthis ca. 4 days. Water samples from the culture tanks were col- experiment were to (1) monitor the glycogen levels of lected daily and fixed with acid Lugol's solution (Saraceni unionids during controlled feeding in quarantine, and (2) and Ruggiu, 1969) forenumeration and identification ofthe compare these results to reported changes in unionid glyco- algae. Water samples from the Ohio River in 1996 and gen levels during starvation in quarantine, as reported by 1997 showed that algal cell densities ranged from 104 Patterson etal. (1997). - 105/cells/ml during the summer (Parker etai, 1998), thus unionids in quarantine were fed ca. 10 cells/ml twice per day, at 8:00 AM and 5:00 PM. Each day, 75% ofthe water METHODS in the quarantine tanks was drained; fresh water and food were added, and vigorous aeration was applied to maintain On 20 July 1997, ten specimens each of Amblema algal cells in suspension. plicata (Say, 1817) and Quadrula pustulosa (I. Lea, The glycogen content of all preserved specimens 1831) were collected from Ohio River Mile (ORM) 175.5 was determined from mantle tissue using the technique of near Parkersburg, West Virginia. Mussels were removed Keppler and Decker (1974) as described in Patterson et al. from the shell and placed in 95% ethanol forthe determina- (1997). Mean glycogen levels were expressed in milligrams tion of initial glycogen levels. Additional specimens ofA. ofglycogen per gram ofpreserved mantle tissue ± standard plicata and Q. pustulosa (N = 200 and 80, respectively) deviation (SD). It should be noted that preserved tissue ORM were collected from 175.5 for placement in individ- weights overestimate dry weights and underestimate wet ual quarantine tanks. Unionids salvaged from zebra mussel- tissue weights because 95% ethanol dehydrates tissue. infested waters were thoroughly scrubbed to remove zebra Dehydration by 95% ethanol also reduces error that can mussels. Cleaned unionids were then hand-inspected before result from changes in tissue water levels during stress. being placed in aerated quarantine tanks without substra- Mean glycogen levels were compared using ANOVA and, tum for a minimum of 30 days. During this 30-day period, if significant differences were detected, the Scheffe F-test water temperatures were maintained around 20°C to allow was used to determine the statistical significance ofindivid- juvenile zebra mussels missed during the scrubbing proce- ual treatments. dure to become visible. At the end of 30 days, individual unionids were inspected under 10X magnification to ensure the absence ofzebra mussels prior to relocation. Ten speci- RESULTS AND DISCUSSION mens of A. plicata and Q. pustulosa were sacrificed after seven, 14, and 30 days ofquarantine, and preserved in 95% During the first 14 d of quarantine, Neochloris ethanol for subsequent glycogen analysis. After the experi- oleoabundans comprised > 95% of the algae in the 250-1 ment, all remaining specimens were returned to the Ohio culture containers. Because culture tanks were maintained River. outside the quarantine facility, cultures were contaminated In 1997, unionids were fed cultures of the chloro- with low densities oftwo green algae, Scenedesmus sp. and phyte, Neochloris oleoabundans Chantanachat and Bold, Ankistrodesmus sp. Once cultures were contaminated, den- 1962. This species was chosen because previous experi- sities of these contaminants continued to increase. After ments indicated that juvenile unionids readily ingest and 30 d, the algal community in the culture containers assimilate this alga (Gatenby etal., 1997). Initial stockcul- had changed significantly, with Scenedesmus and PATTERSON ETAL. GLYCOGEN LEVELS IN UNIONIDS 49 : Ankistrodesmus comprising ca. 40% ofthe available algae, ± 3.06 mg/g, respectively) and 30 days (1.2 ± 0.5 mg/g and and N. oleoabundans comprising the remaining 60%. 1.9 ± 1.4mg/g, respectively). Despite changes in the algal community, cell densities Glycogen, the primary energy reserve in bivalves, remained at 106 cells/ml throughout the experiment. drives many important physiological processes and can be Both the fed and starved treatments had some intial used to endure short-term exposure to anoxia, emersion, or mortality likely as a result ofcollection and handling, how- reduced food supplies (Bayne, 1976; Gabbott, 1983; Bayne ever, no mortality occurred during the remainder of the et al, 1985; Hummel et al, 1988). Although exposure to quarantine period. Mean glycogen levels ofAmblemaplica- anoxia and emersion can be limited if unionids are relocat- ta and Quadrula pustulosa during controlled feeding in ed to suitable habitat, unionids will likely experience short- quarantine remained the same, whereas mean glycogen lev- term, localized shifts in food abundance and long-term food els declined in a previous starvation experiment by shortages during the winter months. Normally, by accumu- Patterson etal. (1997) (Fig. 1). Initial mean glycogen levels lating glycogen when food is abundant, bivalves are able to forA. plicata (9.4 ± 2.4 mg/g) and Q. pustulosa (7.9 ± 1.8 withstand these food shortages (Gabbott, 1983; Hummel et ORM mg/g) collected from 175.5 in July 1997 were not al, 1988). However, unionid survival after relocation could significantly different (p > 0.3) from the mean glycogen be greatly reduced if glycogen stores are depleted in quar- levels ofA. plicata (8.1 ± 4.2 mg/g) and Q. pustulosa (6.2 antine and do not recover prior to the onset of winter. ± 2.9 mg/g) collected from the same site in July 1996 Regardless ofeffects on survival, decreased glycogen levels (Patterson etal, 1997). Glycogen stores ofunionids enter- in adult bivalves also can have sublethal effects including ing quarantine, therefore, were similar in both the starvation reduced fecundity and reduced growth rates of developing and controlled feeding experiments. After seven days of offspring (Bayne, 1972; Helm et al, 1973; Bayne et al, feeding in quarantine, mean glycogen levels of A. plicata 1975). Thus, the provision of adequate food resources for (12.3 ± 2.3 mg/g) and Q. pustulosa (7.1 ± 3.7 mg/g) did unionids in quarantine is pertinent to maintaining glycogen not change significantly (p > 0.1) relative to wild-caught levels and enabling mussels to develop reproductively specimens, and were significantly larger (p < 0.05) than viable populations afterrelocation. mean glycogen levels ofstarved individuals (3.6 ± 1.8 mg/g Results from this study indicate that relatively high and 3.5 ± 2.3 mg/g, respectively). Similarly, mean glycogen cell densities of the green alga, Neochloris oleoabundans, levels ofA. plicata and Q. pustulosa after 14 days (8.1 ± 3.3 in combination with Scenedesmus and Ankistrodesmus, is mg/g and 7.7 ± 3.3 mg/g, respectively) and 30 days (9.9 ± an adequate food resource for the maintenance of unionid 4.8 mg/g and 8.4 ± 2.7 mg/g, respectively) of feeding were glycogen stores in the short term (30 d). Currently, no infor- significantly larger (p < 0.01) than mean glycogen levels of mation exists on the ability ofunionids to digest and assim- starved specimens after 14 days (3.27 ± 1.74 mg/g and 5.37 ilate Scenedesmus and Ankistrodesmus, but recent studies show that unionids assimilate Neochloris oleoabundans with relatively high efficiency (> 50%, M. Patterson, unpub. A.plicata(starved) 1I Q.pustulosa(starved) data). Additional studies to determine which algal species !IAQ.ppluisctautlaos(faed()fed) are readily digested and assimilated by unionids are critical, because some algal species might not be readily digested and assimilated by certain bivalve species (Peirson, 1983). Regardless of the digestibility of a particular algal food resource, large amounts ofalgae will be required ifmanage- ment agencies hope to relocate large numbers of native oo 10 - mussels away from zebra mussel-infested areas. In this study, the quarantine of 300 mussels required constant cul- ture of 750 1 of living algae. Discovering ways to shorten 6 the quarantine period would make the production of algae more feasible and decrease the time that unionids must be 1 maintained in captivity, outside their natural habitat. Studies dealing with more efficient methods of removing zebra mussels from the shells ofunionids could prove to be 0 7 14 30 the best avenue for reducing the quarantine period. Time(days) Ultimately, a short quarantine period along with the provi- Fig. 1.Glycogen levels ofAmblemaplicata and Quadrulapustulosaat0, sion of food will improve the body condition of unionids 7, 14, and 30 d ofstarvation and controlled feeding in quarantine (N = and improve the success offuture relocations. 10/samplingperiod). . 50 AMER. MALAC. BULL. 15(1) (1999) ACKNOWLEDGMENTS Unionidae), reared on algal diets and sediment. American MalacologicalBulletin 14(l):57-66. We would like to thank Patty Morrison, Mitch Ellis, and every- Griffith,B.,J.M.Scott,J.W.Carpenter,andC.Reed. 1989.Translocation one else at the Ohio River Islands National Wildlife Refuge Office, as as a species conservation tool: status and strategy. Science wellasDr. Andrew MillerandtheUnitedStatesArmyCorpsofEngineers 245:477-480. fortheir help in collecting mussels fromthe Ohio River. We would also Haag,W. R„ D. L. Berg, D. W. Garton, andJ. L. Farris. 1993. Reduced liketothankthemanyvolunteersthatassistedwithcollectionandprocess- survivaland fitness in native bivalves in response to fouling by ingofmussels in the field. ThanksalsogotoLi-Yen Chen forassistance the introduced zebra mussel (Dreissena polymorpha) in western in developing the glycogen assay and Catherine Gatenby forbuilding the LakeErie. Canadian Journal of Fisheries andAquaticSciences quarantine facilityand assistingwith field work, algaeculture, and manu- 50(1):13-19. scriptrevisions. Finally, very special thanks go toJim Dotson forensur- Helm, M. M., D. L. Holland, and R. R. Stephenson. 1973. The effect of ingthatmusselsreceivedplentyoffoodandforhisincredibleabilitytofix supplementary algal feeding of a hatchery breeding stock of anythinginquarantine. Thisstudy was fundedbyQuickResponseFunds Ostrea edulis L. on larval vigor. Journal ofthe Marine oftheBiologicalResourcesDivisionofUSGS. Biological Associationofthe UnitedKingdom53:673-684. Hummel, H„ L. de Wolf, and A. W. Fortuin. 1988. The annual cycle cf glycogen in estuarine benthic animals. Hydrobiological Bulletin 22:199-202. Keppler,D. andK. Decker. 1974. Glycogendeterminationwithamyloglu- LITERATURE CITED cosidase. In: Methods ofEnzymaticAnalysis, H. U. Bergmeyer, ed.pp. 11-17.AcademicPress,NewYork. Mann, R. 1978. A comparison ofmorphometric, biochemical andphysio- Bayne, B. L. 1972. Someeffectsofstress inthe adultonthe larval devel- logical indexes of condition in marine bivalve molluscs. In: opmentofMytilus edulis. Nature237:459. Energy and Environmental Stress in Aquatic Systems, J. H. Bayne, B. L. 1976. Aspects of reproduction in bivalve molluscs. In: Thorpe and J. W. Gibbons, eds. pp. 484-497. Technical Estuarine Processes, M. L. Wiley, ed. pp. 432-448. Academic Information Center, United States Department of Energy, Press,NewYork. WashingtonDC. Bayne, B. L., D. A. Brown, K. Burns, D. R. Dixon, A. Ivanovici, D. R. Nichols, H. W. 1973. Growth media - freshwater. In: Handbook of Livingstone, D. M. Lowe, andM. N. Moore. 1985. TheEffectsof Phycological Methods, J. R. Stein, ed. pp. 7-24. Cambridge StressandPollution in MarineAnimals. Praeger, New York. 384 UniversityPress,NewYork. pp. Parker,B.C, M. A. Patterson,andR. J.Neves. 1998.Feedinginteractions Bayne, B. L., P. A. Gabbott,andJ.Widdows. 1975. Someeffectsofstress between native freshwater mussels (Bivalvia: Unionidae) and in the adult on the eggs and larvae ofMytilus edulis. Journalof zebra mussels (Dreissena polymorpha) in the Ohio River. the Marine Biological Association ofthe United Kingdom AmericanMalacological Bulletin 14(2):173-179. 55:675-689. Patterson,M. A.,B.C. Parker,andR.J. Neves.1997.Effectsofquarantine Bayne, B. L. and R. J. Thompson. 1970. Some physiological conse- times on glycogen levels ofnative freshwater mussels (Bivalvia: quences ofkeeping Mytilus edulis in the laboratory. Helgolander Unionidae) previously infested with zebra mussels. American wissenschaftlicheMeeresuntersuchungen20:528-552. Malacological Bulletin 14(l):75-79. Calvin, D. B. 1931. Glycogen content of fresh-water mussels. Peirson,W. M. 1983. Utilizationofeightalgal speciesbythebayscallop, Proceedings of the Society of Experimental Biology and Argopecten irradians concentricus (Say). Journal ofExperi- Medicine 29:96-97. mentalMarineBiologyandEcology68:1-11 Cope, G. W. and D. L. Waller. 1995. Evaluation of freshwater mussel Pora, E. A., C. Wittenberger, G. Suarez, and N. Portilla. 1969. Theresis- relocation as aconservation and management strategy. Regulated tance of Crassostrea rhizophorae to starvation and asphyxia. Rivers:ResearchandManagement 11(2):147-155. Marine Biology3:18-23. Gabbott, P. A. 1983. Developmental and seasonal metabolic activities in Saraceni, C. and D. Ruggiu. 1969. Techniques for sampling water and marine molluscs. In: The Mollusca, Vol. 2, Environmental phytoplankton. In:A Manualon MethodsforMeasuringPrimary BiochemistryandPhysiology, P.W. Hochachka,ed. pp. 165-217. ProductioninAquaticEnvironments, R. A. Vollenweider, ed. pp. AcademicPress,NewYork. 5-7. BlackwellScientificPublications,Oxford. Gabbott, P. A. and A.J. M. Walker. 1971. Changesintheconditionindex Walne,P.R. 1970.Theseasonalvariationofmeatandglycogencontentof andbiochemicalcontentofadultoysters(Ostreaedulis L.)main- sevenpopulations ofoysters Ostrea edulisL. and areview ofthe tainedunderhatcheryconditions.Journal du Conseil 34:99-106. literature.FisheriesInvestigationSeriesII26,35pp. Galtsoff, P. S. 1964. The American oyster (Crassostrea virginica). Williams,J. D., M.L.Warren,Jr., K. S.Cummings,J.L. Harris,andR.J. UnitedStatesFishandWildlifeServiceFisheriesBulletin64,480 Neves. 1993. Conservation status of freshwater mussels ofthe pp. UnitesStatesandCanada. Fisheries 18(9):6-22. Gatenby,C. M.,B. C. Parker,andR. J. Neves. 1997. Growthandsurvival ofjuvenile rainbow mussel, Villosa iris (Lea, 1829) (Bivalvia: Dateofmanuscriptacceptance: 2October 1998

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