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Ion Transport in the Freshwater Zebra Mussel, Dreissena polymorpha PDF

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Reference: ;<>/. Bull 183: 297-303. (October. Ion Transport in the Freshwater Zebra Mussel, Dreissena polymorpha JANICE HOROHOV. HAROLD SILVERMAN. JOHN W. LYNN, AND THOMAS H. DIETZ* Department ofZoologyandPhysiology, Louisiana State University. Baton Rouge, Louisiana, 70803 Abstract. Theblood soluteconcentration (36 mosm)of and there is extensive European literature on the ecology pondwater acclimated zebra mussels isamong the lowest and gross morphology (Stanczykowska, 1977; Morton, found in freshwater bivalves. Blood ion concentrations 1979; Mackie et al.. 1989). However, there are few os- were Na (11-14 m.U) and Cl (12-15 m.U). with lesser moregulatory studiesand most physiological studies have amounts ofCa (4-5 m.U). HCO3 (about 2-4 m.1/). and focusedon methodsforcontrolorextermination (Morton, K (0.5 m,U). Sodium. Ca and Cl transport rateswere 20- 1979; Mackie et al.. 1989). 30 jueq (gdry tissue h) ' for pondwater acclimated mus- In a study by Fisher et al. (1991), a buffered artificial sels. The influx ofboth Na and Cl was stimulated by ex- soft water was found to be lethal to Dreissena. Some ar- ogenous serotonin (0.1 m.U). Sodium transport in zebra tificial freshwater solutions are buffered with up to 30 mussels was not inhibitmedMby amiloride. Zebra mussels mMKH2PO4 and 19 m.UNaOH to maintain neutral pH became isosmotic in 30 NaCl solutions and did not (Porcella, 1981). Thisconcentration ofpotassium and so- survive beyond a week in 45 m,U NaCl. Zebra mussels dium and the ionic ratio are exceptional for an artificial arewell adapted to theirdilute freshwater habitat, but are freshwaterbut theprimary soluteresponsible forthemor- more stenohaline than other freshwater bivalves as re- talityinDreissenaispotassium (Fisheretal., 1991). Others flected bytheirintoleranceofelevated ion concentrations have noted that zebra mussel distribution is restricted by in the bathing solution. salinity (see Morton. 1979; Deaton andGreenberg, 1991). Studies demonstrating that zebra mussels are sensitive to Introduction ionic concentration have opened avenues for possible The zebra mussel (Dreissena polymorpha) is the most methodsofcontrollingtheirpopulations. However, other recentfreshwaterbivalveintroduced intothe UnitedStates studies have demonstrated that many fresh-waterbivalves from Europe(Mackieela!., 1989). Unlikeotherfreshwater are killed by low concentrations ofpotassium (see Dietz bivalves, adult zebra mussels attach to solid substrate with and Byrne, 1990). byssal threadsand may reach densitiesexceeding 105/m3. Thisreportdescribessomeofthecharacteristicsofionic In addition, reproduction involves gametes that are dis- and osmotic regulation in the zebra mussel and some charged into the water column and develop into free- conditions limiting theirsurvival. Because ofthe potential swimming veliger larvae that may remain planktonic for similarities with indigenous bivalves, the basic biology of weeks or months, allowing them to move considerable zebramussels mustbe understood tobeabletoselectively distances before settling (Mackie et a/., 1989; Morton. control their numbers or distribution. 1979). Dreissena hasbeen documented asa seriouseconomic Materials and Methods pest because ofits propensity to foul raw-water systems. Animals Zebra mussels (Dreissena polymorpha) were collected Received 26 March 1992; accepted 20July 1992. * Addresscorrespondence to: T. H. Dietz. Dept. Zoology and Phys- from Lake Erie near Cleveland, Ohio, and acclimated to iology. LouisianaState University. Baton Rouge. LA 70803. artificial pondwater for a minimum of 5 days (Dietz, 297 298 J. HOROHOV ET AL 1979). Mu2sCsels were tored unfed in aerated pondwater dium. Un=idire-ctional efflux (J ) was calculated by differ- at 22 b ;. Zebra mussels usually survived ence (J J, Jn). 6-8 weeks at ~" ;i no mortality. Forlonger mainte- The effectsofexogenousbiogenicamines on ion trans- nance, mu?? \1 in pondwater at 16 1C and port were determined by the addition ofmonoamines to subseque" sferredto room temperature forat least bringthe bathing medium concentration to0.1 mA/. Sev- 24-48 1 illy 5 days) before use in experiments. eral biogenic amines (dopamine, epinephrine, norepi- We nor .elected larger specimens for study (2-3.5 nephrine, octopamine, and serotonin) were tested. All cm length) with a dry tissue mass of 15-40 mg. monoamine neurotransmitters were obtained from Sigma Toavoidcontaminating local watersystemswithzebra Chemical Company (St. Louis, MO). musselsorveligerlarvae, all acclimation waterand animal Data are expressed as mean one standard error. The containers were treated with 1% chlorine bleach for 24 h Student's /-test was used to compare means with equal before being discarded. Mussels were dissected from the variances, and differences were considered significant if shell and dried at 95C, and weighed before being dis- P < 0.05. Time-course studies and the effects ofion con- carded. centrations on mussel blood, where variances were un- equal, were analyzed by ANOVA and Scheffe's f-test on Bloodanalyses log transformed data. Bloodwascollected by heart puncture(Fyhn andCost- low, 1975) and centrifuged 8000 g-min before use. We Results could routinely collect blood volume equal to 10% ofthe The blood composition ofD. polymorpha acclimated animal weight. However, the mantle cavity retains more to pondwater (PW) is shown in Table I. Zebra mussels pondwater than other freshwater bivalves and was more were hyperionic to PW with sodium and chloride being difficult todrain. Failure todrain the mantle cavity water the principal solutes. The measured solutes account for insmallerzebra musselswill likelycontaminatetheblood 88% ofthetotal solute but thereisan ion deficit("other") sample ifthesyringe needle passesbeyond the pericardia! of5.1 m.\/. From anothergroupofanimals, we measured ddrbCcTmeeeaeyhigpnrtneirtlaeeoreetrbnasdom.aitsmniciibaiaonoTlyncrneoy.btdtieoaainlnbclSbetaasyoclhtostdeerfogripllbaocutauslmoitmmeonceoetochnrdaerewinnmsowcatdpimasrestasacsiptdtttimoorieroetagoonttaarsn,eissacsorsuonapmi.wprnhiuyeednT.mr(deBhecdoCaceaushnoltlobnCicbotcyliiOreicur:ienamfordtrruueraewbtsaeoiaiwtznnansaiiieagno,sltagnayes-1dsHpm9ewcao8ateeoyi5ecarne)nrh-e-d.t- t(pWaaoBthb"nryeseaoo2r.etb,nt3nrhaoeooCetbRbtar.l,cil"etycdBtsat3yiohillt.lnur.lh7,usnyattet1e9hf,,9e5rm90Sa%o1of.l)Umsl7o.oNtrozfYmfmBeot-bMlthfForohe;trafeoChedmeHCmOduaop,CmOsjniHsOow2sierosal23oiu.s)fian6l.otag7dnc.nssc4eeolx5a0ulii.tnushm4rttdaaaesatmltse(oMbdtt7Heao,0tleC%oanb)nOlplkmwoo3a=enaol(adisdu6snwn)CCeuap(rtuOOpsebeeH22.dre,. suredbutwereestimated fromaliquotsofbloodthatwere The blood solute in D. polymorpha is among the equilibrated in air. From previous studies, 95-98% ofthe lowest recorded for freshwater mussels (see Dietz, 1979). COi would be in the form of bicarbonate over the pH To test their ability to osmoregulate, we challenged the range 7.5-8.1 (Byrne ct ai. 1991). mussels with NaCl added to pondwater and measured Ionfluxes twhaesbalosoidgniifoincacnotnc(ePnt<ra0t.i0o1n)s a1f1t.e8rm96Mh r(iTsaebline bIIl).ooTdheNrae Unidirectional ion influxes (J,) were calculated by monitoring the disappearance ofisotope from the bathing medium usingpreviouslydescribed methods(Gravesand Table I Dietz, 1982). The animals were removed from theirstor- liloojandpondwaterioncomposition inpondwateracclimated age containers by cutting the byssal thread with scissors Dreissena polymorpha or scraping the thread from the container, not by pulling the thread from the animal. The mussels were rinsed in Ion deionized water for about 30 min and transferred to a small containerwiththeappropriate bathingsolution. The animals ordinarily did not reattach with byssal threads during the briefperiod ofstudy. Bath samples were col- lected at timed intervals and radioactivity determined by liquid scintillation counting. Net flux (Jn) was calculated from the change in ion concentration in the bathing me- IONIC AND OSMOTIC REGULATION IN ZEBRA MUSSELS 299 Table II ilc<>iicenti'titiii 111 Dreissena polymorpha after4 duy\ acclimation inpondwalercuiiiaiiuiit; additional \'ui I 300 J. HOROHOV ET AL. Table IV 'inhlood" "' '" Dreissena polymorphafollowingacutetransfertopondwatercontaining45 rriMNaCl mosm IONIC AND OSMOTIC REGULATION IN ZEBRA MUSSELS 301 unionid bivalve sodium transport system is inhibited by Table VII amiloride. In contrast, corbiculid Na transport is not. So- Effectsotaniilondc(0,5 mM) addition topondwateron unidirectional dium transport in D. polymorpha was not inhibited by sodium fluxes inpondwalcracclimatedDreissena polymorpha 0.5 m.U amiloride (Table VII). Some mussels were slow to open their valvesand initiate siphoningand this raised (gdry tissue h) the variabilityofthe measured fluxes. However, theamil- Treatment Influx Efflux Net flux oride-treated mussels that were observed to be open and siphoning had transport rates that equalled or exceeded Control 22.22 + 4.24 25.04 + 2.34 -2.92 4.12 the controls. Amiloride 19.00 5.96 30.34 + 7.33 -11.34 2.29 Discussion Mean SEM. n = 8. Dreissenapolymorphaexhibited several characteristics that were significantly different from the other freshwater pondwater. However, storage of zebra mussels in PW, bivalvesthat havebeenstudied. TheCl transport ratewas withoutfood, beyond 2 monthsledtoan increase in mor- higherthan observed in other freshwater mussels and the tality. Coincidentally, mussels maintained in the labora- rateofNatransport isequaled only bythe fingernail clam tory tended to lose solutes and ion fluxes became more Miiscitliiim (= Sphaeriiim) transversum (Dietz. 1979). variable, but this phenomenon has not been studied sys- Chloride transport was double the transport rate of fin- tematically. gernail clams and 10-20X that of unionids. This is the Sodium transport in zebra mussels was the same in first report in a freshwater mussel of chloride transport solutions of either NaCl or Na2SO4 indicating an inde- being dependent on Na and Cl uptake being stimulated pendence from chloridetransport. Unionidandcorbiculid by exogenous serotonin. Preliminary data indicate that Natransport are also independent ofCl, using instead an both Na and Cl transport also may be stimulated by se- apparent Na/H exchange component (Dietz, 1978; rotonin in corbiculids (unpub. obs.). Serotonin has been McCorkle and Dietz, 1980). We have not examined the reported to stimulate only sodium transport in unionid exchange mechanism in zebra mussels. Recent studies bivalves (Dietz et a!., 1982). have indicated that Na flux across amphibian skin is The blood ofPW acclimated zebra mussels has signif- largely regulated by availability of intracellular protons icantly less total solute than other mussels and was com- rather than a directly coupled exchange mechanism posed primarily ofNaCl with onlyabout 2-4 m.UHCO3. (Harvey and Ehrenfeld, 1988; Kirschner, 1988). Organic solutescontribute littletothetotal solute offresh- This isthe first evidence that Cl transport isdependent watermussels(Hanson and Dietz, 1976). The ionic com- on Na in a freshwater mussel. These data indicate that position in zebra mussel blood is similar to a Canadian there may be a NaCl co-transport system in D. polymor- unionid,Anodontagrandissimpsoniana, butdiffers from pha. This inference was further supported by the stimu- most other unionids in that they contain a combination lation ofboth Na and Cl uptake by exogenous serotonin. ofNa, Cl, and HCO, (Dietz, 1979; Byrneand McMahon, Because we have not measured transepithelial electrical 1991). Corbiculid blood composition is largely NaCl at characteristics in zebra mussels, it is premature to spec- about twice the concentration found in D. polymorpha. ulate on primary or secondary transport mechanisms. Corbiculaflumineaalso hastwicethecalcium concentra- Both Dreissena and Corbicula have elevated Na trans- tion asthe zebra mussel (Dietz, 1979; Byrne et at.. 1989). portratescompared to unionids. Zebra musselssharewith mM Acutetransferofzebramusselsto45 NaCl resulted Corbicula the unusual property that sodium transport is in an elevated blood NaCl concentration within 8 h, but insensitivetoamiloride(McCorkleandDietz, 1980). Since 48 h was required for acclimation. Corhicula fluminea Corbicula displays a substantial Na/Na exchange com- rapidly adjust blood total solutes within 12 h after being ponent not found in unionids, it is tempting to speculate transferred from freshwater to 5%o (172 mosm), but vol- that zebramusselsalso may havealargeNa/Naexchange ume regulation is incomplete even after 120 h (Gainey, mechanism contributingtothehigh isotopeturnover,but 1978). Zebra musselsbecame isosmoticand suffered con- this has not been measured. It is possible that these Na/ siderable mortality when acutely transferred to NaCl so- Naexchangepathwayspresentinsomefreshwaterbivalves lutionsabove 30 mM. In contrast, unionids become isos- are insensitive to amiloride inhibition. motic above 50 mMNaCl and survive 75 mM NaCl and Alternatively, the large Na exchange diffusion com- corbiculidscan tolerateeven highersoluteconcentrations ponent may be a characteristic ofrecent brackish-water (Dietz and Branton. 1975; Gainey, 1978). ancestry ofCorhicula and Dreissena. Although they have Although D. polymorpha displayed high ion turnover invaded freshwater independently, both genera contain rates, they were able to maintain a steady state in dilute species that inhabit brackish-water (for review see 302 J. HOROHOV ET AL McMahon. 1983: ,' al.. 1989; Deaton and be useful in controlling zebra mussels in a specific case Greenberg, 199: such as freshwater ballast in trans-oceanic vessels. The Freshwat s :ire capable hyper-regulators and addition of 5-10% seawater, in this example, would be usually ar> : crate hyperosmotic conditions that lethal to adult zebra mussels. would more iouble their normal total solute con- centration iton and Greenberg. 1991; Kirschner, Acknowledgments 1991). >n..-i 'in is uniquely stenohaline in showingmelMe- Wethank Drs. Robert McMahon and Roger Byrne for vated mortality at low solute concentrations (30 providingthezebra musselscollected from Lake Erieand tNoaC4l5),maMndNabeCilngbeiynocnapdaablweeeokf.suWrevivhianvgeannotaecdutperetvriaonussfleyr afonrdtDheiomndainyLessusgagredstpiroonvsidaenddtcecohmnmiecanltsa.ssiJsutlaineceC.heTrhriys that Corbicula subjected to a loss ofbody waterwill shift workwassupported, inpart,bythe LSUCenterforEnergy Na and Cl out of the blood compartment presumably Studies grant 91-01-1 1 and NSF grant DCB90-17461. intotheintracellularfluid(Byrneelal., 1989). Itispossible that thechanges in intracellular ioniccomposition due to Literature Cited the gain in Na and Cl may be an attempt to preserve cell Boutilier, R. G., G. K. Iwama, T. A. Homing, and D. J. Randall. volume. Suchamechanism wouldhavemajorlimitations. 1985. The apparent pK ofcarbonic acid in rainbow trout blood Either the addition of NaCl to the cells or the resultant plasmabetween 5 and 15C. Resp. Physiol. 61: 237-254. imbalance in the Na:K ratio could interfere with electri- Byrne, R. A., and B. R. McMahon. 1991. Acid-base and ionic regu- callyexcitable tissue (nerve, skeletal, cardiac muscle) and lation,duringandfollowingemersion,inthefreshwaterbivalve.An- maybe a critical factor limiting survival ofDreissenapo- odonla t;ranilis simpsomana (Bivalvia: Unionidae). Biol. Bui/. 181: 289-297. lymorpha. Byrne, R. A., R. F. McMahon, and T. H. Dietz. 1989. Theeffectsof Alternatively, Deaton andGreenberg(1991)have noted aerial exposure and subsequent reimmersion on hemolymph os- a correlation between the osmoregulatory capability of molality, ion composition and ion flux in the freshwater bivalve, bivalves and their ability to mobilize calcium. They sug- Cnrhiciilallnminea. Physiol. Zooi 62: 1187-1202. gested that the mode ofaction ofelevated calcium is to ByrnMec,MRa.hoA.n,.B.19N9.1.ShiApcmiadn-,basNe.bJa.lSamncaetrdeusrki,ngT.prHo.loDnigeeldz,eamnedrgRe.ncFe. regulate membrane permeability. Dreissena blood cal- in the freshwater bivalve, Corbicula flummea. Physinl. Zool 64: cium concentration was similar to other freshwater mus- 748-766. sels but it remained constant during periods ofhyperos- Deaton, L. K.,and M.J.Greenberg. 1991. Theadaptation ofbivalve motic stress. Perhaps the critical feature leading to their molluscs to oligohaline and freshwaters: Phylogenetic and physio- stenohaline characteristic is their inability to add Ca as logical aspects. Mulacot. Rev. 24: 1-18. an osmolyte to the blood when under stress. Dietczu,liTn.aIIl.ex1c9i7sc8n.sisS(oLedailu.mAmtr.anJspPohrytsiion/t.he23f5r:esRh3w5at-eRr4m0u.ssel, Carun- The variability in ion transport and the magnitude of Dietz,T.H. 1979. Uptakeofsodiumandchloridebyfreshwatermus- ion losses in some Dreissena polymorpha acclimated to sels. Can. J Zool. 57: 156-160. pondwater exceed the range found in other freshwater Dietz,T.H.,and\V.D.Branton. 1975. Ionicregulationinthefreshwater bivalves. Freshwater mussels are normally nocturnally mussel. Ligumiasubroslrala(Say). J. Comp. Physiol. 104: 19-26. Dietz,T. H.,and R. A. Byrne. 1990. Potassium andrubidium uptake active and tend to gain saltsat night and lose ions during in freshwater mussels.J. Exp. Biol. 150: 395-405. theday(GravesandDietz, 1980; McCorkle-Shirley, 1982). Dietz, T. H., J. I. Scheide, and D. G. Saintsing. 1982. Monoamine Perhaps Dreissena has more pronounced diurnal rhythms transmitters and cAMP stimulation ofNa transport in freshwater ofion transport. Zebra mussels also form byssal threads mussels. Can. J. /-.ool. 60: 1408-141 I. and the secreted material may be in ionic form contrib- Fisher, S. \V., P. Stromberg, K. A. Bruner, and L. D. Boulet. uting to some of the apparent salt losses. Alternatively, D1r9e9i1s.senMaoplolluyscniwcripdhaila:aTcotixviictiytyoafndpomtoadsseioufmacttoiont.heAqzueabtriacTmouxsisceoll., Dreissenamay be more sensitive to starvation conditions 20: 219-234. imposed by laboratory storage. Furtherstudies are needed Fyhn, H. J., and J. D. Costlow. 1975. Anaerobic sampling ofbody to resolve these issues. fluidsin bivalve molluscs. Comp. Biochem. Physiol. 52A: 265-268. The basis forzebra mussels' intolerance ofsalt loading Gainey, L. F. 1978. The response ofthe Corbiculidae (Mollusca: Bi- valvia) to osmotic stress: The organismal response. Physiol. Zool. is offundamental interest. There have been few studies 51:68-78. ofsalt tolerance in freshwater mussels and these studies Graves, S. V., and T. H. Dietz. 1980. Diurnal rhythms of sodium provide little insight with regard to the physiological transport in the freshwater mussel. Can. J. Zoo/ 58: 1626-1630. vmiercohnamnenitsamll(yDesaotuonndanpedrsGpreecetnibvee,rga.n19i9o1ni)c. Fcrhaolmleanngeeni-s Gravperso,staS.glaY.n,diannidnhTi.bitHi.onDoifetNz.at1r9a8n2s.portCyicnlifrcesAhMwaPterstmiusmsuellast.ioCninannp.d Biochem. Physio/ 71A: 65-70. likely to be too nonspecific and detrimental to all fresh- Hanson,,1. A.,and T. H. Dietz. 1976. Theroleoffreeaminoacidsin waterbivalvestobe a suitable method forgeneral control cellularosmoregulationinthefreshwaterbivalve.Ligiuniasubrostrata ofzebra mussel populations. However, KC1 or NaCl may (Say). Can. J Zool. 54: 1927-1931. IONIC AND OSMOTIC REGULATION IN ZEBRA MUSSELS 303 Ilar\c>, B. J., and .1. Khrenfeld. 1988. Role ofNa*/H+ exchange in McCorkle-Shirley, S. 1982. Effectsofphotopenodon sodium flux in thecontrolofintracellular pH and cell membrane conductancesin Corbicuia Ihuninea (Mollusca: Bivalvia). Comp. Biochem. Physiol. frogskinepithelium. / Gen. Physinl. 92: 793-810. 71A: 325-337. Kirschncr, I.. B. 1988. Basis for apparent saturation kinetics ofNa* McMahon, R. F. 1983. Ecologyofaninvasivepestbivalve,Corbicuia. influxinfreshwaterhyperregulators.Am.J Pliyxml. 254:R984-R988. Pp. 505-561 in TheMollusca. Vol. 6. Ecology. W. D. Russell-Hunter, Kirschner, 1,. B. 1991. Waterandions. Pp. 13-107 in Environmental ed. Academic Press, San Diego. andMetabolicAnimalPhysiology.C. L. Prossered. Wiley-Liss,New Morton, B. 1979. Freshwaterfoulingbivalves. Pp. 1-14inProceedings. York. First International Corbicuia Symposium. J. C. Bntton. ed. Texas Mackie, G. L., VV. N. Gibbons, B. \V. Muncaster, and I. M. Gray. Christian University Research Foundation, Fort Worth. 1989. The/.ebramussel,Dreissenapolymorpha:AsynthesisofEu- Porcclla, D. B. 1981. Bioassay methods for aquatic organisms. Pp. ropean experiences and a preview for North America. Pp. 1-76 in 615-649inStandardMethodsforExaminationo/"H'aterand\\'aste- WaterResources Branch Great Lakes. Ontario Ministry ofthe En- H-ater. A. E. Greenberg, J. J. Conners. and D. Jenkins, eds. 15th vironment. Ontario. edition. American Public Health Association, Washington, DC. McCorkle,S.,and I.II.Dietz. 1980. Sodiumtransportinthefreshwater Slanczykowska, A. 1977. Ecology of Dreissena polymorpha (Pall). Asiaticclam, Corbicuia lluminca Biol Bull 159: 325-336. (Bivalvia) in lakes. Pol. Arch. Hydrobwl. 24:461-530.

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