Molecular Ecology and Biotechnologyeprints.bice.rm.cnr.it/16460/1/Technical procedures... ·...

Post on 19-Jan-2020

4 views 0 download

transcript

Technical procedures for stimulation with organic and inorganic pollutants, in a controlled environment, of model organism Mytilus galloprovincialis(Lamarck1819)

1

Technical procedures for stimulation with organic and inorganic pollutants, in acontrolledenvironment,ofmodelorganismMytilusgalloprovincialis(Lamarck1819)

C.Benniciᴬ,A.Nicosiaᴬ,G.Biondoᴬ,M.V.DiNataleᴬ,T.Masulloᴬ,C.Monasteroᴬ,G.M.Armeriᴬ,M.Tagliaviaᴬ,A.Cuttittaᴬ,

a-LaboratoryofMolecularEcologyandBiotechnology,Istitutoperl’AmbienteMarinoCostierodelConsiglioNazionaledelleRicerche(IAMC-CNR),UOSdiCapoGranitola,viadelMare3–91021,TorrettaGranitola(CampobellodiMazara,Tp),Italia;

Molecular Ecology and Biotechnology

Technical procedures for stimulation with organic and inorganic pollutants, in a controlled environment, of model organism Mytilus galloprovincialis(Lamarck1819)

2

Index1. 1Introduction………………………………………………………………………………………………………………………….3

1.1. CISASproject……………………………………………………………………………………………………………………3

1.2. Workpackage3,ecosystemandcontaminant…………………………………………………………………3

1.3. Task3.3,invivoexperiments…………………………………………………………………………………………..4

2. Musselsasamodelorganism………………………………………………………………………………………………….4

3. Invivoexperimentaldesign…………………………………………………………………………………………………….5

4. Acknowledgments………………………………………………………………………………………………………………….6

5. References………………………………………………………………………………………………………………………………7

Technical procedures for stimulation with organic and inorganic pollutants, in a controlled environment, of model organism Mytilus galloprovincialis(Lamarck1819)

3

1Introduction

1.1CISASproject

TheproceduresdescribedhavebeencarriedoutwithintheprojectCISAS“InternationalCentreofadvancedstudyinenvironment,ecosystemandhumanhealth”.

Thepresent researchprogramaimsat investigatingenvironmental pollution and its connectionwith theecosystemandhumanhealth,startingfromasignificantnumberofcasestudies(SIN’sofAugusta,MilazzoandCrotone)astruenaturallaboratoriessuitableformodernmultidisciplinaryinvestigation.Thewidespreaddevelopmentofhumanactivitiesintheindustrialfield,sincethepost-warperiod,inadditionto the creation of an economy that places our country in the eighth place among the world’s majorindustrialized Countries has been causing an important and complex phenomenon of environmentalcontamination,withcrucialeffectsonterrestrialandmarineecosystemsandhumanhealth.AdecisiveactionoftheGovernmentandtheMinistriesinchargeofenvironmentalprotectionallowedtoidentifyanumberofcontaminatedareasintheItalianterritoryinneedofanurgentandimportantrecoveryaction.Theyaretheso-calledcontaminatedSitesofNationalInterest(SIN),characterizedbysevereenvironmentaldegradationandhumanimpactphenomenaofvariousorigin,substantiallycausedbythedevelopmentofmajorindustrialactivities.Inrelationtotheenvironmentalcharacterizationoftheseareas,ithasrecentlybeenconsideredcrucialandnecessarytounderstandthespecificimpactofthesefactorsonthehealthofthepeoplelivinginproximityof theabovementionedsites.Theenvironmentandhumanhealtharegenerallyobservedandinvestigatedwithasectorialapproach:rarelysynergicactionshavebeencarriedouttostudyquantitativelycause-effectrelationshipsbetweenpollutionandpopulationhealthconditions.Thecollectionofimpactontheenvironmentandonhumanhealthisamandatorystepforthedevelopmentofmoderntechnologiesinthefieldsofchemistry,systembiology,biotechnology,medicine,etc.

1.2EcosystemandcontaminantWP3

ThisWPisfocusedonpollutantstoxicityandrelatedmolecularresponsemechanismsinmarineecosystem.Biological and toxicological responses to different contaminants, including emerging ones, will beinvestigatedinthethreestudyareas(Priolo-Augusta,Crotone,Milazzo),withtheaimtohighlightpossiblerelationshipswithhumandiseases.Biological responseswillbe investigatedthroughawidepanelofbio-markers inmodelmarineorganismswithdifferentcomplexity. Inordertoanalyzetoxiceffectsatvariouslevelsofbiologicalorganization,asystemicecotoxicologycalapproachwillbeemployed.Transcriptomicandepigeneticanalyseswillbecarriedoutinordertounveilresponsesandmodificationsinducedbyexposuretoselectedpollutants.Moreover,edible,benthicandnectobenthicmarinespecieswillbeanalyzed,withtheaimtoinvestigatepollutantsuptakeroutesbyhumansthroughseafoodconsumption.Dataobtainedbytheanalysesofnaturalsampleswillbevalidatedundercontrolledconditionsinmesocosm.

1.3Invivoexperiments,Task3.3

Task 3.3 The use of model organisms to unveil novel toxicity mechanisms (IFC) Based on critical issuesrecognizedinthethreestudyareas,possiblemechanismsinvolvedinemergentdiseaseswillbeinvestigatedin model systems (i.e. Danio rerio, Paracentrotus lividus, Dicentrarchus labrax, Octopus vulgaris, etc.)(Schnitzleretal.2011;Campinhoetal.20\13,2014;Coudercetal.2016;Marellietal.2016).Thestrategyisbased on the widely recognized and accepted knowledge of the evolutionary conservation of themostmolecularmechanismsinvolvedinbasalfunctions,inbothembryonalandadulttissues(likestressresponse,cell cycle regulation, embryodevelopment andmorphogenesis, etc.) (Piconeet al. 2016).Moreover, theoverlapping between many molecular mechanisms involved in tumoral and endocrine diseases and

Technical procedures for stimulation with organic and inorganic pollutants, in a controlled environment, of model organism Mytilus galloprovincialis(Lamarck1819)

4

development/differentiation is well known. Thus, embryonal/larval stages of selected species (easy tomanageandmanipulate,andwellcharacterizedatmolecularlevel)arewellsuitablebothforthepreliminarydetectionofphenotypicaleffects(i.e.teratogenicity,etc.)(Kinchetal.2016)oftheexposuretopollutantsandforfurtheranalysesfocusedtounveilmolecularmechanismsinvolved(Zhuoetal.2014;Guoetal.2014).Furthermore, transcriptomicanalyses (carriedoutbymeansofNextGenerationSequencing)willprovideglobal transcriptional profiles, suitable to detect variations involving any RNA species, including ncRNAs,inducedbyenvironmentalpollutantfoundinthethreestudyareas(Caoetal.2016;Chenetal.2016).

2Musselsasamodelorganism

Bivalves can filter large volumes of water, processingmicroalgae, bacteria, sediments, particulates, andnaturalnanoparticles,potentiallyaccumulatingdifferentchemicals in their tissues.Theseorganismshavebeen long recognized as valuable indicators of pollution, and extensive background information is nowavailableontheirbiologicalresponsestoawiderangeofbothinorganicandorganicchemicals(Dagninoetal.,2007;Mooreetal.,2006).Inparticular,themusselMytilusgalloprovincialis(Fig.1),abundantincoastalmarineandestuarineenvironments,canrepresentasuitablemodelorganismforcharacterizingthepotentialimpactinmarineMediterraneanecosystem.

Figure1Mytilusgalloprovincialis

Foodparticlestrappedbythegillsievearemovedtowardsthelabialpalpsandthemouththusenteringthegut,andreachingthedigestivegland,wheredigestionoccurs.Digestivecellshaveanextremelydevelopedlysosomalsystemforintra-cellulardigestionandnutrientaccumulationforgametogenesis(Gosling,1992).

Bivalvehemocytesresembleinstructureandfunctionthemammalianmonocyte/macrophagelineage:theyareresponsibleforcell-mediatedimmunitythroughphagocytosisandvariouscytotoxicreactions(suchaslysosomalenzymeandantimicrobialpeptidereleaseandoxyradicalproduction);hemolymphserumcontainshumoraldefensefactors,suchassolublelectins,hydrolyticenzymesandantimicrobialpeptides(Canesietal.,2002).Althoughbivalvehemocytesareextremelyheterogeneous, inMytilusspp.granularhemocytesrepresentthedominantcelltype;theyarecharacterizedbyalownucleus/cytoplasmratio,highphagocyticactivity and capacity for oxyradical production (Garcia-Garcia et al., 2008). The responses of Mytilusgalloprovincialishemocytestobacterialsignals,cytokines,hormones(Canesietal.,2006a),andtoanumberofenvironmentalcontaminantshasbeen largelycharacterized (Canesietal.,2003,2006b,2007a,2007b,2007c,2007d).Inthesecells,likeinmammalianimmunocytes,theimmuneresponseismodulatedbythe

Technical procedures for stimulation with organic and inorganic pollutants, in a controlled environment, of model organism Mytilus galloprovincialis(Lamarck1819)

5

activation stateof rapidpathways involving tyrosine-mediated cell signalling,with a key roleofMitogenActivatedProteinKinases(MAPKs),inparticularthestress-activatedMAPKsp38andJNKs,andofPKC(Canesietal.,2006b).Conservationofbasiccellularprocessesofinnateimmunityfrominvertebratestomammalsrepresentsanusefulbasisforstudyingcommonbiologicalresponsestoenvironmentalexposuretodifferentfamilyofcontaminants.

TheuseofMytilusinthecontextoftheCISASprojectwillfollowtwomainways:

1-.Validationofstressedconditionsthroughwidelyacceptedresponsemarkers

2-Indentificationofnovelmechanismsofmolecularresponsebymeansofcomprehensiveomictools

3Invivoexperimentaldesign

Mediterraneanmussels(M.galloprovincialis)withamaximumshell lengthof5cmwereobtainedfromacommercial shellfish farm from Ganzirri e Faro lake (Messina). They were acclimated in aquarium withartificialseawater(36perthousandsalinity)for3daysat18°Cwithcontinuousaerationandtheywerefeddailywhitcommercialmicroalgaefrozenmixture.

Fugure2:GroupofsixM.galloprovincialisinexperimentalcondition

Individualsweremaintained in the laboratory for 3 days before testing, in separate aquaria, in order torelease metals and microorganisms (Freitas et al., 2012 ; Maffei et al., 2009). During this period theorganismsweremaintainedattemperature17.0±1.0°C;pH7.80±0.10,12light:12darkphotoperiodandcontinuous aeration, in artificial seawater (salinity 35 ± 1) (TropicMarin® SEA SALT from TropicMarineCenter).Seawaterwasrenewedeverytwodays(Coppolaetal.,2017).Afterthisperiod,organismsweredistributedindifferentglassaquarium(6Lseawater,salinity35�),with6individualspercontainerand3concentrationcorrespondingtolow,intermediateandhighlevelofpollution(Biblio)for7contaminants(Cd,Mn,Ni,Pb,Zn,Cu,alltheprecedentinmixture),asreportedinTable1.Duringtheexposureperiodcontainerswerecontinuouslyaerated,temperatureandsalinity(35±1)weredailycheckedwithathermometerandrefractometer.Whennecessarysalinityvalueswereadjustedaddingwatertothecontainers,accordingtotheabovestatedconditions.Mortalitywasdailycheckedandorganismswereconsidereddeadwhentheirshellsgapedandfailedtoshutagainafterexternalstimulus.Aerationwasnotintensiveanditwassimilaramongaquaria.

Technical procedures for stimulation with organic and inorganic pollutants, in a controlled environment, of model organism Mytilus galloprovincialis(Lamarck1819)

6

Mortalitywasrecorded.

Thefollowingtableliststheusedcontaminantsandtherelativeconcentrations.

Low[µg/l] Medium[µg/l] High[µg/l]

Cd²⁺ 0.01µg/l 0.1µg/l 1µg/l

Mn²⁺ 0.01µg/l 0.1µg/l 1µg/l

Ni²⁺ 0.01µg/l 0.1µg/l 1µg/l

Pb²⁺ 5µg/l 10µg/l 20µg/l

Cu²⁺ 5µg/l 10µg/l 20µg/l

Zn²⁺ 5µg/l 10µg/l 20µg/l

Mix* Mix1Σlowconcentration Mix2ΣMedconcentration Mix3ΣHighconcentration

Table1.( *Mixcomposition:Cd²⁺;Mn²⁺;Ni²⁺;Pb²⁺;Cu²⁺;Zn²⁺.)

Ateachsamplingperiod(12h,2hand5days),organismsweredissectedindifferentanatomicaltissues(gills,adductormuscle,digestivegland,gonads,haemocytes)andmainteinedat-80°Cforsubsequentanalysisandposteriorlymanuallyhomogenizedwithamortarandapestleundericeinpresenceoftrizollysisbuffer.

Eachhomogenizedtissueswasdividedindifferentaliquots,fromamaximumof0.5gformuscleto0,05mgforhaemocytes,usedformolecularandbiomarkeranalyses.

6. Acknowledgments

ProjectCISAS“InternationalCentreofadvancedstudyinenvironment,ecosystemandhumanhealth”.

7. References

[1] Schnitzler JG1,CelisN, KlarenPH,BlustR,DirtuAC,CovaciA,DasK. Thyroiddysfunction in seabass(Dicentrarchuslabrax):underlyingmechanismsandeffectsofpolychlorinatedbiphenylsonthyroidhormone

Technical procedures for stimulation with organic and inorganic pollutants, in a controlled environment, of model organism Mytilus galloprovincialis(Lamarck1819)

7

physiologyandmetabolism.AquatToxicol.2011Oct;105(3-4):438-47.doi:10.1016/j.aquatox.2011.07.019.Epub2011Aug4.

[2] CampinhoMA, Saraiva J, Florindo C, PowerDM.Maternal thyroid hormones are essential for neuraldevelopmentinzebrafish.MolEndocrinol.2014Jul;28(7):1136-49.doi:10.1210/me.2014-1032.

[3]CoudercM1,MarchandJ2,Zalouk-VergnouxA1,KamariA1,MoreauB2,Blanchet-LetrouvéI1,LeBizecB3,MouneyracC4,PoirierL5.ThyroidendocrinestatusofwildEuropeaneels(Anguillaanguilla)intheLoire(France).Relationshipswithorganiccontaminantbodyburdens.SciTotalEnviron.2016Apr15;550:391-405.doi:10.1016/j.scitotenv.2015.12.136.Epub2016Feb2.

[4]MarelliF,CarraS,AgostiniM,CotelliF,PeetersR,ChatterjeeK,PersaniL.Patternsofthyroidhormonereceptorexpressioninzebrafishandgenerationofanovelmodelofresistancetothyroidhormoneaction.

[5]PiconeM,BergaminM,LossoC,DelaneyE,ArizziNovelliA,GhirardiniAV.AssessmentofsedimenttoxicityintheLagoonofVenice(Italy)usingamulti-speciessetofbioassays.EcotoxicolEnvironSaf.2016Jan;123:32-44.doi:10.1016/j.ecoenv.2015.09.002.

[6]KinchCD,KurraschDM,HabibiHR.Adversemorphologicaldevelopmentinembryoniczebrafishexposedto environmental concentrations of contaminants individually and in mixture. Aquat Toxicol. 2016Jun;175:286-98.doi:10.1016/j.aquatox.2016.03.021.

[7]ZhuB,WangQ,WangX,ZhouB.Impactofco-exposurewithleadanddecabromodiphenylether(BDE-209) on thyroid function in zebrafish larvae. Aquat Toxicol. 2014 Dec;157:186-95. doi:10.1016/j.aquatox.2014.10.011.

[8]GuoC,ChenX,SongH,MaynardMA,ZhouY,LobanovAV,GladyshevVN,GanisJJ,WileyD,JugoRH,LeeNY,CastronevesLA,ZonLI,ScanlanTS,FeldmanHA,HuangSA. Intrinsicexpressionofamultiexontype3deiodinase gene controls zebrafish embryo size. Endocrinology. 2014 Oct;155(10):4069-80. doi:10.1210/en.2013-2029.

[9]CaoC,WangQ,JiaoF,ZhuG.Impactofco-exposurewithbutachlorandtriadimefononthyroidendocrinesysteminlarvalzebrafish.ExpToxicolPathol.2016Sep;68(8):463-9.doi:10.1016/j.etp.2016.07.004.

[10]ChenL,ZhuB,GuoY,XuT,LeeJS,QianPY,ZhouB.High-throughputtranscriptomesequencingrevealsthe combined effects of key e-waste contaminants, decabromodiphenyl ether (BDE-209) and lead, inzebrafishlarvae.EnvironPollut.2016Jul;214:324-33.doi:10.1016/j.envpol.2016.04.040.

[11]A.Dagnino,J.I.Allen,M.N.Moore,K.Broeg,L.Canesi&A.Viarengo.Developmentofanexpertsystemfortheintegrationofbiomarkerresponsesinmusselsintoananimalhealthindex.Received28Feb2006,Publishedonline:08Oct2008Biomarkers,MarchApril2007;12(2):155172

[12]Moore, J.L., Rush, L.M., Breneman, C.,Mohideen,M.A., and Cheng, K.C. (2006) Zebrafish GenomicInstabilityMutantsandCancerSusceptibility.Genetics174(2):585-600.

[13]Gosling,E.M.,1992b.GeneticsofMytilus.In:Gosling,E.(Ed.),TheMusselMytilus:Ecology,Physiology,GeneticsandCulture.Elsevier,Amsterdam,pp.309–382.

Technical procedures for stimulation with organic and inorganic pollutants, in a controlled environment, of model organism Mytilus galloprovincialis(Lamarck1819)

8

[14]CanesiL,PezzatiE,StauderM,etal.VibriocholeraeinteractionswithMytilusgalloprovincialishemocytesmediatedbyserumcomponents.FrontiersinMicrobiology.2013;4:371.doi:10.3389/fmicb.2013.00371.

[15]García-García,E.,Prado-Alvarez,M.,Novoa,B.,Figueras,A.,Rosales,C.,2008. ImmuneResponsesofMusselhemocytesubpopulationsaredifferentiallyregulatedbyenzymesofthePI3-K,PKC,andERKkinasefamilies.DevelopmentandComparativeImmunology32,637e653.

[16]Canesi,L.,Ciacci,C.,Lorusso,L.C.,Betti,M.,Guarnieri,T.,Tavolari,S.,Gallo,G.,2006a.Immunomodulationby17b-Estradiolinbivalvehemocytes.TheAmericanJournalofphysiology,regulatory.IntegrativeandComparativePhysiology291,R664eR673

[17] Canesi, L., Ciacci, C., Betti, M., Scarpato, A., Citterio, B., Pruzzo, C., Gallo, G., 2003. Effects of PCBcongeners on the immune function of Mytilus hemocytes: alterations of tyrosine kinase-mediated cellsignalling.AquaticToxicology63,293e306.

[18]Canesi,L.,Betti,M.,Ciacci,C.,Lorusso,L.C.,Pruzzo,C.,Gallo,G.,2006b.Cellsignalingintheimmuneresponseofmusselhemocytes.InvertebrateSurvivalJournal3,40e49.

[19]Canesi, L.,Ciacci,C., Lorusso,L.C.,Betti,M.,2007a.Effectsofendocrinedisruptingchemicalson theimmune system of the edible bivalve mollusc Mytilus. In: Marino, M., Mita, D.G. (Eds.), The EndocrineDisruptors.TransworldResearchNetwork,Trivandrum,Kerala,India,pp.1e12.

[20] Canesi, L., Ciacci, C., Lorusso, L.C., Betti,M., Gallo, G., Poiana, G.,Marcomini, A., 2007b. Effects ofTriclosan onMytilus galloprovincialis hemocyte function and digestive gland enzyme activities: possiblemodesofactiononnontargetorganisms.ComparativeBiochemistryandPhysiologyC145,464e472.

[21]Canesi,L.,Lorusso,L.C.,Ciacci,C.,Betti,M.,Regoli,F.,Poiana,G.,Gallo,G.,Marcomini,A.,2007c.Effectsof blood lipid lowering pharmaceuticals (bezafi- brate and gemfibrozil) on immune and digestive glandfunctionsofthebivalvemollusc,Mytilusgalloprovincialis.Chemosphere69,994e1002

[22] Canesi, L., Lorusso, L.C., Ciacci, C., Betti, M., Rocchi, M., Poiana, G., Marcomini, A., 2007d.ImmunomodulationofMytilushemocytesbyindividualestrogenicchemicalsandenvironmentallyrelevantmixturesofestrogens:invitroandinvivostudies.AquaticToxicology81,36e44.

[23]Canesi,L.,Betti,M.,Ciacci,C.,Lorusso,L.C.,Pruzzo,C.,Gallo,G.,2006b.Cellsignalingintheimmuneresponseofmusselhemocytes.InvertebrateSurvivalJournal3,40e49.

[24] Freitas, R., Gómez-Marín, C., Wilson, J.M., Casares, F., and Gómez-Skarmeta, J.L. (2012) Hoxd13contributiontotheevolutionofvertebrateappendages.DevCell23(6):1219-1229.

[25]MaffeiA., LamboM.E., TurrigianoG.G. (2010).Developmental regulationofexperience-dependentinhibitoryplasticity.J.Neurosci.30,3304–3309

[26] Coppola, L., E. Diamond Riquier, and T. Carval(2016), DYFAMED observatory data, SEANOE,doi:10.17882/43749.