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Toxoplasma gondii in stranded marine mammals from the North Sea and Eastern Atlantic Ocean: Findings and diagnostic difficulties

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Veterinary

Parasitology

j o u r n a l h o m e p a g e :w w w . e l s e v i e r . c o m / l o c a t e / v e t p a r

Research

paper

Toxoplasma

gondii

in

stranded

marine

mammals

from

the

North

Sea

and

Eastern

Atlantic

Ocean:

Findings

and

diagnostic

difficulties

Norbert

van

de

Velde

a

,

Brecht

Devleesschauwer

b,c,∗

,

Mardik

Leopold

d

,

Lineke

Begeman

e,1

,

Lonneke

IJsseldijk

f

,

Sjoukje

Hiemstra

f

,

Jooske

IJzer

f

,

Andrew

Brownlow

g

,

Nicholas

Davison

g

,

Jan

Haelters

h

,

Thierry

Jauniaux

i

,

Ursula

Siebert

j

,

Pierre

Dorny

b,k

,

Stéphane

De

Craeye

l

aDepartmentofPathology,BacteriologyandAvianDiseases,FacultyofVeterinaryMedicine,GhentUniversity,Merelbeke,Belgium bDepartmentofVirology,ParasitologyandImmunology,FacultyofVeterinaryMedicine,GhentUniversity,Merelbeke,Belgium cDepartmentofPublicHealthandSurveillance,ScientificInstituteofPublicHealth(WIV-ISP),Brussels,Belgium

dWageningenIMARESInstituteforMarineResourcesandEcosystemStudies,DenHelder,TheNetherlands eViroscience,ErasmusMedicalCentre,Rotterdam,TheNetherlands

fUtrechtUniversity,FacultyofVeterinaryMedicine,Dept.Pathobiology,TheNetherlands

gScottishMarineAnimalStrandingScheme,SACConsulting.VeterinaryServices,Drummondhill,Inverness,IV24JZScotland,UK hRoyalBelgianInstituteofNaturalSciences(RBINS),Ostend,Belgium

iDepartmentofMorphologyandPathology,FacultyofVeterinaryMedicine,UniversityofLie`ge,Liège,Belgium jInstituteforTerrestrialandAquaticWildlifeResearch,UniversityofVeterinaryMedicineHannover,Büsum,Germany kDepartmentofBiomedicalSciences,InstituteofTropicalMedicine,Antwerp,Belgium

lNationalReferenceLaboratoryforToxoplasmosis,DepartmentofCommunicableandInfectiousDiseases,ScientificInstituteofPublicHealth(WIV-ISP),

Brussels,Belgium

a

r

t

i

c

l

e

i

n

f

o

Articlehistory: Received16June2016

Receivedinrevisedform19October2016 Accepted22October2016 Keywords: Toxoplasmagondii Marinemammals Seroprevalence PCR MAT IFA ELISA

a

b

s

t

r

a

c

t

Theoccurrenceofthezoonoticprotozoanparasite Toxoplasmagondiiin marinemammals remains apoorlyunderstoodphenomenon.Inthisstudy,samplesfrom589marinemammalspeciesand34 Europeanotters(Lutralutra),strandedonthecoastsofScotland,Belgium,France,TheNetherlands andGermany,weretestedforthepresenceofT.gondii.Brainsampleswereanalysedbypolymerase chainreaction(PCR)fordetectionofparasiteDNA.Bloodandmusclefluidsamplesweretestedfor spe-cificantibodiesusingamodifiedagglutinationtest(MAT),acommercialmulti-speciesenzyme-linked immunosorbentassay(ELISA)andanimmunofluorescenceassay(IFA).Outof193animalstestedbyPCR, onlytwoharbourporpoise(Phocoenaphocoena)cerebrumsamples,obtainedfromanimalsstrandedon theDutchcoast,testedpositive.Theserologicalresultsshowedawidevariationdependingonthetest used.Usingacut-offvalueof1/40dilutioninMAT,141outof292animals(41%)werepositive.Using IFA,30outof244testedsamples(12%)werepositiveata1/50dilution.ThecommercialELISAyielded 7%positiveswithacut-offofthesample-to-positive(S/P)ratio≥50;and12%whenthecut-offwasset atS/Pratio≥20.ThehighnumberofpositivesinMATmaybeanoverestimationduetothehighdegree ofhaemolysisofthesamplesand/orthepresenceoflipids.TheELISAresultscouldbean underestima-tionduetotheuseofamultispeciesconjugate.OurresultsconfirmthepresenceofT.gondiiinmarine mammalsinTheNetherlandsandshowexposuretotheparasiteinboththeNorthSeaandtheEastern AtlanticOcean.WealsohighlightthelimitationsofthetestsusedtodiagnoseT.gondiiinstrandedmarine mammals.

©2016ElsevierB.V.Allrightsreserved.

∗ Correspondingauthorat:DepartmentofPublicHealthandSurveillance, Sci-entificInstituteofPublicHealth(WIV-ISP),RueJulietteWytsmanstraat14,1050 Brussels,Belgium.

E-mailaddress:brechtdv@gmail.com(B.Devleesschauwer).

1 Duringthisresearch,LBwasworkingatUtrechtUniversity,FacultyofVeterinary

Medicine,TheNetherlands.

1. Introduction

Toxoplasma gondiiis a globallydistributed zoonotic parasite. Itisassumedthatallwarm-bloodedanimals,includinghumans, canact asintermediate hosts, whileonly felidsactas thefinal hosts(Tenteretal.,2000).AprimaryinfectioninfelidsallowsT. gondiitocompleteitssexualcycle,resultinginthefaecalshedding ofmillionsofoocystsintotheenvironment(Dubey,2010).These http://dx.doi.org/10.1016/j.vetpar.2016.10.021

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oocystsareabletoreachcoastalseawatersandseveralstudieshave demonstratedthepresenceofT.gondiiinmarinemammalspecies includingpinnipeds,cetaceans,sirenians,seaotters(Enhydralutris) andpolarbears(Ursusmaritimus)(Coleetal.,2000;Dubey,2010; Mathewsetal.,2012;Oksanenetal.,2009).Different transmis-sionroutessuchascoastalrun-offandmechanicalvectorshave beenhypothesized,buttheexactmodeoftransmissionremains unknown(Arkushetal.,2003;Lindsayetal.,2001;Massieetal., 2010).Immunosuppressivefactors,suchaspolychlorbiphenylsand Morbillivirusinfection couldmakemarine mammalsmore sus-ceptibletodiseaseinducedbyT.gondiiinfection(Mazzarioletal., 2012).Besidesbeingapathogenicagentcapableofaffectingmarine mammalhealth,T.gondiiactsasanindicatorofmarinepollution (Jessupetal.,2004),withmarinemammalsbeingexcellentsentinel species(Conradetal.,2005;deMouraetal.,2014;Jessupetal., 2004;Moore,2008;Stewartetal.,2008).

VariousserologicaltestsareavailabletodetectthepresenceofT. gondiiantibodiesinhumansandanimals.TheSabin-Feldmandye testisconsideredthegoldstandard test,butistimeconsuming andmakesuseofliveparasites.Althoughnotvalidatedformarine mammals,themodifiedagglutinationtest(MAT)maybean appeal-ingalternativemethod,becauseofitsspeedandeaseofuse,butalso becauseitdoesnotrequirespecies-specificsecondaryantibodies (DesmontsandRemington,1980).Thisisparticularlyusefulwhen testingwildlife,suchasmarinemammals(Cabezónetal.,2011; Santosetal.,2011;Jensenetal.,2012).Recently,however,Blanchet etal.(2014)questionedthereliabilityofMATintheserological diagnosisofT.gondiiinfectioninharbourporpoises(Phocoena pho-coena).ThiswasbasedonacomparisonofMATonuntreatedserum sampleswithenzyme-linkedimmunosorbent assay(ELISA) and polymerasechainreaction(PCR),whichsuggestedthatMATmay givefalsepositiveresults.Adherenceofcomponentstotachyzoites otherthanspecificantibodies,suchassamplesrichinparticulate matterandlipids,mayberesponsibleforthesefalsepositive reac-tions.Achloroform‘clean-up’ofserumsamplesmaypreventthis problem(Blanchetetal.,2014).Withtheexceptionofharbour por-poises(Phocoenaphocoena),however,thismethodhasnotbeen evaluatedforothermarinemammalspecies.

TheaimofthisstudywastoassesstheprevalenceofT.gondii invariousmarinemammalspeciesstrandedonScottish,Belgian, French,Dutchand Germancoastlinesof theNorth Seaand the AtlanticOceanaroundScotland.AsthereliabilityofMATinmarine mammalsampleshasbeenquestioned(Blanchetetal.,2014), it wasdecidedtoperformadditionaltestingtoevaluateandcompare variousserologicaldetectionmethods.

2. Materialsandmethods 2.1. Samples

From589free-rangingstrandedmarinemammalsnecropsiedat differentinstitutesinTheNetherlands,Belgium,France,Germany and Scotland (Table 1), a selection of samples including cere-brumandcerebellum, serumand/ormusclefluid wasobtained. Additionally,samplesfrom34free-rangingEuropeanotters(Lutra lutra)livingalongtheNorthSeacoastinScotlandwerealso ana-lysed.Convenience-basedsamplingfromthesedifferentinstitutes resultedinacollectionofsamplesfromatimeperiodof1992–2013 thatcovered17differentmarinemammalspecies.Anoverviewof thenumbersandspeciesofcollectedandtestedanimalsisgivenin Table2.Brainsamples(n=193)weretestedbyPCR.PositivePCR sampleswerefurtheranalysedbyhistopathologyand immunohis-tochemistry.Allserum(n=292)andmusclefluid(n=193)samples wereanalysedwithMATandalargepartofthecollectedserum sampleswasfurtheranalysedwithanimmunofluorescenceassay

(IFA)(n=244)andamultispeciesELISA(n=241)(Table3).Dueto therelativelylargevolumesrequiredbyMATandIFA,itwasnot possibletotestallsampleswithallthreetests.

2.2. PCR

2.2.1. DNAextraction

DNAfromthebrainsampleswasisolatedwiththeQIAmpDNA MiniKit(Qiagen,Venlo,TheNetherlands)aspreviouslydescribed byDeCraeyeetal.(2011).Briefly,400mgofeachbrainsample wasmixedwith20␮lofproteinaseKand400␮l ofafirstlysis bufferand vortexedthoroughlypriortoovernightincubationat 56◦C.Thenextday,400␮lofasecondlysisbufferwasaddedand themixturewashomogenizedandfurtherincubatedat70◦Cfor 20min.Aftercoolingonice,600␮lofachloroform/isoamylalcohol (24/1)mixturewasaddedandeachsamplewasvortexedandthen centrifugedat22,000×g(4◦C)for30min.Thesupernatant was transferredintoanewtubeandtheDNAwasprecipitatedbyadding 400␮lof95%ethanolcooledat−20◦C.Fromthispointonwards,the

manufacturer’sprotocolwasfollowed.Themixturewastransferred toaspin-columnandwashedoncewith500␮lofafirstwashing bufferandoncewith500␮lofasecondwashingbuffer.Thepurified DNAwasthenelutedfromthecolumnusing200␮lofanelution buffer.Thesampleswerestoredat−20◦Cuntilfurthertesting.

2.2.2. Real-timePCR,histopathologyandimmunohistochemistry TheisolatedDNAsamplesweretestedbyduplexreal-timePCR (qPCR)asdescribedbyDeCraeyeetal.(2011).The529-basepair repeatelementwasusedasatarget(Homanetal.,2000).Table4 givesanoverviewoftheprimersandprobesusedandtheirfinal concentrationperreaction.DNAqualityandPCRinhibitionwere assessedusingcellularr18Sasa target(Table4).Sampleswere runandanalysedonaBioRadCFX96thermocycler/detection sys-tem(BioRad,Hercules,CA,USA).Ineachrun,apositiveextraction control sample consisting of DNA extracted froma brain sam-plefromamouseexperimentallyinfectedwiththe1984-IPB-GAN T. gondii strainwas includedas wellas onesample containing onlyphosphatebufferedsaline(PBS)asanegativecontrol. Pos-itiveresultsfromPCRwereevaluatedusinghistopathologyand immunochemicalstainsfordetectingT.gondiitachyzoites. Neutral-buffered 10% formalin fixed samples were routinely processed in paraffin for light microscopy using haematoxylin-eosin and immunohistochemicalstaining.For immunohistochemical stain-ing,anavidin-biotincomplexmethodusingpolyclonalantibodies againstT.gondii(1:100)wasapplied(Key,2009).

2.3. Serologicalexamination

2.3.1. Modifiedagglutinationtest(MAT)

TheseraweretestedwithacommercialMATkit(Toxo-Screen DA® kit,Biomérieux,Marcy-l’Etoile,France)accordingto

manu-facturer’sinstructions.Briefly, samplesweredilutedin PBSand 25␮lofeachdilutionwasappliedinaroundbottommicrotiter platewith25␮l2-mercaptoethanolat0.2mol/l.Tothis,50␮lof a1/5dilutionofwholeformolizedtachyzoitesinbovinealbumin boratesaline(suppliedinthekit)bufferwasadded.Theplatewas mixedfor1minonaplatemixerat300revolutionsperminute andincubatedovernightatroomtemperature.Thenegativeand positivecontrolswerebothsuppliedbythemanufacturerand con-sistedofgoatserum.Thepositivecontrolwascalibratedagainstthe WorldHealthOrganizationstandard,apositivestandardserum cal-ibratedtointernationalunits.Agglutinationina1/40dilutionwas consideredtobeapositiveresultaccordingtothemanualofthe diagnostickitandearlierstudiesonmarinemammalsera(Jensen etal.,2010,2012;Oksanenetal.,1998).Accordingtothe

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manufac-Table1

Institutesfromwhichsampleswerecollected.

Name Location Locationofthestrandedanimals

UtrechtUniversity FacultyofVeterinaryMedicine,Dept. Pathobiology,Utrecht,TheNetherlands

Dutchcoastline–NorthSeaand WaddenSea

InstituteforMarineResourcesand EcosystemStudies(IMARES)

Texel,TheNetherlands Dutchcoastline–NorthSeaand WaddenSea

InstituteforTerrestrialandAquatic WildlifeResearch(ITAW)

UniversityofVeterinaryMedicine Hannover,Büsum,Germany

Germancoastline–NorthSeaand WaddenSea

RoyalBelgianInstituteofNatural Sciences

Ostend,Belgium Belgiancoastline–NorthSea

UniversityofLiège FacultyofVeterinaryMedicine,

UniversityofLiège,Belgium

Belgian,DutchandnorthernFrench coastline–NorthSea

ScottishMarinemammalStranding Scheme(SMASS)

Scotland’sRuralCollege,Inverness, Scotland

Scottishcoastline–AtlanticOceanand NorthSea

Table2

NumberandspeciesofanimalstestedforToxoplasmagondiifromthedifferentlocations.

Serum Serum+Brain Brain Brain+Muscle Muscle Total

Belgiancoastline–NorthSea

Finwhale(Balaenopteraphysalus) 1 1

Greyseal(Halichoerusgrypus) 2 2

Harbourporpoise(Phocoenaphocoena) 20 1 48 69

Harbourseal(Phocavitulina) 8 1 9

Hoodedseal(Cystophoracristata) 1 1

White-beakeddolphin(Lagenorhynchusalbirostris) 1 1

NorthernFrenchcoastline–NorthSea

Finwhale(Balaenopteraphysalus) 1 1 2

Greyseal(Halichoerusgrypus) 1 1

Harbourporpoise(Phocoenaphocoena) 3 12 15

Harbourseal(Phocavitulina) 2 3 5

Stripeddolphin(Stenellacoeruleoalba) 1 1

Dutchcoastline–NorthSeaandWaddenSea

Harbourporpoise(Phocoenaphocoena) 16 15 68 5 81 185

Harbourseal(Phocavitulina) 28 28

Germancoastline–NorthSeaandWaddenSea

Harbourporpoise(Phocoenaphocoena) 2 19 21

Harbourseal(Phocavitulina) 2 19 21

Scottishcoastline–AtlanticOcean

Atlanticwhite-sideddolphin(Lagenorhynchusacutus) 7 7

Bottlenosedolphin(Tursiopstruncatus) 4 4

Finwhale(Balaenopteraphysalus) 1 1

Greyseal(Halichoerusgrypus) 5 5

Harbourporpoise(Phocoenaphocoena) 47 47

Harbourseal(Phocavitulina) 6 6

Killerwhale(Orcinusorca) 2 2

Long-finnedpilotwhale(Globicephalamelas) 6 6

Minkewhale(Balaenopteraacutorostrata) 2 2

Risso’sdolphin(Grampusgriseus) 4 4

Short-beakedcommondolphin(Delphinusdelphis) 9 9

Sowerby’sbeakedwhale(Mesoplodonbidens) 2 2

Spermwhale(Physetermacrocephalus) 1 1

Stripeddolphin(Stenellacoeruleoalba) 5 5

White-beakeddolphin(Lagenorhynchusalbirostris) 4 4

Scottishcoastline–NorthSea

Atlanticwhite-sideddolphin(Lagenorhynchusacutus) 11 11

Bottlenosedolphin(Tursiopstruncatus) 2 2

Greyseal(Halichoerusgrypus) 12 12

Harbourporpoise(Phocoenaphocoena) 56 56

Harbourseal(Phocavitulina) 14 14

Killerwhale(Orcinusorca) 1 1

Long-finnedpilotwhale(Globicephalamelas) 5 5

Minkewhale(Balaenopteraacutorostrata) 3 3

Risso’sdolphin(Grampusgriseus) 4 4

Seiwhale(Balaenopteraborealis) 1 1

Short-beakedcommondolphin(Delphinusdelphis) 4 4

Sowerby’sbeakedwhale(Mesoplodonbidens) 2 2

Spermwhale(Physetermacrocephalus) 1 1

Stripeddolphin(Stenellacoeruleoalba) 4 4

White-beakeddolphin(Lagenorhynchusalbirostris) 2 2

Europeanotter(Lutralutra) 34 34

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Table3

ResultsbyspeciesofserumsamplestestedforToxoplasmagondiiwithmodifiedagglutinationtest(MAT),enzyme-linkedimmunosorbentassay(ELISA)witha sample-to-positiveratio(S/P)cut-offat20and50,andimmunofluorescentassay(IFA).

MAT ELISA(S/P≥20) ELISA(S/P≥50) IFA

No.tested No.positive(%) No.tested No.positive(%) No.tested No.positive(%) No.tested No.positive(%)

Dutchcoastline–NorthandWaddenSea 31 4(13)

Harbourporpoise(Phocoenaphocoena) 31 4(13)

Scottishcoastline–AtlanticOcean 105 54(51) 98 7(7.1) 98 3(3.1) 100 7(7.0)

Atlanticwhite-sideddolphin(Lagenorhynchusacutus) 7 7(100) 7 0(0) 7 0(0) 7 0(0)

Bottlenosedolphin(Tursiopstruncatus) 4 3(75) 4 0(0) 4 0(0) 4 0(0)

Finwhale(Balaenopteraphysalus) 1 0(0) 1 0(0)

Greyseal(Halichoerusgrypus) 5 2(40) 4 0(0) 4 0(0) 4 0(0)

Harbourporpoise(Phocoenaphocoena) 47 22(47) 43 0(0) 43 0(0) 44 1(2)

Harbourseal(Phocavitulina) 6 0(0) 6 0(0) 6 0(0) 6 0(0)

Killerwhale(Orcinusorca) 2 1(50) 2 0(0) 2 0(0) 2 0(0)

Long-finnedpilotwhale (Globicephalamelas) 6 5(83) 5 3(60) 5 2(40) 5 3(60)

Minkewhale (Balaenopteraacutorostrata) 2 0(0) 2 0(0) 2 0(0) 2 0(0)

Risso’sdolphin(Grampusgriseus) 4 2(50) 4 1(25) 4 0(0) 4 1(25)

Short-beakedcommondolphin(Delphinusdelphis) 9 5(56) 9 1(11) 9 0(0) 9 1(11)

Sowerby’sbeakedwhale (Mesoplodonbidens) 2 1(50) 2 0(0) 2 0(0) 2 0(0)

Spermwhale(Physetermacrocephalus) 1 1(100) 1 0(0) 1 0(0) 1 0(0)

Stripeddolphin(Stenellacoeruleoalba) 5 2(40) 5 0(0) 5 0(0) 5 0(0)

White-beakeddolphin(Lagenorhynchusalbirostris) 4 3(75) 4 2(50) 4 1(25) 4 1(25)

Scottishcoastline–NorthSea 156 63(40) 143 21(15) 143 13(9.1) 144 23(16)

Atlanticwhite-sideddolphin(Lagenorhynchusacutus) 11 4(36) 11 0(0) 11 0(0) 11 0(0)

Bottlenosedolphin(Tursiopstruncatus) 2 0(0) 1 0(0) 1 0(0) 1 0(0)

Greyseal(Halichoerusgrypus) 12 3(25) 9 1(11) 9 0(0) 9 0(0)

Harbourporpoise(Phocoenaphocoena) 56 21(38) 53 0(0) 53 0(0) 54 1(2)

Harbourseal(Phocavitulina) 14 4(29) 11 2(18) 11 1(9) 11 2(18)

Killerwhale(Orcinusorca) 1 1(100) 1 0(0) 1 0(0) 1 0(0)

Long-finnedpilotwhale (Globicephalamelas) 5 3(60) 5 1(20) 5 1(20) 5 1(20)

Minkewhale(Balaenopteraacutorostrata) 3 1(33) 3 0(0) 3 0(0) 3 0(0)

Risso’sdolphin(Grampusgriseus) 4 2(50) 3 1(33) 3 0(0) 3 1(33)

Seiwhale(Balaenopteraborealis) 1 1(100) 1 0(0) 1 0(0) 1 0(0)

Short-beakedcommondolphin(Delphinusdelphis) 4 3(75) 4 1(25) 4 0(0) 4 1(25)

Sowerby’sbeakedwhale (Mesoplodonbidens) 2 1(50) 2 0(0) 2 0(0) 2 0(0)

Spermwhale(Physetermacrocephalus) 1 0(0) 1 0(0) 1 0(0) 1 0(0)

Stripeddolphin(Stenellacoeruleoalba) 4 2(50) 4 0(0) 4 0(0) 4 0(0)

White-beakeddolphin(Lagenorhynchusalbirostris) 2 1(50) 2 1(50) 2 0(0) 2 0(0)

Europeanotter(Lutralutra) 34 16(47) 32 14(44) 32 11(34) 32 17(53)

Total 292 121(41) 241 28(12) 241 16(6.6) 244 30(12)

Table4

Primersandprobesusedinthereal-timePCR.

Target Name Sequence53 5Modificationa 3Modificationb Concentrationc

Primers T.gondii T2 CGGAGAGGGAGAAGATGTT 400nM

T3 GCCATCACCACGAGGAAA 400nM

Cellularr18S VF1 GATTAAGTCCCTGCCCTTT 200nM VR1 CACACCGCCCGTCGCTACTACC 200nM Probes T.gondii TP CTTGGCTGCTTTTCCTGGAGGG FAM488 BHQ1 66nM

Cellularr18S VP CACACCGCCCGTCGCTACTACC TexasRed547 BHQ2 66nM

aFluorophoreusedasreporter. b Quenchermolecule.

c Finalconcentrationperreaction.

turer’sinstructions,sampleswerealsotestedata1/4000dilution tomonitorforapotentialprozoneeffectata1/40dilution.

2.3.2. Enzyme-linkedimmunosorbentassay(ELISA)

Two hundred and forty-one sera of the 292 collected sera were tested for the presence of anti-T. gondii IgG withthe ID Screen Toxoplasmosis Indirect Multi-species ELISA kit (ID.vet, Montpellier,France).Samplesweretestedand analysed accord-ingtothemanufacturer’sinstructions.Briefly, eachsamplewas diluted1/10inthesupplieddilutionbufferand100␮lwasapplied in the antigen-coated 96 well plate. After 45min of incuba-tionat room temperature,the platewas washed 3 timeswith the supplied washing buffer. 100␮l of the multispecies con-jugate diluted 1/10 in the supplied buffer was then applied in each well.The plate was incubated for another 30min and

washed3times.Thecolorimetricreactionwasdonewiththe sup-plied3,3,5,5-tetramethylbenzidineand stoppedafter15min withthesuppliedstopsolution.Foreachsamplethe sample-to-positive(S/P)ratiowascalculatedusingtheopticaldensity(OD) as (ODsample−ODnegativecontrol)/(ODpositivecontrol−ODnegativecontrol),

with the positive and negative controlssupplied with the kit. Accordingtothemanufacturer’sinstructions,asamplewas con-sideredpositiveiftheS/Pratiowas≥50.

2.3.3. Immunofluorescentassay(IFA)

Twohundredandforty-fourofthe292collectedserumsamples weretested forthepresenceofanti-T.gondiiIgGusingIFA.The IFAwasperformedusingcommerciallyavailableantigencoated slides(Toxo-SpotIF,Biomerieux,Capronne,France).Theserawere diluted1/50inPBSand50␮lofeachserumdilutionwasappliedon

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Table5

Conjugatesusedintheimmunofluorescenceassay.

Fluoresceinisothiocyanatelabelledconjugatea Manufacturer Usedfor

goatanti-bovineIgG(H+L) KPL(Gaithersburg,Maryland,USA) Dolphins,porpoises,whalesb

goatanti-dogIgG(H+L) KPL(Gaithersburg,Maryland,USA) Sealsc

goatanti-ferretIgG(H+L) KPL(Gaithersburg,Maryland,USA) Otterc

a(H+L)conjugateagainstIgGheavyandlightchains. bNollensetal.(2008).

c Milleretal.(2002).

theantigencoatedslides.Theslideswereincubatedat37◦Cina sat-uratedmoistatmospherefor30min.Theslideswerethenwashed oncewithPBSandoncewithdistilledwater.Afterdrying,30␮lof thefluoresceinisothiocyanatelabelledconjugatewasappliedina 1/25dilutioninPBSwithEvansBlueascounterdye.Thefollowing conjugateswereused:anti-bovineIgGtotestcetaceansera(Jaber etal.,2003),anti-ferretIgGtotestottersera(Milleretal.,2002)and anti-dogIgGtotestsealsera(Carlson-Bremeretal.,2015).Table5 liststheconjugatesusedpertestedanimalspecies.Afterwashing anddrying,theslideswerereadwithafluorescencemicroscope (NikoneclipseNi-U).Samplesthathadtestedpositiveand nega-tiveinELISAwereusedaspositiveandnegativecontrolsforeach typeofconjugate.

2.3.4. Musclefluid

MusclefluidsamplesweretestedusingMAT.Musclefluidwas collectedbysqueezingthedefrostedmusclesamplesabovea15ml centrifugetube.Firstly,47samplesfromharbourporpoises (Pho-coenaphocoena)fromTheNetherlandsweretestedatthefollowing dilutions:1/4,1/200and1/400.Sincenopositivitywasfoundat the1/200and1/400dilution,theremaining146musclefluid sam-plesweretestedata1/2,1/10and1/64dilutiontobetterestimate theantibodytitres.Doubtfulresultswereretestedfor confirma-tion.Forbesetal.(2012)showedthata1/10dilutionofmuscle fluidsamplesfrombothexperimentallyinfectedandnegativepigs identifiedallpositivecases.Therefore,samplesinthissurveythat showedagglutinationat1/10dilutionwereconsideredpositive. 3. Results

3.1. PCR

Thepositiveandnegativecontrolsandthenegativeresultsofthe non-templatecontrolsconfirmedpropertestingconditions with-outcontaminationduringextraction.

Twooutof193brainsampleswerepositiveforT.gondiiDNA:a cerebrumsamplefromayoungmaleharbourporpoise(Phocoena phocoena)strandedin2010nearKatwijk,TheNetherlands(Ctvalue of 34.4)and a cerebrum samplefrom anadult femaleharbour porpoise(Phocoenaphocoena)strandedin 2010nearNoordwijk, TheNetherlands(Ctvalueofcycle40.4).Thecerebellumsamples frombothporpoisestestednegative.Furtherhistopathologicaland immunohistochemicalexaminationsofbraintissuesofboth ani-malscouldnotconfirmthepresenceofT.gondii.Othertissuesof theseanimalswerenotavailableforfurtherserologicaltesting. 3.2. Serology—serumsamples

Table3summarizestheresultsoftheserologicalassaysper ani-malspecies.MarinemammalscollectedfromtheDutchcoastline, theScottishcoastline alongtheAtlanticOceanand theScottish coastlinealongtheNorthSeashowedaseroprevalenceof13%,51% and39%,respectivelyinMAT.Sixteenofthe34(47%)Europeanotter (Lutralutra)samplesfromtheScottishcoastlinealongtheNorthSea

testedpositive.Fromthe261seracollectedfromScotland,244and 241serawereretestedusingIFAandELISA,respectively.InIFA,13 outof212marinemammalsamples(6.1%)testedpositiveata1/50 dilutionand17ofthe32(53%)Europeanotter(Lutralutra)samples testedpositive.ThecommercialELISAyieldedaseroprevalenceof 2%inmarinemammalsampleswhenusingaS/Pratiocut-offof50, and7%whenloweringthecut-offto20.ELISAidentified11(34%) and14(44%) ofthe32Europeanotter(Lutralutra)samplesper cut-offrespectively.

Theoneharbourporpoise(Phocoenaphocoena)fromtheAtlantic Ocean,whichtestedpositiveinIFA,alsotestedpositiveinMAT. Theoneharbourporpoise(Phocoenaphocoena)fromtheNorthSea, whichtestedpositiveinIFA,testednegativeinMAT.Theonegrey seal(Halichoerusgrypus)fromtheNorthSea,which tested posi-tiveinELISAwitha cut-offvalueof20, testedpositivein MAT. Table 6 shows the agreement betweenresults in testing long-finnedpilotwhale(Globicephalamelas),Risso’sdolphin(Grampus griseus), short-beaked common dolphin (Delphinus delphis) and white-beakeddolphin(Lagenorhynchusalbirostris)samples. Agree-mentwasdefinedasasimilarresultinallthreediagnosticmethods. Ofthe209marinemammalstestedwithallthreeserological tech-niques,4(1.9%)marinemammals(1harbourseal(Phocavitulina),2 long-finnedpilotwhales(Globicephalamelas)and1white-beaked dolphin(Lagenorhynchusalbirostris))testedpositiveonalltestsand 104marinemammals(50%)testednegativeonalltests,leaving101 marinemammals(48%)withinconsistentresultsacrosstests.Nine outof32(28%)Europeanotter(Lutralutra)samplestestedpositive onallthreetests.

3.3. Serology—musclefluidsamples

Out of the first batch of 47 muscle samples from The Netherlands,21(43%)testedpositiveina1/4dilutioninMAT.No positivitywasfoundat1/200and1/400dilutions.Furthertesting wasdoneusinglowereddilutions,i.e.,1/2,1/10,1/64.Outofall146 animalstestedwiththeselatterdilutions,only12samples(8.2%) showedagglutinationina1/2dilution(datanotshown).Allthese sampleswerenegativeusingthecut-offvalueof1/10.

4. Discussion

Inthisstudy,589marinemammalsof17differentspeciesand 34Europeanotters(Lutralutra)wereexaminedforthepresence ofT.gondii,usingvariousdetectionmethods.PreviousstudiesonT. gondiiinmarinemammalsshowedthatthisparasiteisabletoreach andinfectmarinemammals(Cabezónetal.,2011;Rengifo-Herrera etal.,2012).InfectionwithT.gondiiinmarinemammalsmayresult inclinicaldisease(Carlson-Bremer etal.,2015;Mikaelianetal., 2000; Van Bressemet al., 2009). Thishasbeenclearly demon-stratedinCaliforniaseaotters(Euhydralutrisnereis)(Milleretal., 2004),Hector’sdolphins(Cephalorhynchushectori)(Roeetal.,2013) andharbourporpoises(Phocoenaphocoena)(Herderetal.,2015).T. gondiiclinicaldiseasehasalsobeenrecordedwithco-infectionsof Brucellaceti,andListeriamonocytogenesinstripeddolphins(Stenella

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Table6

Agreementbetweenresultsinserologicaltestingoflong-finnedpilotwhale,Risso’sdolphin,short-beakedcommondolphinandwhite-beakeddolphinsamples.

Animalno. MAT ELISA(S/P≥20) ELISA(S/P≥50) IFA Agreement Long-finnedpilot

whale

(Globicephalamelas)

AtlanticOcean 1 N N N N Yes

2 P P P P Yes

3 P P N P No

4 P − − − −

5 P P P P Yes

6 P N N N No

NorthSea 1 N N N N Yes

2 P N N N No 3 N N N N Yes 4 P N N N No 5 P P P P Yes Risso’sdolphin (Grampusgriseus)

AtlanticOcean 1 N N N N Yes

2 N N N N Yes 3 P P N P No 4 P N N N No NorthSea 1 N − − − − 2 N N N N Yes 3 P P N P No 4 P N N N No Short-beakedcommon dolphin (Delphinusdelphis) AtlanticOcean 1 P N N N No 2 P N N N No 3 P N N N No 4 P N N N No 5 P N N N No 6 N P N P No 7 N N N N Yes 8 N N N N Yes 9 N N N N Yes NorthSea 1 P P N P No 2 P N N N No 3 P N N N No 4 N N N N Yes White-beakeddolphin (Lagenorhynchus albirostris)

AtlanticOcean 1 P P P P Yes

2 P N N N No

3 P N N N No

4 N N N N Yes

NorthSea 1 P P N N No

2 N N N N Yes

MAT=modifiedagglutinationtest;ELISA=enzyme-linkedimmunosorbentassay;S/P=sample-to-positiveratio;IFA=immunofluorescentassay;P=positive,N=negative, −=nottested.

coeruleoalba)(DiGuardoetal.,2010;Grattarolaetal.,2016),and withmorbillivirusinfinwhales(Balaenopteraphysalus)(Mazzariol etal.,2012).Additionally,researchonT.gondiiinmarinemammals isrelevantasT.gondiiactsasanindicatorformarinepollutionand marinemammalsaresentinelspeciesforthehealthofthemarine ecosystemstheylivein(deMouraetal.,2014;Gibsonetal.,2011; Moore,2008).

Samplingofwildlifeischallengingandcomeswithunknown factorsandbiases(Nusseretal.,2008).Convenience-based sam-pling is not a random selection of animals and therefore does notrepresentthecompletewildlifepopulation.Inthisstudyonly strandedanimalsweretested.Sealsaremore coastalspecies in comparisonwithmostcetaceansandcouldthereforebe overrepre-sented.Thesampledpopulationwaslargelydominatedbyharbour porpoises(Phocoenaphocoena),asthis isthemostabundantsea mammalspeciesintheinvestigatedareas.Theconvenience-based samplingfurtherexplains thedifferences in sampling methods usedacrossanimals.Indeed,thesetof samplesperanimal var-iedacrossinstitutesandfurtherdependedonfactorssuchasthe preservationstateoftheanimalcarcass–e.g.,fewersampleswere takenfromdecomposed animals.Asourstudycoveredsamples takeninatimespanof21years,notallnecropsiedanimalswere sampledspecificallyfor Toxoplasmaresearch; brainand muscle sampleswerethereforenotavailablefromallanimals.

Thediagnostictechniquesusedinthisstudyarenotvalidated for marinemammalsby themanufacturers and thereforetheir

diagnostictestcharacteristicsformarinemammalsamplesarenot exactlyknown.For detectingT. gondii inwildanimals, brainis demonstratedtobeausefulsamplingtissue(DeCraeyeetal.,2011). Outof193animalstestedbyPCR,twoharbourporpoise(Phocoena phocoena)cerebrumsamplesprovedpositiveforT.gondiiDNA.The cerebellumsamplesofthesametwoanimalstestednegativein PCR,whichmightbeduetotheheterogeneousdistributionofT. gondiiinthehost’sorgansortoalowintensityofinfection.Also thesamplesizeof400mgforDNAextractionislow.UsingPCRon marinemammalsamplestodetectT.gondiiDNAhasnotidentified manypositiveanimalsinotherstudieseither(Dubeyetal.,2009; Omataetal.,2006).Furthermore,alargediscrepancybetweenthe PCRandserologicresultswasfound, similartootherstudieson T.gondiiprevalenceinotherhosts(DeCraeyeetal.,2011;Wang etal.,2011;Prestrudetal.,2007).Thiscouldbedueto difficul-tiesindeterminingserologicalparameterssuchassensitivityand specificity.

Blanchetetal.(2014)testedtissuefluidandblood(thawedand centrifuged)withMATandELISA.Inthecurrentstudy,no chloro-formclean-upwasappliedontheserumsamples.Inaccordanceto thefindingsofBlanchetetal.(2014),theresultsobtainedbyIFA andELISAindeedgavealowernumberofpositiveanimals com-paredtotheMATresults.MATmightbeusefulasafirstscreening method,buttheresultsmustbeinterpretedwithcaution.

Inthecurrentstudy,usingMAT,51%and39%oftheserafrom marinemammalsstrandedonScottishcoastlinesalongtheAtlantic

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OceanandtheNorthSea,respectively,werefoundpositive com-pared to13% of thesera from animals strandedon the Dutch coastline.Extrapolatingthesedifferencesinseroprevalenceshould bedonewithcaution,becausethesamplingwasbiasedandnot representativeforthewholepopulation.Nevertheless,the differ-enceinseroprevalencebetweentheanimalsfoundonDutchand Scottishcoastlinesisstrikinganddeservesfurtherinvestigation.

WhileMATwasdesignedfortestingserumsamples,the Toxo-Screen DA® test kit wasreported togivereliable resultswhen

usedonswinemusclefluid(Forbesetal.,2012).MAThasproven itsusefulnessasadiagnosticmethodinexperimentallyinfected seals(Gajadharetal.,2004).Inourstudy,nopositiveresultswere obtainedfromthemusclefluidsamplesata1/10cut-offvalueas describedbyForbesetal.(2012).Themusclefluidsamplesshowed variousdegreesofdegradation,whichmayhaveinterferedwith thereadingofMAT.

Acrossthethreeserologicalmethodsusedinthisstudy,more sampleswerefoundpositiveinMATthaninELISAandIFA.Amajor differencebetweenthesetestsistheuseofamultispeciesconjugate inELISAandspeciesspecificconjugatesinIFA.Finding appropri-atespecificconjugatesforallthetestedspeciesofseamammalsis notonlychallenging(asformostofthemtheyarenotcommercially available),itisalsoratherexpensiveandimpractical.Therefore,for theIFAwereliedonpreviouslypublishedcross-reactivitybetween species(Milleretal.,2002;Nollensetal.,2008)(Table5).Another waytoapproachthisproblemisusingamultispeciesconjugate consistingofproteinG,whichnon-specificallybindstotheFc por-tionofIgGantibodies.ThecommercialmultispeciesELISAusedin thisstudyreliesonsuchaproteinGconjugatefordetectingthe adsorbedIgG’s.However,it is alsopossiblethattheconjugates usedinIFAandthecommercialELISAarenotoptimal,leadingto possiblefalsenegatives.Thefactthatweobtainedsimilarresults withIFAandELISAwhenloweringtheS/Pcut-offratioofthe lat-terto≥20,couldbeexplainedbyproteinGhavinglessaffinityfor marinemammalantibodies.Indeed,differencesinbinding affini-tiesbetweenproteinGandimmunoglobulinshavealreadybeen describedforvariousotheranimalspecies(Phillips,2015).

Althoughitremainspoorlyunderstoodhowmarinemammals acquireT. gondiiinfection,it hasbeenshown that certainprey species,suchasanchovies(Engraulidaefamily),sardines (Clupei-daefamily)andbivalves,areabletoconcentrateviableT.gondii oocystsintheirdigestivetract(Massieetal.,2010).Astheseprey speciesarealsoconsumedbyhumans,T.gondiiinfectioninmarine mammalscouldbeanindirectindicatoroftheriskthesespecies poseforcausingT.gondiiinfectioninhumans.Ottersare hypothe-sizedtobeaninterestinglinkinthetransmissionofT.gondiifrom landtomarineenvironmentsandwerethereforeincludedinthis study(Conradetal.,2005).Ahigherpercentageofsamplestesting positiveonallthreetestswasfoundinotters(28%)comparedto marinemammals(2%),supportingthishypothesis.Thepresenceof T.gondiioocystsinthemarineenvironmentcouldbeanindicator ofmarinepollutioningeneral(Meirelesetal.,2004;Stewartetal., 2008).However,formarinemammalstobetrulyusedassentinels forboththezoonoticandecologicalimplicationsofT.gondii infec-tion,furtherresearchisneededtoovercomethecurrentdiagnostic difficulties.

5. Conclusions

ThisstudyhasconfirmedthepresenceofT.gondiiDNAand anti-bodiesinmarinemammalslivingintheNorthSea(andEastern AtlanticOcean), toour knowledge for thefirst time. The com-parisonbetweenthedifferentdetectionmethodshighlightedthe diagnosticdifficultieswhentestingmarinemammalsamplesfor thisparasite.Togainmoreinsightsinthesignificanceandpotential

threatofT.gondiiinmarinemammals,theserologicaltechniques fordetectingT.gondiiantibodiesinmarinemammalsshouldbe furtheroptimized.Despitethesediagnosticdifficulties,the differ-enceinseroprevalencebetweenanimalsfoundontheScottishand Dutchcoastlinesshouldbefurtherinvestigated.

Acknowledgments

WewouldliketothankZehraYildirimer,NabilaElMoussaoui, Mariel ten Doeschate, Kornelia Schmidt, Miriam Hillmann, Jur-genWillemsandLaurieFlamentfortheirkindcooperationduring thisproject.SamplesgainedfromUtrechtUniversitywere possi-blethroughagrantfromtheDutchMinistryofEconomicAffairs (140000353).Wearegreatlyindebtedtoallvolunteersspending theirtimeandefforttocollectthestrandedanimals.Withouttheir dedication,thisprojectwouldnothavebeenpossible.Themarine mammalswashedashoreinBelgiumwerecollectedbytheRoyal Belgian InstituteofNatural Sciences(RBINS). We wouldlike to thankandacknowledgeallmembersoftheFrenchstranding net-worksfortheircontinuouseffortincollectingstrandingdata.We specificallywouldliketothankthefollowing natureprotection associationsofNorthernFrance:OCEAMM(Observatoirepourla Conservationetl’EtudedesAnimauxetMilieuxMarins),LPA (Ani-malProtectionLeague)andCMNF(CoordinationMammalogique duNorddelaFrance)andtheObservatoirePELAGISinchargeofthe nationalstrandingnetwork.TheObservatoirePELAGISisfundedby theministryinchargeoftheenvironment,andbytheCommunauté d’AgglomérationdelaVilledeLaRochelle,withsupportfromthe RégionPoitou-CharentesandtheEuropeanUnion.

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