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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
laDepartmentofPathology,BacteriologyandAvianDiseases,FacultyofVeterinaryMedicine,GhentUniversity,Merelbeke,Belgium bDepartmentofVirology,ParasitologyandImmunology,FacultyofVeterinaryMedicine,GhentUniversity,Merelbeke,Belgium cDepartmentofPublicHealthandSurveillance,ScientificInstituteofPublicHealth(WIV-ISP),Brussels,Belgium
dWageningenIMARES–InstituteforMarineResourcesandEcosystemStudies,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
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 wasmixedwith20lofproteinaseKand400l ofafirstlysis bufferand vortexedthoroughlypriortoovernightincubationat 56◦C.Thenextday,400lofasecondlysisbufferwasaddedand themixturewashomogenizedandfurtherincubatedat70◦Cfor 20min.Aftercoolingonice,600lofachloroform/isoamylalcohol (24/1)mixturewasaddedandeachsamplewasvortexedandthen centrifugedat22,000×g(4◦C)for30min.Thesupernatant was transferredintoanewtubeandtheDNAwasprecipitatedbyadding 400lof95%ethanolcooledat−20◦C.Fromthispointonwards,the
manufacturer’sprotocolwasfollowed.Themixturewastransferred toaspin-columnandwashedoncewith500lofafirstwashing bufferandoncewith500lofasecondwashingbuffer.Thepurified DNAwasthenelutedfromthecolumnusing200lofanelution 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 25lofeachdilutionwasappliedinaroundbottommicrotiter platewith25l2-mercaptoethanolat0.2mol/l.Tothis,50lof 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
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
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 Sequence5→3 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 diluted1/10inthesupplieddilutionbufferand100lwasapplied in the antigen-coated 96 well plate. After 45min of incuba-tionat room temperature,the platewas washed 3 timeswith the supplied washing buffer. 100l 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 diluted1/50inPBSand50lofeachserumdilutionwasappliedon
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,30lof 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
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
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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