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Genes2018,9,100;doi:10.3390/genes9020100www.mdpi.com/journal/genes
Article
HighPrevalenceofQuorum‐SensingandQuorum‐
QuenchingActivityamongCultivableBacteriaand
MetagenomicSequencesintheMediterraneanSea
AndreaMuras
1
,MarioLópez‐Pérez
2
,CeliaMayer
1
,AnaParga
1
,JaimeAmaro‐Blanco
1
andAna
Otero
1,
*
1
DepartamentodeMicrobioloxíaeParasitoloxía,FacultadedeBioloxía‐CIBUS,UniversidadedeSantiagode
Compostela,SantiagodeCompostela15782,Spain;andrea.muras@usc.es(A.M.);celiammayer@gmail.com
(C.M.);anapargamartinez@yahoo.es(A.P.);jaimeamaro85@gmail.com(J.A.‐B.)
2
EvolutionaryGenomicsGroup,DivisióndeMicrobiología,UniversidadMiguelHernández,SanJuande
Alicante03202,Spain;mario.lopezp@umh.es
*Correspondence:anamaria.otero@usc.es;Tel.:+34‐881‐816‐913
Received:12December2017;Accepted:12February2018;Published:16February2018
Abstract:ThereisincreasingevidencebeingaccumulatedregardingtheimportanceofN‐acyl
homoserinelactones(AHL)‐mediatedquorum‐sensing(QS)andquorum‐quenching(QQ)
processesinthemarineenvironment,butinmostcases,datahasbeenobtainedfromspecific
microhabitats,andsubsequentlylittleisknownregardingtheseactivitiesinfree‐livingmarine
bacteria.TheQSandQQactivitiesamong605bacterialisolatesobtainedat90and2000mdepthsin
theMediterraneanSeawereanalyzed.Additionally,putativeQSandQQsequencesweresearched
inmetagenomicdataobtainedatdifferentdepths(15–2000m)atthesamesamplingsite.The
numberofAHLproducerswashigherinthe90msample(37.66%)thaninthe2000msample
(4.01%).However,thepresenceofQQenzymaticactivitywas1.63‐foldhigherinthe2000msample.
TheanalysisofputativeQQenzymesinthemetagenomessupportstherelevanceofQQprocesses
inthedeepestsamples,foundincultivablebacteria.Despitetheunavoidablebiasesinthe
cultivationmethodsandbiosensorassaysandthepossiblepromiscuousactivityoftheQQenzymes
retrievedinthemetagenomicanalysis,theresultsindicatethatAHL‐relatedQSandQQprocesses
couldbecommonactivityinthemarineenvironment.
Keywords:quorumsensing;quorumquenching;AHL;lactonase;acylase;marinebacteria
1. Introduction
Quorumsensing(QS)isabacterialcommunicationsystembasedontheproductionandsecretion
ofsmallsignalmoleculescalledautoinducersthataccumulateintheextracellularenvironmentwhen
highcelldensitiesarereached[1].Onceathresholdintracellularconcentrationisachieved,thesignaling
moleculetriggersthesynchronousexpressionofmultiplegenesinthepopulation,initiatinga
coordinatedaction.Althoughdifferenttypesofsignalmoleculeshavebeendescribed[2],thebest
characterizedQSsignalsaretheN‐acylhomoserinelactones(AHLs).TheseQSsignalmoleculesare
constitutedbyahomoserinelactonering(HSL)linkedbyanamidebondtoafattyacid(between4and
18carbons).AHLsareQSsignalsthatareconsideredtypicalofGram‐negativebacteria[3],although
theyarealsoproducedbydifferentcladesofbacteria[4,5],includingtheGram‐positiveExiguobacterium
sp.[6].ThemostcommonAHL‐basedQSsystemcomprisesaLuxI‐typesignalsynthaseandaLuxR‐
typereceptor[7].OtherAHLsynthasesbelongingtothefamiliesLuxM/AinSandHdtShavebeen
described,notsharinghomologywiththeLuxIsynthasefamily[8,9].Somebacteriadonotproduce
AHLsorhavearecognizableLuxIautoinducersynthasebutpossessLuxRhomologs,calledLuxR
Genes2018,9,100 2of20
orphans,thatcaninteractwiththeautoinducerssynthetizedbyotherbacteria[10].Recently,LuxR
homologueshavebeendescribedtoactassensorsforQSsignalsdifferentfromAHLs,makingthe
picturemorecomplex[11].Despitebeingmoreinfrequentlyreported,LuxIorphansarealsopresentin
somebacteria[12].
InspiteofthelowbacterialpopulationintheopenseaandthelowchemicalstabilityofAHLsatthe
highpHofseawater,newevidencereinforcestheideaoftheimportanceofAHL‐mediatedQS
mechanismsinmarineenvironments[3,5,13,14].Morerecently,numerousstudieshavereportedthe
isolationofAHL‐producingbacterialstrainsfrommarinesamples[15–20].Thepresenceofbacteriawith
theabilitytoproduceAHLsinthesemarinemicrohabitatswasreportedinsubtidalbiofilms[21],sponges
[16,22],cnidarians[23,24],andmarinesnow[15,19,25].Itisnowgenerallyacceptedthatthe
AHL‐mediatedQSsystemsplayanimportantroleinrelevantmarineecologyprocessesincludingthe
settlementofinvertebratelarvae[26,27]andofmacroalgaezoospores[28].TheAHLsproducedby
bacteriaassociatedwiththecyanobacteriaTrichodesmiumareproposedtomediateandcoordinatethe
processingandacquisitionofphosphorus[29],alimitingnutrientinoligotrophicopenocean
environments.Furthermore,symbioticandpathogenicinteractionswithaeukaryotichostalsoactas
examplesoftheseecologicallyrelevantniches[28,30].Inaddition,theexpressionofimportantvirulence
genesinmarinefishpathogenicbacteriaiscommonlycontrolledthroughAHL‐mediatedprocesses[31].
ThepresenceofAHLsinopenmarineenvironmentshasbeenalsoreportedusingdirect,
non‐cultivation‐dependentmeasurements[25,32].AlargephylogeneticdiversityoftheAHLs
synthaseswasobservedintheGlobalOceanSampling(GOS)metagenomicdatabase[33],suggesting
thatAHLproductionisawidespreadmechanisminmarineenvironments.TheAHLsareproposed
toparticipateinthemarinecarboncyclebyincreasingtheactivityofcertainkeyhydrolyticenzymes
forthedegradationofparticulateorganiccarboninseawater,playinganimportantroleinthe
remineralisationdepthdistributionofsinkingparticulateorganiccarbon(POC)[25,34].QS‐mediated
processeshavebeensuggestedtobeevenmoreecologicallyrelevantinspecificmarinemicrohabitats
inwhichthebacterialpopulationismoreconcentrated,formingcellclusters[13,14].
SinceQSsystemshaveimportanteffectsintheinteractionsbetweenprokaryotesandalsowith
eukaryotes,itmakessensethatcompetitorshaveevolvedmechanismsforsilencingotherbacterial
QSsystems.Theabilitytodisruptbacterialcommunicationisawidespreadstrategyusedbydifferent
kindsoforganisms:marinealgae[35],terrestrialplants[36],mammaliancells[37],andbacteria
[4,38,39].Thetermquorumquenching(QQ)wascoinedtodescribetheenzymaticinactivationof
AHLQSsignals[40],althoughatpresentthistermisoftenusedinageneralsensetodescribeany
typeofQSdisruption[41].EnzymaticQQisthebeststudiedQSinhibitorystrategy[40].Thegenes
thatcodifythistypeofenzymesareclassifiedintwomaingroups:lactonasesandacylases,although
othertypesofQQenzymeshavealsobeendescribed[39].Thepioneerstudiesontheecological
relevanceofQQprocessescarriedoutwithbacteriaisolatedfromsoilandrhizosphereindicatedthat
2–4.8%ofthesestrainshadtheabilitytointerferewithAHLs[42–44].Morerecentstudiesrevealeda
highprevalenceofQQenzymesinthemarineenvironment:enzymaticQQactivitywasobservedin
bacterialstrainsisolatedfromcorals[23,45],sponges[46],marinebiofilms[47],estuarineandopen
oceansuperficialseawater[48,49],andfishandbivalvehatcheries[50,51],presentinghigher
frequenciesofbacteriawiththiscapability(2–46%)incomparisontoterrestrialsamples[46,48,52–54].
TheimportanceofQQprocessesinthemarineenvironmentwasfurthersupportedbymetagenomic
studiesshowingahighfrequencyofQQenzymesinmarinemetagenomiccollectionsincludingthe
GlobalOceanSamplingcollection[48].DespitetherelevanceofQSandQQinnichemarine
environmentsseemsclearandalltheavailabledatapointstoahighprevalenceofQSandQQ
activitiesintheseawater,thereisnostudyinwhichametagenomicanalysisiscombinedwiththe
analysisoftheQSandQQactivitiesamongcultivableisolatesforthesamesample.Thisdouble
approachwouldallowustoavoidthehandicapsofbothmethodsandtoassesstherelevanceofthese
processesinfree‐livingbacteria.Therefore,theaimofthisworkwastostudytheAHLproduction
anddegradationactivityinfree‐livingbacteriafromtheMediterraneanSeausingtwodifferentbut
complementaryapproaches,suchasfunctionalscreeninginbacteriaabletogrowinstandardculture
Genes2018,9,100 3of20
conditionsandmetagenomicanalysisinordertoimproveourunderstandingoftheecologic
relevanceofAHL‐mediatedprocessesinthemarineenvironment.Themetagenomicanalysiswas
carriedoutfromseawatersamplescollectedfromsixdepthsinthephoticzoneat15mintervals(15,
30,45,60,75,and90m)andfromtwodepthsintheaphoticzone(1000and2000m)atthesametime,
whilecultivablebacteriawereobtainedfromthe90and2000msamplesinordertoassessthespatial
distributionoftheQSandQQprocesses.
2.MaterialsandMethods
2.1.SampleCollection,BacterialQuantification,andStrainIsolation
Eightseawatersamplesfromdifferentdepthswerecollectedformetagenomicanalysesas
describedpreviously[55,56]onOctober15,2015atasinglepointintheMediterraneanSea(37.35361°
N,0.286194°W)bytheresearchvessel‘GarcíadelCid’.Samplesfrom90and2000mdepthwerealso
usedforbacterialisolationandfunctionalscreening.The90msampleisconsideredthelimitofthe
photiczone,withachlorophyll‐a(Chl‐a)valueof0.13mg/m3,atotalorganiccarbon(TOC)of1.35
mgC/L,totalNof6.9μM,totalPof0.25μM,and1.37×105heterotrophicbacteriacounts.The2000
msamplewascharacterizedbyanalmostundetectableChl‐aconcentration(0.01mg/m3),lowerTOC
(0.94mgC/L),highertotalNandp‐values(8.62and0.5μM,respectively),andlowerheterotrophic
bacteriacounts(4.5×104)[55,56].Bothrichandoligotrophicculturemediawereusedforbacterial
isolationaspreviouslydescribed[47].Therichmediaincludedtryptonesoyagar1%NaCl(TSA‐1)
andmarineagar(MA)suitableforeutrophicbacteria,andtheloworganicformulationsincludedMA
diluted1/100withseawater(salinity35g/L)andfilteredautoclavedseawatermedium(FAS)
supplementedwith0.5g/Lofeachofthefollowingpolymers:agarose,chitin,andstarch(FAS‐POL).
Fiveseriesof10‐folddilutionswerepreparedinsterilizednaturalseawaterforeachsampleand
platedintheabove‐mentionedculturemedia.Theplateswereincubatedat22°Cfor15days.Forthe
estimationofcolonyformingunits(CFUs),plateswith30–300colonieswereselected.Atotalof605
strainswererandomlypickedupandisolatedtobeusedforQSandQQfunctionalscreening(Table
S1).AllthemarineisolatesobtainedwereabletogrowonMAat22°C,hencethesecultureconditions
wereselectedasstandardforlaboratorymaintenanceandassays.
2.2.16S‐BasedBacterialIdentification
Theidentificationofthecollectionof605cultivablemarinebacteriawascarriedoutusing200
μLofculturesobtainedinmarinebrothandpooledingroupsof65–80strains.Thesepoolswere
centrifuged,andtheDNAwasextractedwithDNeasyPowerSoilKit(Qiagen®,Hilden,Germany).
Theamplificationof16SrRNAgeneswasperformedusingadiversityassayillumineinhouse
bTEFAP®(Lubbock,TX,USA).PCRwerecarriedoutunderthefollowingstandardconditions:initial
stepof94°Cfor3minfollowedby28cyclesat94°Cfor30s,53°Cfor40s,and72°Cfor1min.
Sequencing(Miseq,Illumina,SanDiego,CA,USA)anddataprocessingwereperformedusing
BLASTnagainstacurateddatabasefromRDPIIandNCBI(MRDNA,Shallowater,TX,USA).
Inordertoanalyzethebacterialdiversityofthecultivablebacteria,the16SrDNAsequences
wereclusteredtooperationaltaxonomicunits(OTUs)definedat95%identityusingCD‐HIT[57].
ThesequenceswereassignedataxonomicidentityusingtheRDPdatabase[58].
Fortheisolatedstrainsshowingwide‐spectrumQQactivity,genomicDNAwasextractedusing
aWizardDNApurificationKit(Promega,Madison,WI,USA),andthebacterial16SrRNAgenewas
amplifiedusingtheuniversalprimers96bfm(5′‐GAGTTTGATYHTGGCTCAG‐3′)and1152uR(5′‐
ACGGHTACCTTGTTACGACTT‐3′)[59].PCRwerecarriedoutunderthefollowingstandard
conditions:initialstepof96°Cfor2minfollowedby35cyclesat95°Cfor1min,53°Cfor30s,and
72°Cfor2min.The16SrRNAsequenceswereidentifiedusingtheweb‐basedtoolEzTaxon[60].
2.3.Quorum‐SensingActivityAssay
Genes2018,9,100 4of20
Themarinebacterialcollection(605strains)wasscreenedforthestrainsʹcapabilitytoactivate
theAHLbiosensorAgrobacteriumtumefaciensNTL4[61,62].Thestrainswereculturedinmicrotiter
platesin200LofMarineBroth(MB)for48h.Theplateswerecentrifuged,andthesupernatants
weretransferredtoanewplate.ThepHofthesupernatantswascheckedtobelessthanpH8inorder
toavoidlactonolysisoftheAHLsproducedathighpHvalues[63].ThepresenceofAHLsafterthe
incubationperiodwasdetectedbyadding50LofamixtureofsoftAgrobacterium(AB)medium
[61](0.2%agar)with5‐bromo‐4‐chloro‐3‐indolyl‐β‐D‐galactopyroside(X‐GAL,80μg/mL)andan
overnightcultureofA.tumefaciensNTL4(1:5)ontopofthesupernatantsinmicrotiterwells.The
plateswereincubatedfor6–8hat30°C,andtheproductionofbluecolouronthesurfaceofthewells
waschecked.ABmediumpH6.5plustheC6‐HSL(10μM)wasusedascontrol.A.tumefaciensNTL4
wasculturedat22°CinLBorABmediumsupplementedwith30μggentamycin/mL.
Thecapacityofthestrainspresentingwide‐spectrumQQactivitytoactivatethesensorA.
tumefaciensNTL4wasconfirmedwithadisk‐diffusionagarplateassay[modifiedfrom50]atdifferent
times.OnemLofanovernightshakencultureofthebiosensorwasmixedwith4mLofsoftAB
medium(0.8%)withX‐GAL(80μg/mL)tocovertheABagarplates.Oncetheplateshadsolidified,
10μLofsupernatantfromthe24hand48hculturesofthe12wide‐spectrumQQstrainswasloaded
inantibiogramdisksanddepositedontheplates.Theplateswereincubatedat22°Cfor24h.PBS
pH6.5plusC6‐HSLwasusedasacontrol,andthepresenceofablueinductionhaloaroundthedisks
waschecked.ThestockofC6‐HSLwaspreparedinacetonitrileataconcentration1mg/mL.This
stocksolutionwasdilutedinPBStoafinalconcentrationof10μMandaddedtothedisks.
2.4.Quorum‐QuenchingActivityAssay
TheQQactivityofthestrainswastestedusingasolidmicrotiterplateassayscarriedoutwith
theAHLbiosensorsChromobacteriumviolaceumVIR07[64]forC12‐HSLandC.violaceumCV026[65]
forC6‐HSL.Twohundredmicrolitersofthe48hculturescarriedoutinmicrotiterplatesinMBwere
centrifuged,andthepelletswerewashedwithphosphatebufferedsaline(PBS)pH6.5and
resuspendedinanother200μLofthesamebuffer.Thesecellsuspensionswereusedforlive‐cellAHL
degradationassaybyaddingeitherC6‐HSLorC12‐HSL(10μMinPBS,preparedfromaconcentrated
stock—1mg/mLinacetonitrile)andincubatingfor24hat22°C.ThepresenceofAHLsafterthe
incubationperiodwasdetectedbyadding50LofamixtureofsoftLuria–Bertani(LB)(0.2%agar)
andanovernightcultureofthecorrespondingC.violaceumbiosensorontopofthecellsuspensionin
microtiterwells.Theplateswereincubatedfor24hat30°C,andtheproductionofviolaceinwas
observed.PBSpH6.5plusthecorrespondingAHL(10μM)wasusedasacontrol[66].Thesame
assaywasusedtocheckthecapacitytodegradetheoxo‐substitutedAHLsOC6‐HSLandOC12‐HSL.
InordertodetectfalsepositivesderivedfromtheinhibitionofthegrowthoftheC.violaceum
biosensors,allpositivestrainswerere‐isolated,andtheiractivityconfirmedwithaPetridishsolid
bioassayasdescribedpreviously[47].ThePetridishbioassaysallowdistinguishinggrowth
inhibition(presenceofatransparenthaloaroundthewell)fromQSinhibition.IntheC.violaceum
assay,becauseofthehighconcentrationofaddedexogenousAHL(10μM),theabsenceorreduction
oftheviolaceinhalowasconsideredindicativeofenzymaticdegradation.Inthisassay,thepresence
ofaninhibitorysubstanceisgenerallyvisualizedasaclear,nottransparent,haloaroundthewell,
surroundedbyanexternalhaloofviolacein.Nevertheless,thepresenceofaveryhighamountofa
QSinhibitorcounteractingtheactionoftheexogenousAHLcouldnotbefullyexcluded.The
biosensorstrainsweremaintainedinLBplatessupplementedwithkanamycin(30μg/mL).
2.5.CharacterizationofAHL‐DegradationActivity
Crudecellextracts(CCE)wereobtainedaspreviouslyreported[67].Briefly,thecellbiomass
wasobtainedbycentrifugation,resuspendedinPBS,sonicatedonice,andcentrifugedagain.Thecell
extractobtainedwasfilteredthrougha0.20μmfilterandstoredat4°C.Todeterminetheminimal
activeconcentration(MAC)oftheCCEs,C6‐HSL(10μM)wasexposedtodifferentdilutionsofCCEs,
Genes2018,9,100 5of20
inPBSpH6.5.Themixturewasincubatedfor24hat22°C,andthepresenceofasignalwasdetected
usingtheC.violaceumCV026Petridishbioassay.ThecontrolwellswerefilledwithsterilePBSpH
6.5plusAHL(10μM).
2.6.MetagenomicSamples
Eightsamples(Med‐OCT2015‐15m,Med‐OCT2015‐30m,Med‐OCT2015‐45m,Med‐OCT2015‐
60m,Med‐OCT2015‐75m,Med‐OCT2015‐90m,Med‐OCT2015‐1000m,andMed‐OCT2015‐2000m)
[55,56]fromdifferentdepthsweretakenformetagenomicanalysesonOctober15,2015atasingle
samplingsiteintheWesternMediterranean(37.35361°N,0.286194°W).Sixsampleswereobtained
fromtheuppermost100mat15mintervalsusingahoseattachedtoaCTD(Seabird).Anothertwo
samplesfromthedepthsof1000mand2000m,weretakenthenextday(October16)intwocasts
(100Leach)usingtheCTDrosette.
Allseawatersamplesweresequentiallyfilteredonboardthrough20,5,and0.22μmporesize
polycarbonatefilters(Millipore,Billerica,MA,USA).Allfilterswereimmediatelyfrozenondryice
andstoredat−80°Cuntilprocessing.DNAextractionwasperformedfromthe0.22and5μmfilters,
aspreviouslydescribed[68].ThemetagenomesweresequencedusingIlluminaHiseq‐4000(150bp,
paired‐endread)(Macrogen,Seoul,Korea).
2.7.MetagenomicAnalysis
Themetagenomicanalysis(readpre‐processing,assemblyandgenepredictionandannotation)
wascarriedoutaspreviouslydescribed[56].Inbrief,eachmetagenomewasassembled
independentlyusingIDBA‐UD[69].Thegenesobtainedontheassembledcontigswerepredicted
usingProdigal[70]transferRNA(tRNA),andtherRNAgeneswerepredictedusingtRNAscan‐LE
[71],ssu‐align[72],andmeta‐rna[73].Ataxonomicandfunctionalannotationwasperformed
comparingthepredictedproteinsequencesagainstNCBINR,COG[74],andTIGFRAM[75]
databaseswereperformedusingUSEARCH6[76].USEARCH6withane‐value<1e‐5wasalsoused
toidentifypotential16Ssequencesfromasubsetof10millionreadsforeachmetagenomeagainst
RDPdatabase[77].Thesecandidateswerethenalignedtoarchaeal,bacterial,andeukaryal16S/18S
rRNAHMMmodels[78],usingssu‐aligntoidentifytruesequences[72],usingathresholdof
sequenceidentity≥80%andalignmentlength≥90bp.Inordertoanalyzethe16SrDNAdiversity,
identicalsequences(99.9%ofidentity)frombothdatasetswereremovedusingCD‐HITsoftware[57].
Therestofthesequenceswereclusteredtooperationaltaxonomicunits(OTUs)definedat95%
identity.TaxonomicaffiliationsoftheseclusterswereassignedusingtheassignedRibosomal
DatabaseProject(RDP)database[58].
OnlyAHLlactonaseandAHLacylasegeneswithdemonstratedactivitywereusedwithinthe
QQenzymes(Supplementarymaterial).TheanalysisofotherQS‐relatedgenes,suchasthosefor
AHLsynthases(LuxI,AinS,andHdtS)andAHLreceptors(LuxRandAinR)aswellasthegenefor
thesynthaseresponsibleforproducingtheAI‐2signal(LuxS),wascarriedoutbyaligningthe
metagenomicreadsagainsttheNRdatabaseusingDIAMOND[79](blastxoption,tophit,≥50%
identity,≥50%alignmentlength,e‐value<10−5).Theabundanceofthesegeneswasnormalizedbythe
numberofreadsmatchingrecA+radAsequencesforeachmetagenome.Thereadsthatgavehitto
viraloreukaryalproteinswerenottakenintoaccount.Inordertoanalysetherelativeabundanceof
theQQenzymesinthewatercolumn,weappliedthesamesequencesearchforgenesinvolvedinthe
normalmetabolismderivedfrommarinebacteria,suchasnitrogen(amoC,amt),phosphate,(pstA),
sulfur(dsrA,soxB),andgeneraloxidativemetabolism(dmdA)[48,80].
2.8.DataAvailability
ThemetagenomicdatasetsusedinthisstudyweresubmittedtoNCBISRAandareavailable
underBioProjectsaccessionnumberPRJNA352798(Med‐OCT2015‐15m,Med‐OCT2015‐30m,
Genes2018,9,100 6of20
Med‐OCT2015‐45m,Med‐OCT2015‐60m,Med‐OCT2015‐75m,Med‐OCT2015‐90m,Med‐OCT2015‐
1000mandMedOCT2015‐2000m).
2.9.StatisticalAnalysis
TheeffectsofdepthandculturemediaonthenumberofCFUs/mLwasanalysedwiththe
non‐parametricMann–Whitneytestatsignificancelevelp<0.05,withIBMSPSSstatisticsV20program.
3.Results
3.1.BacterialGrowthandIsolation
ThenumberofCFUs/mLwassignificantlyhigherinthe2000m(0.8–5.8×103CFUs/mL)thanin
the90mwatersample(0.2–0.6×103CFU/mL)forthedifferentculturemediatested(Mann–Whitney
Test,p<0.05),despitetheisolationconditionsexcludedtheretrievalofbarophilicorpsychrophilic
strainsfromthedeep‐seasample.TheculturemediadidnotaffectthenumberofCFUs/mLobtained
inthe90m,photicsample(Figure1,Mann–WhitneyTest,p>0.05).Onthecontrary,theCFUs
obtainedinMAandFAS‐POLculturemediaweresignificantlyhigherinthesamplefrom2000m,
yieldingthreetimesmoreCFUsthantheothermedia(Figure1,MannWhitneyTest,p<0.05).
Figure1.Cultivablebacteriaconcentration(colonyformingunits(CFU)/mL,average±s.d.,n=5)
obtainedinthephotic(90m,whitebars)andaphotic(2000m,blackbars)samplesfortheculture
mediaTSA‐1%NaCl(TSA‐1),MarineAgar(MA),Marineagardiluted1:100inseawater(MA1/100),
andFilteredautoclavedsea‐waterenrichedwithpolymers(FAS‐POL).
3.2.TaxonomicDiversityoftheCultivableStrains
Atotalof605isolates,231fromthe90mand374fromthe2000msample,werecollectedand
screenedfortheircapacitytoactivateaQSbiosensorandfortheirQQactivityagainstAHLs
(SupplementaryTableS1).ThemostcultivablestrainsbelongedtoGammaproteobacteria(34.88%),
Firmicutes(30.95%),andAlphaproteobacteria(17.44%).MembersoftheActinobacteria(6.84%)and
Bacteroidetes(7.14%)werelessrepresented(Figure2A).Firmicuteswerehighlyrepresentedinthe
cultivablecollection(30%inbothsamples),incomparisonwiththedataobtainedfromthe
metagenomicanalysisatthesamedepth(<1%)[56].Gammaproteobacteria(35%)werealso
overrepresentedinthe90msampleincomparisonwiththemetagenomicdata(13.56%).Therelative
abundanceatthefamilylevelshowedsimilarprofilesatbothdepths,exceptforVibrionaceaeand
Rhodobacteraceaewhichwereonlyidentifiedat2000m(Figure2A).However,whentheOTUswere
clusteredat95%ofidentityfrombothdatasetstoseparatethematgenuslevel,56and82generacould
beidentifiedat90and2000m,respectively,showingthattherewasagreatergeneticdiversityat2000
mthatcouldnotbeappreciatedathighertaxomoniclevels.Inthefuture,thegenomesequencingof
theseorganismscouldclarifyandshedlightonmanyofthedifferencesbetweenthesetwodepths.
Despiteofthis,thetwocollectionsofcultivablebacteriashared11ofthe13mostabundantgenera
Genes2018,9,100 7of20
(Figure2B).Surprisingly,Bacilluswasthemostabundantgroupamongthecultivablebacteria,
representing15.74%and16.6%,inthe90and2000msamples,respectively.ThegeneraMicrobacterium
(2.38%)andSphingomonas(2.38%)wereexclusivelyidentifiedinthesamplefromthe90mdepth,
meanwhilethegenusPantoeaandVibrioappearedonlyinthesamplefrom2000m(Figure2B).
Figure2.(A)Bacterialdiversityincultivablebacteriaisolatedfromphotic(90mdepth,n=231)and
aphotic(2000mdepth,n=374)samples;(B)relativeabundanceofthe13mostabundantgenerain90
and2000mdepthsamples.Thegenerarepresentedbyasingleisolatearegroupedas“other”.
3.3.Quorum‐SensingandQuorum‐QuenchingActivitiesamongCultivableBacteria
Theactivationofthebeta‐galactosidasegeneofthesensor,whichsuggeststhepresenceofAHLs
intheculturemedia,wasrelativelyfrequentamongthe605marineisolates(20.84%).Thenumberof
positiveswashigherinthesamplesfrom90m(37.66%)thaninonesfrom2000m(4.01%)(Figure
3A).TheoligotrophicMA1/100culturemediumallowedtheisolationofthehigherpercentageof
strainswithputativeQSactivityatboth90(60%)and(12.67%)2000m.Onthecontrary,thestrains
isolatedfromTSA‐Ipresentedalowercapacitytoactivatethereporter(4.76and2.52%for90and
2000msamplesrespectively).
Genes2018,9,100 8of20
Figure3.(A)PercentageoftheisolatedstrainswiththeabilitytoactivatetheN‐acylhomoserine
lactone(AHL)sensorAgrobacteriumtumefaciensNTL4inthe90m(whitebars)and2000m(blackbars)
samples;(B)percentageofisolateswithquorum‐quenching(QQ)activityagainstC6andC12‐HSL
isolatedfromeachculturemediainthe90m(whitebars)and2000m(blackbars)samples,as
confirmedbyusingthePetridishsolidassaywithChromobacteriumviolaceumCV026andVIR07.
Mediaused:tryptonesoyagar1%NaCl(TSA‐1),marineagar(MA),dilutedmarineagar(MA1/100),
andfilteredautoclavedseawatermedium(FAS)supplementedwith0.5g/Lpolymers:agarose,chitin
andstarch(FAS‐POL).
Thecapacityofthemarinebacterialcollectiontointerferewithbothlong‐ (C12‐HSL)and
short‐chain(C6‐HSL)AHLswasfirsttestedusingaC.violaceum‐basedbioassayin96‐wellmicrotiter
plates.NoneoftheQQpositivesinthepreliminaryassayshowedinterferencewiththegrowthofthe
biosensors.TheabilitytoquenchtheQSsignalC12‐HSLwasobservedinalargenumberofcultivable
bacteria(38.24%).Theaverageactivitywashigherinthe2000m,aphoticsample(47.05%)thaninthe
90mphoticone(29.43%,Figure3B).Amongthe68strainsisolatedfromthe90mdepthwiththe
capacitytoquenchC12‐HSL,fourstrains,representing1.73%ofthetotalstrains,werealsoableto
eliminatetheC6‐HSLQSsignal,andasimilarpercentagewasobtainedfortheisolatesfromthe2000
msample(2.12%).AlltheisolateswiththeabilitytointerferewithC6‐HSLcouldalsodegrade
C12‐HSL,butnoisolatewasfoundthatcouldonlyeliminatetheactivityoftheshort‐chainAHL.The
oligotrophicMA1/100culturemediumallowedtheisolationofthehighestpercentageofstrainswith
QQactivityagainstC12‐HSL(84.5%)inthe2000msample.Onthecontrary,inthe90msample,the
richculturemedia(TSA‐IandMA)presentedthehighestpercentagesofQQactivity(50–52%).The
mosteffectiveculturemediumtoisolatestrainswithQQactivityagainsttheshort‐chainsignal
Genes2018,9,100 9of20
C6‐HSLweretheoligotrophicFAS‐POL(3.22%)andMA1/100(9.85%)forthesamplesfrom90and
2000m,respectively.
3.4.IdentificationoftheWide‐SpectrumQuorum‐QuenchingStrainsandCharacterizationofQuorum‐
QuenchingActivity
ThetaxonomiclabelofthebesthitisshowninTable1forthe12strainspresenting
wide‐spectrumQQactivity.Thefourmarinestrainsselectedfromthe90msamplebelongedto
Firmicutes(Planomicrobiumchinense),Alphaproteobacteria(Sphingopyxisalaskensis,Erythrobacter
citreus),andActinobacteria(Microbacteriumschleiferi).Amongtheeightstrainsfromthedeepest
sample,oneofthembelongedtoBetaproteobacteria(Ralstoniapickettii),sixtoAlphaproteobacteria(5
Erythrobacterflavusstrains,Citomicrobiumsp.),andonetoGammaproteobacteria(Pantoeasp.).Despite
thehighnumberofBacillussp.strainspresentinthecollections,noBacillusstrainwithwide‐spectrum
QQactivitywasidentified.
Table1.IdentificationandcharacterizationofthemarineisolatesshowingwideQuorum‐Quenching
(QQ)activity.ThepresenceofQQactivityinthecellextractsandtheminimalactiveconcentrationof
extract(MAC,μgprotein/mLcellextract)neededtofullyeliminatetheactivityof10μMofC6‐HSL
wasalsoinvestigated.
LiveCell CellExtrac
t
MACC6‐
HSL(μg
Protein/mL
CellExtract)
StrainClosestCultivated
Bacteria
%IDat16S
rRNAGene
Locus
C6‐
HSL
OC6‐
HSL
C12‐
HSL
OC1
2‐
HSL
C6‐
HSL
C12‐
HSL
90m
1F1Planomicrobiumchinense99.93 + + + + ++104.7
2E12Sphingopyxisalaskensis99.93 + + + + ++18.67
2G12Erythrobactercitreus99.04 + + + + ++1918
3A3
M
icrobacteriumschleiferi99.71 + + + + ‐ +nd
2000m
2F1Ralstoniapickettii95.79 + + ± + ++17.6
3G7Erythrobacterflavus99.34 + + + + ++786
4B4Erythrobacterflavus99.34 + + + + ++216
4B7Pantoeasp.96.01 +‐+‐‐‐ nd
4B9Erythrobacterflavus99.71 + + + + ++961
4B10Erythrobacterflavus99.49 + + + + ++223.9
4B12Erythrobacterflavus99.49 + + + + ++965
4C3Citromicrobiumsp.98.33 + + + + ‐ +nd
Nd:Notdetermined.
Theisolate2F1mayrepresentanewspecieswithinthegenusRalstoniabecauseofthelow
identitywiththeknownspeciesofthegenus(95.79%).Thecellextractsofthreeisolates,3A3
(Microbacteriumschleiferi),4B7(Pantoeasp.),and4C3(Citromicrobiumsp.)didnotpresentQQactivity
againstC6‐HSL.Theabilitytointerferewithoxo‐substitutedAHLswasalsotestedforthe12selected
strains(Table1).Mostofthemarinestrainswereabletoinactivatetheoxo‐substitutedAHL,except
forstrain4B7(Pantoeasp.)thatdidnotshowQQactivityagainstanyofthesubstitutedAHLstested,
namelyOC6andOC12‐HSL.Inordertochecktherelativeactivityofthestrains,theminimalactive
concentration(MAC,μgprotein/mL)wascalculatedinthecellextracts.Themarineisolateswiththe
highestactivitywere2E12(Sphingopyxisalaskensis)and2F1(Ralstoniasp.),sincetheirQQactivitywas
atleastoneorderofmagnitudehigherthanthatoftheotherQQstrains(<20μg/mL).
Amongthe12strains,Sphingopyxisalaskensis2E12andErythrobactercitreus2G12couldactivate
thebiosensorA.tumefaciensNTL4using24hsupernatants.Thisactivitywasmaintainedin48h
supernatantsonlyforSphingopyxisalaskensis2G12,butdisappearedinErythrobactercitreus2G12.
AHL‐likeactivitywasalsodetectedin48hsupernatantsofCitromicrobiumsp.4C3.
3.5.Quorum‐SensingandQuorum‐QuenchingGenesinMetagenomicSamples
AsearchforQS‐relatedgenes,AHLsynthases(LuxI,AinSandHdtS)andAHLreceptors(LuxR
andAinR)aswellasthesynthaseresponsibletoproducetheAI‐2signal(LuxS),wascarriedoutin
Genes2018,9,100 10of20
themetagenomicsamplesfromthedepthprofile.TherelativeabundanceofQS‐relatedgenesseemed
toslightlydecreasewithdepthinthefirst100m(7.59–3.41,Figure4A).However,ahighrelative
abundanceofAHLreceptorswasobservedinthetwoaphoticzonesamples,the1000m(9.02)and
especiallythe2000msamples(20.52).Remarkably,anextremelylowpresenceofAHLsynthaseswas
foundinthemetagenomicanalysisalongthewholewatercolumnincomparisonwiththereceptors
frequency(Figure4A).Surprisingly,noAI‐2synthaseLuxShomologsweredetectedinanyofthe
testedsamples,despitethepresenceofVibriointhebacterialcultivablecollection(3.5%).
Figure4.(A)RelativefrequenciesofAHLsynthasesandAHLreceptors;(B)relativefrequenciesof
QQgenesincludinglactonasesandacylases;(C)relativefrequenciesofAHL‐basedQSandQQ
sequencesincomparisontoothergenesinvolvedinnitrogen(amoC,amt),phosphate(pstA),andsulfur
(dsrA,soxB)acquisition,aswellasinoxidativemetabolism(dmdA).Thedatawasnormalizedin
functionoftheabundanceoftherecAandradAhousekeepinggenes.
WesearchedforthepresenceofAHL‐lactonasesandacylasesgenes,usingsequenceswith
provedactivity,inthesamemetagenomicsamples.AmongtheQQgenes,AHLacylasesweremore
frequentthanAHLlactonasesinmostmetagenomicsamples(0.99,Figure4B).Theanalysisshowed
aclearincreaseofthefrequencyofacylasesat2000m(0.99,Figure4C),inthesamesamplethat
yieldedthehighestnumberofLuxRhomologues(Figure4A).TheincreaseintotalQQsequencesat
2000mwasduetoanincreaseinacylasesequences,sincetherelativeabundanceofacylasesequences
wassimilarinthefirst1000m(0.11–0.32)butincreasedsharplyat2000m(0.99)(Figure4B).In
contrast,thelactonasesequencesreachedthehighestpresenceinthe75msample(0.22)and
decreasedinthesamplesfromgreaterdepths.
InordertoanalyzetherelativeabundanceoftheQQenzymesinthewatercolumn,weapplied
thesamesequencesearchforgenesinvolvedinthenormalmetabolismofmarinebacteria,suchas
thoseinvolvedinnitrogen(amoC,amt),phosphate,(pstA),sulfur(dsrA,soxB),andgeneraloxidative
metabolism(dmdA)(Figure4C)[43,65].TherelativefrequencyofQS‐ andQQ‐relatedgeneswas
Genes2018,9,100 11of20
smallerthanthefrequencyofthegenesrelatedtothecommonuptaketransportersforammonia(amt)
orphosphate(pstA).However,thefrequencywasinthesamerangeofthoseofamoCandofgenes
relatedtosulfurmetabolism(dsrA,soxB).
4.Discussion
Understandinghowbacteriainteractwitheachotherisessentialforpredictingtheirroleinthe
marinemicrobialenvironmentandtheirpotentialimpactsonmarineecology[14].Theabilityof
microorganismstomodulatethebehaviorofanentirepopulationthroughthecoordinationand
regulationofgeneexpressionisviewedasanevolutionaryadaptationtosurviveinachanging
environment[81].DespitetheQSandQQinhibitionprocesseswerediscoveredinthemarine
environment[35,82],littleattentionhasbeenpaidtotheecologicalsignificanceofQSandQQ
mechanismsinseawater,andthisissuehasbeenthecenterofcontroversy[13,14].Increasing
evidencepointstoanimportantroleofAHL‐mediatedQSindifferentmarineenvironments[14],and
thefrequentpresenceofQQactivityamongmarinebacteriaisolatedfromseveralnichehabitats
furthersupportstheecologicalsignificanceofAHL‐dependentQSinthehighlycompetitivemarine
environment.HighQQactivitymaybeinterpretedastheresultofeitheranadaptativetraitofstrains
presentingthisQQcapacityinasituationinwhichQSprocessesincreasebacterialspeciesfitness,or
asituationinwhichtheconcentrationofAHLmoleculesishighenoughtoconstituteasignificant
sourceofcarbon.Inpreviousworks,ahighnumberofstrainswithQQactivity(2–46%)wereisolated
fromdifferentmarineenvironments[46–48,50–54].However,themajorityofthestudiesonlyused
cultivation‐dependenttechniques,introducinganimportantbiasintheevaluationofthesignificance
ofthisactivity.Inthepresentcase,wehavecomparedthepotentialAHLproductionanddegradation
activityinbacteriaisolatedfromtheMediterraneanSeaatdifferentdepthsthroughbiosensor‐based
screeningmethods,withthenumberofputativeQSandQQgenesfoundinmetagenomesobtained
fromthesamemarinesamples.Thissimultaneousstudyallowedustoobtainamorecomplete
assessmentofthepossibleprevalenceoftheseprocesses,avoidingthelimitationsofthe
culture‐derivedandmetagenomicsearchmethodologies.Whileacultivablebacteriaanalysisonly
allowstoevaluateasmallpercentageofthetotalpopulation,metagenomicanalysisresultsdonot
takeintoaccountthepossiblepromiscuityofsubstratesintheretrievedQQsequencesandtheactual
expressionofthesegenesunderenvironmentalconditions.
Ahighercultivablebacterialdensitywasobservedintheaphotic,2000mdepthsample(upto
5.64×103CFU/mL)thaninthe90m,photicsample(upto0.6×103CFU/mL),despitenospecific
culturestrategywasappliedtoretrievepsychrophilicorbarophilicstrains.Theculturemediumused
fortheestimationisanimportantfactor,asdemonstratedbytheresultsobtainedinthe2000mdepth
sample(Figure1)andinpreviousstudiesintheAtlanticSea[42,48].Theoppositetrendwasobserved
inthecountsofheterotrophicbacteriaobtainedbyflowcytometrythatyieldedthreetimesmore
bacteriaat90thanat2000mdepth[56].Thisdiscrepancymayreflectahigherdensityofcultivable,
copiotrophicbacteriaintheaphoticsample,whichisfurthersupportedbythehighercountsobtained
incarbon‐richAMandFAS‐POLculturemediaforthissample.HighertotalPandNwereavailable
at2000m(0.5μMand8.6μMrespectively)incomparisontothesamplefrom90m(0.25μMand6.9
μM),whichmayalsoexplainthehigherCFUs/mLretrievedintheaphoticzonesample.Onthe
contrary,lowerTOCwasavailableinthe2000maphoticsample(0.94mgC/Lagainst1.35mgC/L),
whichcouldgenerateahighlycompetitive,nutrient‐limitedenvironmentintheaphoticsample.
Whileimportantdifferencesinthecommunitystructurewerefoundassociatedwithdepthin
themetagenomicsanalysis[56],thediversityoftheisolatedstrainswasverysimilarinthesamples
collectedat90and2000m,withmoststrainsbelongingtotheProteobacteriaandFirmicutesphyla.
Thisdifferenceisnotunexpected,asonlyabout1%ofthetotalmarinemicrobescanbeisolatedon
artificialmedia,whilethevastmajorityremainsuncultivable[83].Moreover,metagenomesavoidthe
biasimposedbyculturingtechniques,whichprioritizesthegrowthofr‐strategiesmicrobesthatare
expectedtodominatethecultivablepopulation.Proteobacteriawerethemostprevalentlineagein
Genes2018,9,100 12of20
boththemetagenomicdataset(43%)andthecultivablebacteriacollection(52.38%),butthe
percentageofreadingsassociatedwithFirmicuteswaslessthan1%inanyofthedepthsinthe
metagenomicdiversity,whilethisclassrepresentedaround30%ofthecultivablebacteria.
Furthermore,whiletheAlphaproteobacteriadominatethebacterialpopulationintheMediterranean
Sea,decreasinginabundancewithdepth[56,84],inthecultivablecollectionsthisgrouprepresented
only18%withnodifferencebetweenthephoticandaphoticsamples.
ThedataobtainedfromtheMediterraneanSeabacterialcollectionsobtainedfrom90and2000
mdepthsshowedahighpercentageofstrainswiththeabilitytoactivatetheAHL‐reporterA.
tumefaciensNTL4.AlthoughthecultureconditionscouldstronglyaffectQSsignalproduction,and
thedetectionofAHL‐likeactivityintheculturesdoesnotguaranteethatthesignalsareproduced
underenvironmentalconditions[5],theresultssuggestthatAHL‐mediatedQSsystemscouldbea
commoncoordinationmechanisminmarinebacterialcommunities.Itshouldbenotedthatthe
microtiter‐basedscreeningmethoddoesnotallowhighgrowthrates,and,therefore,thenumberof
AHLproducerscouldbeunderestimated,atleastunderlaboratoryconditions,asdemonstratedfor
theidentificationofadditionalpositivestrainswhenculturedinhigher‐volume,shakencultures.A
higherabundanceofputativeAHLproducerswasfoundinthephotic,90msample(37.66%)in
comparisonwiththedeep‐seasample(4.01%).LowerPavailabilityandhigherbacterialdensitymay
justifythehigherrelevanceofQSmechanismsat90m,sinceAHLshavebeenproposedtomediate
andcoordinatethemechanismsofprocessingandacquisitionofP[29].AprevalenceofQSsystems
hasbeendemonstratedinnutrient‐deficientconditions[85],whichcouldalsobecorrelatedwiththe
higherputativeQSactivityfoundunderlaboratoryconditionsamongisolatesobtainedwiththe
oligotrophicculturemediaMA1/100andFAS‐POL.
ThescreeningforQQactivityshowedthat38.24%ofthestrainswereabletointerceptthe
long‐chainQSsignalC12‐HSL.AlthoughAHL‐likeactivitywasalsodetectedinthesupernatants
fromsomeoftheseQQstrains,itisunlikelythattheobservedinhibitoryeffectcansimplybeascribed
totheinhibitoryeffectofnon‐cognateAHLs,sincetheQQactivityisstillpresentinthecellextracts,
andtheconcentrationofthesignalwouldbetoolowtocounteractthehighAHLconcentrationused
intheQQscreeningassays(10μM).Inthesameway,andalthoughwecannotfullydisregardthe
factthatsomeofthestrainswithQQactivitywereproducingahighconcentrationofaQSinhibitory
substance,thehighAHLconcentrationusedinthebioassayssupportsthefactthattheobservedQQ
activityshouldbemainlyofenzymaticnature.Additionalbiochemicalanalysisshouldbeperformed
toconfirmthishypothesis[86].Thehighpercentageofcultivablestrainsidentifiedinbothphoticand
aphoticsampleswiththiscapacityindicatesthatQQmaybeacommonactivityintheMediterranean
Sea,whichisgenerallycharacterizedbyoligotrophy[87].OppositetotheputativeQSactivity,QQ
activityagainstC12‐HSLwasalmost1.63‐foldat2000m(47.05%)incomparisonwiththesample
from90m(29.43%).ThisabundancecorrelateswithlowerPOCavailabilityinthedeepersampleand
maythereforeindicateahighlycompetitiveenvironmentinwhichthebacterialpopulationcapable
ofusingthelong‐chainAHLasasourceofcarbonmayhaveanecologicaladvantage.AlthoughpH,
salinity,pressure,andintensityoftheUVirradiationoftheseawaterhaveasignificantinfluenceon
theproduction,stability,andperceptionoftheQSsignalmolecules[13,24,88,89],thedifferencesin
thephysicochemicalparametersbetweenthetwosamples[56]donotjustifythedifferencesinQS
andQQactivity.
Alargedifferencewasobservedbetweentheabilityofthestrainstodegradethelong‐chain
signalC12‐HSL(38.24%)ortheshort‐chainsignalC6‐HSL(1.93%).Unlikethedegradationof
C12‐HSL,thepercentageofstrainsbeingabletodegradeC6‐HSLwassimilarinbothsamples(1.73
and2.12%).Thislowprevalenceofstrainswithwide‐spectrumQQactivityissimilartothe
percentagereportedforsoilsamplesagainsttheC6‐HSL(2.5%)[43].Themorediffuseddegradation
oflong‐chainAHLssignalsamongmarinebacteriacouldberelatedtotheself‐degradationprocess
thatthelactoneringsuffersatthehighpHofseawater,whichoccursfasterfortheshort‐chainAHLs
[53];therefore,specificenzymaticdegradationwouldbemorenecessaryforthelong‐chain
molecules.ThisdatawouldalsosupporttheideathatQSsignalscanbeusedasanadditionalcarbon
Genes2018,9,100 13of20
andenergysourceundercarbon‐limitationconditions,sincethedegradationofalong‐chainsignal
suchasC12‐HSLcouldcontributemoreefficientlythanthatoftheshorteronestothemetabolic
budgetofthecells.
Thewide‐spectrumQQstrainsidentifiedinthisstudybelongtoAlphaproteobacteria(eight
strains),Betaproteobacteria(onestrain),Gammaproteobacteria(onestrain),Actinobacteria(one
strain),andFirmicutes(onestrain).Additionally,anovelspeciesbelongingtothegenusRalstonia
wasidentified(strain2F1).MicrobacteriumschleiferiandRalstoniasp.,isolatedfrom90mand2000m
depth,respectively,belongtoagenuswithpreviouslyreportedQQactivity[89–92].Onthecontrary,
thisisthefirstreportontheabilitytointerceptAHL‐mediatedcommunicationofmembersfromthe
genusPlanomicrobium,Sphingopyxis,Erythrobacter,Pantoea,andCitromicrobium.Aspreviously
reported[46–48,50],thetaxonomicdiversityfoundinthemarinebacteriawithwide‐spectrumQQ
activityismuchhigherthaninsoilandplantsamples,wheremainlyBacillusstrainswereidentified
[43,44].Surprisingly,inourcase,despitethehighnumberofBacillusstrainspresentinthecollection
(15%),noneofthemshowedwide‐spectrumQQactivity.MostofthestrainswithQQactivityisolated
inthisstudybelongtotheAlphaproteobacteria,includingrepresentativesofthegenus
Citromicrobium,Erythobacter,andSphyngopyxis.Alphaproteobacteriarepresentmorethan15%ofthe
cultivablebacteriaanalyzedand25%ofthemetagenomicdiversity(Figure2)[56].Althoughthe
abundanceofErythrobacterstrainsinthecultivablecollectionwassimilarinbothsamples(2.30%),
surprisingly,thosefrom2000mdepthpresentedQQactivitymorefrequently(fivestrainsagainst
one).DifferencesintheQQactivityamongspeciesofthesamegenushavebeenalreadyreported
[66],and,inthiscase,thehigheractivityamongisolatesfromthedeepersamplemayfurthersupport
anadaptativevalueofthisactivityincarbon‐limitedenvironments.Regardingtheactivitypresentin
thecrudecellextract(CCE)ofthewide‐spectrumQQstrains,strains2E12(Sphingopyxisalaskensis)
and2F1(Ralstoniasp.)presentedthestrongestQQactivity,sincetheirMACwere18.67and17.6μg
CCEprotein/mL,respectively.ThisvalueissimilartotheMACreportedforTenacibaculumsp.20J,a
bacteriumwithhighQQactivity[66,67].FurthercharacterizationoftheQQactivityofthesestrains
inordertoconfirmtheirQQenzymaticactivitywithadditionalbiochemicalanalyses[86,93]will
certainlycontributetothesearchfornovelanti‐pathogeniccompoundswithpotentialapplications
tocontrolbacterialinfectionsinplants[42],aquaculture[31,51,67],andmorerecentlyinbiomedicine
[94].
WehaveobservedaclearincreaseinthepresenceoftheQSandQQputativesequenceswith
thesampledepth.Therelevanceofthesegenesisespeciallyevidentintheaphoticsamples,inwhich
theabundanceoftheQSandQQsequenceswashigherthanthatofsequencesrelatedtosulfur(dsrA
andsoxB),nitrogen(amoC),andoxidativemetabolism(dmdA).ThesimilarfrequencyofQQenzymes
inrelationwithotherimportantprocessesmightsuggestapotentialrelevanceoftheseprocessesin
thesea,mainlyindeeperwaters.AfurtheranalysiswouldbenecessaryinordertoassesifQSand
QQgenesareactuallyexpressedinthemarineenvironment.
WhilethemetagenomicdataareconsistentwiththehigherQQactivityfoundamongcultivable
bacteriaindeepersamples,animportantdiscrepancywasfoundbetweenthehigherpresenceof
QS‐relatedgenesinthe2000msampleandthelowerputativeQSactivityinthecultivablebacteria
obtainedfromthesamesample.Asexplainedbefore,thebiasderivedfromtheuseofculture
conditionsnotresemblingthenaturalmarineenvironmentmaybethecauseofthisdiscrepancy.A
recentstudyonfourdifferentEscherichiacolistrainsshowedthatthe47%ofthevarianceinexpression
levelsisdependentprimarilyontheenvironment(medium‐dependentgenes)[95].Therefore,the
presentinvitroexperimentsindicatetheabilityofahighpercentageofthemarinestrainstoactivate
AHLsensorsandquenchtheAHLmolecules;however,furtherenvironmentalinvivostudiesare
neededtoconfirmandcompleteourknowledgeregardingtheroleandrelevanceofAHL‐mediated
QSinthemarineenvironment.
ThehigherpercentageofcultivablestrainswithAHL‐typeQSandQQactivitystronglysupports
thesignificanceofthisactivityinmarinesamples,however,theresultsderivedfromthe
metagenomicsanalysisshouldbeinterpretedwithcaution.First,thedetectionofsequenceswithhigh
Genes2018,9,100 14of20
similaritiesdoesnotensuretheconservationofthefunctionalityortheexpressionofthegeneunder
specificenvironmentalconditions.Secondly,sinceotherpossiblebiochemicalactivitiescouldbe
attributedtotheQQenzymes,thehighprevalencecannotbeunequivocallyrelatedtoAHL
degradation.Inthissense,theMediterraneanmetagenomesanalyzedyieldedahighernumberof
acylasesthanlactonases(Figure4),despitethewidestdiversityofAHLlactonasesidentifiedsofar
[4,39].AhigherprevalenceofacylaseshasalsobeenreportedpreviouslyintheGOSsequences[48],
eventhoughatthattimethenumberofknownlactonaseswasmuchlower.Typically,AHLacylases
areconsideredmoresubstrate‐specificthanlactonasesandhavebeendefinedasexclusiveAHL
degraders.However,therecentidentificationofacylaseswithabroadspecificitywhichcanalso
degradepenicillinG[96,97],hasaddedcomplexitytothemetabolicroleofAHLacylases.This
promiscuityofsubstratescouldpartiallyexplainthishigherfrequencyandquestiontheexclusive
activityoftheseenzymesinthedegradationofAHL‐typeQSsignals.Therefore,anddespitethedata
obtainedfromthemetagenomicanalysisseemtoconfirmthehighestprevalenceofQQactivitiesin
deepersamples,thisresultshouldbeinterpretedwithcautionuntiltheQQactivityofsomeofthe
retrievedsequencescanbeconfirmed.
Inthisstudy,wehavefoundthatthepresenceofthethreetypesofAHLsynthaseswasverylow
intheentirewatercolumn.ThestudyofmetagenomicdatabasesfromtheAtlantic,Pacific,andIndian
Oceans[33]demonstratedthattheQSgenesLuxI,AinS,andespeciallyHdtSarepresentinamuch
widerdiversityofmarinebacteriathanpreviouslysuspectedfromcultivablebacteria,andtheywere
morefrequentlyidentified(0.02–14.8)incomparisontothepresentstudy(0.01–0.17).Asdescribed
hereforthevariabilityintheQQactivity,differencesinnutrientavailabilityorphysicochemical
conditionsmayberesponsibleforthesedifferencesamongsamplingsites,althoughdifferencesin
themethodologyappliedcannotbedisregardedasasignificantsourceofvariation.AHLreceptors
weremuchmorecommonthanAHLsynthasesintheMediterraneansamples,especiallyat2000m
depth(Figure4A),correlatingwithahigherabundanceofQQactivityandgenes.Inagreementwith
thisunbalancebetweenQSsynthasesandreceptors,apreviousstudyshowedthatamongthe68
genomesofProteobacteriacompared,45containedorphanLuxRhomologsbutnoadditionalLuxI
homologs,and66%showedmoreLuxRthanLuxIhomologs[98].Thisunbalancecanbeattributed
toalargeprevalenceoforphanLuxRreceptorsinthebacterialpopulation.Themicroorganismswith
anorphanLuxRdonotregulatedirectlytheAHLsynthesis,buttheycanparticipateinthecell‐to‐
cellbacterialcommunication.Thissupportstheideathattheabilityto“sense”otherbacteriaismore
efficientthanthecapacityto“talk”tothem,sincetheAHL‐productionishighlyenergycostly.
Moreover,othermolecules,suchascinnamoyl‐HSL,p‐coumaroyl‐HSL,α‐pyrones,and
dialkylresorcinols,havebeenreportedtoactivateLuxR‐typereceptors[11].Nevertheless,intheview
ofthelargeunbalancebetweenthenumberofsynthasesandreceptorsidentifiedinthe
Mediterraneanmetagenomes,thehypothesisoftheexistenceofotheryetunknownAHLsynthases
cannotbeexcluded.
Surprisingly,anddespiteVibriosp.representinga3.5%ofthebacterialpopulationinthe
analyzedsamples,noLuxShomologscouldbeidentifiedintheentirewatercolumn,indicatingthat
theAHL‐mediatedQSprocessesaremoreabundantthantheAI‐2signalingpathwayinthemarine
environment.Incoherencewiththisresult,LuxShomologuescouldbeidentifiedinonly3ofthe13
sitesincludedintheGOSdatabase,withanormalizedfrequencyof0.7[33].Thisdataonthe
prevalenceoftheluxSgenecontrastswiththe653sequences(14.8)affiliatedtoHdtSinthesame
study,confirmingthattheAHL‐mediatedQSprocessesaremorefrequentthantheAI‐2signalingin
themarineenvironment.
ThehighpercentageofisolatedstrainswiththeabilitytoactivateAHLbiosensorandtodisrupt
long‐chainAHLQSsignalsintheMediterraneanSea,combinedwiththehighfrequencyofQQand
QSgenesthatcorrelatewithlowerCavailability,indicatesthatQSandQQcouldbeusualstrategies
inthismarinehabitatthatmayconferacompetitiveadvantageinoligotrophicconditions.
Furthermore,theanalysisofthemetagenomicdataindicatesthatQSandQQprocesseshavean
importantroleindeepmarinehabitats.Onsite,ecologicalstudiesonQSandQQactivityandthe
Genes2018,9,100 15of20
identificationofmoreQS‐andQQ‐relatedsequencesinthemarinehabitatswouldprobablyprovide
keyknowledgetofurtherelucidatetheecologicalimportanceofAHL‐mediatedQSandQQprocesses
inthemarineenvironment.
SupplementaryMaterials:Thefollowingareavailableonlineathttp://www.mdpi.com/2073‐4425/9/2/100/s1,
TableS1:Totalisolatedstrainsfromdifferentsamplesandculturemedia,showingthenumberandpercentage
ofstrainswithputativeQSandQQactivityagainstC6‐andC12‐HSLobtainedusingthesolidplateC.violaceum
assay.Mediaused:tryptonesoyagar1%NaCl(TSA‐1),marineagar(MA),dilutedmarineagar(MA1/100),and
filteredautoclavedseawatermedium(FAS)supplementedwith0.5g/Lpolymers:agarose,chitin,andstarch
(FAS‐POL).
Acknowledgments:Thisworkwassupportedbythenon‐profitorganizationsFundaciónRamónAreces
(CIVP16A1814),theEUProjectByefouling(grantagreementno612717),andbythegrant“AxudasdoPrograma
deConsolidacióneEstructuracióndeUnidadesdeInvestigaciónCompetitivas(GPC)”fromtheConselleríade
Cultura,EducacióneOrdenaciónUniversitaria,XuntadeGalicia(ED431B2017/53).A.M.wassupportedbya
predoctoralfellowshipfromtheConselleríadeCultura,EducacióneOrdenaciónUniversitaria,XuntadeGalicia
(ED481A‐2015/311).M.L.P.wassupportedbyaPostdoctoralfellowshipfromtheValencianConselleríade
Educació,Investigació,CulturaiEsport(APOSTD/2016/051).WewouldliketothankPaulWilliamsfrom
UniversityofNottinghamandTomohiroMorohoshifromUtsunomiyaUniversityforkindlyprovidinguswith
theChromobacteriumviolaceumCV026andVIR07biosensorstrains,respectively.
AuthorContributions:A.M.,C.M.,A.P.,J.A.,andA.O.carriedouttheisolation,screening,andselectionofthe
marinestrains.Theyalsocharacterizedandidentifiedthequorumquenchingstrains.M.L.carriedoutthe
metagenomicanalyses.A.M.,M.L.,andA.O.wereinchargeofthewritingofthepaper.
ConflictsofInterest:Theauthorsdeclarenoconflictofinterest.
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