The role of seasonality in shaping the interactions of honeybees with other taxa
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This is a self-archived version of an original article. This version may differ from the original in pagination and typographic details. Author(s): Title: Year: Version: Copyright: Rights: Rights url: Please cite the original version: CC BY 4.0 https://creativecommons.org/licenses/by/4.0/ The role of seasonality in shaping the interactions of honeybees with other taxa © 2023 the Authors Published version Wirta, Helena; Jones, Mirkka; Peña‐Aguilera, Pablo; Chacón‐Duque, Camilo; Vesterinen, Eero; Ovaskainen, Otso; Abrego, Nerea; Roslin, Tomas Wirta, H., Jones, M., Peña‐Aguilera, P., Chacón‐Duque, C., Vesterinen, E., Ovaskainen, O., Abrego, N., & Roslin, T. (2023). The role of seasonality in shaping the interactions of honeybees with other taxa. Ecology and Evolution, 13(10), Article e10580. https://doi.org/10.1002/ece3.10580 2023
Ecology and Evolution. 2023;13:e10580. | 1 of 16 https://doi.org/10.1002/ece3.10580 www.ecolevol.org Received:10July2023 | Revised:19September2023 | Accepted:20September2023 DOI: 10.1002/ece3.10580 RESEARCH ARTICLE The role of seasonality in shaping the interactions of honeybees with other taxa Helena Wirta1 | Mirkka Jones2,3 | Pablo PeñaAguilera4 | Camilo ChacónDuque5,6 | Eero Vesterinen7 | Otso Ovaskainen2,8,9 | Nerea Abrego1,8 | Tomas Roslin1,4 ThisisanopenaccessarticleunderthetermsoftheCreativeCommonsAttributionLicense,whichpermitsuse,distributionandreproductioninanymedium, provided the original work is properly cited. ©2023TheAuthors.Ecology and EvolutionpublishedbyJohnWiley&SonsLtd. 1DepartmentofAgriculturalSciences, UniversityofHelsinki,Helsinki,Finland 2OrganismalandEvolutionaryBiology ResearchProgramme,FacultyofBiological andEnvironmentalSciences,Universityof Helsinki,Helsinki,Finland 3HelsinkiInstituteofLifeScience, UniversityofHelsinki,Helsinki,Finland 4DepartmentofEcology,Swedish UniversityofAgriculturalSciences, Uppsala,Sweden 5CentreforPalaeogenetics,Stockholm, Sweden 6DepartmentofArchaeologyandClassical Studies,StockholmUniversity,Stockholm, Sweden 7DepartmentofBiology,Universityof Turku,Turku,Finland 8DepartmentofBiologicaland EnvironmentalScience,Universityof Jyväskylä,Jyväskylä,Finland 9DepartmentofBiology,Centrefor BiodiversityDynamics,Norwegian UniversityofScienceandTechnology, Trondheim,Norway Correspondence HelenaWirta,DepartmentofAgricultural Sciences,UniversityofHelsinki,P.O.Box 27,Helsinki00014,Finland. Email:helena.wir[email protected] Funding information AcademyofFinland,Grant/Award Number:322266,336212and345110; H2020EuropeanResearchCouncil,Grant/ AwardNumber:101057437,101059492 and856506;JanejaAatosErkonSäätiö; KoneenSäätiö,Grant/AwardNumber: 2018104360;NorgesForskningsråd, Grant/AwardNumber:223257 Abstract TheEltoniannicheofaspeciesisdefinedasitssetofinteractionswithothertaxa. Howthissetvarieswithbiotic,abioticandhumaninfluencesisacorequestionof modernecology.Inseasonalenvironments,therealizedEltoniannicheislikelytovary duetoperiodicchangesintheoccurrenceandabundanceofinteractionpartnersand changesinspeciesbehaviorandpreferences.Also,humanmanagementdecisionsmay leavestrongimprintsonspeciesinteractions.Tocomparetheimpactofseasonality tothatofmanagementeffects,honeybeesprovideanexcellentmodelsystem.Based onDNAtracesofinteractionpartnersarchivedinhoney,wecaninferhoneybeeinteractionswithfloralresourcesandmicrobesinthesurroundinghabitats,theirhives, andthemselves.Here,weresolvedseasonalandmanagement-basedimpactsonhoneybeeinteractionsbysamplingbeehivesrepeatedlyduringthehoney-storingperiod ofhoneybeesinFinland.Wethenuseagenome-skimmingapproachtoidentifythe taxonomiccontentsoftheDNAinthesamples.Tocomparetheeffectsoftheseason totheeffectsoflocation,management,andthecolonyitselfinshapinghoneybee interactions,weusedjointspeciesdistributionmodeling.Wefoundthathoneybee interactionswithothertaxavariedgreatlyamongtaxonomicandfunctionalgroups. AgainstabackdropofwidevariationintheinteractionsdocumentedintheDNAcontentofhoneyfrombeesfromdifferenthives,regions,andbeekeepers,theimprintof theseasonremainedrelativelysmall.Overall,ahoney-basedapproachoffersunique insightsintoseasonalvariationintheidentityandabundanceofinteractionpartners amonghoneybees.Duringthesummer,theavailabilityanduseofdifferentinteractionpartnerschangedsubstantially,buthive-andtaxon-specificpatternswerelargely idiosyncraticasmodifiedbyhivemanagement.Thus,thebeekeeperandcolonyidentity are as important determinants of the honeybee's realized Eltonian niche as is seasonality. KEYWORDS Apis mellifera,Eltonianniche,honey,jointspeciesdistributionmodeling,management,microbe, plant,wholegenomesequencing
2 of 16 | WIRTA et al. 1 | INTRODUCTION Theecologicalnicheofaspeciescanbecharacterizedfromtwo perspectives:asthespecies'responsetoabioticconditions(the Grinnellianniche;Grinnell,1917;Whittakeretal.,1973) and as its interactions with other taxa in the surrounding community (the Eltonian niche; Elton, 1927). Over the past few decades, there hasbeenasignificantinterestfocusedoncharacterizingspecies' Grinnellian niches due to changes in global abiotic conditions. However, the Eltonian niche is as important as the Grinnellian niche to be understood (see, e.g., Wirta et al., 2022), as environmentaleffectsonbothaspectsofthenicheareequallylikely (Graveletal.,2019; Pellissier et al., 2018).Thus,weshouldfurther ourunderstandingofhowexternalimpactsshapecommunitydynamicsandecologicalinteractionnetworks,namelytheEltonian niche(Graveletal.,2019). Inseasonalenvironments,therealizedEltoniannichesetislikely tovaryacrosstheseason,asdrivenbyperiodicchangesintheoccurrenceandabundanceofinteractionpartnersandbychangesin speciesbehavior.Seasonalityreferstomajorchangesinaspecies' environmentthatarepredictablyrepeatedeachyear.Howspecies' interactionsare influencedby seasonalcycleshas been the focus ofintenseresearch,inparticularinthecontextofchangingspecies' phenologies(e.g.,Ekholmetal.,2019; Kešnerová et al., 2020;Rabeling et al., 2019). Species inhabiting seasonally fluctuating environments experience variations in the intensity of their interactions, which are influencedbythechangingseasons.Inotherwords,seasonalityis likelytoshapedifferentdimensionsoftherealizedEltonianniche differently,wheresomeinteractionsarestronglyaffectedwhereas othersareweaklyaffectedorremainunaffected.Ononeendofthe spectrum, certain interaction partners are only accessible during specifictimewindows,dictatedbytheirownphenologicalpatterns. Thisleadstoasignificantturnoverininteractionpartnersovertime. Ontheoppositeend,anothergroupofinteractionpartnersremains activeconsistentlythroughdifferentseasons,resultinginminimal turnoverininteractions.Nonetheless,it'sworthnotingthattheimpact of seasonality on species interactions has traditionally been examinedforonlyalimitedsubsetofinteractingtaxaatanygiven time.(e.g.,Bauer&Hoye,2014;Hutchisonetal.,2020;Rasmussen et al., 2013, 2014;Rudolf,2019). Beyond seasonal effects, human management decisions may leavestrongimprintsonspeciesinteractionsandtherefore,onthe realized Eltonian niches. By affecting the availability of resource species across landscapes, humans may strongly affect the set of realizedinteractions(Kortschetal.,2023).Fordomesticatedorhalf- domesticatedspecies,theseeffectswillbemostpronounced,asthe human actor will affect both the focal species and which species itinteractswithbyactivelyaltering,forexample,itsaccesstoresources and its pathogen load. A challenge for exploring the wholesale seasonal and anthropogenicdriversoftheEltoniannicheisthecomplexityofresolving largesetsofinteractionsinempiricalsystems.Here,thehoneybee, Apis mellifera,offersauniquestudysystemforassessingseasonal andothereffectsontherealizedEltonianniche(Wirtaetal.,2022). Honeybeeshavebeeninsertedbyhumansinenvironmentscharacterizedbydifferentseasonalityanddifferentmanagementpractices throughouttheworld.Importantly,theseinteractionscanbereconstructed from DNA traces left in honey (Bovo et al., 2018, 2020; Cirtwill et al., 2022;Galanisetal.,2022;Leponiemietal.,2023).Such studiestodatehaveshownthathoneybeesinteractwithamultitude ofothertaxa,mostimportantlyfloweringplants,butalsomicrobes (Aizenberg-Gershteinetal.,2013;Engeletal.,2016; Moran, 2015; Wirtaetal.,2022). While interactions between honeybees and plants tend to be mutualistic in nature, interactions between bees and microbes can be either pathogenic, mutualistic, or neutral in nature (Engel et al., 2016; Morse, 1994).Asanexampleofapathogenicinteraction,theinteractionofhoneybeeswiththebacteriumPaenibacillus larvaewillcauseseverediseaseinhoneybees.Incontrast,interactionsofhoneybeeswithSnodgrassella alvi or Gilliamella apicola can bedescribedasmutualisticsincethesebacterialiveinthehoneybee'sgut,sustainingthehoneybee'shealth(Fünfhausetal.,2018; Raymann&Moran,2018). The strongest effects of seasonality on honeybee niches willlikelyoccurathighlatitudes,whereseasonalenvironmental changes are most pronounced. Here as everywhere else, bees will encounter a wide range of floral resources (Lehmuskallio & Lehmuskallio,2006; Ruottinen et al., 2003;Salonenetal.,2009), butalsointeractwitharangeofmicrobes,includingthosepresent onflowers(Jonesetal.,2018).Bothmicrobeslivinginthehiveand beepathogenshavebeenfoundtochangeseasonally(Donkersley et al., 2018; Runckel et al., 2011),possiblyfollowingthephenologiesofdifferentplantspecies.Thus,seasonalityislikelytoaffect bothmutualisticandantagonisticinteractionsbetweenbeesand othertaxa. Apart from seasonal effects on the honeybees, their Eltonian niche is likely to be shaped by anthropogenic factors with an impact on how the colony explores and utilizes its environment. Of particular interest are management practices, including measures ofdiseasecontrol,overwintering,andhivesize.Theseeffectscan becapturedbytheidentityofthebeekeeper,whowillapplysimilar methodstotheirhives(Morse,1975, 1994; Ruottinen et al., 2003). However,evenwithsimilarmanagementpractices,individualhives sustainedbyanindividualbeekeeperwillalsodifferfromeachother. Thisisduetodifferencesinforagingbehavior,foragingcapacity,and TAXONOMY CLASSIFICATION Agroecology,Appliedecology,Communityecology 20457758, 2023, 10, Downloaded from https://onlinelibrary.wiley.com/doi/10.1002/ece3.10580 by University Of Jyväskylä Library, Wiley Online Library on [12/10/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
| 3 of 16 WIRTA et al. susceptibilitytodiseasesoftheindividualcolony(Wrayetal.,2011). Suchaspectsarestronglyaffectedbythecharacteristicsandhealth ofthe queen, shaping the performance of thecolonyandfurther modifyingitsbehavior(Amirietal.,2017).Theeffectsofthesefactorscanthusbecapturedbytheidentityofthehive.Additionally, thespecificenvironmentinwhichthehiveisplacedalsoaffectsthe behaviorofthecolony. Inthispaper,we usehoneysamplesfromFinlandto compare the role of seasonality to that of management in determining the interactionsofhoneybees with other taxa (plants,bacteria, fungi, andviruses).Forthispurpose,wedrawonagenome-skimmingapproachtotheDNAtracesstoredinthehoney.Toresolvetemporal variationintheinteractionrecordsofhoney,wesampledhivesrepeatedlyduringthehoney-storingperiodofhoneybeesandasked thefollowingquestions: 1. How does time of the season compare to the geographical location (site), management practices (beekeeper), and colony identity (hive) in terms of its influence on the taxa which honeybees encounter and interact with? 2. Howdoestheuseoffloweringplantsbyhoneybeeschangeduringthemainfloweringseason(i.e.,summer)? 3. How do the interactions between honeybees and microbes changeduringthesummer,andhowdopatternsdifferbetween differenttaxonomicandfunctionalgroupsofmicrobes? 4. Willco-occurrencepatternsamongtaxadetectedintemporally- resolvedhoneysamplessuggestinteractionsorphenologicalassociationsamongthetaxathemselves? 2 | MATERIALS AND METHODS 2.1 | Seasonality in NorthEuropean honeybee resources InnorthernEurope,beescanactivelyinteractwithorganismsoutsidetheirhiveforabout6 months(BennoMeyer-Rochow,2008; Ruottinen et al., 2003).PollenforagingtypicallystartsinMarchor April,withthecolonyreachingitsmaximumsizeinMayandJune. From mid-June to mid-August, the bees work on storing honey, andbylate-August,thecolonybeginspreparingforoverwintering byproducingthelastworkersoftheyear(Ruottinenetal.,2003). Duringthis6-monthperiod,thebeeswillinteractwitharangeof flowering plants, each with its own phenology. Floral resources aretypicallymostabundantinlate-JuneandJuly,whenbothearly andlatesummerfloweringspeciesareinbloomsimultaneously. Thisconcernsboththespeciesrichness offloweringplantsand theirfloralabundance.Ofthetypicalplantsusedbyhoneybees in Finland, willows (Salixspp.)anddandelion(Taraxacum spp.) begintobloominMay,thenrapeseed(Brassicaspp.),raspberry (Rubus idaeus),clovers(Trifoliumspp.),andfireweed(Epilobium angustifolium)flowerfromJuneonwards,andthistles(Cirsium spp.) andheather(Calluna vulgaris)begintheirfloweringonlylaterin July (Benno Meyer-Rochow, 2008; Lehmuskallio & Lehmuskallio, 2006;Salonenetal.,2009). 2.2 | Using honey as an archive of interaction partners Alargeproportionoftaxathathoneybeesencounterorinteract withcanbefoundinandidentifiedfromhoney,whereDNAtraces ofthesetaxatendtobewellpreserved.ByidentifyingtheDNA foundinhoney,onecanthustellwhatothertaxahoneybeeshave encounteredorinteractedwith,especiallyfortheirinteractions withmicrobesandplants(Bovoetal.,2020;Wirtaetal.,2022). Addingtotheinformationvalueofhoney,nectarisspreadinto opencombsfordrying,andbeesaddenzymaticsecretionsduringtheprocessingofnectarintohoney(Crane,1979), and these processingstageswouldallowDNApresentinanyformwithin the hive to enter the nectar, turning it into honey. In practice, recently produced honey can be distinguished by its looks and position:onthehoneyframesofahive,thisfreshhoneysitsnext tohoneystilluncoveredbywax,andpartofthecombsareyet toreceiveafullwaxcover.Thisnewhoneyconveysasampleof thehoneybees'interactionsduringthelastweek,corresponding tothetimeduringwhichthisnectarhasbeencollectedandprocessedintohoneybythebees.Ingeneral,thetimetakenbynectartoripenintohoneytendstovaryfrom3to7 days,depending onweather,colonystrength,andnectaravailability(Crane,1979; Morse, 1975, 1994). Overall, the many processing stages involved in converting nectartohoney,therepeatedmanipulationofthenectarbythe bee,andthetimespentdryingin opencombsallowDNApresent in multiple forms within the hive to enter the nectar. Thus, thehoneyofabeehiveoffersawell-preservedrecordofrecent interactionpartnersofitsbees.However,it'scrucialtonotethat notallDNAfrominteractionsiscarriedbacktothehive,andconsequently,someofitdoesnotbecomeapartofthehoney.For instance,whenhoneybeesarepreyedupon,theDNAofthepredator is not included in the honey, leading to the undetected nature oftheseinteractions. 2.3 | Sampling Tocharacterizeseasonalvariationinthemicrobialandfloralinteractionpartnersofhoneybees,weobtainedhoneysamplesdirectly frombeehivesbelongingto14Finnishbeekeepers(Figure 1).Each beekeeperselectedtwoorthreeoftheirhives,totaling41hives forthestudy.Fromeachhive,honeywascollectedatthreetime points during the season, before the final harvest of all honey from the hives. Thus, samples were obtained from late-June to mid-August.Allbeekeeperswereaskedtosampletheirhivesduringthesameweeks,correspondingtothe22ndto28thofJune, the13thto19thofJuly,andthe3rdto9thofAugustof2020. 20457758, 2023, 10, Downloaded from https://onlinelibrary.wiley.com/doi/10.1002/ece3.10580 by University Of Jyväskylä Library, Wiley Online Library on [12/10/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
4 of 16 | WIRTA et al. Toensurethatthehoneysamplerepresentedthespecifiedtime of the season, the beekeepers were instructed to collect only honeynewlycoveredbywax.Toobtainuncontaminatedsamples, weprovidedthebeekeeperswithDNA-freesamplingequipment. To ensure that the sample was representative of the variety of nectarrecentlycollected,aspoonfulofhoneyfromthreedifferent frames was combined in each sample. Additionally, we also obtainedasampleofhoneyfromtheendofseasontotalyieldof eachbeekeeper.Thissamplewasusedtoassesswhethersucha time-aggregatedsamplewillincludealltheinformationgathered fromtheseparatetime-specificsamples. DuetoadryperiodinearlyJulyof2020,therewasashortage offlowersinpartsofthestudyarea.Therefore,Julysamplescould notbeobtainedforallhives.Furthermore,forsomeofthesamples, notenoughDNAcouldbeextractedfromthe20 gofhoney.Thus,in total,wewereabletosequence115samplesfromindividualhives and13samplesofcompound,endofseasonhoneyasharvestedby individualbeekeepers. 2.4 | Laboratory methods ToidentifythetaxonomicoriginofDNAinhoneysamplesfromdifferentpartsofFinland,weusedaPCR-freemetagenomicapproach. Instead of metabarcoding, where single genes are amplified and sequencedinasampleusingprimerstargetedtothespecificgene region(e.g.,Vesterinenetal.,2018),weutilizedagenome-skimming approachtosequencerandomfragmentsofeachspecies’genome presentinasamplewithoutanylocus-specificPCR(see,e.g.,Coissac et al., 2016). FIGURE 1 Locationsofbeehives sampledforhoneyinFinland,colored bybeekeeperidentity(with2–3hives sampledperbeekeeper).Notethatsome beekeepershadhivesatmorethanone site. To resolve overlapping sites, the locationsofhiveshavebeenslightly jitteredinboththehorizontalandvertical planes. 20457758, 2023, 10, Downloaded from https://onlinelibrary.wiley.com/doi/10.1002/ece3.10580 by University Of Jyväskylä Library, Wiley Online Library on [12/10/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
| 5 of 16 WIRTA et al. To prepare the samples for DNA extraction, two subsamples of10 gwereeachdiluted with30 mL of DNA-free water(double- distilled“MQ-water”).These subsampleswere allowedtodissolve for 1 h at +60°C. To collect all the tissue material and to remove excesswater,thesubsampleswerecentrifugedfor60 minat8000 g (Centrifuge5810R,Eppendorf).Mostofthesupernatantwasdiscarded, and the pellets from the two subsamples were combined into a 2 mL tube. The tube contents were further centrifuged for 5 minat11,000 g(Heraeus Pico 21 centrifuge, ThermoScientific). The remaining supernatant was discarded, and the pellets were storedat−20°CuntilDNAextraction. Total DNA was extracted from each sample with the DNeasy PlantMiniKit(Qiagen)withthefollowingmodificationstotheprotocol:Initially,thepelletwasresuspendedin400 μLofbufferAP1,and then 4 μL RNase, 4 μL proteinase K (20 mg/mL, Macherey-Nagel), and one 3 mm tungsten carbide bead was added to each sample tube.Thesamplewasthendisruptedfor2 × 2 min30 Hz(MixerMill MM400,Retsch).DNAextractionthenfollowedtheprotocol,exceptthattheQIAshreddercolumnstepwasomittedtoavoidDNA loss.Alllaboratorystepsweredoneinalaminarhoodwipedwith ethanolandcleanedofDNAwith1 hofUVlighteverynight.We onlyusedDNA-freetubes,pipettetips,andPCRplates,aswellas DNA-freewater. DNAquantitywasmeasuredwithaQubit4fluorometer(Thermo FisherScientific).Forpreparingthesequencinglibrary,thesamples weredilutedtoaconcentrationof1 ng/μL.SampleswithDNAconcentrations <1 ng/μLwerenotdiluted.Thequalityandquantityof DNAin eachsample were measuredwithgenomic DNA TapestationandD500HSTapestation,beforethepreparationofthelibrary. TheNexteraXTtransposome,providedwiththeIlluminaNextera XTlibraryPreparationKit(Illumina,Inc.),wasusedtofragmentthe DNAinto150-bp-longpiecesandtotagtheDNAwithadaptersequences, following the Nextera XT Protocol. After this, an indexingPCR to anneal sample-specific indexes to theDNAfragments wasrun,andtheindexingPCRproductswerecleaned.Thesample- specificlibrarieswerenormalizedtothesamequantity,afterwhich theywerecombinedintothepooledlibrarytobesequenced.Allthe stepstopreparethesequencinglibraryfromthetotalDNAfollowed theNexteraXTProtocol(IlluminaInc,2019).Thelibrarywasthen sequencedinanIlluminaNovaSeq6000S4flowcell,using80%of one(outoffour)flowcelllane,equaling20%ofthetotalsequencing capacityoftherun.AllsequencingwasperformedbytheFunctional GenomicsUnitattheUniversityofHelsinki,Finland.Todetectpossiblecontamination,wesequencedaDNAextractionblankcontrol inthesameway. 2.5 | Bioinformatic processing Toremove anylow-qualitybasesfromthestart and endofreads and the Illumina adapter sequences, the raw reads were trimmed using Trimmomatic version 0.39 (Bolger et al., 2014) with the ILLUMINACLIP adapter-clipping settings “adapters.fa: 2:30:10 LEADING:3 TRAILING:3 SLIDINGWINDOW:4:15 MINLEN:50”. Toassembletrimmedreadsintodenovoscaffolds,weapplieddifferentk-merlengths[k-mer = 21,33,55,77,99,and121;following Nurketal.(2017)]usingtheSPAdesassemblytoolkitversion3.15.0 (Bankevichetal.,2012; https://github.com/ablab/spades) with the— meta flag (recommended for metagenomic data sets). To reduce heterozygosity, we then applied the Redundans pipeline (Pryszcz &Gabaldón,2016)totheassembledscaffolds,withdefaultvalues ofidentity0.51andoverlap0.8,andaligningallreads(alignsubset ofreadswithalimitvalueof1).ThereducedscaffoldswereannotatedtoNCBITaxIDsusingBLASTNsearchesagainsttheNCBInon- redundantnucleotidedatabase(nt)database(November–December 2021),keepingonealignedsequenceperscaffold(max_target_seqs 1),savingonlythebestalignmentforeachquery-subjectpair(max_ hsps 1), and with an E-valuelessthan1 × e−25.Tomapalltheoriginal trimmedandcorrectedsequencestothetaxonomicallyannotated referencescaffolds,BWAMEM(Li&Durbin,2009, 2010) was used, andtheresultsweresortedintobamformatfilescontainingsample,sequence,andmappedreaddatawithSAMtools(Lietal.,2009). Foreachassembly,theassociatedstatisticsatfourtaxonomicranks (phylum,family,genus,andspecies)weregeneratedwithBlobtools (Laetschetal.,2017)basedontheBLASTnsimilaritysearchresults. Tofurtherfilterallreads,withtheintentofremovingpotentially misassignedreadsandfalsepositivesduetotagjumpingorcontamination,wefollowedaconservativeapproach(followinge.g.,Alberdi et al., 2012; Lee et al., 2018).Asasmallnumberofreadsrepresentingalimitednumberoftaxawerefoundinthecontrolsample,we subtractedthesereadsfromthereadnumbersofthecorresponding taxainthehoneysamples.Asafinalfilteringstepaimedatremoving extremelyrareand/orspuriousreads,wecalculatedthemeanrelativereadabundance(RRAhereafter;Deagleetal.,2019)oftaxa(here genera)withinsamplesandremovedanytaxaandreadsassignedto taxawithasample-specificRRAof<0.001%.Fortheanalyses,we onlyincludedgenerawith≥0.01%meanRRAacrossthesamples. 2.6 | Occurrence of taxa and relative read abundances InanalysesbasedonRRA,astrongincreaseintheabundanceofany taxonwill,pernecessity,bereflectedinareductionintheproportionalrepresentationofothertaxa.Threegeneradominatedsome samples: Apilactobacillus(A. kunkeii), Zygosaccharomyces(Z. rougii), and the virus Apis mellifera filamentous virus (AmFV; see Text S1 and Figure S1).Forsomeofthesamples,thesetaxaaccountedfor mostreads(upto85.8%,91.2%,and99.1%forA. kunkeii, Z. rougii, andAmFV,respectively).Thus,torestricttheimpactofthesetaxa onpatternsinothertaxa,wealsocalculatedRRAafteromittingall readsassignedtothethreedominanttaxaidentifiedabove.Inthe analyses,weusedthepresence–absencedataofalltaxa(withmean RRA across samples ≥0.01%), but for abundance data, we omittedthethreetaxawithhighyetvariableproportions(TextS1 and Figure S1). 20457758, 2023, 10, Downloaded from https://onlinelibrary.wiley.com/doi/10.1002/ece3.10580 by University Of Jyväskylä Library, Wiley Online Library on [12/10/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
6 of 16 | WIRTA et al. The proportions of reads assigned to individual kingdoms of associated taxa (plant, bacterial, fungal, and viral genera) varied substantially between samples even after removing Apilactobacillus, Zygosaccharomyces, and AmFV (Figure S2). Thus, while we includedbothplantsandmicrobesintheanalyses,wealsodescribed thechangesinplantsandinmicrobesseparatelyfromeachother (Figures S 3 – S 5 ). The sequencing of the samples by Illumina NovaSeq s4, with 80%ofaflowcelllane,resultedin3.72billionreadspassingthefilter(thissequencingrunincluded140samples,outofwhich118plus anegativecontrol sampleare partofthisstudy).Forthesamples inthisstudy,2689.8millionreadspassedthequalitycontrols,averaging23.0millionreadsper sample. 85.8% ofthesereadswere assignedtothegenuslevelandthusretainedforfurtheranalyses. Inadditiontoplants,microbes,fungi,andviruses,weidentified11 animalgenerainthesamples,butthesewerenotconsideredinthe analyses. 2.7 | Functional groups of taxa Toresolvetaxaofdifferentfunctionalaffinitiesandofdifferentassociationswithhoneybees,weclassifiedthegenerafollowingWirta etal.(2022).Theliteratureusedinassigningtaxatospecificfunctional groups is shown in Table S1.Whenreadswithinagenuswere primarily(>90%)assignedtoagivenspecies,webasedthefunctional assignmentofthegenusoninformationassociatedwiththisspecific species.Whenreadswithinagenuswereassignedtomultiplespecies,weassessedthefunctionbasedonaspeciesknowntobeassociatedwithhoneybees.Finally,inthecasewherereadswerenot assignedtoanyparticularspecies,weassessedthefunctionbased onthegeneralbiologyofthegenus. Plants were classified into two groups based on their nectar- producingability.Microbescloselyassociatedwithbeeswereclassifiedascommonbeegutmicrobes,asbeehivemicrobes,orasbee pathogens.Microbeswithoutanyknownassociationwiththebees wereclassifiedasplantpathogens,asanimalpathogens,orasmicrobes known to be beneficial or neutral for plants and animals. Those microbe genera, which were known to have multiple roles, were categorized according to their relationship with honeybees. For instance, bacteria in the genus Lactobacilluscould bepresent innectar,butsomespeciesofthisgenusareconsideredubiquitous inhoneybeeguts,andthusweclassifiedLactobacillusasabeegut microbe (Raymann & Moran, 2018; Vannette, 2020). When the functionalattributeofagenuswasuncertain,thenthegenuswas classifiedasunknown. 2.8 | Statistical modeling To examine the strength and patterns of seasonal imprints on honeybee associations and to compare them to the impacts of thebeekeeper,thesite,thehive,andthesampleitself,weapplied the joint species distribution modeling framework of Hierarchical Modeling of Species Communities (HMSC; Ovaskainen & Abrego,2020). Toaccountforthezero-inflatednatureofthedata,weapplied a hurdle modeling approach, modeling presence–absence with probit regression and abundance conditional on presence using a log-normalmodel.Asresponsedata,weusedamatrixofpresence– absencesofallgenerainthepresence–absencemodelsandthematrixoflog-transformedRRA'sinmodelsofabundanceconditionalon presence(henceforthreferredtoasabundancemodels).Sincetaxa withaparticularlyloworhighprevalencecontainlittleinformation onthefactorsaffectingtheiroccurrence,weexcludedgenerathat werepresentinlessthan5%ofthesamplesfrombothmodels.We notethatwhilepresence–absencesandabundancesweremodeled separately, these two models were used simultaneously to make predictions(seebelow). Theexplanatorypartofthemodelswasidentical,asfollows: As fixed effects, we included the sampling period (a categorical variable with three levels) and the log-transformed number ofreadspersample.Thevariableoflog-transformednumberof readsaccountsfortechnicalvariationinsequencingdepthamong samples.Namely,thisvariableismeanttocapturetheeffectof varying sampling effort among samples due to variation in sequencingdepth.Toaccountforthestructureofthestudydesign, weincludedasexplanatoryrandomeffectsthesite(n = 30),the hive(n = 41),thebeekeeper(n = 14),andthesample(n = 115),of whichthesitewasdefinedasaspatiallyexpliciteffect.Wenote thatthesample-levelrandomeffectwasincludednotnecessarily to account for the spatial structure of the data but to estimate the speciestospecies association networks through latent variable modeling(Ovaskainen etal.,2016).Totestwhetherdifferent taxonomic groups respond differently to sampling time, we includedbroadtaxonomic(plants,bacteria,fungi,andviruses)and functionalgroups(describedabove)asgenus-leveltraitvariables. The models were fitted with the R-package Hmsc (Tikhonov et al., 2020),assumingthedefaultpriordistributions(seeOvaskainen&Abrego,2020,pp.184–216).WesampledtheposteriordistributionwithfourMarkovChainMonteCarlo(MCMC)chains,each ofwhichwasrunfor375,000iterations,ofwhichthefirst125,000 wereremovedasburn-in.Thechainswerethinnedby1000toyield 250 posterior samples per chain and 1000 posterior samples in total. We examined MCMC convergence as a function of the potentialscalereductionfactors(Gelman&Rubin,1992)ofthemodel parameters. The explanatory and predictive powers of the presence– absence models were examined through the metrics of Tjur's R2 (Tjur, 2009) and the Area Under the Curve(AUC;Fielding& Bell, 1997). For the abundance models, we used the R2ofthe linear model(Ovaskainen & Abrego, 2020). Tocompute explanatorypower,wemademodelpredictionsbasedonmodelsfitted toallthedata.Tocomputepredictivepower,weperformedtwofoldcross-validation,inwhichthesubstrateunitswereassigned randomlytotwofolds,andpredictionsforeachfoldwerebased 20457758, 2023, 10, Downloaded from https://onlinelibrary.wiley.com/doi/10.1002/ece3.10580 by University Of Jyväskylä Library, Wiley Online Library on [12/10/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
| 7 of 16 WIRTA et al. onamodelfittedtothedataontheotherfold.Toquantifywhat portionoftheexplained variance wasattributedtoeach of the explanatoryfactorsincludedinthemodels,weappliedavariance partitionapproach.Wethenusedthefittedmodelstobuildpredictionsontheresponsesofthegeneratotheseason.Todoso, weusedthefixedeffectpartofthemodelonlyandpredictedfor eachgenusitsoccurrenceprobabilityforeachofthethreetime points.Werepeatedthepredictionforthe1000samplesofthe posterior distribution to compute the posterior probability by whichthegenushadahigheroccurrenceprobabilityinlateseason(August)thanearlyseason(June).Wefurtherconvertedthe genusresponsestotheseasontoatemporalco-occurrencematrix 𝛀 ,withtheelementcorrespondingtogenuspair( j1,j2 )computed as Ω j 1 ,j 2 =𝛽 T2,j 1𝛽 T2,j 2 +𝛽 T3,j 1𝛽 T3,j 2 , where 𝛽T2,j and 𝛽T3,j are the genus responsestotimepointsT2(July)andT3(August),withtimepoint T1(June)beingsetasthereferencelevel.Toexaminethelevelof statisticalsupportbywhicha givengenuspair co-occursatthe sametime,wecomputedtheposteriordistributionof 𝛀 and then evaluated the posterior probabilities by which each matrix elementwaspositiveornegative. 3 | RESULTS Overall,wedetectedatotalof49plantgenera,45bacterialgenera, 23 fungal genera, and three viral genus-level groups with a mean relativereadabundance(RRA)exceeding0.01%.Theproportionsof readsassignedtodifferentkingdoms(plants,bacteria,fungi,andviruses)variedconsiderablybetweensamples(Figure S2).Persample, theaverageproportionsofplants,bacteria,fungi,andviruseswere 51%,38%,7%,and3%,respectively. 3.1 | Model fit statistics The fittedjoint species distribution models showed high explanatory power both for the presence–absence (Tjur's R2 = 0.42 and AUC = 0.93) and abundance conditional on presence (R2 = 0.64) models(Table 1 and Figure 2a).Nonetheless,theexplanatorypower variedwidelyamonggeneraaswellasamongtaxonomicandfunctional groups. Among taxonomic groups, the explanatory power washighest forfungi,explaining65%and91%ofthevariationin thepresence–absenceandabundancemodels,respectively.Among functionalgroups,animal pathogens reachedthehighestexplanatorypower,explaining69%and92%ofthevariation. Thepredictivepowerwasfarlowerthantheexplanatorypower forboththepresence–absence(Tjur'sR2 = 0.11andAUC = 0.63)and abundance models (R2 = 0.02). However, this result seems attributabletothefactthatthesamplingunit-levelrandomeffects(i.e., samplelevel)accountedforalargepartoftheexplainedvariation (22.3% for the presence–absencemodel and 22.6%for the abundancemodel).Theserandomeffectswillcontributetotheexplanatorypowerbutnottothepredictivepowerofthemodels. 3.2 | Seasonal effects on the interactions of honeybees A variance partitioning among the fixed and random effects showedthattheseasonalimprintexplained,onaverage,3.2%of therawvarianceinthepresence–absencesand7.4%intheabundancesofthetaxa.Thestrengthoftheimprintofthebeekeeper, hive, and site on the occurrences of the interactions of honeybeeswassimilartothatoftimeoftheseason(withthebeekeeper, hive,andsiteexplaining3.2%,2.3%,and4.0%ofthevariance,respectively).However,thehivehadastrongereffectontheabundancesofthetaxahoneybeesinteractwith,explaining14.2%of the variance. Theproportionofvarianceattributedtothetimeoftheseason variedgreatlyamongtaxaandamongbothtaxonomicandfunctional groups (Table 1 and Figure 2). Among taxonomic groups, viruseswerethemostinfluencedandfungitheleastinfluenced bythetimeoftheseason(bothintermsofpresence–absenceand abundance). Among functional groups, the no-nectar-producing planttaxawere the most influenced bythe time of the season. Theamountofvariationexplainedbythetimeoftheseasonvariednotonlyamongtaxonomicandfunctionalgroupsbutwithin groups as well (Figure 2). The occurrences and abundances of sometaxawerewellexplainedbythetimeoftheseason,whereas the occurrences and abundances of other taxa were totally unaffectedbythetimeoftheseason.Asexamples,theoccurrence ofsomeplantswasstronglyimpactedbythetimeoftheseason. ForChamaenerion,samplingtimeaccountedfor11.1%ofthevariationinthepresence–absencemodel,whileforLactuca,thetime oftheseasonaccountedforonly0.7%ofthevariation(Table S2). Intermsofabundances,Taraxacumwasthegenusmostimpacted by the time of the year (with time accounting for 31.6% of the variation), while Medigaco and Cicerfellattheoppositeextreme (withtimeaccountingfor1.0%ofvarianceexplained;Table S3). Inregardtomicrobes,thetimeoftheseasonimpactedtheoccurrencesofthetwoviralgroupsthemost(accountingfor8.3%and 10.0%oftheirvariationforthepresence–absencemodel),while thetimeoftheseasonhadtheleastimpactonthefungalgenus Histoplasma (accounting for 0.5% of its variation; Table S2). For theabundances,thetimeoftheseasonhadastrongimpactonthe bacterialgenusAcinetobacter(accountingfor22.4%ofthevariation),whilethebacterialgeneraPantoea and Pectobacterium were theleastimpactedbytime(accountingfor1.2%and1.5%ofvariation, respectively; Figure 2 and Table S3). Furthermore, the temporal patterns of honeybee interactions withdifferentplantgeneradifferedstronglyamonghives.Somebee colonies,thatis,honeybeesfromparticularhives,usedasimilarset ofplantgenerathroughoutthesummer,withonlygradualchangesin theirrelativeproportions(TextS2).Othercoloniesshiftedstrongly to a particular plant genus, such as Brassica,fromonetimepointto theother(Figure S3).Theoccurrencesandrelativeabundancesof microbes differed greatly among colonies and across time points (Figure S4).Curiously,forsomecoloniesandsamples,themicrobe 20457758, 2023, 10, Downloaded from https://onlinelibrary.wiley.com/doi/10.1002/ece3.10580 by University Of Jyväskylä Library, Wiley Online Library on [12/10/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
8 of 16 | WIRTA et al. TABLE 1 Meanpercentagesofvarianceexplainedbythefixedandrandomeffectsincludedinthemodels,andtheirsummedtotalexplanatorypowerquantifiedbyTjurR2forthepresence– absencemodelandR2fortheabundanceconditionalonpresencemodel. Taxonomic groups Functional groups Total Plants Bacteria Fungi Viruses Nectar producing No nectar producing Bee gut Beehive Bee pathogens Plant pathogens Neutral or positive Animal pathogens Presence– absence Time 3.2 3.9 3.1 1.4 9.2 3.3 7.3 3.3 3.9 3.5 2.2 2.2 2.0 Total_reads 2.9 2.1 4.2 2.1 0.9 1.8 4.0 2.8 3.3 3.6 3.5 2.3 4.2 Random:sample 26.3 15.8 21.0 58.0 14.7 16.0 14.2 11.6 26.9 29.6 46.2 26.1 61.1 Random:site 4.0 7.8 1.7 1.0 0.6 8.0 6.8 1.5 1.3 4.1 0.7 0.9 0.9 Random:hive 2.3 3.0 2.4 0.9 1.5 2.7 4.7 3.9 2.3 1.9 0.7 2.3 0.6 Random:beekeeper 3.2 2.6 4.8 1.5 0.8 2.8 2.0 2.3 5.9 2.9 0.7 21.1 0.5 Explanatorypower Tjur R2 42 35 37 65 28 35 39 25 44 46 54 55 69 Abundance conditional on presence Time 7.4 7.7 5.4 9.8 15.7 8.0 6.0 5.4 2.8 7.7 8.7 7.5 7.0 Total_reads 3.7 2.7 3.4 6.3 3.4 2.8 2.3 2.7 1.3 3.6 5.8 1.5 5.0 Random:sample 22.6 20.4 33.2 8.0 5.5 23.4 2.2 16.3 60.7 16.6 27.6 28.0 38.5 Random:site 5.3 4.8 5.0 7.0 4.0 5.0 3.5 4.8 2.5 6.7 5.4 6.5 4.8 Random:hive 14.2 3.8 5.7 55.1 4.4 4.1 2.3 5.2 3.2 21.1 32.7 13.9 33.4 Random:beekeeper 8.1 10.3 7.2 5.2 2.5 10.6 8.3 7.2 1.7 7.7 4.8 14.9 2.8 ExplanatorypowerR261 50 60 91 36 54 25 42 72 64 85 72 92 Note:Oneachrowwereporttheaveragevaluesoverallthetaxamodeled(column“total”)andperindividualtaxonomicandfunctionalgroup(allothercolumns). 20457758, 2023, 10, Downloaded from https://onlinelibrary.wiley.com/doi/10.1002/ece3.10580 by University Of Jyväskylä Library, Wiley Online Library on [12/10/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
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