Posted on Authorea 3 Apr 2020 | CC BY 4.0 | https://doi.org/10.22541/au.158592546.63181639 | This a preprint and has not been peer reviewed. Data may be preliminary. 99 n opooia dpain oteciaei hc hylv My 96 nilta 2009). Angilletta, 1976; (May, live fundamental May, they maintain 1980; which 1989). in Corbet, to Kingsolver, climate basking; and & the or to active wing-whirring Huey adaptations be (e.g. 2009; morphological behavioural and to (Angilletta, several 1979) environment reproduction evolved process- have and their ectotherms a Ectothermic growth from Therefore, ambient 2007). to including the energy al., with et approach processes, thermal Violle species straightforward physiological 2004; a absorb Robinson, of A 2009; & physiology must Gaston, Kembel, the (Chown, species link occurs & 2004). species that Fine, the traits Ricklefs, which Kozak, functional in investigate environment 2006; Cavender-Bares, to within Westoby, 1987; is is & understanding Maurer, assemblages based & of Weiher, (Brown composition Enquist, the research and McGill, ecological distributions of species’ centre shape the that processes the Understanding assemblages, local INTRODUCTION | hypothesis, hypothesis 1 habitat-stability-dispersal melanism thermal insects, adaptation, thermal freshwater Odonata, macrophysiology, dispersal, rule, Bergmann’s trait-based into KEYWORDS highlight species also of responses. ability assemblages biological dispersal climate-driven to lotic the of species and of understanding lentic lentic proxies our enable with between improving to mechanisms adaptations differences for seems thermal These documented ability of models, interactions The dispersal importance. integrating higher of general changes. but underlying importance their climatic species, mechanism the historical indicating lotic the with and assemblages, that lentic better local show for cope to results significance scale Our evolutionary equal variations stronger 4. of were size were but body autocorrelation. types phylogenetic and habitat for both lightness of accounting colour the of assemblages when in lightness for relationships assemblages important Trait-environment colour lentic equally The temperature. were in increasing strength 3. component with and predicted autocorrelation. decreased importance phylogenetic phylogenetic size relative and and their body average precipitation spatial and in and increased differences for temperature odonates assessed accounting effects of and while assemblages for assemblages assemblages, tested local 99 assemblages lotic we of of local and volume dataset, volume 518 lentic body explicit for between body and spatially data and lightness survey yet lightness trait- colour continent-wide with colour the these this information the on trait on dispersal whether quantified of these We Based greater assess predictions combined their 2. Europe. also and the to across We (Odonata) habitats. due whether damselflies (lotic) habitats, test and (lentic) stable assemblages. We stable dragon- to local less European adapted unexplored. to for those adapted largely to hold species remains compared rule for propensity dispersal important Bergmann’s by more the are modified and relationships assemblages be environment hypothesis local strongly can to melanism variations they scale thermal size relationships which the body trait-environment to these and extent whether lightness the but colour and ectotherms, temperature-driven in that patterns suggested biogeographical studies influence macrophysiological Previous 1. Abstract 2020 28, April 1 Lamptey - Acquah Daniel by modified are but dispersal Odonata for propensity European of scale assemblages variation local size to body and lightness colour Temperature-driven Philipps-Universit¨at Marburg 1 atnBraendle Martin , 1 1 oadBrandl Roland , 1 n tfnPinkert Stefan and , 1 Posted on Authorea 3 Apr 2020 | CC BY 4.0 | https://doi.org/10.22541/au.158592546.63181639 | This a preprint and has not been peer reviewed. Data may be preliminary. is eldsrbtoa ags(ulet&Jt,20;Mrw isn ez 07.Scn,teinherent the Second, 2017). Jetz, spe- & overestimate Wilson, of to Merow, estimations tends 2007; robust information Jetz, allow & distribution to (Hurlbert underlying considered ranges the generally distributional species, First, real are of limitations. cies’ maps range important 2017). range environmental three Pinkert, Brandl, full expert has & (e.g., the thermoregulation scales Brunzel, habitats size-based geographical Zeuss, and suitable 2014; at expert colour- Brunzel, on across although of & based Br¨andle, records evidence are Rahbek, Brandl, so previous species occurrence Zeuss, conducted ectothermic Hence, species 2017; in studies Zeuss, size interpolating the & body of by Brandl, and all generated lightness almost colour determining maps However, of in 2000). variation range role physiological interspecific Blackburn, important the fundamental & an on play the (Gaston far thereof influence niche consequences are fundamental traits the patterns macrophy- functional species’ whereas diversity These as a populations large-scale 2004). and organisation, for individuals al., biological explanations of the et of rates that levels (Chown assumption lower patterns approach the at biodiversity powerful on found shape a based offer that are traits inferences processes physiological siological general in can variation the interspecific dispersal elucidate of theoretical extent to patterns strong what large-scale to despite the However, patterns, of past. the biogeographical Analyses unexplored. on the to largely ability in due remains dispersal changes habitats relationships species’ climatic climates. trait-environment lotic of with temperate modify than impact cope in lentic an to diverse of for former disproportionally reasons odonates the other are ma- in Odonata of all 2008) the ability relationships almost lotic constitute al., greater trait-environment to and that et contrast stronger 2003) lentic (Kalkman in suggests Rehn, in globally of Thus, This Libellulidae; species richness highest 2008). and lentic al., the is (Coenagrionidae et of for animals families (Kalkman jority lotic lentic youngest reported scale of two of been global richness the richness a has the Odonata, on the pattern that damselflies) whereas showed similar and Europe, (2010) broadly (dragonflies al. northern A et to Europe. Dehling southern central instance, from For to habi- decreases led 2008). (Abell´an, lotic Ribera, have animals Mill´an, Brandl, groups and differences & two Br¨andle, & these lentic the Moreover, Hof, to between 2016). 2009; patterns Ware, adapted diversification & species and Gottsberger, adaptations between biogeographical (Letsch, behavioural differences contrasting signal phylogenetic ecological as a the well carry that as tats shown 2018) climatic have al., studies with Recent et cope Br¨andle, & to Pinkert Hof, 2012; syndromes) 2006; al., trait Brandl, 1980). et (i.e., Br¨andle, & (Corbet, (Arribas adaptations Marten, mobility adapted to of facilitate the Species 2006; back suite that therein). throughout Brandl, sources adaptations water date a and morphological evolved carry and 1995 including that therefore ephemeral (Bohle, changes, waters) have Mesozoic are (lotic waters the lakes) streams lentic since and and to unaltered rivers ditches largely of remained (e.g., have an locations bodies year 1977). provide the (Southwood, water Freshwaters whereas hypothesis” lentic 1977). Pleistocene, of “habitat-stability-dispersal hemisphere, (Southwood, the this stability of habitats northern the predictions lower stable the to the have less In test habitats related to stable to are system temporally the adapted model and disperse live, The species ideal spatially can ability. to to than it dispersal restricted propensities abilities which its species and in dispersal on general, abilities climate In depends habitats. the niche species’ respective environmental determine in their potential should ratio differences the species volume realises important a to species of most area that size surface which body lower to and Pell, a extent lightness as & colour conditions, Reeson, the 1981). dry Cotter, While Remmert, under bodies Bl¨uthgen, Wilson, 2017; advantageous & smaller 1969; is (K¨uhsel, Heethoff, than Br¨uckner, loss size Rapoport, Schmelzle, efficiently water of rule, body more by reduces reduction larger (Gloger’s heat pathogens, a a cells against retain implies and of resistance to size 2001) integrity increases able body structural melanisation al., are in the greater et of increase bodies thermoregulation, (Clusella-Trullas enhancing an absorption larger Besides melanism since ratio, the thermal hand, 2012). volume determines as other & (Shelomi, to cuticle the Wyk, to area the van On referred surface (Clusella-Trullas, of mechanism 1941). the organism melanisation a Kalmus, 2 Posted on Authorea 3 Apr 2020 — CC BY 4.0 — https://doi.org/10.22541/au.158592546.63181639 — This a preprint and has not been peer reviewed. Data may be preliminary. inl(es ta.21;Ltc ta. 06 ikr ta. 07.Bsdo eetpyoeyo the of phylogeny recent a on Based comparative lightness 2017). 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Data may be preliminary. e fooae cosErp smil rvnb eprtr.I iewt h rdcin ftethermal the of predictions the with line In temperature. by rule assembla- driven of Bergman’s volume) mainly (i.e., and is size hypothesis Europe body melanism and across lightness colour odonates in of variation and spatial ges lightness the 2). that (Table colour demonstrate assemblages results in lotic Our variation to the compared of lentic as in part average stronger between species-specific the 4 mostly strength with the their were variables in of climate similar climate to responses were of traits size contrast, relationships the body By all in variation of groups. the two slopes of mean part the the predicted size, annual phylogenetically body the only to as of were well annual similarly response 5 to one responded responses and models). for were regression lentic mostly assemblages Except single lotic for groups in for significant significant S4 two only only Table were The were (see that precipitation 6 relationships 2). of autocorrelation), the assemblages, (Table spatial all slopes lotic and assemblages and the temperature and phylogenetic lotic as lentic for for both well corrected 24 significant for traits, as the significant two Among precipitation, were assemblages. the annual lotic 6 of and and (models lentic temperature relationships between differed considered mean relationships, annual trait-environment considered of the importance relative The asaerbs oped-elctoso oocrecsadteihrn egahclsrcue fspecies of range structures expert geographical on inherent based the studies and of co-occurrences findings of the pseudo-replications that to show robust odonates rule are European Bergmann’s by maps for support purely data findings our survey can 2017), explicit based al., explained spatially et temperature are Zeuss Despite (c.f. studies 2017). size al., demonstrated macroecological lato body et in been (Hawkins most variance traits low has which recently species’ comparatively it on of have a patterns as scales information geographical studies, different in distribution result assemblage-level at of chance large-scale obtained type of results the reliability the small that the at in European conducted about contradictions in studies Even in debate These rule temperature. especially Bergmann’s motivated scales. 2012), for increasing (Shelomi, taxonomic support with equivocal and found generally decreased (2017) is spatial insects al. odonates in et of support Zeuss rule its assemblages by Bergmann’s odonates, study of of al., macroecological size organisms recent et predictions ectothermic a body Zeuss the though in average 2018; with importance the al., consistent fundamental et that Furthermore, of Xing found scales. mechanism 2019; other a and al., is of regions et melanism Stelbrink assemblages across thermal 2015; for that Beierkuhnlein, reported confirm 2008; & Schweiger Chown, lightness 2014), & lightness 2018; survey colour Blackburn, al., colour Terblanche, on in (Clusella-Trullas, et based the scales patterns Heidrich analyses that geographical regions our geographical large found warm at of similar we organisms in results hypothesis, the ectothermic ectotherms The this with lighter temperature. of together and increasing support with gain, data In increased heat assemblages radiation. colour-based Odonata solar of are of more because ectotherms and reflect darker regions dragon- they hypothesis, cool of melanism because in composition thermal advantage the the influence an to and thermoregulation According at in lightness Europe. involved ability. across colour traits dispersal/recolonisation assemblages of that damselfly low drivers showed and climatic clearly high of study the size-based with assemblages Our of and species physio- lotic importance between colour- the and relative considerably of vary lentic and with importance size of strength size overall body the relationships the body trait-environment that to and revealed the addition lightness odonates of In colour comparison species. of evidence our ectotherm 2007) links and thermoregulation, of al., mechanistic 2017) distribution et 2014, Clusella-Trullas of and al., in importance logy et reviewed general Zeuss 2010; Tsubaki, 2017; assessment the & al., explicit indicating Samejima et spatially 1991; (Pinkert yet May, macroecological continent-wide (e.g. previous Our experimental and reconciles dragon- regions. of relationships cooler species these smaller in of and assemblages coloured to lighter average, compared on damselflies of, composed consistently were regions warmer see 1, (Table volume body in variation the of % 4 and % 3.2 models). 2 regression between single and for lightness S3 Table colour in variation the | DISCUSSION | nErpa dnts u upr o ohtetemlmlns yohssadBrmn’ ueusing rule Bergmann’s and hypothesis melanism thermal the both for support Our odonates. 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Data may be preliminary. ag-cl tde Pnete l,21;Sebike l,21;Zuse l,21) lhuhsuishave studies Although 2014). al., et several Zeuss by 2019; supported the al., strongly supports et generally finding Stelbrink been This have 2017; wet. which and al., warm 2001), et both al., (Pinkert are et studies that (Wilson large-scale regions rule in Gloger’s adaptation larger of an significantly as (K predictions lower size were surface of body habitats regions to body lotic points in the which to assemblages through regions, lotic humid size- loss that in higher water found those a to than we smaller Specifically, of average of advantage trait. constrain on additional also this volume were that precipitation via an annual body 2010), have thermoregulate Nentwig, to to and and & ability Brandl, seem lightness temperature Bacher, their species Schmidt-Entling, colour mean that lentic (Entling, these tolerance the not annual show desiccation of but in based results both lotic, patterns patterns our Although odonates, geographical geographical of assemblages. temperature, the overall assemblages lotic with shaping the drove and in size in consistently differences lentic precipitation precipitation body the between versus and Besides temperature differs based lightness 2018). of traits size Zeuss, colour importance & and of Pinkert relative colour- relationships variation also the that (see the the Odonata suggested most niche of of whereas temperature tropical climates, al., part strengths by colder initial to et driven predicted their adaptation the Pinkert strongly retained phylogenetically in with is role lineages 2014, that central differences size a al., finding played have these body et our might thermoregulation and associated (Zeuss Therefore, lightness and lineages 2019). colour tropical families al., in in butterfly et a differences thermoregulation between Stelbrink as documented well colour-based 2017, have melanism as simple importance studies assemblages thermal (a recent butterfly lower of scale and Furthermore, a global odonates 2008). importance Latitudinal of the al., 2018). lightness the at colour et al., and odonates in the Kalkman for et continent in lineages; shown signal (Pinkert the phylogenetic of been temperature strong of diversity have diversity contemporary richness north-east in the phylogenetic genus the for persist the the or by proxy and to that family driven colonise south-west decreasing found mainly to we of the was study, gradients ability from recent pattern the decreased a are this acquired In assemblages odonates that in lineages 295). that Odonata the few differences p. hypothesised European favours a documented 1916 been of melanism only Tillyard, long the that (e.g., has thermal 1998), It regions and that Sternberg, climates. temperate origin suggest (Abell´an temperate 2018; evolutionary species in damselflies al., tropical odonates lotic and of et of and Pinkert dragon- lineages lentic of 2008; on of colonisation al., studies relationships et phylogeographical trait-environment Kalkman and the 2009; zoogeographical al., time previous et evolutionary of over responding light species. species species lotic that In lotic lentic than suggest and with changes results lentic relationships, climatic Our trait-environment for recent lineages. modified to importance lentic dispersal/recolonisation responses stronger high by similar historical higher evolution and of that from size success are but only body distributional scales, body-size not and the result and colour fact, adaptive to colour In an seem adaptive 2018). from regions al., also temperate et but and in Pinkert ability cause historical species over 2008; to lentic habitats al., hypothesised of lotic et been diversity and (Hof have lentic colour- scales to may Accordingly, time adapted ability 2018). evolutionary species al., reco- dispersal between recently et with high patterns in Pinkert equilibrium with biogeographical dominate Europe; an contrasting should together of to hence thermoregulation parts closer and northern size-based 2018) be glaciated and al., to formerly et assumed (e.g., Pinkert propen- are regions 2010; dispersal Br lonised habitats al., and lentic et persistence & habitat (Dehling to Brandl, between temperature adapted relationship Dehling, ambient the Species suggested negative phy- Hof, of have the 1962). the Grewe, to relationships studies (Southwood, due of Several whereas (e.g. sity 2006) assemblages. responses climate, al., dispersers lentic similar et to stronger in Marten of species are 2006; stronger result lotic mostly species the and were lentic lentic is traits that the of this of traits that part and showed the species-specific lightness decomposing of size However, colour part assemblages. body average of lotic predicted and of and importance logenetically lightness lentic relationships relative between colour the strong the of in equally he ta. 07.Frhroe esoe htseisadapted species that showed we Furthermore, 2017). al., et uhsel ¨ 6 nl,21;Hfe al., et Hof 2013; ¨ andle, Posted on Authorea 3 Apr 2020 — CC BY 4.0 — https://doi.org/10.22541/au.158592546.63181639 — This a preprint and has not been peer reviewed. Data may be preliminary. re,J . iln .M,Hgr .J,Pte,M . ute,B 21) rtrat ne lo- infer to and constraints Criteria avifauna. energetic of American (2015). Effects North B. assemblages: the species of Luttbeg, https://doi.org/10.1086/284694 of diversification Evolution 1-17. the & (1987). on A. A., dynamics B. species Maurer, M. & Patten, H., J. J., Brown, surveys. B. dragonfly adult Hager, standardized M., in ps://doi.org/10.1086/682668 A. residency Dillon, species cal T., J. Bried, (1995). W. H. 1.1-7). Bohle, version package https://cran.r-project.org/package=ncf R (Version at: Functions Covariance Available Nonparametric from Spatial Retrieved ncf: (2016). N. O. Bjornstad, water lotic and lentic between size 2699.2011.02641.x range in differences Hydrophilidae). drives (Coleoptera: tolerance (2012). beetles ecological T. than D. rather Bilton, ability Dispersal . . Abell´an, S´anchez-Fern´andez, . P., P., J., Velasco, Calosi, And´ujar, P., C., D., Arribas, Press. University Oxford (2009). beetles. J. phylogeographical water M. the saline Angilletta, in Mediterranean differences of habitat-driven lineages https://doi.org/10.1111/j.1365-294X.2009.04319.x Parallel independent 3885-3902. (2009). two I. of Ribera, structure & Mill´an, A., Abell´an, P., Ghana REFERENCES of Service. Government Exchange the Academic by German funding the PhD acknowledges and Lamptey - Acquah Daniel Repository. Digital Dryad with study of this ACKNOWLEDGEMENTS history for climatic data the archive to with intend combination changes. We in climatic lentic historical former for with the cope importance of STATEMENT AVAILABILITY better evolutionary DATA ability them similar allowed dispersal of have contributions greater to be relative a scatter seem to the but Europe the seem in species explaining differences adaptations pro- lotic to to thermal dispersal as contributes and Thus, species’ well habitats predictors. in as their climatic difference relationships that of of trait-environment indicate stability considered results spatio-temporal the thermoregulation our the around in species, involved in number odonate traits embedded for a of of rule of pensities distribution role Bergmann’s results crucial the and the the shaping melanism with highlighting thermal together in geographical of besides findings the However, importance our influence organisms. general of to the consistency ectothermic seemed underlines The lightness extent. analyses assemblages colour some macroecological and of to of size composition traits body the both and of of shaping Colour- functions patterns mechanisms (Odonata). other dominant damselflies although the and tempe- odonates, the far dragon- of with by of size were patterns body biogeographical and thermoregulation lightness the size-based colour shapes of links which mechanistic regime the rature of importance the highlights in study variations Our the of or driver humid important extreme an include not 5 not was did assemblages. precipitation sites Odonata annual study European study the lightness our water of colour in against gradient secondly, protection environmental and colour-based potential the regions Parkash, firstly, a dry 2008; interpreting reasons; Ramniwas, about two & cautious for are Rajpurohit loss we (Parkash, 2009), resistance Kalra, & desiccation Sharma impacts melanisation that shown | CONCLUSION Spezielle hra dpain hoeia n miia Synthesis Empirical and Theoretical A Adaptation: Thermal klge insh Systeme Limnische Okologie: ¨ ora fBiogeography of Journal 7 95,9494 https://doi.org/10.1111/j.1365- 984-994. 39(5), , elnua:Springer. u.a.: Berlin . rswtrScience Freshwater h mrcnNaturalist American The oeua Ecology Molecular 43,10-13 htt- 1105-1113. 34(3), , - iityo Education of Ministry xod e York: New Oxford, . 18(18), , 130(1), , Posted on Authorea 3 Apr 2020 — CC BY 4.0 — https://doi.org/10.22541/au.158592546.63181639 — This a preprint and has not been peer reviewed. 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(1/2), no Ooaa S i (Odonata) ¨ andor Odonatologica 12 oaohoaarctica Somatochlora sebwruguddrbioindikation. der und ¨ asserbewertung ,13-29. 5, , 82,5-1 https://doi.org/10.17951/c.2013.68.2.57. 57-71. 68(2), milj , pigmhscecilia Ophiogomphus nximperator Anax rushegrntrudiceSchrriften, naturkundlische Braunschweiger -och. ¨ o- 93,217-224. 39(3), , 7 9-0.https://doi.org/10.1002/rrr.664 493-507. 17, , ¨ odert ce raumes. ucker ¨ lekmu nlsa ett av analys – kommun ¨ alje ET ndrS der in ZETT) ec nenmHcmo in Hochmoor einem in Leach Fuco,1785). (Fourcroy, nae eLimnologie de Annales 2 23-29. 32, , Libellula oua odona- Notulae ded (Nie- udheide ¨ Denisia 5(3/4), , Annales 3, , Posted on Authorea 3 Apr 2020 — CC BY 4.0 — https://doi.org/10.22541/au.158592546.63181639 — This a preprint and has not been peer reviewed. Data may be preliminary. uie,D,Vno . ilvs,M,&Mke,J .(02.Cnrbto otekoldeo h Odonata the of 2012. knowledge ECOO the the to of Contribution Results (2012). – J. Herzegovina J. 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D., Kitanova, Holderegger, & R., Home, Helvetica C., Forrer, mercuriale in I., enagrion Gomphidae) Seidl, D., (Odonata: Gomphidae Keller, of frequency occurrence Gauja. and river distribution Latvia. The of Kalni¸nˇs, fauna (2006). the M. in species dragonfly new Darter Romania. Banded in Kalni¸nˇs, (2002). surroundings M. its and 129-145. (Some¸s) river 7(3/4), Szamos the of Szeged. H in fauna Tisza odonate river the the odonatologicae of On Notulae reach (2000). the on A. behaviour data Huber, emergence exuviae the on and based Gomphidae) larvae (Odonata: (Steier- their Feldes dragonflies of riverine Leibnitzer of des Assessment Laßnitzauen (2012). und Horv´ath G. Sulm- Mur-, der Libellenfauna Die mark, (1992). Gew E. und W. Libellenfauna Holzinger, zur Untersuchungen (1986). R. flißgew Kull, & H., implications Heidemann, and communities aquatic of dynamics Temporal 0223-9 (2012). conservation. A. 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(2), Osterreich). seni hiln-fl n Baden-W und Rheinland-Pfalz in ¨ assern ¨ ,87-99. 6, , 12,1924 https://doi.org/10.17109/AZH.61.2.189.2015 189-204. 61(2), caUiesttsLatviensis, Universitatis Acta Libellula Ooaa onginde mBipe e mrg-eit Oberaargau. Smaragd-Gebiets des Beispiel am Coenagrionidae) (Odonata: idvriyadConservation and Biodiversity () 69-84. 5(6), , 134,175-180. 11(3/4), , yptu pedemontanum Sympetrum eerho h aua eiaeo iceoD ead n Val and Celarda Di Vincheto of Heritage Natural the on Research 1,17-28. 710, avjsEntomologs Latvijas urttemberg. ¨ 13 13,8982 https://doi.org/10.1007/s10531-011- 829-852. 21(3), , 11831196 Libellula ple clg n niomna Research, Environmental and Ecology Applied auaSloveniae, Natura Aloi 76 Ooaa iellde a – Libellulidae) (Odonata: 1766) (Allioni, 9 50-51. 39, , clgclEngineering Ecological caZooiaAaeieScientiarum Academiae Zoologica Acta (/) 46-62. 5(1/2), , ,101-116. 5, – . auaMneern,Podgorica Montenegrina, Natura se uc Libellen. durch ¨ asser Tiscia ¨ asserg 42,23-38. 14(2), netbaiD n Fo- Una Di Invertebrati t nausgew an ute ¨ 9 9-15. 39, 5 16.htt- 51-61. 55, , Libellula Entomo ¨ ahlten Co- , Posted on Authorea 3 Apr 2020 — CC BY 4.0 — https://doi.org/10.22541/au.158592546.63181639 — This a preprint and has not been peer reviewed. Data may be preliminary. akv . ik,D,&Aadlvc .(02.Fuitcrslsfo h n aknOdonatological (2014). Balkan S. Libellulidae). Hardersen, 2nd & (Odonata: the fauna R., from Italian Moratin, results the P., Faunistic Leo, A., (2012). Rattu, A. Serbia. Arandelovic, 2012, BOOM & – D., Meeting Vinko, surveys. S., delusion: biased Rajkov, dragonfly avoid The to (2011). exuviae J. sample D. Thompson, to https://doi.org/10.1007/s10841-010-9281-7. W., essential D. is Macdonald, P., it Riordan, why damselflies, T., Merckx, the M., E. of Raebel, Emergence (2003). J. Entomology of D. Thompson, anthropogenic tenellum & small riagrion some V., of B. (Odonata) Purse, Dragonflies City. Cracow the (2006). in Kwarci´nska, to M. Finland. bodies & submitted University, water Halmstad thesis B., Wachowicz, the BSc. of Sweden? K., diversity Central Piksa, species UK. in and changing Cambridgeshire, conservation composition fen, Nature dragonfly Wicken of the Department at Is odonata (2011). S. on Persson, patterns management ditch of Conservation Effects Biological 1998. D. Painter, species, Odonata four of mixta Journal status changing Naturalists’ Aeshna and Montenegro.Irish parthenope, Colonization and (2003). Anax R. Albania imperator, Thompson, of Anax & fauna C., Ronayne, Odonata B., the Nelson, to Contribution Matraensis (2013). Musei Naturalia T. Historico Kovacs, & D., Muranyi, floodplain. https://doi.org/10.1023/A:1021220220039 river Hungarian 167-179. a 12, on assemblages dragonfly on activities fisherman Reserve. M Biosphere Berezinskii the Plecoptera, in rivers (Insecta: the insects Review, of Aquatic Trichoptera) Buczy´nski, 2006. and P. & Odonata, K. Ephemeroptera, Lewandowski, Ukraine. S. and Czachorowski, M.D. Belarus Moroz, between currents water cross-border of Review insects Planina). logical Aquatic (Stara (2013). Balkan-Gebirge M.D. Moroz, Bulgarischen dem aus Libellenbeobachtungen Libellula (1990). R. Mauersberger, Gew the angegelegten of neu einem north an wetlands 45-61. Libellen the von Kolonisationserfolg to (1991). reference A. Martens, A special accidentals? with Bulgaria. or Rhodopes, South active Western Smolyan, caves: the of in of town Odonata occurrence (2007). Odonata M. (2013). Marinov, F. G. Ficetola, study. & case E., new M. Siesa, R., Manenti, Alps). Italian of (Eastern occurrence Trentino The 36. (2012). in V. Libellulidae) Lencioni, (Odonata, & M., 1825) Odonata Gobbi, (2013). Italy. M., E., L. central Gaino, A. Umbria, & Macagno, S., of Piersanti, areas M., Rebora, protected E., some Goretti, in A., biodiversity Spezialle, A., Dell’Otto, G., Porta, La le,Z,Jkb . ´t,A,Dea,G,S´las,N,Ks,B,&Hr´t,R 20) ffc fsports of Effect (2003). Horv´ath, R. & B., Kiss, Sz´allassy, N., D´evai, G., T´oth, A., T., Jakab, Z., uller, ¨ 69,9794 https://doi.org/10.1134/S0013873806090028 987-994. 86(9), (/) 43-59. 9(1/2), , 37,8486 https://doi.org/10.1134/S0013873813070099 874-886. 93(7), , 0,9-9 https://doi.org/10.14411/eje.2003.018 93-99. 100, , ora fCv n as Studies Karst and Cave of Journal Ooaa onginde,a hi otenrnemris nBritain. in margins, range northern their at Coenagrionidae), (Odonata: 42,189-195.https://doi.org/10.1016/S0006-3207(97)00095-5 84(2), , 77,266-272. 27(7), , rget Faunistica, Fragmenta auaSloveniae Natura oua Odonatologicae Notulae 7 29-41. 37, , rget entomologica Fragmenta , and 17 53,2529 https://doi.org/10.4311/2012LSC0281 205-209. 75(3), , 92,81-89. 49(2), 14 2,67-76. (2), yptu fonscolombii Sympetrum ilcdslefebvrii Diplacodes () 97-108. 6(9), , Odonatologica ora fIsc Conservation, Insect of Journal td rniid cez Naturali, Scienze di Trentini Studi 612,121-124. 46(1-2), , ecrhnapectoralis Leucorrhinia onginmercuriale Coenagrion 22,125-137 42(2), idvriyadConservation, and Biodiversity nSrii,anwseisfor species new a Sardinia, in nIead2000-2002. Ireland in ¨ asser. Libellula uoenJournal European . Entomological (Charpentier, 4 523-533. 14, 10(1/2), , Entomo- and 2 33- 92, Folia The Ce- Posted on Authorea 3 Apr 2020 — CC BY 4.0 — https://doi.org/10.22541/au.158592546.63181639 — This a preprint and has not been peer reviewed. Data may be preliminary. oeeial rdce ato h epcietatadS-cmoetrpeet h epciedvainof deviation respective the phy- represents the component. component represents - - P component S the - and from P trait trait The respective average the (AP). the of precipitation part annual predicted and ( logenetically and (AMT), relationships temperature temperature Significant z-standardised mean given. with annual odonates are pseudo- (Nagelkerke European weight models of dependency regression assemblages addition, 518 In variables. of precipitation volume body and lightness in ( fish regressions and Dragonflies other? 1 the TABLE shape community one Does (2010). lakes. F. Swedish Suhling, & Sahl´en, Aeshnidae). G. T., (Anisoptera: dragonfly Wittwer, habitats the natural by recognition in site approach province, oviposition experimental Zamora and an Tera, selection Habitat Rio (1992). from H. dragonflies Wilderuth, (VS). protected Bretolet of de Records Col (2006). (Odonata). dem S. Spain Weihrauch, auf & (Odonata) F., Libellen Weihrauch, von Beobachtungen (2015). S. Helvetica Entomo Althaus, & M., Thoma, Corduliidae). (Anisoptera: (Pictet) Sch 41-60. 31(1/2), Mediterranean , a of sahlbergi habitats Somatochlora different in communities Schr dragonfly Larval Grie- (1994). system. Nordost- water F. in running Suhling, Libellenbeobachtungen & (1996). P. K. Schridde, Ullmann, & F., Suhling, chenland. P., Schridde, I., stichprobe. Schnapauff, kleiner beitrag bei Ein Odonaten-Artenspektren (FRG) Garmlsch-Partenkirchen/Obb. von bei analyse Geroldsees des zur Odonatenfauna habi- Zur to (1987). relation E. in Schmidt, Odonata) (Insecta: associations approach. Dragonfly multivariate (2003). a variables: A. Chovanec, tat & C., Fesl, valley. M., Schindler, Rhine of Upper requirements Southern habitat the in the Coenagrionidae) On (1998). F-J. Schiel, species general of bioindicators lakes. as forest (Odonata) boreal dragonflies in of richness Identification (2001). K. Ekestubbe, Sweden. & Sahl´en, central G., M in diversity near dragonfly pools on forestry small Odonatology of very impact of The (1999). fauna Sahl´en, G. dragonfly the on Republic. Notes Federal (1978). R. Rudolph, K˜oszeg-mountains. the in S´elys, 1843) ( Dragonfly L˜okk G., Rozner, Gew einem an Libellenarten mehrerer massenvorkommen 193-198. Ein (1997). K. Reinhardt, te . uln,F 19) ebctne u otflnugvratnvon Fortpflanzungsverhalten zum Beobachtungen (1997). F. Suhling, & C., utte, ¨ tr . cnie,T,Shedr . ajlie,S,&H & S., Karjalainen, E., Schneider, T., Schneider, A., ¨ oter, Libellula odlgse heros Cordulegaster ffc ie zsoe)adteepandvrac fpeitrvralsfo igeadmultiple and single from variables predictor of variance explained the and (z-scores) sizes Effect r () 7-8.https://doi.org/10.1080/13887890.1999.9748128 177-186. 2(2), , netCnevto n Diversity and Conservation Insect 2 / sA,&Ferincz, & A., ¨ os R oe´ nScea Entomol´ogicaBolet´ın Aragonesa Sociedad oua odonatologicae Notulae ,97-109. 8, , 534,169-183. 15(3/4), , 2 fteaeae hlgntcadseisseiccmoet fteaeaecolour average the of components species-specific and phylogenetic average, the of ) dacsi Odonatology in Advances pce trs u orgoa lmt hne Ooaa Corduliidae). (Odonata: change? climate regional to due risk at species a – idvriyadConservation, and Biodiversity hicigr 99 n odnRne rgny( Dragonfly Ringed Golden and 1979) Theischinger, .(00.Peiiaysuiso h itiuino ag odnRinged Golden Large of distribution the on studies Preliminary (2010). A. ´ Libellula Hydrobiologia oi itrc auai ue Matraensis Musei Naturalia Historico Folia , 1 612,81-84. 16(1/2), , 1,1-16. (1), ,89-100. 6, , ,1413 https://doi.org/10.1111/j.1752-4598.2010.00083.x 124-133. 3, , 9,1910 https://doi.org/10.1023/A:1025476220081 169-180. 497, , 15 rtrmanajas Erythromma ausht s Naturschutz p < 05,6360 https://doi.org/10.1023/A:1016681524097 673-690. 10(5), 8 337-338. 38, , .5 r hw nbl.Tepeitr are: predictors The bold. in shown are 0.05) ¨ am Libellula ¨ al ie,M 21) bevtoso adult on Observations (2012). 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