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What is a tree in the mediterranean basin hotspot? A critical analysis

Médail, Frédéric; Monnet, Anne Christine; Pavon, Daniel; Nikolic̈, Toni; Dimopoulos, Panayotis; Bacchetta, Gianluigi; Arroyo Marín, Juan; Barina, Zoltán

Abstract

Background: Tree species represent 20% of the vascular plant species worldwide and they play a crucial role in the global functioning of the biosphere. The Mediterranean Basin is one of the 36 world biodiversity hotspots, and it is estimated that forests covered 82% of the landscape before the first human impacts, thousands of years ago. However, the spatial distribution of the Mediterranean biodiversity is still imperfectly known, and a focus on tree species constitutes a key issue for understanding forest functioning and develop conservation strategies. Methods: We provide the first comprehensive checklist of all native tree taxa (species and subspecies) present in the Mediterranean-European region (from Portugal to Cyprus). We identified some cases of woody species difficult to categorize as trees that we further called “cryptic trees”. We collected the occurrences of tree taxa by “administrative regions”, i.e. country or large island, and by biogeographical provinces. We studied the species-area relationship, and evaluated the conservation issues for threatened taxa following IUCN criteria. Results: We identified 245 tree taxa that included 210 species and 35 subspecies, belonging to 33 families and 64 genera. It included 46 endemic tree taxa (30 species and 16 subspecies), mainly distributed within a single biogeographical unit. The countries with the highest tree richness are Greece (146 taxa), Italy (133), Albania (122), Spain (155), Macedonia (116), and Croatia (110). The species-area relationship clearly discriminated the richest central-eastern (Balkans) and northern (Alpine and Cevenno-Pyrenean) biogeographical provinces, against the five western provinces in the Iberian Peninsula. We identified 44 unrecognized “cryptic trees”, representing 21% of the total trees. Among the 245 taxa identified, 19 are considered to be threatened (15 CR + EN + VU) or near threatened (4 NT) by IUCN. Conclusions: The Mediterranean-European region includes an unsuspectedly high number of tree taxa, almost 200 tree taxa more than in the central European region. This tree diversity is not distributed evenly and culminates in the central-eastern part of the Mediterranean region, whereas some large Tyrrhenian islands shelter several narrow endemic tree taxa. Few taxa are recognized as threatened in the IUCN Red list, and the vulnerability of these species is probably underestimated.

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RESEARCH Open Access Wha is a ee in he Medi e anean Basin ho spo ? A c i ical analysis F édé ic Médail 1* , Anne-Ch is ine Monne 1 , Daniel Pa on 1 , Toni Nikolic 2 , Panayo is Dimopoulos 3 , Gianluigi Bacche a 4 , Juan A oyo 5 , Zol án Ba ina 6 , Ma wan Cheikh Albassa neh 7 , Giannian onio Domina 8 , B uno Fady 9 , Vlado Ma e ski 10 , S ephen Mi sud 11 and Aga he Le iche 1 Abs ac Backg ound: T ee species ep esen 20% o he ascula plan species wo ldwide and hey play a c ucial ole in he global unc ioning o he biosphe e. The Medi e anean Basin is one o he 36 wo ld biodi e si y ho spo s, and i is es ima ed ha o es s co e ed 82% o he landscape be o e he i s human impac s, housands o yea s ago. Howe e , he spa ial dis ibu ion o he Medi e anean biodi e si y is s ill impe ec ly known, and a ocus on ee species cons i u es a key issue o unde s anding o es unc ioning and de elop conse a ion s a egies. Me hods: We p o ide he i s comp ehensi e checklis o all na i e ee axa (species and subspecies) p esen in he Medi e anean-Eu opean egion ( om Po ugal o Cyp us). We iden i ied some cases o woody species di icul o ca ego ize as ees ha we u he called “c yp ic ees”. We collec ed he occu ences o ee axa by “adminis a i e egions”, i.e. coun y o la ge island, and by biogeog aphical p o inces. We s udied he species-a ea ela ionship, and e alua ed he conse a ion issues o h ea ened axa ollowing IUCN c i e ia. Resul s: We iden i ied 245 ee axa ha included 210 species and 35 subspecies, belonging o 33 amilies and 64 gene a. I included 46 endemic ee axa (30 species and 16 subspecies), mainly dis ibu ed wi hin a single biogeog aphical uni . The coun ies wi h he highes ee ichness a e G eece (146 axa), I aly (133), Albania (122), Spain (155), Macedonia (116), and C oa ia (110). The species-a ea ela ionship clea ly disc imina ed he iches cen al-eas e n (Balkans) and no he n (Alpine and Ce enno-Py enean) biogeog aphical p o inces, agains he i e wes e n p o inces in he Ibe ian Peninsula. We iden i ied 44 un ecognized “c yp ic ees”, ep esen ing 21% o he o al ees. Among he 245 axa iden i ied, 19 a e conside ed o be h ea ened (15 CR + EN + VU) o nea h ea ened (4 NT) by IUCN. Conclusions: The Medi e anean-Eu opean egion includes an unsuspec edly high numbe o ee axa, almos 200 ee axa mo e han in he cen al Eu opean egion. This ee di e si y is no dis ibu ed e enly and culmina es in he cen al-eas e n pa o he Medi e anean egion, whe eas some la ge Ty henian islands shel e se e al na ow endemic ee axa. Few axa a e ecognized as h ea ened in he IUCN Red lis , and he ulne abili y o hese species is p obably unde es ima ed. Keywo ds: Plan biogeog aphy, Medi e anean egion, Th ea ened ees, T ee de ini ion, T ee dis ibu ions * Co espondence: [email p o ec ed] 1 Aix Ma seille Uni , A ignon Uni , CNRS, IRD, IMBE. Technopôle de l’A bois-Médi e anée, cedex 4, BP 80, 13 545 Aix-en-P o ence, F ance Full lis o au ho in o ma ion is a ailable a he end o he a icle © The Au ho (s). 2019 Open Access This a icle is dis ibu ed unde he e ms o he C ea i e Commons A ibu ion 4.0 In e na ional License (h p://c ea i ecommons.o g/licenses/by/4.0/), which pe mi s un es ic ed use, dis ibu ion, and ep oduc ion in any medium, p o ided you gi e app op ia e c edi o he o iginal au ho (s) and he sou ce, p o ide a link o he C ea i e Commons license, and indica e i changes we e made. Médail e al. Fo es Ecosys ems (2019) 6:17 h ps://doi.o g/10.1186/s40663-019-0170-6 Backg ound A ecen census o he biomass dis ibu ion on Ea h in- dica es ha plan s, mos ly e es ial species, ep esen abou 80% (i.e. ≈450 G C) o he sum o he biomass ac oss all axa wo ldwide, and ha plan biomass in- cludes abou 70% s ems and ee unks (Ba -On e al. 2018). This esul unde lines he c ucial ole o ees in he global unc ioning o he biosphe e. Wi h ca. 60,000 ee species ep esen ing 20% o he ascula plan spe- cies wo ldwide acco ding o GlobalT eeSea ch (Beech e al. 2017), ees cons i u e a majo componen o he s uc u e and unc ion o o es ecosys ems loca ed in empe a e and opical biomes. Highe le els o ecosys- em se ices, such as biomass p oduc ion, wa e supply, nu ien cycling and soil ca bon s o age, cha ac e ize o es s wi h a highe ee di e si y (Gam eld e al. 2013). Since o es s play a c ucial ole in he conse a- ion o e es ial biodi e si y by p o iding habi a s and ecological niches o a majo i y o plan s and animals (www.global ees.o g), i is necessa y ha assessmen s o he di e en ee axa in ol ed in o he composi ion o ecosys ems should be comp ehensi e and obus by in- cluding a biogeog aphical pe spec i e. Ne e heless, he global knowledge o he numbe and dis ibu ion o ee species emains su p isingly low bo h a he in e na ional le el (Beech e al. 2017) and o la ge biogeog aphic a eas ( egions and p o - inces). While h ea s on he opical o es s u ge he scien is s o ill he gap in knowledge on hei di e si y (Se a-Diaz e al. 2017), he i e Medi e anean eco e- gions (Medi e anean Basin, Cali o nia, cen al Chile, Cape Region o Sou h A ica and sou h-wes e n Aus alia) s ill equi e u he s udies. Wi h only 2% o he wo ld’s e es- ial su ace, Medi e anean eco egions con ain nea ly 20% o he Ea h’s o al plan di e si y, making e y signi ican biodi e si y ho spo s, second only a e opical ones (Cowling e al. 2005). The Medi e anean Basin is one o hese 36 cu en biodi e si y ho spo s wo ldwide (Médail and Mye s 2004), including bo h egional (Médail and Quézel 1997) and local ho spo s, i.e. mi- c o- and nano-ho spo s sensu Cañadas e al. (2014). I is es ima ed ha Medi e anean o es s co e ed 82% o he landscape be o e he beginnings o human impac s on ecosys ems housands o yea s ago (WWF 2001). Bu he whole Medi e anean Basin s ill comp ises a high ee ichness es ima ed o 290 indigenous axa (species and subspecies) including 201 endemics (Quézel and Médail 2003;Médail2008). The spa ial dis ibu ion o his woody plan biodi e si y is s ill impe ec ly known e en in Medi e anean-Eu opean egion. A biogeo- g aphical ocus on ee species dis ibu ion is needed o conse a ion o he Medi e anean o es s which ha e unde gone apid changes in s uc u e and com- posi ion in ecen decades (Mazzoleni e al. 2004), e en i o es su ace emains s able on he global scale (FAO and Plan Bleu 2018). Among he woody di e si y, he de ini ion o a ee pe se migh be p oblema ic and equi es some ag ee- men (e.g. Gschwan ne e al. 2009). This is especially he case o his o ically dis u bed ee species ha o en appea s as sh ubs and display as ue ees only a e a long pe iod wi hou dis u bance o in cul i a ion in ga - dens. This aspec is pa icula ly impo an in he Medi- e anean egion whe e he impac s o na u al and human dis u bances a e bo h e y old and se e e. In his s udy, we p o ide he i s checklis o all ee axa (species and subspecies) p esen in he no he n pa o he Medi e anean eco egion (i.e. he Medi e anean-Eu opean egion), since Medi e anean o es s occu mainly in his a ea (in Eu ope, o es s co e ca. 33% o o al land a ea: see Albe di Asensio e al. 2015) and he a ailable da a a e mo e obus and eadily a ailable he e han in he sou he n and sou h-eas e n Medi e anean. The e o e, he main objec i es o his s udy a e: (i) o examine whe he an ex ensi e su ey o he whole pu a i e ee axa challenge he de ini ion o wha is gene ally conside ed as a Medi e anean ee; (ii) o p o ide a comp ehensi e checklis o ee axa o he Medi e anean-Eu opean egion,i.e. om Po ugal o Cyp us; (iii) o examine he global spa ial dis ibu ion o ee axonomic di e si y (na i es and endemics) a he biogeog aphical and adminis a i e scales. Finally, we compa ed he dis ibu ion o ee di e si y in he Medi e anean-Eu opean egion om p e ious assess- men made in he whole Medi e anean Basin and he Eu opean con inen and discussed he implica ions o conse a ion. Me hods S udy a ea We de ined he Medi e anean-Eu opean egion as he No h Medi e anean e es ial eco egion ollowing he de ini ion o e es ial eco egions o he wo ld om Olson e al. (2001) (Fig. 1). They p o ide a biogeog aphic scheme de ined by exis ing global maps o lo is ic p o inces and by egional maps o uni s based on he dis ibu ion o selec ed g oups o plan s and on pub- lished egional classi ica ion sys ems o e es ial habi- a s. The biogeog aphical limi s o he Medi e anean egion a e simila o hose p oposed by Médail and Quézel (1997), excep o some a eas o he moun ain idge o he I alian peninsula and o he Balkans. Indeed, clima e indices a e no s ic ly ele an o de ine he bio- geog aphical limi s pe se, no ably o he uppe pa s o he Medi e anean moun ains. To al co e ed a ea, including islands, is 1,610,200 km 2 , wi h coas line o app oxima i ely 45,200 km. The o o- g aphic a ia ion in he a ea is la ge, and he al i udes Médail e al. Fo es Ecosys ems (2019) 6:17 Page 2 o 19 ange om 0 m a.s.l. up o 3482 m a.s.l. (Mulhacén, Sie a Ne ada –Spain). The s udy a ea co e s he ollowing coun ies (as admin- is a i e uni s) om wes o eas : Po ugal, Spain, F ance, I aly, Mal a, Slo enia, C oa ia, Mon eneg o, Albania, Macedonia, G eece and Cyp us. La ge Medi e anean islands (in addi ion o Mal a and Cyp us) co esponding o he Balea ic a chipelago, Co sica, Sa dinia, Sicily and C e e, a e ea ed as independen uni s o achie e a be e spa ial esolu ion o ee axa and island speci ici ies. The s udy a ea does no include he non-Eu opean Medi e anean a ea, i.e. No h A ica and Nea Eas . The a ea is cha ac e ized by a Medi e anean clima e ypes ma ked by mild and humid win e s, ho and d y summe s and a ela i e long pe iod o a idi y each yea which impose an e ec i e and se e e d ough on he plan s. Rain all pa e ns and he oceani y a e ex emely a ied, and his explain why he Medi e anean Basin is cha ac e ized by he lowes ain all eliabili y (quan i ied as in e annual a ia ions in mon hly and seasonal ain- alls, and as he equency o indi idual ain alls) o he i e Medi e anean-clima e ecosys ems o he wo ld (Cowling e al. 2005). In gene al, annual ain alls a e g ea e in he no he n han in he sou he n a eas o he Medi e anean Basin and inc ease wi h ele a ion in he moun ain anges. Du ing mois season he ain all can be unp edic able and o en in ense om au umn h ough sp ing. Medi e anean ege a ion ypes a y widely wi h en i - onmen al cons ain s (clima e, geology, geomo phology, soil ype), dominan plan species, and dis u bances in- duced by man and i s he ds. The woody ege a ion is cons i u ed by di e se ypes o ma o als o sh ublands (maquis, ga igue, ph ygana) and o es s. In ela ion o hebioclima e ypeand heal i ude,se e almajo ypeso his ege a ion can be ecognized in he Medi e anean- Eu opean egion (Quézel and Médail 2003; Ri as-Ma ínez e al. 2007; Médail 2008): (i) a he mo-Medi e anean bel om sea le el o ~ 200–500(800) m a.s.l., domina ed by scle ophyllous communi ies mos o en as a na ow s ip along he coas (wi h Olea eu opaea,Ce a onia siliqua, Chamae ops humilis,Pis acia len iscus,Pinus halepen- sis,Pinus b u ia, e c.); (ii) a meso-Medi e anean bel , be ween ~ 100–500(1000) m a.s.l., mainly wi h scle - ophyllous o es s (Que cus ilex,Que cus sube and Q. cocci e a)o Pinus halepensis/P. b u ia o es s in a eas wi h low ain all o o me ly dis u bed by man; (iii) a sup a-Medi e anean bel , be ween ~ 500–1500(1800) m a.s.l., wi h di e se deciduous oaks o es s (including Ace , Ca pinus,Os ya,Que cus and So bus) in he mo e humid omb o ypes; (i ) a moun ain-Medi e anean le el (~ 1500– 2000 m a.s.l.) including Fagus and deciduous and semi-de- ciduous Que cus o es s and no ably coni e ous o es s wi h Pinus nig a, Pinus syl es is and i s (Abies alba and mos o he Medi e anean Abies spp.) and e en ceda (Ced us libani s.l.)onCyp us. An ex emely impo an ea u e o his woody Medi e anean ege a ion is ha i has been d ama ic- ally in luenced by human ac i i ies o housands o yea s (e.g. Thi good 1981; Blondel e al. 2010). Fo es log- ging, i es, g azing, ag icul u e de elopmen , soil dis u - bances, excessi e up ake o wa e o he de imen o ipa ian ees, changes in he dis ibu ion o na i e species due o la ge e o es a ions, a o es a ions, and in oduc ions o alien axa led o massi e landscape ans o ma ions and changes in he s uc u e and dynamics o hese na u al o - es ecosys ems (Quézel and Médail 2003;Blondel2006). Fig. 1 Numbe o na i e ee axa (species o subspecies –including endemic and pu a i e na i e) in each con inen al adminis a i e a ea and main islands in he Medi e anean-Eu opean egion. Da ke g eens indica e highe ichness Médail e al. Fo es Ecosys ems (2019) 6:17 Page 3 o 19 Medi e anean islands a e in his espec o pa icula conce n, due o he highe h ea hey su e , as a com- bina ion o highe ypical sensi i i y o dis u bances, and long his o y o human occupancy (e.g. Médail 2017). Fo his eason, we conside ed la ge islands as sepa a e uni s in ou analysis. T ee de ini ion The IUCN’s Global T ee Specialis G oup (GTSG) de ines a eeas“a woody plan wi h usually a single s em g owing o a heigh o a leas wo me e s, o i mul i-s emmed, hen a leas one e ical s em i e cen ime e s in diame e a b eas heigh ”(Beech e al. 2017). Ou de ini ion is sligh ly di e en and we de ine as ee he plan s wi h he ollowing biological ea u es: (i) seconda y g ow h (Fahn 1990); (ii) pe ennials ( hey li e many yea s, mos ly o de- cades o cen u ies); (iii) ypically (a leas in some en i on- men al condi ions o loca ions) ha ing a single s em o unk, g owing o ho opic wi h monopodial o mo e o en sympodial b anching sys ems, and bea ing la e al b anches a some dis ance om he g ound; and (i ) he heigh o he ma u e indi idual is a leas h ee me e s. Such plan s co espond o he g ow h- o m “phane o- phy es”acco ding o Raunkiæ (1934) and Ellenbe g e al. (1991) (o iginally P, excluding NP = nanophane ophy es, heigh 0, 5–5 m), o phane ophy es “scapose”(o iginally Pscap), phane ophy es “caespi ose”(o iginally Pcaesp) and phane ophy es “s iscian i”(o iginally P ep ) acco ding o Pigna i (1982). By s ic ly ollowing hose c i e ia, we iden i ied some cases o woody species di icul o ca ego ize ha we u - he called “c yp ic ees”. Indeed, his de ini ion includes some axa ha gene ally occu as sh ubs wi h poo ly de- ined mul icolous s ems bu can o m ue ees unde ce - ain en i onmen al condi ions o in si ua ions whe e he dis u bances ha e been absen o e y educed o a leas se e al decades. Su p isingly, i u ned ou ha hese cases we e no a e in he s udy a ea. This is he case o ins ance o Spa ium junceum o Genis a e nensis (Fabaceae) which usually g ows in he o m o a bush (nanophane ophy e) o less han 5 m high. We included hem in he checklis be- cause in some locali ies o Co sica, Sa dinia and Sicily (Aeolian islands) hese axa mee he abo e c i e ia o ee. Many o he ee species epo ed in his s udy may e y equen ly appea as sh ubs o e en p os a e sc ubs due o in ense dis u bance, pa icula ly he bi o y. Occu ences and s a us by adminis a i e o by biogeog aphical a eas Occu ences o each ee axa we e compiled (i) by coun y (n= 12) and la ge island (n= 5) (he ea e , “ad- minis a i e egions”), and (ii) by biogeog aphical p o - inces. To da e, a ine spa ial app oach is no a ailable o all axa pe coun ies h oughou he s udy a ea. The de ini ion o he biogeog aphical p o inces ollowed he Biogeog aphic map o Eu ope p o ided by Ri as-Ma í- nez e al. (2004). Hence, hi een biogeog aphic p o inces occu in he s udy a ea (Fig. 3a). Th ee o hem a e in- cluded in o he Eu osibe ian biogeog aphical egion bu a e ep esen a i e o ansi ion zones be ween he Medi- e anean and he Eu osibe ian egions (Ce enno-Py e- nean, Alpine, and Apennino-Balkan); he o he en a e included in he Medi e anean egion. We s udied he species-a ea ela ionship wi hin he adminis a i e o biogeog aphical egions by plo ing he o al na i e ee axa ichness o each geog aphic uni as a unc ion o hei su ace, a e log ans o ma ion. Fo each species o subspecies, he p esence in each adminis a i e o biogeog aphical uni , was de ined as na i e (N) o in oduced (I). We conside endemic ee axa as ange- es ic ed axa in and ou side o he s udy a ea, in gene al loca ed wi hin a unique biogeog aphical p o ince sensu Ri as-Ma ínez e al. (2004). We ma ked axa wi h unclea au och honous o alloch- honous o igin as pu a i e na i e (i.e. “N?”, e.g. Te aclinis a icula a in Mal a), o pu a i e in oduced (i.e. “I?”). Taxa o which hep esenceisno con i medbu possiblewe e quo ed as pu a i e p esence (i.e.“?”,e.g.C a aegus pen a- gyna in Mon eneg o). Many cul i a ed and some ime na u- alized ee species ha e no been conside ed. We ocused only o a small numbe o axa ha ha e been cul i a ed o a long pe iod (a cheophy es, i.e. p esen be o e he clas- sical da e o he “disco e y”o Ame ica in 1492) and, apa om cul u e, a e widely na u alized in some pa s o he s udied a ea bu also na i e in some a eas o he Medi e anean-Eu opean egion i.e. Cas anea sa i a Mill., Ce a onia siliqua L., Cup essus sempe i ens L., Ficus ca ica L., Juglans egia L., e c. (see Addi ional ile 1). We conside ed h ea ened ee axa using he IUCN (2018) classi ica ion sys em, as axa included in o he h ee classes: c i ically endange ed (CR), endange ed (EN), o ulne able (VU). The o he ca ego ies included nea h ea ened axa (NT), leas conce n axa (LC), and da a de- icien axa (DD) a e also conside ed in he p esen wo k. Da a sou ces The da a we e collec ed and agg ega ed o each coun y and la ge island. The p ima y sou ces o da a we e he in e na ional da abase Eu o + Med Plan Base (h p://www.emplan base.o g/home.h ml), Flo a Eu o- paea (Tu in e al. 1964–1993), and he olume se ies Cho ology o ees and sh ubs in sou h-wes Asia and adjacen egions (B owicz 1982–1996). These comp e- hensi e da a we e ca e ully comple ed and checked wi h a ailable na ional lo as, na ional da abases, egional da abases, o he publica ions, and ou own expe ise, when he a o emen ioned sou ces we e no a ailable: Albania (Ba ina e al. 2017; Z. Ba ina pe s. comm.), Médail e al. Fo es Ecosys ems (2019) 6:17 Page 4 o 19 Co sica (Jeanmonod and Gamisans 2013; CBN Co se pe s. comm.), C e e (Chil on and Tu land 1997;h p:// www.c e an lo a.com/;S id2016), C oa ia (Nikolić 2004–onwa d), Cyp us (Hand e al. 2011–onwa d), con- inen al F ance (Silene-Flo e da abase: h p:// lo e.silene.eu, IGN In en ai e Fo es ie : h p://in en ai e- o es ie .ign. /, Tison e al. 2014), G eece (Dimopoulos e al. 2013,2016; S id 2016), Ibe ian Peninsula i.e. Balea ic Islands, Spain and Po ugal (An hos: h p://www.an hos.es;Cas o iejo 1986–2015; Sociedade Po uguesa de Bo ânica 2014), I aly (Ba olucci e al. 2018; Galasso e al. 2018; Vegi aly: h p:// www. egi aly.i /), Macedonia (V. Ma e ski ined.), Mal a (Mazzocchi 1969; Baldacchino and S e ens 2000;Mi sud 2002–2014;Casha2015; Baldacchino 2018;Calleja2018); Mon eneg o (F. Médail & A.-C. Monne obs. pe s.), Sa - dinia (A igoni 2006–2015; Bacche a e al. 2012;G.Bac- che a obs. pe s.), Sicily (Gia dina e al. 2007), Slo enia (Jogan e al. 2001). In addi ion, some o he mo e hema ic and comp e- hensi e da a sou ces we e used such as he Eu opean A las o Fo es (San-Miguel-Ayanz e al. 2016) and com- ple ed by some ecen pape s conce ning he desc ip ion o some new ee axa, such as Tama ix minoa in C e e (Villa e al. 2015) o wo c yp ic species in he Alnus glu inosa g oup (Ví e al. 2017). Da a syn hesis was led by D. Pa on & F. Médail be ween 2014 and 2018. Taxonomy and nomencla u e The p esen checklis o Medi e anean-Eu opean ees includes only he axa a he species and subspecies le els which mee bo h c i e ia: “s udy a ea”and “ ee de ini ion”. This lis does no con ain o he sub-speci ic le els, such as a ie ies, o ms, o hyb ids, because o hei axonomical and nomencla u al ins abili ies. We ollowed he classi ica ion o he Angiospe m Phylogeny G oup o he de ini ion o amilies (APG III 2009;APGIV 2016). The nomencla u e o Medi e anean and Eu opean ees is o en luc ua ing and con o e sial be ween he di e en majo axonomic wo ks. We conside ed in p io - i y he Eu o+Med da abase (h p://www.emplan base.o g/ home.h ml) and he Plan Lis da abase (h ps://www. he- plan lis .o g), bu also he majo na ional lo as (see e - e ences in he “da a sou ces”pa ag aph). In case o axonomic-le el disag eemen , we e ained he mos consensual axonomic le el based also on ecen phylo- gene ic s udies o sys ema ic e ision o a gi en g oup, i a ailable, adding consul ing local expe s o ecen lo as. Resul s Medi e anean-Eu opean ees in a nu shell Ou analysis o all he axa ha can po en ially be ee species in he Medi e anean-Eu opean egion p o ides a checklis o 245 ee axa (i.e. species and subspecies), in- cluding 210 species and 35 subspecies (see Addi ional ile 1). These axa belong o 33 di e en amilies; he mos ep esen ed amilies a e Rosaceae (42 axa), Fagaceae (33 axa), Pinaceae (21 axa), Salicaceae (20 axa), Sapindaceae (19 axa), Be ulaceae (16 axa), Tama ica- ceae (16 axa), and Cup essaceae (14 axa). These ee axa a e included in 64 di e en gene a which ep esen s 86% o he o al ee gene a (n= 74) ound in he whole Medi e anean biogeog aphic egion (Quézel and Médail 2003). Fou o hese gene a (Cha- mae ops,Philly ea,Spa ium,Te aclinis) ha e hei dis- ibu ion cen e ed in he Medi e anean egion and can be conside ed as Medi e anean endemics sensu la o (a he biogeog aphical egion le el), whe eas h ee axa ha e a Te hysian o igin (Ce a onia, My us,Ne ium) and occu in adjacen biogeog aphic egions as well. The o he gene a ha e la ge dis ibu ions, in he Palea c ic ealm o beyond. Among his checklis , 46 a e endemic ees (30 spe- cies and 16 subspecies), i.e. mainly loca ed wi hin a sin- gle biogeog aphic p o ince sensu Ri as-Ma ínez e al. (2004). This means ha he a e o endemism is equal o 18.9% i we conside he species and subspecies le els, o 14.3% a he species le el. The gene a wi h hemo eendemic axaa eQue cus (6 axa), Abies, Ace , and Pinus (4 axa each), Alnus,Salix and So bus (3 axa each). The p esence o h ee na ow endemic species included in wo elic gene a (Liquidamba and Zelko a) and cha ac e is ic o he Cenozoic paleo lo a dis ibu ed in he Palea c ic ealm should also be no ed (Palama e 1989). E en hough we only ook in o accoun axa consid- e ed as indigenous o a gi en coun y o a biogeog aph- ical a ea, he na i e s a us o some ee species can some imes be di icul o es ima e, no ably when hey a e equen ly cul i a ed o used o a o es a ion, o when hei cen e o o igin o na i e ange a e s ill unclea (e.g. Cas anea,Ce a onia,Ficus,Juglans, Olea: see discussion). O e all, i conce ns 24 axa (ca. 10% o he o al checklis ) ha a e widely cul i a ed o selec ed o a o es a ion pu posed by o es se - ices. The dis ibu ion o hose na i e bu locally do- mes ica ed Medi e anean ee axa will be discussed in de ail below since i ep esen s a c ucial issue o he conse a ion o local gene ic esou ces. This checklis also includes 44 un ecognized eal ees o “c yp ic ees”, i.e. usually wi h a sh ubby habi bu which o m a ee habi unde ce ain en i onmen al condi ions (Table 1).These axabelong o ou main amilies (Rosaceae: 11 ee species, Cup essaceae: 5 ee species, Anaca diaceae and Faba- ceae: 4 ee species each), and o wo main gene a (9 ee species in C a aegus and 5 in Junipe us). These c yp ic ees ep esen he imp essi e and unexpec ed a e o ≈18% o he Medi e anean-Eu opean ees. Médail e al. Fo es Ecosys ems (2019) 6:17 Page 5 o 19 Table 1 The 44 un ecognized eal ees o “c yp ic ees”, i.e. usually wi h a sh ubby o m, occu ing in he Medi e anean-Eu opean egion, wi h indica ions abou hei dis ibu ion and ecology Taxa Family Global dis ibu ion a ea Ecology Alnus i idis (Chaix) DC. Be ulaceae A c ico-Alpine Subalpine and o o-medi e anean sc ublands Buxus balea ica Lam. Buxaceae SW Medi e anean, S Ana olia Sc ublands on p edominan ly ca bona e subs a es Buxus sempe i ens L. Buxaceae Medi e anean-Eu opean Submedi e anean sc ublands Chamae ops humilis L. A ecaceae CW Medi e anean The mophilous sc ublands, coas al sc ee and cli s Co inus coggyg ia Scop. Anaca diaceae S Eu opean, I ano-Tu anian Eumedi e anean and submedi e anean d y sc ublands, wa m and mesophilous habi a s o sou he n exposu e inland Co oneas e g ana ensis Boiss. Rosaceae Endemic o S Spain (Andalusia) Rocky ma o als, deciduous and pine o es s C a aegus aza olus L. Rosaceae E Medi e anean Open sc ublands C a aegus held eichii Boiss. Rosaceae Balkan Open coni e ous o es s, mixed sc ubs, d y ocky meadows C a aegus lacinia a Uc ia Rosaceae CW Medi e anean Clea ings o moun ain woods C a aegus lae iga a (Poi .) DC. Rosaceae CW Medi e anean Mesophilic shingles and hedges o he hilly and moun ainous ege a ion bel , oak o es s ou side he lood, moun ain beech o es s C a aegus monogyna Jacq. Rosaceae Medi e anean-Eu opean Coas al d y sc ublands, Inland mesophilic shingles and hedges C a aegus ne adensis K.I.Ch . Rosaceae Endemic o S Spain (Andalusia) Clea ings and edges o moun ain woods C a aegus o ien alis Pall. ex M.Bieb. Rosaceae E Medi e anean and SW Asia Rocky places in meadows and open woodlands C a aegus pen agyna Willd. Rosaceae Balkan Open o es , mixed sc ubs, d y ocky meadows C a aegus pycnoloba Boiss & Held . Rosaceae Endemic o G eece (Peloponnese) Rocky limes one idhes and slope, d y g assy pla eau, sc ubs and open Abies cephalonica o es s Cy isus aeolicus Guss. Fabaceae Endemic o Sicily (Aeolian Islands) D y slopes and open sc ublands on olcanic subs a es E ica a bo ea L. E icaceae Medi e anean, Maca onesian, E. A ica, Saha a The mophilous sc ublands in non-ca bona ic subs a es Fon anesia philli aeoides Labill. Oleaceae E Medi e anean D y maquis F angula alnus Mill. Rhamnaceae C Eu opean, Medi e anean Ripa ian o es s o alde and ash Genis a e nensis (Ra .) DC. Fabaceae Endemic o Sicily, Sa dinia and Co sica A bo escen ma o als on non-ca bona ic subs a es Genis a y hena Valsecchi Fabaceae Endemic o Sicily (Aeolian Islands) and Lazio (Pon ian Islands) A id olcanic slopes on ocky and sandy subs a es Junipe us communis L. Cup essaceae Eu asia ic Rocky meadows, moun ain pas u es, mesophilic hedges and sh ubs, o es s edges in submon ane a eas Junipe us del oides R.P.Adams Cup essaceae CE Medi e anean Open woodlands and sc ublands on mid-al i udes Junipe us na icula is Gand. Cup essaceae Endemic o SW Ibe ian Peninsula A bo escen ma o al on ma i ime sands Junipe us oxyced us L. Cup essaceae Medi e anean-Pon ic Eumedi e anean and submedi e anean d y a eas in open o es s and ma o als Junipe us phoenicea L. Cup essaceae Medi e anean, Maca onesian, Red Sea Eumedi e anean d y and wa m a eas in e e g een oak and pine o es s, coas al ma o als My ica aya Ai on My icaceae Maca onesia, S Po ugal Unde wood o pinewoods on siliceous My us communis L. My aceae Medi e anean, Maca onesian, I ano-Tu anian The mophilous sc ublands on non-ca bona ic subs a es, small swampy o es s ands Ne ium oleande L. Apocynaceae Medi e anean, Saha a The mophilous and empo a y i e beds, we lowlands Médail e al. Fo es Ecosys ems (2019) 6:17 Page 6 o 19 Medi e anean-Eu opean ee di e si y by adminis a i e egions Mapping he p esence o ee species in each Medi e anean-Eu opean coun y is impo an o es- ima e conse a ion p io i ies a he adminis a i e le el. Ou analysis shows ha he coun ies (con inen al pa s) wi h he highes o al ichness o na i e ees (> 110 axa) a e G eece (146 axa), I aly (133 axa), Albania (122 axa), Spain (115 axa), Macedonia (116 axa), and C oa ia (110 axa) (Fig. 1a, Table 2). The e is a s ong dispa i y in o al ichness be ween he la ge Medi e anean islands: Sicily has he highes ichness (88 axa), and he Balea ic Islands he lowes one (35 axa), whe eas Co sica and Sa dinia in he wes e n Medi e anean Basin exhibi a simila ichness ( espec i ely 70 and 76 axa) and Cyp us and C e e in he eas e n basin sha e qui e simila le el o ee ichness ( espec i ely 42 and 52 axa). While he o al ee ichness is concen a ed mainly in he Balkans, endemic ees mos ly occu ed in he la ge coun ies o he h ee peninsula in wes e n, cen al and eas e n Medi e anean a ea (Table 2). G eece (11 endemic axa), Spain (9 endemic axa), and I aly (7 endemic axa) exhibi ed he highes numbe o endemic axa. Emphasis should be gi en o he place o some la ge Ty henian islands ha shel e a signi ican numbe o endemic ees (Sicily: 10 axa, Sa dinia: 7 axa). The species-a ea ela ionships show con as ing e- sul s be ween adminis a i e egions and la ge Medi e - anean islands (Fig. 2). The ela ionship is signi ican o he islands (log ichness islands: −1.89841 + 0.25788 log su ace islands, p= 0.01) bu no o he con inen al a eas o he coun ies (log ichness con inen s: 3.8459 + 0.03493 log su ace con inen s, p= 0.41). The con in- en al a eas o he cen al and eas e n Medi e anean coun ies, om I aly o G eece (i.e. mainly he Balkans), ha e a signi ican ly highe ee axonomic ichness han hose loca ed u he wes o on he la ge islands. Thus, he islands always ha e a lowe ichness pe uni a ea han con inen s. This is pa icula ly he case o Mal a and he Balea ic Islands. Ne e heless, in Sicily and Sa dinia, he a io is close o some con inen al si ua- ions (e.g. F ance, Slo enia) and is e en highe ha Po ugal which shows he lowes a ea-species a io o a con inen al coun y. Table 1 The 44 un ecognized eal ees o “c yp ic ees”, i.e. usually wi h a sh ubby o m, occu ing in he Medi e anean-Eu opean egion, wi h indica ions abou hei dis ibu ion and ecology (Con inued) Taxa Family Global dis ibu ion a ea Ecology Philly ea angus i olia L. Oleaceae W Medi e anean E e g een oak and alepo pine o es s, d y and wa m habi a s o en s ony, ma o als Philly ea la i olia L. Oleaceae Medi e anean E e g een oak and alepo pine o es s, on d y and wa m habi a s o en s ony, ma o als Pis acia len iscus L. Anaca diaceae Medi e anean, Maca onesian, E e g een oak o es s and ma o als Pis acia e ebin hus L. Anaca diaceae Medi e anean, S Eu opean E e g een oak o es s and ma o als P unus mahaleb L. Rosaceae S Eu opean-Pon ic The mophilous o es s o pubescen oak and ma o als Que cus cocci e a L. Fagaceae Medi e anean E e g een oak o es s and ma o als Rhamnus ala e nus L. Rhamnaceae Medi e anean Mixed e e g een and deciduous o es s, ma o als domina ed by e e g een oaks Rhododend on pon icum L. E icaceae S Ibe ian Peninsula, Lebanon, Pon ic egion Mixed woodlands in humid a ines on siliceous Sambucus nig a L. Adoxaceae Eu opean-Caucasian Mesophilous unde b ushs and hedges in hilly and moun ains a eas, deciduous o es s Sea sia ipa i a (Uc ia) Mo e Anaca diaceae S Medi e anean, Saha a Open ocky ma o als in a id and dese ic a eas, empo a y i e banks Spa ium junceum L. Fabaceae Medi e anean, Eu opean Eumedi e anean d y, wa m and s ony a eas, o en in mo e o less pu e s ands S y ax o icinalis L. S y acaceae CE Medi e anean Rocky and d y g asslands, he mophilous ma o als wi h e e g een oaks and alepo pine Vi ex agnus-cas us L. Lamiaceae Medi e anean, I ano-Tu anian Ri e beds, we lowlands, he mophilous damp o loodes unde b ushes Zelko a abelicea (Lam.) Boiss. Ulmaceae Endemic o C e e Rocky slopes o la alley bo oms in he moun ains Zelko a sicula Di Pasquale, Ga i & Quézel Ulmaceae Endemic o Sicily Sc ublands on basal ic soil, i e beds Médail e al. Fo es Ecosys ems (2019) 6:17 Page 7 o 19 Medi e anean-Eu opean ee di e si y by biogeog aphical a eas To go beyond hei dis ibu ion in he adminis a i e e- gions, we ex ac ed he numbe o na i e ee axa (species and subspecies) o each o he 13 biogeog aphic p o inces sensu Ri as-Ma ínez e al. (2004)(Fig.3a). The aw numbe s o ee ichness a e culmina ing in he cen al-eas e n p o inces o he Medi e anean-Eu opean egion: Apennino-Balkan (142 axa), G aeco-Aegean (137 axa), Ad ia ic (135), and I alo-Ty henian (128 axa). The lowes ichness (40 axa) is ound in he Cilicio-Phoenician p o ince which co esponds only (in ou s udy a ea) o he island o Cyp us (Fig. 3b). The highes axonomic ich- ness in endemic ees occu s in he I alo-Ty henian (n= 16 axa) and in he G aeco-Aegean (n=12 axa) p o inces, hen in he Be ican (n=9 axa) and Ad i- a ic (n= 8 axa) p o inces (Fig. 3c). The lowes en- demic ichness (n=1 axa) is ound in sou he n F ance, and in he sou he n pa s o he Alpine and Ce enno-Py enean p o inces. The species-a ea ela ionship o biogeog aphic p o - inces clea ly disc imina ed he cen al-eas e n (mainly Balkans) and no he n (Alpine and Ce enno-Py enean) p o inces, agains he i e wes e n p o inces in he Ibe - ian Peninsula (Fig. 4). Th ea ened ees Among he 245 ee axa o he checklis , 15 cons i u e h ea ened axa sensu IUCN (2 CR, 7 EN, 6 VU) and 4 a e classi ied as nea h ea ened axa (NT) (Table 3). Only 154 ee axa (145 species and 9 subspecies) a e classi ied as “leas conce n”(LC), and 23 species wi h da a gap o assessmen (DD). Wha is mos wo ying is ha 84 axa (19 species and 65 subspecies) included in he checklis a e no conside ed a all in he global IUCN assessmen . Ele en o hese h ea ened ee axa, including some e y na ow endemic ees such as Abies neb odensis,Cy isus aeolicus,Rhamnus pe sici olia,Zel- ko a abelicea and Zelko a sicula a e only dis ibu ed on some la ge (no ably Sicily, C e e, Cyp us and Sa dinia) o medium ( ew C oa ian islands shel e ing Pinus nig a subsp. dalma ica popula ions) sized islands o he Medi e anean Sea. Discussion Dis ibu ion o ee di e si y in he Medi e anean- Eu opean egion Ou comp ehensi e analysis o ee axonomic di e si y in he Medi e anean-Eu opean egion iden i ied 210 ee species o 245 species and subspecies, including 46 endemic ees o he s udy a ea. This is o cou se a iny po ion o he es ima ed ee di e si y wo ldwide (ca. 60,065 ee species cu en ly known o science, see Beech e al. 2017), bu an impo an numbe ega ding o he Eu opean o es s. T ee axonomic di e si y was es ima ed a 135 species and subspecies wi hin he medio-Eu opean egion (Quézel and Médail 2003), whe eas only 42 ee species om 11 amilies occu in Cen al Eu ope (Leuschne and Meie 2018). I ep e- sen s also o high ee di e si y compa ed o he one in he en i e Medi e anean biogeog aphical egion which was es ima ed a 290 species and subspecies (Quézel and Médail 2003), i.e. 85% o he ees o he whole Medi e - anean egion occu in he Eu opean pa . This key e- sul shows he impo ance o he sou he n pa o Eu ope in p ese ing his ich biological he i age o a empe a e egion. The axonomic ichness o he Medi e anean-Eu opean egion is also ound in ee gene a, since 86% o he o al gene a (n= 74) o he whole Medi e anean biogeog aphic egion a e p esen in his Eu opean pa . Only 11 gene a (Acacia,Amygdalus,A gania,Balani es,Calo opis,Dios- py os,D acaena,Mo inga,P ospis,P e oca ya,Ziziphus) a e es ic ed o he sou he n o eas e n pa s o he Medi e anean egion. These esul s a e no su p ising since Medi e anean o es s a e e y di e se and he e ogeneous ega ding hei s uc u e, hei speci ic composi ion and hei dy- namics (Quézel and Médail 2003), and his explains he exis ence o 35 e es ial sub-eco egions including Table 2 Numbe o o al na i e ee axa (including endemic and pu a i e na i e axa), endemic ee axa, and pu a i e na i e ee axa) by adminis a i e a eas and main islands o he Medi e anean-Eu opean egion. “Taxa”include bo h species and sub-species le el Coun ies To al na i e axa ichness Endemic axa ichness Pu a i e na i e axa ichness P esence unce ain y Albania 122 2 3 0 Balea ic 33 1 0 0 Co sica 70 5 0 0 C e e 52 4 0 0 C oa ia 110 2 0 0 Cyp us 42 3 0 0 F ance 102 1 3 0 G eece 146 11 0 0 I aly 133 7 0 0 Macedonia 116 3 3 2 Mal a 25 0 5 0 Mon eneg o 108 1 0 1 Po ugal 69 3 3 0 Sa dinia 76 7 0 0 Sicily 88 10 0 0 Slo enia 85 0 1 1 Spain 115 9 0 0 Médail e al. Fo es Ecosys ems (2019) 6:17 Page 8 o 19 o es s (WWF 2001). The main o es ypes a e: (i) scle ophyllous o es s (no ably wi h he oaks Que cus ilex, Q. sube ,Q. cocci e a); (ii) d y coni e (Pinus halepensis,P. b u ia) o es s; (iii) deciduous mixed o es s wi h b oad-lea ed oaks (Que cus pubescens,Q. aginea,Q. i ha- bu ensis) and o he gene a (Ace ,Ca pinus,F axinus, So bus); (i ) moun ain coni e o es s wi h Abies, Ced us,Junipe us,Pinus nig a. T ee di e si y and he ecological complexi y in o es ypes can be explained bo h by he complex paleogeog aphy and his o ical bio- geog aphy o he Medi e anean egion, and also by he high he e ogenei y in he clima e (Médail 2008;Blondel e al. 2010). This woody biodi e si y is une enly dis ibu ed wi hin he Medi e anean-Eu opean egion. Ou analysis, pe - o med ei he a he adminis a i e o biogeog aphic le el, indica e ha he con inen al a eas o he cen al and eas e n Medi e anean coun ies, om I aly o G eece (i.e. mainly he Balkans), ha e a signi ican ly highe ee ichness compa ed o hose loca ed u he wes (Ibe ian Peninsula) o on la ge Medi e anean islands. The highe axonomic di e si y in he eas e n Medi e anean Basin is ound in se e al o he s udies and his pa e n is p obably ela ed o he key biogeog aphical c oss oad o his a ea and o he exis ence o mo e sui able condi ions du ing he LGM (no ably wa me summe empe a u es) inducing la ge biodi e si y e ugia (Médail and Diadema 2009; Fady and Cono d 2010). Ou esul s a e also consis en wi h hose ob ained om wo s udies ha included a mo e educed sampling o ees in Eu ope: (i) he dis ibu ion o 55 Eu opean ee species sug- ges s ha he ee ichness is maximal in he Balkans, especially o ees wi h a es ic ed dis ibu ion (S enning and Sko 2007); (ii) he dis ibu ion o ee ichness ( o al n= 187 species) o Eu ope shows he signi ican concen- a ion o ee di e si y along a la ge coas al a ea ex ended om C oa ia o no h-wes e n G eece (Mon oya and Rod íguez 2007). Bo h s udies concluded ha he main d i e o he a ia ion o ee ichness is he cu en clima e, and ha he clima e du ing he Las Glacial Maximum (LGM, ca. 20 ky ago) o he pe iod since an a ea became ee o ice ha e a signi ican in luence, no ably o explain he concen a ion o ange- es ic ed ee axa. Some s udies also e ealed ha olde clima ic e en s h oughou he Miocene we e also c i ical o ex- inc ion in he wes e n pa o he Medi e anean Basin ( he Ibe ian Peninsula) and may pa ly explain he ela i e lowe ichness o ee axa he e (Pos igo Mija a e al. 2009). The species-a ea ela ionships indica e ha Medi- e anean islands always ha e a lowe ichness pe uni a ea, and only he wo la ges islands, Sicily and Sa dinia, a e g ouped wi h he con inen al e i o ies o highe ee Fig. 2 Linea eg essions be ween he o al na i e ee axa ichness and he su ace o con inen al adminis a i e a eas (black eg ession line and black ci cles) o main islands (g ey eg ession line and black iangles) in he Medi e anean-Eu opean egion wi h hei espec i e 95% con idence in e al. Abscissa and o dina e axes ha e a loga i hmic scale. Do s abo e each line indica e highe ichness han p edic ed by he species-a ea ela ionship, and do s below each line indica e lowe ichness han expec ed Médail e al. Fo es Ecosys ems (2019) 6:17 Page 9 o 19 minoa, occu ing in a unique locali y o NW C e e on sandy i e banks close o he sea (Villa e al. 2015), is quo ed Da a De icien (DD). Among he o he DD axa, a leas wo cha ac e is ic axa (Pla anus o ien alis,Vi ex agnus-cas us) cu en ly expe ience a se e e educ ion o hei popula ions due o he a i icializa ion o hei habi a s, e en i hey s ill coun a qui e la ge numbe o popula ions. Ano he unde es ima ed h ea is in og ession be- ween phylogene ically ela ed ee axa. This is he case o he g oup o black pines (Pinus nig a) whe e in o- g ession isk is likely be ween Pinus nig a subsp. nig a, equen ly plan ed o e o es a ion, and wo o he sub- species ha ing a mo e es ic ed dis ibu ion ange: subsp. dalma ica in C oa ia, and subsp. salzmannii in F ance and Spain. Al hough in equen and po en ially bene icial o some ai s, such gene low om plan ed o na i e ees o could con ibu e o wo sen local adap- a ion, o example o diseases such as Do his oma sp. (Sco i-Sain agne e al. 2018). F om a geog aphical poin o iew, we mus emphasize he ole o he la ge Medi e anean islands, which in- clude 11 o he 19 ee axa cu en ly p esen in he IUCN da abase. This shows he impo ance o hese is- land ecosys ems o he di e en ia ion and pe sis ence o axonomically singula ees, bu also he se e e h ea s in hese spa ially es ic ed sys ems. This is he case o Sicily which includes h ee a e na ow endemics (Abies neb odensis,Cy isus aeolicus,Zelko a sicula) among which he wo la e a e only p esen on some small islands o he Aeolian a chipelago (T oia 2012). Some o he na ow endemic ees (Genis a y hena om Aeolian and Pon ine a chipelagos in I aly, and Que cus alni olia es ic ed o he T oodos ange in Cyp us) a e classi ied as leas conce n (LC), bu due o hei es ic ed ange and popula ion size hese e alua- ions a e p obably oo op imis ic. A mo e p ecise isk analysis by egion would also p obably highligh he high le el o h ea o locally se e al Medi e anean ees. Fo example, he y henian insula endemic Genis a e nensis which is anked globally as LC is classi ied as c i ically endange ed (CR) in Co sica. This is also he case o se - e al ees wi h a pa chy dis ibu ion in specialized moun- ain habi a s such as Junipe us d upacea,J. oe idissima, J. hu i e a, and Pinus held eichii which a e classi ied as LC as well. Some o he locally h ea ened axa (Buxus balea ica,Rhododend on pon icum) wi h a highly e- s ic ed ange in he N. Medi e anean egion a e no e en conside ed in he IUCN da abase. Conclusion This s udy p o ides he i s comp ehensi e assessmen o ee dis ibu ions in he Medi e anean-Eu opean e- gion. The p esen checklis includes an unsuspec edly high numbe o ee axa (245 species and subspecies), wi h a leas 44 axa ha a e gene ally bushy bu can exp ess a ue ee a chi ec u e unde ce ain condi ions (“c yp ic ees”). This means ha he Medi e anean-Eu opean e- gion has almos 200 ees mo e han he Cen al Eu opean egion. This axonomic biodi e si y is highes in he cen al-eas e n pa o he Medi e anean egion, no - ably in he Apennino-Balkan p o ince. We mus also emphasize he ole o some la ge Ty henian islands (especially Sicily and Sa dinia) ha shel e a signi ican numbe o endemic ees. These a eas a e pa icula ly impo an om he poin o iew o unc ional conse - a ion because ee species ichness is posi i ely linked o highe le els o mul iple ecosys em se ices (Gam eld e al. 2013), and a e species –like mos o he Medi e a- nean endemic ees –suppo o iginal and ulne able unc ion (Mouillo e al. 2013). Bu h ea s o his woody biodi e si y a e o en signi ican and may especially a ec ees wi h na ow dis ibu ions. Howe e , he IUCN Red lis includes so a only 19 Medi e anean ees conside ed o be h ea ened (CR + EN + VU) o nea h ea ened (NT). The e o e, he ulne abili y o se e al o hese ees is p obably unde es ima ed and u he assessmen s a e needed in he nea u u e. Fo Medi e anean ees a o ed o cul i a ed by man, some imes o millennia, i is necessa y o de- elop app oaches combining phylogeog aphy and paleoecology, a he scale o he dis ibu ion a ea spe- ci ic o each axon. This will allow a be e es ima e o he na i e s a us o each biogeog aphical a ea, and o conside he e olu iona y dimension in he p ese - a ion o hese ees. This checklis ep esen s he i s s ep owa ds a be e unde s anding o he di e si y o ees in he Medi e a- nean egion. The nex s ep should be o imp o e he co e age in occu ences eco ds o hese ee axa in he egion in he exis ing ee species da abase (Noce e al. 2016; Se a-Diaz e al. 2017). These da a will help o explo e he key scien i ic ques ions associa ed o he d i e s o he dis ibu ion pa e n and o he shape o he species-a ea ela ionship. Quan i a i e in es iga ions o ecological (e.g., clima e, soil, dis u bance) e sus his- o ical (e.g., pas clima e, gene ic o iginali y) d i e s o cu en ee biodi e si y can he e o e be conside ed. This checklis will cons i u e also an essen ial back- g ound o unc ional and phylogene ic analyses o his key biological con ingen o e es ial ecosys ems. The p ac ical issues conce n a be e assessmen o he h ea ened s a us o some hese unapp ecia ed ees wi hin a highly human-modi ied egion. We also hope such wo k will ca alyze u he assessmen o ee di e - si y a he scale o he whole Medi e anean egion (i.e. also No h A ica and Middle-Eas ) e en i he da a a e s ill e y complex o syn hesize. Médail e al. Fo es Ecosys ems (2019) 6:17 Page 16 o 19 Addi ional ile Addi ional ile 1: Table S1. Checklis o he ee axa (species and subspecies) occu ing in heMedi e anean-Eu opean egion, om Po ugal o Cyp us. The de ini ion o he amilies ollows he Angiospe m Phylogeny G oup (APG III 2009; APG IV 2016). The e ained nomencla u e o he ee axa is compa ed wi h hose o he Eu o+Med da abase (h p://www.emplan base.o g/home.h ml), he olume se ies Cho ology o ees and sh ubs in sou h-wes Asia and adjacen egions (B owicz 1982– 1996) and he Wo ld Checklis Kew. Fo he occu ence o each ee axa in a coun y o a la ge island, we indica e he endemism s a us, he cul i a ed s a us, heau och honous (na i e: N) o alloch honous (in oduced: I) s a us. Taxa o which he p esence is no con i med bu possible a e quo ed as "pu a i e p esence », i.e.“?”. (XLSX 71 kb) Acknowledgmen s The au ho s hank Aggeliki Doxa (Ins i u e o Applied and Compu a ional Ma hema ics, He aklion), Lae i ia Hugo and Paula Spinosi (Conse a oi e bo anique na ional de Co se / O ice de l’en i onnemen de la Co se), Vi gile Noble (Conse a oi e bo anique na ional médi e anéen), Sal a o e Pas a (CNR Pale mo), Es e anía San os Ba ea (Uni e sidad de Se illa) o hei help in acqui ing he da a o o hei commen s on he dis ibu ion o s a us o he di e en ee species. Funding This wo k was unded by he F ench Founda ion o Resea ch on Biodi e si y (FRB) h ough i s Cen e o Syn hesis and Analysis o Biodi e si y da a (CESAB) p og amme, as pa o he WOODIV esea ch p ojec . ACM and MCB we e unded by Labex OT-Med (n° ANR-11-LABX-0061). The unde s had no ole in s udy design, da a collec ion and analysis, decision o publish, o p epa a ion o he manusc ip . A ailabili y o da a and ma e ials A e accep ance da a will be made publicly a ailable as an addi ional ile. Au ho s’con ibu ions Concei ed and designed he da abase: FM, DP, ACM, GB, PD, TN and AL. Analyzed he da a: ACM and FM. W o e he pape : FM, ACM and TN. All au ho s pa icipa ed o he discussions leading o he aming o he manusc ip du ing WOODIV wo kshops. All au ho s ead, con ibu ed sugges ions and app o ed he inal manusc ip . E hics app o al and consen o pa icipa e No applicable. Consen o publica ion No applicable. Compe ing in e es s The au ho s decla e ha hey ha e no compe ing in e es s. Au ho de ails 1 Aix Ma seille Uni , A ignon Uni , CNRS, IRD, IMBE. Technopôle de l’A bois-Médi e anée, cedex 4, BP 80, 13 545 Aix-en-P o ence, F ance. 2 Facul y o Science, Uni e si y o Zag eb, Ho a o ac 102a, HR-10000 Zag eb, C oa ia. 3 Depa men o Biology, Di ision o Plan Biology, Labo a o y o Bo any, Uni e si y o Pa as, Uni e si y Campus, 26504 Rio, G eece. 4 Cen o Conse azione Biodi e si à, Dipa imen o di Scienze della Vi a e dell’Ambien e, Uni e si à degli S udi di Caglia i, Viale S. Ignazio da Laconi, 13, 09123 Caglia i, I aly. 5 Depa amen o de Biologia Vege al y Ecologia, Uni e sidad de Se illa, Apa ado 1095, 41080 Se illa, Spain. 6 Depa men o Bo any, Hunga ian Na u al His o y Museum, P . 137, Budapes 1431, Hunga y. 7 So bonne Uni e si y, IEES Bâ 44-34, cc 237. 4, Place Jussieu, Pa is, F ance. 8 Depa men o Ag icul u e, Food and Fo es Sciences, Uni e si y o Pale mo, Viale delle Scienze bldg. 4, 90128 Pale mo, I aly. 9 INRA, UR629, Ecologie des o ê s médi e anéennes, A ignon, F ance. 10 Macedonian Academy o Sciences and A s, K s e Misi ko 2, 1000 Skopje, Republic o Macedonia. 11 EcoGozo, Regional De elopmen Di ec o a e - Minis y o Gozo, Fla 6, Sunse Cou B, T iq Ma sal o n, Xagh a, Gozo, Mal a. 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