Fagus sylvatica
European beech

European beech (Fagus sylvatica) is a large, deciduous tree species with a wide continuous distribution from southern Scandinavia to the Mediterranean. The species is monoecious, wind pollinated, and even self-fertile. It thrives in temperate climates and favours well-drained soils. European beech forms dense stands and is shade-tolerant, allowing it to dominate many European forests. This makes it a key element of forest ecosystems offering critical habitats for a wide range of wildlife. Historically, beech has been valued for its wood and adaptability and is currently one of the most important and widely cultivated trees in Europe, where it is used for furniture, flooring, firewood and charcoal, and veneer due to its fine grain and durability.

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ex situ genetic conservation unit
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Acknowledgements

This distribution map has been developed by the European Commission Joint Research Centre (partly based on the EUFORGEN map) and released under Creative Commons Attribution 4.0 International (CC-BY 4.0)


Caudullo, G., Welk, E., San-Miguel-Ayanz, J., 2017. Chorological maps for the main European woody species. Data in Brief 12, 662-666. DOI: https://doi.org/10.1016/j.dib.2017.05.007

The following experts have contributed to the development of the EUFORGEN distribution maps:

Fazia Krouchi (Algeria), Hasmik Ghalachyan (Armenia), Thomas Geburek (Austria), Berthold Heinze (Austria), Rudi Litschauer (Austria), Rudolf Litschauer (Austria), Michael Mengl (Austria), Ferdinand Müller (Austria), Franz Starlinger (Austria), Valida Ali-zade (Azerbaijan), Vahid Djalal Hajiyev (Azerbaijan), Karen Cox (Belgium), Bart De Cuyper (Belgium), Olivier Desteucq (Belgium), Patrick Mertens (Belgium), Jos Van Slycken (Belgium), An Vanden Broeck (Belgium), Kristine Vander Mijnsbrugge (Belgium), Dalibor Ballian (Bosnia and Herzegovina), Alexander H. Alexandrov (Bulgaria), Alexander Delkov (Bulgaria), Ivanova Denitsa Pandeva (Bulgaria), Peter Zhelev Stoyanov (Bulgaria), Joso Gracan (Croatia), Marilena Idzojtic (Croatia), Mladen Ivankovic (Croatia), Željka Ivanović (Croatia), Davorin Kajba (Croatia), Hrvoje Marjanovic (Croatia), Sanja Peric (Croatia), Andreas Christou (Cyprus), Xenophon Hadjikyriacou (Cyprus), Václav Buriánek (Czech Republic), Jan Chládek (Czech Republic), Josef Frýdl (Czech Republic), Petr Novotný (Czech Republic), Martin Slovacek (Czech Republic), Zdenek Špišek (Czech Republic), Karel Vancura (Czech Republic), Ulrik Bräuner (Denmark), Bjerne Ditlevsen (Denmark), Jon Kehlet Hansen (Denmark), Jan Svejgaard Jensen (Denmark), Kalev Jðgiste (Estonia), Tiit Maaten (Estonia), Raul Pihu (Estonia), Ülo Tamm (Estonia), Arvo Tullus (Estonia), Aivo Vares (Estonia), Teijo Nikkanen (Finland), Sanna Paanukoski (Finland), Mari Rusanen (Finland), Pekka Vakkari (Finland), Leena Yrjänä (Finland), Daniel Cambon (France), Eric Collin (France), Alexis Ducousso (France), Bruno Fady (France), François Lefèvre (France), Brigitte Musch (France), Sylvie Oddou-Muratorio (France), Luc E. Pâques (France), Julien Saudubray (France), Marc Villar (France), Vlatko Andonovski (FYR Macedonia), Dragi Pop-Stojanov (FYR Macedonia), Merab Machavariani (Georgia), Irina Tvauri (Georgia), Alexander Urushadze (Georgia), Bernd Degen (Germany), Jochen Kleinschmit (Germany), Armin König (Germany), Armin König (Germany), Volker Schneck (Germany), Richard Stephan (Germany), H. H. Kausch-Blecken Von Schmeling (Germany), Georg von Wühlisch (Germany), Iris Wagner (Germany), Heino Wolf (Germany), Paraskevi Alizoti (Greece), Filippos Aravanopoulos (Greece), Andreas Drouzas (Greece), Despina Paitaridou (Greece), Aristotelis C. Papageorgiou (Greece), Kostas Thanos (Greece), Sándor Bordács (Hungary), Csaba Mátyás (Hungary), László Nagy (Hungary), Thröstur Eysteinsson (Iceland), Adalsteinn Sigurgeirsson (Iceland), Halldór Sverrisson (Iceland), John Fennessy (Ireland), Ellen O'Connor (Ireland), Fulvio Ducci (Italy), Silvia Fineschi (Italy), Bartolomeo Schirone (Italy), Marco Cosimo Simeone (Italy), Giovanni Giuseppe Vendramin (Italy), Lorenzo Vietto (Italy), Janis Birgelis (Latvia), Virgilijus Baliuckas (Lithuania), Kestutis Cesnavicius (Lithuania), Darius Danusevicius (Lithuania), Valmantas Kundrotas (Lithuania), Alfas Pliûra (Lithuania), Darius Raudonius (Lithuania), Robert du Fays (Luxembourg), Myriam Heuertz (Luxembourg), Claude Parini (Luxembourg), Fred Trossen (Luxembourg), Frank Wolter (Luxembourg), Joseph Buhagiar (Malta), Eman Calleja (Malta), Ion Palancean (Moldova), Dragos Postolache (Moldova), Gheorghe Postolache (Moldova), Hassan Sbay (Morocco), Tor Myking (Norway), Tore Skrøppa (Norway), Anna Gugala (Poland), Jan Kowalczyk (Poland), Czeslaw Koziol (Poland), Jan Matras (Poland), Zbigniew Sobierajski (Poland), Maria Helena Almeida (Portugal), Filipe Costa e Silva (Portugal), Luís Reis (Portugal), Maria Carolina Varela (Portugal), Ioan Blada (Romania), Alexandru-Lucian Curtu (Romania), Lucian Dinca (Romania), Georgeta Mihai (Romania), Mihai Olaru (Romania), Gheorghe Parnuta (Romania), Natalia Demidova (Russian Federation), Mikhail V. Pridnya (Russian Federation), Andrey Prokazin (Russian Federation), Srdjan Bojovic (Serbia) , Vasilije Isajev (Serbia), Saša Orlovic (Serbia), Rudolf Bruchánik (Slovakia), Roman Longauer (Slovakia), Ladislav Paule (Slovakia), Gregor Bozič (Slovenia), Robert Brus (Slovenia), Katarina Celič (Slovenia), Hojka Kraigher (Slovenia), Andrej Verlič (Slovenia), Marjana Westergren (Slovenia), Ricardo Alía (Spain), Josefa Fernández-López (Spain), Luis Gil Sanchez (Spain), Pablo Gonzalez Goicoechea (Spain), Santiago C. González-Martínez (Spain), Sonia Martin Albertos (Spain), Eduardo Notivol Paino (Spain), María Arantxa Prada (Spain), Alvaro Soto de Viana (Spain), Lennart Ackzell (Sweden), Jonas Bergquist (Sweden), Sanna Black-Samuelsson (Sweden), Jonas Cedergren (Sweden), Gösta Eriksson (Sweden), Markus Bolliger (Switzerland), Felix Gugerli (Switzerland), Rolf Holderegger (Switzerland), Peter Rotach (Switzerland), Marcus Ulber (Switzerland), Sven M.G. de Vries (The Netherlands), Khouja Mohamed Larbi (Tunisia), Murat Alan (Turkey), Gaye Kandemir (Turkey), Gursel Karagöz (Turkey), Zeki Kaya (Turkey), Hasan Özer (Turkey), Hacer Semerci (Turkey), Ferit Toplu (Turkey), Mykola M. Vedmid (Ukraine), Roman T. Volosyanchuk (Ukraine), Stuart A'Hara (United Kingdom), Joan Cottrell (United Kingdom), Colin Edwards (United Kingdom), Michael Frankis (United Kingdom), Jason Hubert (United Kingdom), Karen Russell (United Kingdom), C.J.A. Samuel (United Kingdom).
 

Status of Fagus sylvatica conservation in Europe

Genetic diversity and variation

European beech has high genetic diversity with significant diversity between populations (von Wuehlisch, 2008). However, up to 95 per cent of genetic variability is within populations, which is typical for long-lived wind-pollinated tree species. Continuous forests in pure or mixed stands dominated by beech may have less genetic diversity than fragmented stands in more mixed forests (Rajendra et al., 2014). Therefore, countries with many isolated populations (such as Italy) may have higher genetic diversity and differentiation than those with fewer but larger populations.

High genetic variation offers resilience against pests and diseases and a high potential to adapt to changing environmental conditions and different ecological niches, ensuring survival and adaptation in diverse ecosystems. Even on the leading edge of European beech’s distribution the species is still able to adapt to better suit the changing environmental conditions even in small populations. For example, in the northeastern range of the species some populations have high frost tolerance as a genetic trait (Kramer et al., 2010). Despite future changes brought on by climate change, genetic diversity of European beech is expected to remain stable or even increase within the centre of its distribution (Kramer et al., 2010).

Genetic distribution and clustering

There is significant genetic differentiation among populations due to glaciation, isolation, intensive management, forest degradation, and local adaptation leading to altered genetic variation patterns (Rajendra et al., 2014). Within Europe, northern populations of beech have lower genetic variability than southern populations, possibly because of the short time they have had to differentiate since the last glaciation, glacial refugia being more common in the south, and a greater variety of ecological conditions for beech to grow in the south (Leonardi and Menozzi, 1995).

In Europe, genetic differentiation within populations of beech is higher in Mediterranean populations, while areas such as Bavaria show low levels of genetic variation. In Italy, northern and southern populations are clearly genetically differentiated, with southern populations possessing higher genetic diversity, as might be expected from areas such as Sicily that may have been glacial refugia (Leonardi and Menozzi, 1995). Genetic studies have identified distinct genetic clusters and unique variations in different regions.

Trees within 30 m of each other are more genetically like each other than would be expected from random distribution of genotypes; this is the result of the limited distance of seed dispersal (Vornam, Decarli, and Gailing, 2004). In dense stands, the migration distance of pollen and seeds may be limited to 50 m, one reason being because the heavy fruits of beech limit seed dispersal.

 

The bibliographic review was conducted by James Chaplin of the EUFORGEN Secretariat in August 2024.

Cultivation and human intervention

Despite being managed for centuries, European beech genetic diversity has not been greatly affected by forestry practices due to the dominance of natural regeneration (Rajendra et al., 2014). The genetic diversity in managed stands is comparable to that of natural stands, although spatial structure is less in managed stands and some rare alleles may be lost (Rajendra et al., 2014). However, artificial stands are often clearly differentiated genetically from native stands, originating from different provenances.

Glacial biogeography evolution

Many European populations of beech have common origins from a few glacial refugial populations, although northern Europe may have been recolonized from a single refugial population in the southeast of the continent (Papageorgiou et al., 2007; Rajendra et al., 2014). Genetic studies reveal glacial refugia in the Balkans, southern France, Greece, the Iberian Peninsula, Istria, and Italy, but most European beech originates from populations in southern France and Istria (Papageorgiou et al., 2007). Beech trees in Germany may have originated from one refuge in Slovenia or the eastern alps according to genetic analysis (Rajendra et al., 2014).

 

The bibliographic review was conducted by James Chaplin of the EUFORGEN Secretariat in August 2024.

Fragmentation of forests and changing land-uses can lead to genetic drift, disrupting gene flow and altering mating patters, and affecting the genetic structure of beech forests in Europe (Rajendra et al., 2014). This is especially the case for beech, which prefers land that is good for agriculture and thus is often cleared; this has resulted in a large proportion of beech genetic diversity being lost and populations fragmented (von Wuehlisch, 2008). Fragmented and marginal populations of beech have less allelic richness and greater instances of inbreeding but still the same genetic diversity as more central populations (Rajendra et al., 2014).

Both in situ and ex situ approaches should be used for optimal conservation of the species, with seed collection from years with abundant production. Enough seed should be collected to ensure the widest range of genetic diversity is sampled. Seeds should be collected over large areas to prevent a bias of a few families (von Wuehlisch, 2008). Ex situ methods includes gene reserve forests that should be at least 100 ha to efficiently contain sufficient genetic variability, but seeds collected from smaller fragment populations can be held in smaller forests (von Wuehlisch, 2008).

 

The bibliographic review was conducted by James Chaplin of the EUFORGEN Secretariat in August 2024.

Genetic Characterisation of Fagus sylvatica and its GCUs

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EUFORGEN’s publications

Technical guidelines for genetic conservation and use

Fagus sylvatica - Technical guidelines for genetic conservation and use for European beech

Publication Year: 2008
Author: von Wühlisch, G.

Genetic diversity of beech should be conserved using a mix of in situ and ex situ approaches. For reforestation, the minimum requirement should be that the origin of the reproductive material is known and its adaptive characters should be appropriate for the ecological conditions at the new site. This is especially important in places where beech is to be re-introduced but little knowledge on site-adapted populations exists, e.g. where beech is used to replace maladapted conifer stands that have been planted on former beech sites.

Besides the present regulations for documenting forest reproductive material in trade, a monitoring system for the use of reproductive materials should be applied. Recommendations should be developed on proper use of different materials in the face of climate change, together with transfer guidelines. The EU directive and OECD scheme provide basic regulations on the transfer of reproductive materials. In years with abundant seed production, beech seed should be harvested and stored in sufficient amounts to capture the widest range of genetic diversity.

Beech can usually be conserved in situ in normal stands. In many parts of Europe seed stands alone may not be enough for the conservation of genetic resources of beech. Therefore, there is a need for gene reserve forests. These are natural stands managed to ensure successful natural regeneration, e.g. through thinning and harvesting older trees. The objective is to maintain continuous evolution of a tree population. Such gene reserve forests should cover at least 100 ha in order to contain sufficient genetic variability. For small, locally adapted populations, however, it may be better to establish a large number of smaller reserves.

The establishment of ex situ conservation plantations of beech may be necessary in order to conserve the genetic variation of threatened populations that cannot be maintained at the original site. The objective is to maintain as much as possible of the original genetic variability and to allow continuing adaptation to local conditions. Ex situ conservation stands should cover 2–5 ha, and can be established by planting seedlings or by direct sowing.

Genetic diversity of beech should be conserved using a mix of in situ and ex situ approaches. For reforestation, the minimum requirement should be that the origin of the reproductive material is known and its adaptive characters should be appropriate for the ecological conditions at the new site. This is especially important in places where beech is to be re-introduced but...

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Further reading

Comps, B., Thiébaut, B., Šugar, I., Trinajstić, I., and Plazibat, M. 1991. Genetic variation of the Croatian beech stands (Fagus sylvatica L): spatial differentiation in connection with the environment. Annals of Forest Science, 48(1): 15–28.

‌de Lafontaine, G., Ducousso, A., Lefèvre, S., Magnanou, E., and Petit, R.J. 2013. Stronger spatial genetic structure in recolonized areas than in refugia in the European beech. Molecular Ecology, 22: 4397–4412.

References

Kramer, K., Degen, B., Buschbom, J., Hickler, T., Thuiller, W., Sykes, M.T., and de Winter, W. 2010. Modelling exploration of the future of European beech (Fagus sylvatica L.) under climate change—Range, abundance, genetic diversity and adaptive response. Forest Ecology and Management, 259: 2213–2222.

Leonardi, S. and Menozzi, P. 1995. Genetic variability of Fagus sylvatica L. in Italy: the role of postglacial recolonization. Heredity, 75: 35–44.

Papageorgiou, A.C., Vidalis, A., Gailing, O., Tsiripidis, I., Hatziskakis, S., Boutsios, S., Galatsidas, S., and Finkeldey, R. 2007. Genetic variation of beech (Fagus sylvatica L.) in Rodopi (N.E. Greece). European Journal of Forest Research, 127: 81–88.

Rajendra, K.C., Seifert, S., Prinz, K., Gailing, O., and Finkeldey, R. 2014. Subtle human impacts on neutral genetic diversity and spatial patterns of genetic variation in European beech (Fagus sylvatica). Forest Ecology and Management, 319: 138–149.

Vornam, B., Decarli, N., and Gailing, O. 2004. Spatial distribution of genetic variation in a natural beech stand (Fagus sylvatica L.) based on microsatellite markers. Conservation Genetics, 5: 561–570.

von Wühlisch, G. 2008. European beech. EUFORGEN Technical Guidelines for Genetic Conservation and Use. Maccarese, Italy, International Plant Genetic Resources Institute.