To learn more about the map elements, please download the "Pan-European strategy for genetic conservation of forest trees"
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 Juniperus communis conservation in Europe
Within-population genetic diversity tends to be higher than between-population genetic diversity in common juniper. Many individuals show 50% similarity with individuals in the population. This is very low and reflects the high level of diversity in the species; almost all show no more than 70% similarity (Van Der Merwe et al., 2000).
Populations in the UK were found to be highly genetically diverse and varied, with greater within-population genetic diversity. However, southern populations in the UK are declining, fragmented, and have lower genetic variability (Van Der Merwe et al., 2000). Populations in Germany, Norway, Slovakia, and Italy showed high genetic diversity and low genetic differentiation between populations (Reim et al., 2016). Low levels of genetic differentiation were found in Dutch and German populations, but higher genetic differentiation and variation found in Irish populations may indicate they are more isolated (Reim et al., 2016; Jacquemart et al., 2020). Genetic variation has been shown to be high even in small populations in common juniper; this is not unusual for long-lived tree species. However, it does show the significant value even small populations have in their genetic variability (Jacquemart et al., 2020).
Common juniper does not show a correlation between geographic distance and genetic variance across most of its range (Reim et al., 2016). Genetic variation between populations of common juniper may be related to the differing habitats. Genetic clusters and the north/south separation in common juniper in Lithuania were linked with lowland coastal populations displaying significantly higher diversity than mountain populations; differences in genetic diversity between populations were significant only for populations found in very different habitats (Vilcinskas et al., 2016).
Irish and English populations also exhibit some geographic structuring, which could be an indicator of different postglacial migration routes from multiple sources for populations in the British Isles (Jacquemart et al., 2020). Central European populations are derived from historically larger and more related and interconnected populations with higher genetic diversity, and thus do not show geographic structuring like that found in the British Isles (Jacquemart et al., 2020).
High genetic diversity, low genetic differentiation, and the negligible spatial structure of common juniper populations may originate from high gene flow frequency between populations (Reim et al., 2016). However, despite being wind pollinated and a gymnosperm (which typically have higher levels of gene flow than angiosperms), the species is still characterized by short-distance pollen dispersal and has little effective gene flow (Jacquemart et al., 2020).
The bibliographic review was conducted by James Chaplin of the EUFORGEN Secretariat in August 2024.
Common juniper was an early colonizer of postglacial landscapes (Van Der Merwe et al., 2000). However, genetic analysis reveals an absence of a correlation between genetic structure and geographical patterns across much of the species' range in central Europe, which suggests a periglacial survival of common juniper (Reim et al., 2016). Common junipers’ tolerance of poor soils, low temperatures, and drought conditions allows it to survive on cold steppe biomes. Therefore, it is one of the few tree species that survived in central Europe during the last glacial maximum (Michalczyk et al., 2010). Its survival in periglacial environments likely also contributed to its high genetic diversity.
The bibliographic review was conducted by James Chaplin of the EUFORGEN Secretariat in August 2024.
Despite a wide distribution, the population of common juniper has been declining for decades and the species is now threatened in many parts of Europe. Small remnant populations and poor natural regeneration are recognized as the main threats to the long-term preservation of the species (Jacquemart et al., 2020). However, typical juniper habitats such as heathlands and calcareous grassland are sharply declining due to land-use change (Reim et al., 2016). The separation of the species into sexes also halves the density of potential pollen donors and seed-producing individuals (Reim et al., 2016).
Existing populations show little natural sexual regeneration and many of them are ageing. In natural populations only around 1% of seeds germinate after up to five winter seasons (Jacquemart et al., 2020). The poor reproductive ability of common juniper and unsuitable local conditions, which offer offspring low chances of survival, explain the excess of aged individuals in populations (Reim et al., 2016). Aging individuals and declining populations are a concern because the proportion of viable seeds produced by female plants reduces as common juniper becomes older (Van Der Merwe et al., 2000). Low regeneration and fragmentation of common juniper populations will impact genetic diversity and genetic structure of the remaining populations (Reim et al., 2016).
Populations of common juniper need to be assessed for genetic diversity and management strategies should be directed to ensuring that the variety of both common and rare habitats is maintained (Vilcinskas et al., 2016). Care of existing habitats and reintroduction of young common juniper plants to existing populations would improve the long-term preservation of this species (Reim et al., 2016). Management actions such as creating openings in old, closed shrub canopies, reducing competition from other species, or protection against herbivores should be considered to optimize seed germination and the survival of the saplings (Jacquemart et al., 2020). Connectivity between populations might be restored by creating linking populations in areas such as field edges or under power-supply lines (Jacquemart et al., 2020).
The bibliographic review was conducted by James Chaplin of the EUFORGEN Secretariat in August 2024.
Genetic Characterisation of Juniperus communis and its GCUs
Availability of FRM
Conifers Network: Report of the first meeting
Conifers Network: Report of the second and third meeting
Conifers Network: Report of the fourth meeting
Contacts of experts
NA
Further reading
Oostermeijer, J.G.B. and De knegt, B. 2004. Genetic population structure of the wind-pollinated, dioecious shrub Juniperus communis in fragmented Dutch heathlands. Plant Species Biology, 19: 175–184. https://doi.org/10.1111/j.1442-1984.2004.00113.x
References
Jacquemart, A.L., Buyens, C., Delescaille, L.M., and Van Rossum, F. 2020. Using genetic evaluation to guide conservation of remnant Juniperus communis (Cupressaceae) populations. Plant Biology, 23: 193–204. https://doi.org/10.1111/plb.13188
Michalczyk, I.M., Opgenoorth, L., Luecke, Y., Huck, S., and Ziegenhagen, B. 2010. Genetic support for perglacial survival of Juniperus communis L. in Central Europe. The Holocene, 20: 887–894. https://doi.org/10.1177/0959683610365943
Reim, S., Lochschmidt, F., Proft, A., Tröber, U., and Wolf, H. 2016. Genetic structure and diversity in Juniperus communis populations in Saxony, Germany. Biodiversity: Research and Conservation, 42: 9–18. https://doi.org/10.1515/biorc-2016-0008
Van Der Merwe, M., Winfield, M.O., Arnold, G.M., and Parker, J.S. 2000. Spatial and temporal aspects of the genetic structure of Juniperus communis populations. Molecular Ecology, 9(4): 379–386. https://doi.org/10.1046/j.1365-294x.2000.00868.x
Vilcinskas, R., Jociene, L., Rekasius, T., Marozas, V., Paulauskas, A., and Kupcinskiene, E. 2016. Genetic diversity of Lithuanian populations of Juniperus communis L. in relation to abiotic and biotic factors. Dendrobiology, 76: 61–71. https://doi.org/10.12657/denbio.076.006