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iForest -Biogeosciences and Forestry
IntroductionIn the first half of the 20 th century, the first Dutch elm disease (DED) pandemic caused a massive loss of elms in Europe and North America. The much more aggressive O. novo-ulmi Brasier took the place of the causal agent, Ophiostoma ulmi (Buisman) Nannf., in the second half of the century. The second pathogen has caused the disappearance of adult elms in many European and North American locations (Brasier & Kirk 2010). O. novo-ulmi is almost impossible to control through chemical, biological or silvicultural methods due to its high virulence and highly effective transmission via small beetles of the Scolytus and Hylorgopinus genera (Webber 2000). Tolerant elm genotype selection and breeding has been the most successful strategy for elm recovery, particularly in urban environments , 2011, Solla et al. 2005a. The Spanish elm breeding and conservation programme began in 1986 as the result of an agreement between the Spanish Environmental Administration and the Technical University of Madrid School of Forestry Engineering. Its two main objectives were to conserve remaining elm genetic resources and to transmit their variability to future generations of tolerant elms obtained through breeding; i.e., hybridisation of selected progenitors (native or tolerant Asian elms) to obtain tolerant trees with the appearance of native elm species.The first elm breeding programme began in the Netherlands in 1928 (Heybroek 1993) and was followed by several programmes in the United States and various European countries Santini et al. 2011, Buiteveld et al. 2014. As a result of crossing these species with native elms, a wide range of hybrid clones of varying tolerance levels and genetic backgrounds is now available on the market. The Spanish programme took advantage of the knowledge, methodologies and plant materials previously developed by the Dutch and Italian programmes. In the first 14 years, U. pumila was used as the main source of resistance, giving rise to 10 crossings tolerant to O. novo-ulmi (Solla et al. 2000). The tolerance of these crossings was tested in clone replicates (N > 16) over several years at various locations, and clone adaptation to different environments in Spain was evaluated. Five crossings with Asian background were recently selected to be released onto the market for ornamental use.In the 1990s the Spanish programme included some native elms, mainly U. minor, in the O. novo-ulmi susceptibility trials. In the following decade the programme focused mainly on selecting native elms. This new strategy complied with European and Spanish legislation governing the quality and genetic background of forest reproductive materials for production and marketing. In the European Union, forest reproductive materials are governed by Council Directive © SISEF http://www.sisef.it/iforest/ 172 iForest (2015) 8: 172-180