, 2014, this special issue)

Much of the history of movem

, 2014, this special issue).

Much of the history of movement of tree commodity crop germplasm is fairly well documented, since transfers were frequently undertaken for commercial reasons by the European powers during their period of colonial expansion (see Mohan Jain and Priyadarshan, 2009 for information on early germplasm movements for a range of tree commodities). The natural rubber industry in Southeast Asia, for example, was first based on seedlings transferred from Brazilian Amazonia via Kew Botanic Gardens in the United Kingdom to Sri Lanka and Singapore in the 1870s (Gonçalves and Fontes, 2012). Successful www.selleckchem.com/products/AZD2281(Olaparib).html early cultivation of tree commodities in exotic locations was due in part to the escape of crops from the pests and diseases that co-evolved www.selleckchem.com/products/CAL-101.html with them in their centres of origin (Clement, 2004). However, the founder germplasm in major production centres was often introduced before much was known about genetic variation in the crops, so was often suboptimal in performance (Mohan

Jain and Priyadarshan, 2009). With the importance of the production of these commodities for smallholders, further investments in genetic improvement, in the delivery of improved cultivars, and in better farm management, have wide benefits (Mohan Jain and Priyadarshan, 2009). Highly genetically-variable landrace

and wild stands found outside major production centres therefore have an important role to play in future tree commodity crop development, especially with the availability and potential of modern ‘genomic’ breeding techniques (see, e.g., Argout et al., 2011 for cocoa’s draft genome), and the conservation of these genetic resources in forest, farmland and other locations is therefore essential. Coffee Nabilone provides an excellent example of the need for the conservation of forest stands of tree commodity crops, as only approximately 2,000 km2 of high quality Ethiopian montane forest containing wild coffee still remains, due to forest conversion to agricultural land (Labouisse et al., 2008), while future threats also include anthropogenic climate change (Davis et al., 2012; climate change threats to tree genetic resources are explored by Alfaro et al., 2014, this special issue). Wild coffee also exemplifies some of the problems in developing a conservation strategy: in theory, the high value of cultivated coffee should provide a strong incentive to conserve wild stands in Ethiopia, but – as for other tree commodity crops – the ‘disconnect’ between the centre of origin of the crop and the major production centres (Brazil and Vietnam in the case of coffee, Fig.

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