INTERACTIVE TOOLKIT FOR
CROP WILD RELATIVE CONSERVATION PLANNING version 1.0
Why link conservation to use?
Some conservationists argue that conservation is an end in itself, that all species have intrinsic value and therefore have a right to be conserved for their own sake irrespective of their value to humankind. We consider this argument well-meaning but mistaken in the case of PGRFA, for the following reasons:
Therefore, conservation of PGRFA and its sustainable utilization is intimately linked. This linkage forms the basis for enduring human food security and well-being, and ultimately the continuing survival of humankind itself.
CWR are defined by their potential for utilization, i.e. the ability of CWR to donate useful traits to crops. The CBD (2010) emphasizes the need to link conservation to use, noting that utilization should be "sustainable" and "meet the needs and aspirations of present and future generations". Maxted and Kell (2009) reviewed the use of CWR in crop improvement for 29 major crops and noted the following points:
The review concludes that there is a wealth of novel traits available for crop improvement in CWR and so far the vast majority of CWR diversity is untapped in terms of its potential utilization value. Also see Some examples of CWR use in crop improvement [2].
There are numerous ways in which the use of CWR diversity for crop improvement can be promoted, but traditionally this has focused on identifying traits of interest through phenotypic characterization and evaluation. However, in many cases this has proved prohibitively expensive. The First SoW Report (FAO 1998) highlights the fact that two thirds of globally conserved ex situ germplasm lacks basic passport data, 80% lacks characterization data and 95% lacks evaluation data, making the use of such germplasm—including CWR germplasm—much more difficult than it need be. The SoWPGR-2 (FAO 2010) details several new international initiatives since 1998 that support the increased characterization and evaluation of germplasm, including the fairly widespread adoption of core collections that are adequately characterized and evaluated. However, it still concludes that “the country reports were virtually unanimous in suggesting that one of the most significant obstacles to a greater use of PGRFA is the lack of adequate characterization and evaluation data and the capacity to generate and manage such data”.
The bottleneck of systematic characterization and evaluation has been acknowledged almost since the late 1960s and early 1970s when the need for their conservation was recognized (Frankel and Bennett, 1970). It could be argued that simply increasing the amount of ‘traditional’ characterization and evaluation is unlikely to result in the required step change in the exploitation of CWR diversity. However, novel techniques such as ‘next generation technologies’—that enable the screening of thousands of samples of germplasm for interesting gene variants that are adaptively important (Nordborg and Weigel 2008)—and ‘predictive characterization’—where spatial analysis of germplasm passport data is used to predict which germplasm accessions might have desired traits (see Bhullar et al. 2009, Thormann et al. 2014)—offer an alternative to conventional characterization and evaluation. Ultimately, the use of conserved CWR (and indeed of all PGRFA) diversity is not likely to improve unless the professionals involved with CWR conservation can ensure that conserved germplasm is more accessible to breeders and other user groups, removing the barrier between conservation and use.