Getting to grips with hairy vetch

A post over at Biofortified entitled “Will cover crops feed the world?” asked an intriguing question:

Why not take a survey of red clover and hairy vetch germplasm, looking for those that fix nitrogen at high rates, have good winter survival, and decay at a reasonable rate to provide fertilizer for crops the following year, and then combine those traits? (And while you’re at it, you could try to do something about hairy vetch’s horrendous seed yield. Non-shattering trait, anyone?)

Well, I thought to myself, maybe you can find those traits already combined. So I looked on Genesys to see what germplasm of Vicia villosa, or hairy vetch, we have to play with. Quite a bit as it turns out: 1374 accessions from 60-odd countries, conserved in 30-odd genebanks. These are the accessions which have georeferences:

I looked in a little more detail at the USDA collection over at GRIN. As luck would have it, there are data on 40-odd accessions from a 2001 evaluation trial. Among the descriptors recorded are N content and winter survival. I downloaded the Excel spreadsheet, and some quick sorting revealed a couple of accessions which are both high in N and have decent winter survival, eg PI 232958 from Hungary and PI 220880 from Belgium. Another dataset shows that some accessions in the collection are non-shattering. Alas, neither of the previous two accessions were characterized for that trait, or at least I couldn’t find the data online, but I was intrigued to see that PI 220879, also from Belgium, is non-shattering.

I posted Biofortified’s question on Facebook too and Dirk Enneking came back almost immediately with more advice:

Provorov and Tikhonovich suggest that the recently domesticated species such as Vicia villosa are better at N-fix. For non-shattering, try the named cultivars such as Ostsaat etc. and grow them where there is sufficient humidity at harvest time to reduce shattering.

Now, where’s my finder’s fee?

Brainfood: OSP adoption, Milk quality, Passport data quality, Historical collections, Sweet potato domestication, African veggies, Baobab diversity and domestication, Cassava diversity, Strawberry breeding, Barley GWA, Pest symbionts, Maize diversity and climate change

Conservation status of European crop wild relatives assessed

The latest IUCN assessment of the conservation status of European biodiversity is out, and is making the news. The bit on plants is co-authored by Melanie Bilz, Shelagh P. Kell, Nigel Maxted and Richard V. Lansdown and, unsurprisingly perhaps given their track record, includes, I believe for the first time, extensive discussion of crop wild relatives as a distinct class. ((Other classes of plants dealt with in detail are those “listed in European and international policy instruments” and aquatic plants.)) The authors, which coordinated input from dozens of experts, conclude that out of a total of 591 CWR species:

Within the EU 27, at least 10.5% of the CWR species assessed are threatened, of which at least 3.5% are Critically Endangered, 3.3% Endangered and 3.8% Vulnerable – in addition, 4.0% of the species are considered as Near Threatened. One species, Allium jubatum, is Regionally Extinct within Europe and the EU; it is native to Asiatic Turkey and Bulgaria, but has not been found in Bulgaria since its original collection in 1844.

It does not even seem to be available from botanic gardens, according to Botanic Gardens Conservation International’s database. I don’t know what has caused its disappearance in Bulgaria, but currently the main threats to CWRs seem to be intensified livestock farming, tourist development and invasives:

And there are maps ((Which I hope are available in versions one can import into Google Earth, but I haven’t looked into this yet.)) of both the distribution of overall CWR species richness and of the most threatened species:

An extremely useful review is provided of previous work assessing the extent to which CWRs are conserved in genebanks, botanical gardens and protected areas in Europe. But here perhaps I would like to quibble with the authors. Although their listing of existing conservation efforts seems to me thorough and comprehensive, there is no attempt made to synthesize the results of all the different initiatives and come up with a list, however preliminary, of high priority plants for immediate conservation intervention. Surely it would not have been particularly difficult to cross-reference their list of threatened species with listings of accessions in Eurisco and the BGCI database, for example. Maybe this was beyond the scope of this particular exercise and is the focus of parallel work. Perhaps Nigel or Shelagh will respond here.

This is a very important contribution to raising the profile of CWRs within the biodiversity conservation community. Let us hope that it will translate into increased support for their conservation, both ex situ and in situ, along the lines so usefully set out by the authors in their recommendations.