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Assessing trends in genetic diversity to inform in 
situ conservation strategies for crop wild relatives 
Thormann I, Fiorino E, Dulloo ME 
4th International Symposium on Plant Genetic Resources: Genetic Resources for Climate Change at 29th 
International Horticultural Congress, 17 - 22 August 2014, Brisbane, Australia
2 
Crop wild relatives (CWR) 
Crop wild relatives are increasingly important for present 
and future agricultural development, as they 
provide adapted genes and traits for crop 
improvement, even more so under changing climate. 
(Hajjar and Hodgkin 2007; Maxted et al. 2012, McCouch, 2013; Dempewolf et al, 2014, etc)
3 
Why is in situ conservation of crop wild relatives 
important? 
• To allow for crop wild relatives populations to continue to 
evolve in their natural habitats and adapt to changing 
environmental conditions; 
• To capture the evolving traits in crop wild relatives that might 
be useful for plant breeders and farmer for current and future 
use
4 
Developing in situ conservation strategies 
• Overview of diversity and current conservation/threat status 
• Prior knowledge about population structure, demography, 
distribution of genetic diversity in target species across their 
areas of occurrence; 
• Access to these information is important to develop in situ 
conservation strategies management plans and Strategic 
Action Plans 
• Inform policymakers of what conservation interventions are 
required for effective management and monitoring of target 
populations
5 
Assessing and monitoring trends and loss in 
genetic diversity 
• Requires knowledge about existing diversity 
• Temporal dimension: at least 3 data points are needed or 
historical information known 
• Potential sources: 
Plant germplasm collections 
can provide past snapshots 
of diversity and data for 
re-collection for assessment 
of current diversity 
• One example: Bioversity International’s 
collecting missions database 
http://bioversity.github.io/geosite/
• 1000 collecting trips between 1975 and 2012 
• 226,618 samples collected, of which ca. 85% between 1975- 
6 
Bioversity International collecting missions 
database 
1995 
• 27% of collected samples are 
wild species 
• 25% of trips collected 
only wild species 
• Passport data and collecting 
mission reports for most 
samples available
7 
Crop wild relatives’ samples in Bioversity 
International’s Collecting Database 
• 60,000 (27%) of collected 
samples are wild species 
collected from 115 different 
countries 
• 73% of wild samples are geo-referenced 
• Numerous examples of 
– groups of species collected 
from the same country 
– single species collected from 
several countries 
53.20% 
7.60% 
10.40% 
7.60% 
9.40% 
11.80% 
Forages Cereals Legumes 
Roots and Tubers Vegetables Others
8 
CWR samples in Bioversity International’s Collecting 
Missions Database 
Group of species collected from same country: forage legumes in Syria 
Note: shows only species for which more than 50 geo-referenced samples were collected during a collecting trip
9 
CWR samples in Bioversity International’s Collecting 
Missions Database 
Single species collected from several countries: Prosopis africana in Africa 
Note: shows only species for which more than 50 geo-referenced samples were collected during a collecting trip
10 
Potential applications 
Fills data gap for CWR diversity assessment studies 
Unique link between original passport data, additional collecting 
documentation and genebank accession numbers allows to: 
• Identify coherent set of samples/sites collected at the same 
time/way (historic snapshot of diversity) 
• Re-visit old collecting sites and re-sample CWR 
• Retrieve original material in genebanks 
• Assess temporal variation in genetic diversity and current 
vulnerability and threat 
• Inform conservation actions 
• Comparative studies among species and different eco-geographic 
realities 
• Investigate effects of climate change 
Original 
passport data 
corresponding 
genebank 
accession 
original 
collecting 
documentation 
Example 
• No changes in varietal diversity at national level 
• Significant shift in adaptive traits: shorter life cycle, reduction in plant 
and spike size
11 
Successful implementation: re-collection of barley in 
Jordan 
• In 2012 re-visited the sites where wild barley 
and LRs were collected in 1981 
– Verified collecting sites based on 
coordinates and location description 
– Re-collected wild barley from 32 old sites 
– Collecting of wild barley samples also from 
additional sites in reserves 
– Re-collected landraces from 26 old sites 
Verification with Google earth and gazetteers
12 
Tracking of 1981 samples: distribution and conservation 
of samples in genebanks 
ICARDA 
Syria 
NordGen 
Sweden 
NCARE 
Jordan 
July 1982 
LR in1981; CWR in 1982; about 50-60 g/acc 
repatriation after 1996; 
100 seeds/acc? 
R = 1- 2 
LR in 1985 or 1996; 
CWR in 1994. R = 2 for 
some CWR 
R = 0 
never integrated in 
collection, kept in freezers 
R = 0 
R = regeneration or multiplication cycles 
LR = landrace 
CWR = crop wild relative 
IPK 
Germany 
transfer in 
2012 
Jordan? 
??
13 
Common garden in IPK – growing season 2013 
• Growing season 2013 
• Wild barley and landrace samples from 1981 
and 2012 + 5 control accessions 
• Leaf tissue and phenotypic trait data collection 
on 16 individuals per accession
14 
Preliminary results from re-collecting trip and common 
garden 
• In most sites wild barley populations are still there, however 
– at the Eastern border of the collecting area some sites have become too dry 
(both for wild barley and landraces) 
– Small residual populations where barley cultivation is abandoned due to 
land use change or change from cereal cultivation to orchards 
– Barley still growing on field margins of barley fields like in 1981 
• Wild barley populations thrive better in disturbed habitats, significantly smaller 
in undisturbed habitats. 
• Wild barley populations are taller and have more tillers in 1981 compared to 
2012 
• Growth habit is prevalently prostrate in 1981 while intermediate growth habit 
dominates in 2012 samples. 
• No significant difference in days to heading and maturity 
• Molecular markers studies on all the samples and accessions are currently 
ongoing
Thank you

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Assessing genetic diversity trends in crop wild relatives informs conservation strategies

  • 1. Assessing trends in genetic diversity to inform in situ conservation strategies for crop wild relatives Thormann I, Fiorino E, Dulloo ME 4th International Symposium on Plant Genetic Resources: Genetic Resources for Climate Change at 29th International Horticultural Congress, 17 - 22 August 2014, Brisbane, Australia
  • 2. 2 Crop wild relatives (CWR) Crop wild relatives are increasingly important for present and future agricultural development, as they provide adapted genes and traits for crop improvement, even more so under changing climate. (Hajjar and Hodgkin 2007; Maxted et al. 2012, McCouch, 2013; Dempewolf et al, 2014, etc)
  • 3. 3 Why is in situ conservation of crop wild relatives important? • To allow for crop wild relatives populations to continue to evolve in their natural habitats and adapt to changing environmental conditions; • To capture the evolving traits in crop wild relatives that might be useful for plant breeders and farmer for current and future use
  • 4. 4 Developing in situ conservation strategies • Overview of diversity and current conservation/threat status • Prior knowledge about population structure, demography, distribution of genetic diversity in target species across their areas of occurrence; • Access to these information is important to develop in situ conservation strategies management plans and Strategic Action Plans • Inform policymakers of what conservation interventions are required for effective management and monitoring of target populations
  • 5. 5 Assessing and monitoring trends and loss in genetic diversity • Requires knowledge about existing diversity • Temporal dimension: at least 3 data points are needed or historical information known • Potential sources: Plant germplasm collections can provide past snapshots of diversity and data for re-collection for assessment of current diversity • One example: Bioversity International’s collecting missions database http://bioversity.github.io/geosite/
  • 6. • 1000 collecting trips between 1975 and 2012 • 226,618 samples collected, of which ca. 85% between 1975- 6 Bioversity International collecting missions database 1995 • 27% of collected samples are wild species • 25% of trips collected only wild species • Passport data and collecting mission reports for most samples available
  • 7. 7 Crop wild relatives’ samples in Bioversity International’s Collecting Database • 60,000 (27%) of collected samples are wild species collected from 115 different countries • 73% of wild samples are geo-referenced • Numerous examples of – groups of species collected from the same country – single species collected from several countries 53.20% 7.60% 10.40% 7.60% 9.40% 11.80% Forages Cereals Legumes Roots and Tubers Vegetables Others
  • 8. 8 CWR samples in Bioversity International’s Collecting Missions Database Group of species collected from same country: forage legumes in Syria Note: shows only species for which more than 50 geo-referenced samples were collected during a collecting trip
  • 9. 9 CWR samples in Bioversity International’s Collecting Missions Database Single species collected from several countries: Prosopis africana in Africa Note: shows only species for which more than 50 geo-referenced samples were collected during a collecting trip
  • 10. 10 Potential applications Fills data gap for CWR diversity assessment studies Unique link between original passport data, additional collecting documentation and genebank accession numbers allows to: • Identify coherent set of samples/sites collected at the same time/way (historic snapshot of diversity) • Re-visit old collecting sites and re-sample CWR • Retrieve original material in genebanks • Assess temporal variation in genetic diversity and current vulnerability and threat • Inform conservation actions • Comparative studies among species and different eco-geographic realities • Investigate effects of climate change Original passport data corresponding genebank accession original collecting documentation Example • No changes in varietal diversity at national level • Significant shift in adaptive traits: shorter life cycle, reduction in plant and spike size
  • 11. 11 Successful implementation: re-collection of barley in Jordan • In 2012 re-visited the sites where wild barley and LRs were collected in 1981 – Verified collecting sites based on coordinates and location description – Re-collected wild barley from 32 old sites – Collecting of wild barley samples also from additional sites in reserves – Re-collected landraces from 26 old sites Verification with Google earth and gazetteers
  • 12. 12 Tracking of 1981 samples: distribution and conservation of samples in genebanks ICARDA Syria NordGen Sweden NCARE Jordan July 1982 LR in1981; CWR in 1982; about 50-60 g/acc repatriation after 1996; 100 seeds/acc? R = 1- 2 LR in 1985 or 1996; CWR in 1994. R = 2 for some CWR R = 0 never integrated in collection, kept in freezers R = 0 R = regeneration or multiplication cycles LR = landrace CWR = crop wild relative IPK Germany transfer in 2012 Jordan? ??
  • 13. 13 Common garden in IPK – growing season 2013 • Growing season 2013 • Wild barley and landrace samples from 1981 and 2012 + 5 control accessions • Leaf tissue and phenotypic trait data collection on 16 individuals per accession
  • 14. 14 Preliminary results from re-collecting trip and common garden • In most sites wild barley populations are still there, however – at the Eastern border of the collecting area some sites have become too dry (both for wild barley and landraces) – Small residual populations where barley cultivation is abandoned due to land use change or change from cereal cultivation to orchards – Barley still growing on field margins of barley fields like in 1981 • Wild barley populations thrive better in disturbed habitats, significantly smaller in undisturbed habitats. • Wild barley populations are taller and have more tillers in 1981 compared to 2012 • Growth habit is prevalently prostrate in 1981 while intermediate growth habit dominates in 2012 samples. • No significant difference in days to heading and maturity • Molecular markers studies on all the samples and accessions are currently ongoing

Editor's Notes

  1. Difference between collecting mission and collecting trip in the context of the IBPGR missions: A collecting mission often took place in different countries and/or different time periods. Collecting missions were therefore subdivided in single collecting trips, each collecting trip identified by a single target country and a specific collecting period. Passport data and mission reports exist for about 80% of the samples
  2. Last two bullets introduce following slides. The following slides are examples of groups of CWR collected from one country or a single species collected from different countries.
  3. CN390F – Jordan 1981 Distribution to NordGen probably via Syrian National Program/genebank 100 seeds per accession for repatriation: this is the quantity that Bilal assumes as standard. Repatriation to Jordan probably in 1999?
  4. Other countries where wild barley was collected was in Greece and Turkey.