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Darius D. and consortium

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1 Darius D. and consortium
This project has received funding from the European Union’s Horizon 2020 research and innovation programme under grant agreement No

2 General info Start date:1st March 2016 Duration: 48 months Budget: 7.9 million Euro (with a 6.7 Million Euro grant from the European Union) Project officer: Silvia Gemini, Research Executive Agency (REA) Coordinator: Dr. Bruno Fady, INRA, France

3 Overall concept and expected impact
Provide the European forestry sector with better knowledge and new tools for efficient management and sustainable use of FGR in the context of environmental change and evolving societal demands. expand the current scientific knowledge on how genetic diversity, phenotypic trait diversity and environmental diversity co-vary over multiple spatial scales, inform on the genetic basis of phenotypic trait variability and plasticity, characterise in-situ and ex-situ conservation units and underused natural resources, and produce models of future species distribution usable for FGR management under diverse policy and environmental scenarios.

4 Partners Institut national de la recherche agronomique (INRA), France Agencia Estatal Consejo Superior de Investigaciones Científicas (CSIC), Spain Uppsala Universitet (UU), Sweden Aristotle University of Thessaloniki (AUTH), Greece European Forest Institute (EFI), Finland Bioversity International, Italy Philipps-Universität Marburg (PUM), Germany Consiglio Nazionale delle Ricerche (CNR), Italy Instituto Nacional de Investigación y Tecnología Agraria y Alimentaria (INIA), Spain University of Oulu (UOULU), Finland IGA Technology Services (IGATS), Italy Norwegian Institute for Bioeconomy Research (NIBIO), Norway Forestry Research Institute of Sweden (Skogforsk), Sweden Johann Heinrich von Thünen Institute (THÜNEN), Germany Bavarian Office for Forest Seeding and Planting (ASP), Germany The Natural Environment Research Council (NERC), Great Britain Aleksandras Stulginskis University (ASU), Lithuania INRA Transfert (IT), France Swiss Federal Institute for Forest, Snow and Landscape Research (WSL), Switzerland Russian Academy of Sciences (RAS), Russia Radiata Pine Breeding Co Ltd (RPBC), New Zealand LIECO Gmbh & Co KGH (LIECO), Austria

5 Ex-situ collections in Europe
Investigated species Tree species Distribution Major threats to FGR Ex-situ collections in Europe Nb in-situ DCUs Abies alba Alp, Con Climate change, habitat loss AT, DE, FR, GR 318 Betula pendula Atl, Bor, Con Habitat loss, grazing FI, GB, LT, NO, SE 50 Fagus sylvatica Atl, Alp, Con, Med Climate change DE, ES, FR, IT, GB, SE 469 Picea abies Alp, Bor, Con Climate change, pests AT, DE, FI, FR, IT, LT, NO, SE 471 Pinus cembra Alp Fragmentation, habitat loss AT 56 Pinus halepensis Med Forest fire ES, FR, IT, GR 26 Pinus nigra Alp, Con, Med Habitat loss, hybridization DE, ES, FR, GR 145 Pinus pinaster Atl, Med Forest fire, pests 42 Pinus sylvestris Alp, Bor, Con, Med DE, ES, FI, FR, LT, NO, SE 313 Populus nigra DE, ES, FR, IT 30 Quercus petraea Atl, Con Pests, hybridization AT, DE, FR, NO 250 Taxus baccata Alp, Atl, Con, Med ES, IT

6 In-situ and ex-situ collections

7 Work packages Network of permanent plots Phenotyping protocols
Extension Genotyping protocols

8 WP3 WP6 WP1 WP4 WP2 WP5 EU FGR database for conservation and use
Papers and conferences for the scientific community Species / FGR distribution models WP3 Physiologically relevant phenotypes Current and potential strengths and weaknesses in the EU FGR conservation network Website and online resources Knowledge, models and tools on local adaptation GenTree nested experimental sampling strategy European wide network of permanent plots WP6 WP1 Tools for sustainable FGR breeding and conservation Workshops for stakeholders WP4 Next Generation genotypes Simple phenotyping and genotyping in collections and in-situ WP2 GenTree stakeholder platform Training courses Links between work packages FGR-friendly policy options New gene and phenotype sampling strategies for conservation and breeding WP5 Good Practices material Economic effects of FGR-friendly regulations Models for FGR-friendly sylviculture FGR monitoring scheme

9 WP1 Innovative conservation strategies
Task1.1 Improving the European in-situ conservation network and ex-situ collections (using provenance data). Task 1.2 Characterization of in-situ collections for 12 species x 1000 trees (genotyping based on a few relevant SNPs across species) Task1.3. Bioversity. Identification of gaps in in situ conservation and of original resources for breeding Task 1.4. ASP Test of strategies and methods for monitoring: which markers, traits, environmental factors (on 2 to 4 model species)

10 WP2 Innovative breeding strategies
Task2.1 Inventory & validation of advanced high throughput phenotyping (NIR etc.) Task 2.2 Design and implementation of allele and genotype sampling strategies to enrich breeding programs Task 2.3 Development of cost- and time-effective breeding strategies and methods Task 2.4 Improvement of genetic diversity management in intensive advanced breeding programs to prevent the decrease of genetic diversity in FRM

11 WP4 - Quantification of key demographic and selection processes affecting genomic diversity
• Create a next-generation genetic diversity map for 7 key European forest tree species, identifying life-history traits and population features associated with high levels of genetic diversity. • Associate genetic variation to environmental variables. • Infer past population transfers and demography. • Use a multi-scale (from local to species-wide) sampling scheme to infer the spatial scale of gene flow and local adaptation and identify alleles under local adaptation.

12 Sampling protocol The sampling protocol provides step-by-step detailed requirements of traits to measure, data to record about the sites and individual trees, wood and leaf material to sample and describes how to prepare the material for DNA sequencing. Photo: Sampling in Finland. Credit: Tanya Pyhäjärvi

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14 Sampling of trees

15 Sampling of trees A total of 12 species are sampled in the project. For each species, trees are sampled in 10 sites. In each site a pair of populations is selected for sampling, within the same type of landscape. The two populations in a pair consist of 25 trees each, and are located at two opposite ends of a the specific ecological gradient which is being investigated. Countries where the sampling is ongoing are: Austria, Finland, France, Germany, Greece, Italy, Lithuania, Norway, Russia, Spain, Sweden, Switzerland, United Kingdom. Photo: Populus nigra in Rio Alberche (Spain). Credit: Barbara Carvalho/CSIC

16 ASU Task 1.4 Genetic monitoring Task 2.1 High throughput phenotyping Task 1.1 Provenance modeling Task 3.3. Seeding experiment

17 Phenology scoring in a Scots pine seed orchard
The on-land scoring scale female Phenology scoring in a Scots pine seed orchard 8 m 16 m 24 m In spring 2017 at 4 occasions, we scored on-land phenology of vegetative, male and female buds of 25 clones At each scoring, we flew a drone at 3 altitudinal modes to photograph these clones at variable resolution Image analysis on going Which areal mode gave the closest scores to the on land measurements?

18 M&M phenology scores and seed color variation between the clones by “targeted RGB method”
Identifying RGB range for current year cones/shoots/strobili at the pixel level Calculating % of pixels within this RGB interval from the toal number of pixels outlined by freehand tool in a crown Problems: error due to similar colors of twigs, then perhaps small squares of equal size can be used instead of the freehand tool Image taken at 4 m above the crowns

19 Cone yield in mature stands of Scots pine
Important for forecasting seed crops on tall trees, seed trees for natural regeneration Counting cones manually on an image segment on the crown section with the greatest cone yield In spring 2017, we flew drone over mature stands at variable H, resolution Testing image analysis: counting an 1, 2, 3 squares Image at 10 m above the crowns

20 Identification of population of Scots pine based on airplain fitted NIR spectroscopy
Equipment: Bekas Ch-32 ultralight aircraft, cruising speed 100 km/hour, altitude 700 m and RIKOLA hyperspectral, operating in the spectral range from 500 to 900 nm, spectral interval 1 nm, connection with RGB/CIR camera for improved object identification (NIKON D800E, RGB/NIR configuration, 28 or 50 mm) lenses. ASU, Lithuania Problem & aims IS NIR able to identify different populations of Scots pine ? Can NIR be used as a fast estimate for genetic diversity? Aim was to run spectroscopy analysis on NIR areal images of provenance trial of distant populations of Scots pine The objective of the study was to investigate capability of the aerial NIR imaging for separation of Scots pine populations based on the spectral image analysis. Pixelmaped crows of a tree from Bashkiria provenance (left) and Kostroma (right) at 0.7 km altitude (ca. 25 pixels per tree)

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22 http://www.gentree-h2020.eu/ @GentreeProject
More information @GentreeProject


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