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Development and use of molecular markers for characterisation of Forest Genetic Resources and for Breeding : a case study, Black poplar (Populus nigra L.)

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HAL Id: hal-02789398

https://hal.inrae.fr/hal-02789398

Submitted on 5 Jun 2020

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Development and use of molecular markers for characterisation of Forest Genetic Resources and for Breeding : a case study, Black poplar (Populus nigra L.)

Véronique Jorge

To cite this version:

Véronique Jorge. Development and use of molecular markers for characterisation of Forest Genetic Resources and for Breeding : a case study, Black poplar (Populus nigra L.). Master. Advanced Studies in Environmental Interactions (DPPS-105) 2018: Engineered Plant Immunity, 2018. �hal-02789398�

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Development and use of molecular markers for

characterisation of Forest Genetic Resources and for

Breeding : a case study, Black poplar (Populus nigra L.)

(3)

.02

SUMMARY

1. Populus nigra: biology, interest

2. Molecular marker development and genotyping

3. Characterization of Genetic resources

a. Structuration of diversity

b. Clonality

c. Gene flow

(4)

Populus nigra

A key species

_01

(5)

.04

Major component of riparian forests in

Europe

Wind pollinated dioecious species

(6)

.05

Threats

Agriculture

Confinement of rivers, dams regulation (no flood)...

Gene flow from cultivated poplars

Villerest dam (France)

Loire River at Orléans

(7)

.06

Use for breeding interspecific cultivated hybrids

Euramerican hybrids

Interamerican hybrids

© A.Dowkiw, INRA Orléans

© A.Dowkiw, INRA Orléans © A.Dowkiw, INRA Orléans

(8)

.07

Black poplar (Populus nigra L.)

Conservation program at national and European level

** * * * * * * * * * * 12 Réserves naturelles

(9)

Marker development

(10)

.09 RFLP SNP AFLP RAPD Microsatellites ISSR Sequence # of repetitions

Molecular

criteria (type of polymorphism) AFLP, AP-PCR, CAPS, DAF,

DGGE, ISSR, MAAP,

tecMAAP, RAPD, RFLP, SCAR, SNP, SSR, STS, VNTR …… ZZZZ Codominant markers Revealed individually Dominants markers Revealed massively

Genetic

criteria

(11)

.010

SSR

AGAGAGAGAGAGAGAGAGAGAG TCTCTCTCTCTCTCTCTCTCTC AGAGAGAGAGAGAGAGAG TCTCTCTCTCTCTCTCTC AGAGAGAGAG TCTCTCTCTC Genotyping Many techniques

Biallelic, seveal millions (in poplar 1 SNP/ 90 pb) Multiallelic, ~4000 available on the reference

genome Populus trichocarpa

(fig. genome studio)

SNP

Allèle 1 Allèle 2 Allèle 3 Allèle « nul » …

(12)

.011

Development of SNP markers:

2 steps : discovery, genotyping

Re-sequencing discovery P. nigra panels Sanger

(21, 48 ind.) (53 ind.)NGS

 Quality and frequency controls  Technical criterias

 Localisation criterias (Candidate gene

& regions)

(Faivre-Rampant et al, Mol Ecol Res 2016)

Several millions of SNP

10 332 SNP bead-chip used for genotyping a P. nigra association population 9127 SNPs technically available

(13)

.012

Next Generation Sequencing (NGS)

1 step : discovery and genotyping

Hiseq Illumina

SMRT – Pacific bioscience

New opportunity for characterization

of forest genetic resources?

(14)

Characterization of Genetic

Resources

(15)

Characterization of Genetic

Resources

Structuration of diversity

_03a

(16)

.015

Management of Forest Genetic Resources

Specific aspects

Ex situ

In situ

Question

 How to sample (define a network, populations, individuals).

AGPF

To answer

Knowledge of existing variability, structuration and evolution potential

(17)

.016

How to measure genetic diversity?

Measures in situ

Sex, phenology

Measures ex situ :

Growth and biomass Foliar traits Phenology Wood properties Pest resistance Molecular markers

SSR

SNP

Neutral

(18)

.017 Sampling in natural area

(Riparian forest)

Comparison in 1 or several environments

Clonal trial

Observations/Measures

How to measure genetic diversity?

Measures ex situ

(19)

.018 Ticino Paglia Basento • Origin : Italy • North-South gradient • Small leaves = adaptation to dry/hot climate

How to measure genetic diversity?

(20)

.019

How to measure genetic diversity?

Leaf size variation reflect population dynamics

Adour

Loire

• Origin : France • 2 dynamics rivers

(21)

.020

How to measure genetic diversity?

Leaf size variation reflect population dynamics

• Origin : Germany • Rhine: no river

(22)

How to measure genetic diversity?

.021

What evolutionary forces have an impact on diversity ?

Genetic

diversity

Drift

Mutation

Gene flow

Selection

-+

+

(23)

0/-How to measure genetic diversity?

.022

Measure genetic diversity with molecular markers

In general….

Genetic

diversity

Drift

Mutation

Gene flow

Selection

-+

+

(24)

0/-.023

Diversity descriptors

Genetic distances

Fst

Examples

Expected heterozygosity (He)

 Probability for 2 alleles randomly drawn to be different  An estimator :

 Vary from 0 to 1 �

𝐻𝐻 = 1 − � 𝑥𝑥𝑖𝑖2 Frequence of i allele

𝐹𝐹𝑠𝑠𝑠𝑠 = 𝐻𝐻𝑠𝑠 −𝐻𝐻𝑠𝑠𝐻𝐻𝑠𝑠

 Loss of heterozygotes due to sous-population subdivision  An estimator :

 Vary from 0 (no differences bewteen sub-populations) to 1 (populations completely different)

 Degree of genetic divergence between populations.  Nei (1978), ...

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Diversity descriptors and type of markers

.024

Storme et al. 2004 TAG 108:969–981

(26)

Structuration variable depending on type of marker

.025 SSR + Isozymes

AFLP

(27)

.026 Rhine F Rh in e D Dur anc e Drôme Allier 12 populations 600 SNP Fst = 0.058 (Jost D)

(Faivre et al 2016, Mol Ecol Res)

Structuration variable depending on type of marker 19 populations

5 SSR Fst = 0.11

(28)

.027

Fst

0.11 0.0391 0.047

19 populations

5 SSR 8 populations10 SSR 22 populations6 SSR

Storme et al. 2004 TAG 108:969–981 Jorge et al, unpublished Imbert et Lefevre, 2003 Journal of Ecology 91: 447–456

(29)

.028 Project Biomareau

(Marin et al., 2014; Poster IPSVI) Photos M. Villar

Fst (between ecotopes) = 0,017**

32 seedlings x 51 spots x 5 ecotopes 10 SSR

(30)

Characterization of Genetic

Resources

Clonality

_03b

(31)

Estimation of rate of clonality in Populus nigra with molecular markers

.030

Resprout form tree stump, Populus spp.,Canada

 Poplars are easy vegetative propagation tree species.  In wild stands, clonalty rate vary between 0% to 97%

(proportion of identical genotype individuals (1)).

Example : in national ex situ collection (Storme et al 2004):

(1)Arens et al. 1998; Barsoum 2002; Barsoum et al. 2004; Cottrell et al. 1997; Koskela et al. 2004; Legionnet 1997;

Pospiskova and Bartakova 2004; Pospiskova and Salkova 2006; Rathmacher et al. 2010; Smulders et al. 2008b; Storme et al. 2004; Winfield et al. 1998

73%

2%

68%

1.4%

(32)

.031

© N. Chenault

11 SSR markers, in situ

Identification of clonal spots  Human action, floods?

(33)

.032

Power of markers

(Chenault et al 2011, TGG)

# ramets MLG : Multi Locus Genotype ; MLL : Multi Locus Lineage

(34)

Characterization of Genetic

Resources

Gene flow

_03c

(35)

Gene flow

.034

Pollen flow

Pollen

(36)

Models for gene flow

Parameters .035 Weather Sex Flowering synchronism Height & circumference Distance Topography GPS position

(37)

Paternity analysis with molecular markers

.036

© M. Villar

Models for gene flow

(38)

.037

Contributions des ♂ de

la zone d’étude = situation ‘observée’

γ(x)

adjustement Paternity analysis wind Dispersion curve

a: scale parameter (distance) b: shape parameter (function) known male

contributions = observed status

(39)

.038

Models for gene flow

Composition du nuage pollinique au point xi, yi

Composition of the pollen cloud at point xi, yi

(40)

.039

255 Black poplars

229 Black poplars♀

Male contributions

1350 seeds (2006)

Pollen dispersal at long distances confirmed (> 1000 m)

Large part of pollen flow outside the site

(51,3%)

Evidences of anisotropic dispersion of pollen

Dowkiw et al, unpublished

(41)

Poplars in European landscapes

Cultivated poplar stands and wild stands strongly intermingled ….

.040 Lombardy poplar

© C. Maître, INRA Cultivated

stands Black poplar

(42)

Gene flow ‘Cultivated’ => ‘wild’

Quantification of F1 hybrids with lombardy poplar at different scales

.041 (after C. Bastien, 2009) 10 SSR markers

In ex situ national collection (310 individuals)

6 %

In 5 natural area (230 individuals)

4,3 %

1,9 %

In a intensive study site11 ha (1350 seeds 2006)

Pollen flow

Lombardy poplar(♂) 1 2 3 5 4

(43)

Species specific markersHybridation / Introgression .042 Populus deltoides P. deltoides x P. trichocarpa P. deltoides x P. nigra Populus nigra

(44)

Markers to detect introgression

.043

Species 1 x Species 2

Multilocus markers needed

Result: random mosaic at genome scale (figure: haploïd genome)

x ?

? x

(45)

.044

Thompson et al 2010, Mol Ecol 19, 132–145

SNP

(Single Nucleotide Polymorphism)

11 P. balsamifera 14 P. nigra 11 P. deltoides P. nigra T TC TA T TAC T TG GC C AG ATA TC AT T T TG CA GC TA CA G GA C A T P. nigra T TC TA T TAC T TG GC C AG ATA TC AT T T TG CA GC TA CA G GA C A T P. nigra T TC TA T TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA C A T P. nigra T TC TAT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA C A T P. nigra T TC TAT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA C A T P. nigra T TC TAT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA C A T P. nigra T TC TAT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA C A T P. nigra T TC TAT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA C A T P. deltoides T TC TAT TA CT TG GC C AG ATA TC ATCT TG CA GC TA CA G GA A A T P. deltoides T TC TAT TA CT TG GC C AG ATA TC ATCT TG CA GC TA CA G GA A A T P. deltoides T TC TA T TA CT TG GC C AG ATA TC ATCT TG CA GC TA CA G GA A A T P. deltoides T TC TAT TA CT TG GC C AG ATA TC ATCT TG CA GC TA CA G GA A A T P. deltoides T TC TAT TA CT TG GC C AG ATA TC ATCT TG CA GC TA CA G GA A A T P. deltoides T TC TAT TA CT TG GC C AG ATA TC ATCT TG CA GC TA CA G GA A A T P. deltoides T TC TAT TA CT TG GC C AG ATA TC ATCT TG CA GC TA CA G GA A A T P. deltoides T TC TAT TA CT TG GC C AG ATA TC ATCT TG CA GC TA CA G GA A A T P. balsamifera T TC TGT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T P. balsamifera T TC TGT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T P. balsamiferaT TC TGT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T P. balsamifera T TC TG T TAC T TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T P. balsamifera T TC TG T TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T P. balsamifera T TC TGT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T P. balsamifera T TC TGT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T P. balsamifera T TC TGT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T P. balsamifera T TC TGT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T P. balsamifera T TC TGT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T P. balsamifera T TC TGT TA CT TG GC C AG ATA TC AT T T TG CA GC TA CA G GA A A T 636 trees 38 SNPs 19 hybrids: 3%

(46)

.045

Management of genetic resources for Populus nigra in France

Ex situ

In situ

 Inventory and characterisation of

natural stands

 Involvement of Natural reserves in

the in conservation program

 Sampling

 Molecular and phenotypis

charcterisation

 Ex situ collection

AGPF

Occurence of the species: - Present in riparian forests - Present as isolated trees

(47)

Breeding

(48)

.047

Poplar breeding program

P. deltoides P. nigra Hybrid X X Evaluation X Evaluation Best Evaluation Best Elite Clones X M. Pégard, PhD thesis

(49)

.048

Selection criteria

5-10 years < 5 years

> 10 years

Poplar breeding program

(50)

.049 20-30 selected founders Year 1 Year 2 Year 3 Year 5 Year 9 Year 17 3000 individuals 1500 clones 800 clones 50 clones 25 clones 2-3 clones Breeding Seedlings Vegetative multiplication Testing

Disease resistance tests Multi-environment tests Approval

Poplar breeding program

Time and selection rate

(51)

.050

Strengths Weaknesses

Biological

Controlled crossings in greenhouses First flowering between 4 and 7 yearsLong selection cycle> 15 years

A large number of available progenies But not used

High vegetative multiplication

Strong correlation between the parent’s breeding value and that of

his offspring in hybridization traits evaluated late and expensive

Operational

Strong selection intensity Multi-steps selection

Precise phenotypic evaluation within clones in productionPoor genetic diversity

What solution can bring genomic selection ?

M. Pégard, PhD thesis

(52)

.051 Training population SNP data Genotypes Trait data Phenotypes Predictive models Y = Xg + e Cross validation SNP data Genotypes Validation population Seedlings B r e e d i n g M. Pégard, PhD thesis

Poplar breeding program

Genomic selection

(53)

.052 M. Pégard, PhD thesis 0.500 0.550 0.600 0.650 0.700 0.750 0.800 0.850 0.900 Pr edi cti ng ab ili ty fo r T 75 .V 25 Predictive methods Predictive models Y = Xg + e Diameter Rust score Branche angle

Poplar breeding program

Genomic selection Training population = factorial mating design Genotypes

➔12K beadchip illumina (Faivre-Rampant et al., 2016)

➔After trimming 7300 SNPs

(54)

.053

Development of cost- and time-effective breeding methods

Target in deployment = ecological restoration of river banks

Multi-Clonal Varieties of Populus nigra

Occurence of the species: - Present in riparian forests - Present as isolated trees

- absent

After M. Villar, coord. National Conservation Programme of Populus nigra

General rules of a MCV of black poplar

Individuals of the species Populus nigra !

 Variety by river basin (six in France)

 Largest diversity as possible (geographic, ecologic and genetic), representative of the river basin

(55)

.054

Development of cost- and time-effective breeding methods

Target in deployment = ecological restoration of river banks

Multi-Clonal Varieties of Populus nigra

Species descriptors and introgression

 In situ phenotype : tree shape, bark characteristics, stem

characteristics, leaf shape, bud shape, male and female catkins

 SSR and SNP markers

One variety per river basin & large ecological regions

GRECO : ‘large ecological regions’ of the French National Forest Inventory

Largest diversity as possible

 Sex ratio

 No clone (SSR markers)

Traits evaluated in trials :

 Phenology: max. variability

 Height and diameter: eliminate extremes

to avoid competiton

 Branching patterns: avoid fastigiate

Populus nigra var. Italica

(56)

15 / 02 / 2013 55

Thanks

Catherine BASTIEN Nicolas CHENAULT Arnaud DOWKIW Vanina GUERIN Marie JUTEAU Romain VALADE Marc VILLAR Patrick POURSAT José ALMEIDA Etienne KLEIN

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