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Population genetic analyses of plant pathogens: new challenges and opportunities<br />

C.C. Linde{ XE "Linde, C.C." }<br />

Botany and Zoology, Research School of Biology, College of Medicine, Biology and Environment, Bldg. 116, Daley Rd, Australian National<br />

University, Canberra, ACT 0200, Australia<br />

INTRODUCTION<br />

The study of population genetics attempts to investigate<br />

evolutionary forces such as mutation, migration, genetic drift,<br />

selection and recombination, and how gene frequencies change<br />

in populations to shape their genetic structure. These<br />

evolutionary forces and the interaction amongst them are<br />

particularly important in plant pathogens where, combined with<br />

the pathogen’s life history characteristics, they determine the<br />

evolutionary potential. The population genetics of plant<br />

pathogens has been investigated for at least 30 years. Early<br />

studies on population genetics of plant pathogens concentrated<br />

on the effect sexual reproduction has on levels of genetic<br />

diversity in populations (Burdon and Roelfs, 1985a, b) and what<br />

impact that had on disease control. Similar studies have<br />

continued with investigations of pathogen capacities to rapidly<br />

adapt to new environments such as developing resistance<br />

against a fungicide or overcoming a resistance gene in the plant<br />

host (McDonald and Linde, 2002).<br />

Although the questions we ask in the population genetics of<br />

plant pathogens has not changed significantly, advances in DNA<br />

sequencing and analytical approaches have significantly<br />

improved the accuracy of parameter estimates. In particular,<br />

coalescent based approaches are a powerful extension of<br />

classical population genetics because it is a collection of<br />

mathematical models that can accommodate biological<br />

phenomena as reflected in molecular data. The emphasis in<br />

coalescent thinking is to view populations backwards in time,<br />

using the divergence observable in a population to estimate the<br />

time to a most recent common ancestor. This ancestor is the<br />

point where gene genealogies `coalesce’, in a single biological<br />

organism.<br />

The barley scald pathogen, Rhynchosporium secalis, will be used<br />

as an example to illustrate the importance of some of these<br />

evolutionary forces and how coalescent based methods<br />

significantly improved our understanding of the pathogens’<br />

biology.<br />

MATERIALS AND METHODS<br />

Populations of R. secalis were characterised with 14<br />

microsatellite loci (Linde et al., 2009) and several sequence loci<br />

(Zaffarano et al., 2009). Several population genetic parameters<br />

were investigated, including migration among populations. This<br />

was investigated with a coalescent method in the program IM<br />

(Hey and Nielsen, 2004) and results were compared to estimates<br />

derived from traditional F ST estimates (Weir and Cockerham,<br />

1984).<br />

pathogen populations are constantly influenced by the host<br />

populations or human‐mediated migration.<br />

With coalescent methods, the direction of migration is obtained.<br />

This means the major source and sink populations for migration<br />

can be determined which is useful in determining breaches of<br />

quarantine or major migration routes due to eg prevailing wind<br />

currents. In R. secalis, unusually high migration rates in both<br />

directions between Australia and South Africa and Australia and<br />

New Zealand cause particular concern for disease management.<br />

A comparison of the results revealed that migration estimates<br />

based on coalescent analyses were frequently non‐symmetric,<br />

meaning one population contributed significantly more migrants<br />

than the other. This contributed to migration estimates derived<br />

from F st being over‐ or under‐estimated. Furthermore, F st derived<br />

migration estimates were usually underestimated when the<br />

migration was high, and/or when population sample sizes were<br />

low.<br />

Coalescent analyses provided population genetic parameter<br />

estimates that are more reliable, are less dependent on<br />

population sizes being stable and are affected less by<br />

populations with small sample sizes. Improved analyses and<br />

their usefulness in plant pathology are discussed.<br />

REFERENCES<br />

1. Burdon, J.J., Roelfs, A.P., 1985a. Isozyme and virulence variation in<br />

asexually reproducing populations of Puccinia graminis and<br />

Puccinia recondita on wheat. Phytopathology 75, 907–913.<br />

2. Burdon, J.J., Roelfs, A.P., 1985b. The effect of sexual and asexual<br />

reproduction on the isozyme structure of populations of Puccinia<br />

graminis. Phytopathology 75, 1068–1073.<br />

3. McDonald, B.A., Linde, C., 2002. Pathogen population genetics,<br />

evolutionary potential, and durable resistance. Annu. Rev.<br />

Phytopathol. 40, 349–379.<br />

4. Linde, C.C., Zala, M., McDonald, B.A., 2009. Molecular evidence for<br />

recent founder populations and human‐mediated migration in the<br />

barley scald pathogen Rhynchosporium secalis. Molecular<br />

Phylogenetics and Evolution 51, 454–464.<br />

5. Zaffarano, P.L., McDonald, B.A., Linde, C.C., 2009.<br />

Phylogeographical analyses reveal global migration patterns of the<br />

barley scald pathogen Rhynchosporium secalis. Molecular Ecology,<br />

279–293.<br />

6. Hey, J., Nielsen, R., 2004. Multilocus methods for estimation<br />

population sizes, migration rates and divergence times, with<br />

application to the divergence of Drosophila pseudoobscura and D.<br />

persimilis. Genetics 167, 747–760.<br />

7. Weir, B.S., Cockerham, C.C., 1984. Estimating F‐statistics for the<br />

analysis of population structure. Evolution 38, 1358–1370.<br />

Keynote speaker<br />

RESULTS AND DISCUSSION<br />

The results of this comparison revealed that coalescent based<br />

approaches offer several advantages over other analytical<br />

methods to estimate parameters such as migration and genetic<br />

drift. Traditional measures of the translation of F ST into gene<br />

flow assume that subpopulations have the same size, population<br />

sizes are constant, or that there are infinitely many populations,<br />

and that migration rates are all symmetric. Due to these<br />

underlying assumptions, migration estimates derived from F ST<br />

are almost always flawed and incorrect estimates are achieved<br />

when these assumptions are not met. This is often the case since<br />

APPS 2009 | PLANT HEALTH MANAGEMENT: AN INTEGRATED APPROACH 51

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