Nuclear and chloroplast microsatellites show multiple introductions in the worldwide invasion history of common ragweed, Ambrosia artemisiifolia

Myriam Gaudeul, Tatiana Giraud, Levente Kiss, Jacqui A Shykoff, Myriam Gaudeul, Tatiana Giraud, Levente Kiss, Jacqui A Shykoff

Abstract

Background: Ambrosia artemisiifolia is a North American native that has become one of the most problematic invasive plants in Europe and Asia. We studied its worldwide population genetic structure, using both nuclear and chloroplast microsatellite markers and an unprecedented large population sampling. Our goals were (i) to identify the sources of the invasive populations; (ii) to assess whether all invasive populations were founded by multiple introductions, as previously found in France; (iii) to examine how the introductions have affected the amount and structure of genetic variation in Europe; (iv) to document how the colonization of Europe proceeded; (v) to check whether populations exhibit significant heterozygote deficiencies, as previously observed.

Principal findings: We found evidence for multiple introductions of A. artemisiifolia, within regions but also within populations in most parts of its invasive range, leading to high levels of diversity. In Europe, introductions probably stem from two different regions of the native area: populations established in Central Europe appear to have originated from eastern North America, and Eastern European populations from more western North America. This may result from differential commercial exchanges between these geographic regions. Our results indicate that the expansion in Europe mostly occurred through long-distance dispersal, explaining the absence of isolation by distance and the weak influence of geography on the genetic structure in this area in contrast to the native range. Last, we detected significant heterozygote deficiencies in most populations. This may be explained by partial selfing, biparental inbreeding and/or a Wahlund effect and further investigation is warranted.

Conclusions: This insight into the sources and pathways of common ragweed expansion may help to better understand its invasion success and provides baseline data for future studies on the evolutionary processes involved during range expansion in novel environments.

Conflict of interest statement

Competing Interests: The authors have declared that no competing interests exist.

Figures

Figure 1. Map and nDNA genetic composition…
Figure 1. Map and nDNA genetic composition (based on Structure) of the studied populations.
For each population, the pie represents the membership coefficients to the five clusters inferred in Structure.
Figure 2. Figure 2. Within-population genetic diversity.
Figure 2. Figure 2. Within-population genetic diversity.
Relationship between nDNA allelic richness and cpDNA mean pairwise number of differences between individuals (the number of haplotypes in the population is indicated within brackets). The correlation was significant (P = 0.041).
Figure 3. Figure 3. Bayesian analysis performed…
Figure 3. Figure 3. Bayesian analysis performed in Structure.
A) on the overall nDNA dataset, relationship between K, lnP(D) and ΔK. B) On the overall nDNA data set, cluster partitioning of the populations at consecutive K-values from K = 2 to K = 5. Each vertical line represents one individual and the colors represent the membership coefficients to the K clusters. The clustering solutions inferred by Instruct and Structurama were highly similar. Colors are the same as in Fig. 1. C) On the North American (K = 3) and European (K = 7) datasets.
Figure 4. Figure 4. Mean pairwise F…
Figure 4. Figure 4. Mean pairwise F ST indices (± S. D.) estimated at nDNA loci between populations from different regions.
Regions include Central Europe (IT9 to PO1; 9 pops.), Eastern Europe (UKR to RU5; 5 pops.), western North America (Utah to Minnesota; 3 pops.) and eastern North America (Missouri to Bronx; 5 pops.).
Figure 5. Figure 5. Median-joining network of…
Figure 5. Figure 5. Median-joining network of cpDNA haplotypes.
Ten haplotypes counting only one individual each (Table S1) were discarded, so that the network includes 23 haplotypes and 600 individuals. The size of each pie is proportional to the frequency of the corresponding haplotype. The colors indicate the geographical origin of the populations displaying each haplotype. Light green: western North America; light blue: eastern North America; dark green: Eastern Europe; dark blue: Western Europe. Purple: Argentina; White: Asia (China, Japan, Korea); Yellow: Australia. Black dots stand for unsampled haplotypes and each segment joining haplotypes represent one mutation. The two ellipses indicate the two areas of the network discussed in the text.
Figure 6. Figure 6. Relationship between mean…
Figure 6. Figure 6. Relationship between mean pairwise differentiation indices at nDNA (F ST) and at cpDNA (N ST) loci.
The correlation was significant (P = 0.002).
Figure 7. Figure 7. Principal Coordinate Analyses.
Figure 7. Figure 7. Principal Coordinate Analyses.
A) At nDNA loci. B) At cpDNA loci. Dots: North America; open squares: Europe; crosses: non-European invasive populations. The percentages of variance explained by each axis are indicated within brackets.

References

    1. Barrett SCH, Colautti RI, Eckert CG. Plant reproductive systems and evolution during biological invasions. Mol Ecol. 2008;17:373–383.
    1. Facon B, Genton BJ, Shykoff J, Jarne P, Estoup A, et al. A general eco-evolutionary framework for understanding bioinvasions. Trends Ecol Evol. 2006;21:130–135.
    1. Olivieri I. Alternative mechanisms of range expansion are associated with different changes of evolutionary potential. Trends Ecol Evol. 2010;24:289–292.
    1. Prentis PJ, Wilson JRU, Dormontt EE, Richardson DM, Lowe AJ. Adaptive evolution in invasive species. Trends Plant Sci. 2008;13:288–294.
    1. Dlugosch KM, Parker IM. Founding events in species invasions: genetic variation, adaptive evolution, and the role of multiple introductions. Mol Ecol. 2007;17:431–449.
    1. Hufbauer RA, Sforza R. Multiple introductions of two invasive Centaurea taxa inferred from cpDNA haplotypes. Divers Distrib. 2008;14:252–261.
    1. Kang M, Buckley YM, Lowe AJ. Testing the role of genetic factors across multiple independent invasions of the shrub Scotch broom (Cytisus scoparius). Mol Ecol. 2007;16:4662–4673.
    1. Prentis PJ, Sigg DP, Raghu S, Dhileepan K, Pavasovic A, et al. Understanding invasion history: genetic structure and diversity of two globally invasive plants and implications for their management. Divers Distrib. 2009;15:822–830.
    1. Dlugosh KM, Parker IM. Invading populations of an ornamental shrub show rapid life history evolution despite genetic bottlenecks. Ecol Lett. 2008;11:701–709.
    1. Rosenthal DM, Ramakrishnan AP, Cruzan MB. Evidence for multiple sources of invasion and intraspecific hybridization in Brachypodium sylvativum (Hudson) Beauv. in North America. Mol Ecol. 2008;17:4657–4669.
    1. Kolbe JJ, Glor RE, Schettino LR, Lara AC, Larson A, et al. Genetic variation increases during biological invasion by a Cuban lizard. Nature. 2004;431:177–181.
    1. Lavergne S, Molofsky J. Increased genetic variation and evolutionary potential drive the success of an invasive grass. P Natl Acad Sci USA. 2007;104:3883–3888.
    1. Valliant MT, Mack RN, Novak SJ. Introduction history and population genetics of the invasive grass Bromus tectorum (Poaceae) in Canada. Am J Bot. 2007;94:1156–1169.
    1. Bossdorf O, Auge H, Lafuma L, Rogers WE, Siemann E, et al. Phenotypic and genetic differentiation between native and introduced plant populations. Oecologia. 2005;144:1–11.
    1. Bassett IJ, Crompton CW. The biology of Canadian weeds: 11. Ambrosia artemisiifolia L. and A. psilostachya DC. Can J Pl Sci. 1975;55:463–476.
    1. Taramarcaz P, Lambelet C, Clot B, Keimer C, Hauser C. Ragweed (Ambrosia) progression and its health risks: will Switzerland resist this invasion? Swiss Medical Weekly. 2005;135:538–548.
    1. Protopopova VV, Shevera MV, Mosyakin SL. Deliberate and unintentional introduction of invasive weeds: A case study of the alien flora of Ukraine. Euphytica. 2006;148:17–33.
    1. Bohren C. Ambrosia artemisiifolia – a motivation for European-wide control. European Weed Research Society Invasive Plants. 2008. Available at .
    1. Friedmann J, Barrett SCH. High outcrossing in the annual colonizing species Ambrosia artemisiifolia (Asteraceae). Ann Bot. 2008;101:1303–1309.
    1. Fumanal B, Chauvel B, Sabatier A, Bretagnolle F. Variability and cryptic heteromorphism of Ambrosia artemisiifolia seeds: what consequences for its invasion in France? Ann Bot. 2007;100:305–313.
    1. Lewis AJ. Ragweed Control Techniques: Effect on Old-Field Plant Populations. Bull Torrey Bot Club. 1973;100:333–338.
    1. Reznik S. Common ragweed (Ambrosia artemisiifolia L.) in Russia: spread, distribution, abundance and control measures. First International Ragweed Conference: 10-13 Sept. 2008; Budapest, Hungary. 2008. Abstract available at .
    1. Kiss L, Beres I. Anthropogenic factors behind the recent population expansion of common ragweed (Ambrosia artemisiifolia L.) in Eastern Europe: is there a correlation with political transitions? J Biogeogr. 2006;33:2154–2157.
    1. Chen H, Chen L, Albright TP. Developing Habitat-suitability Maps of Invasive Ragweed (Ambrosia artemisiifolia.L) in China Using GIS and Statistical Methods. In: Lai PC, Mak SH, editors. GIS for health and the environment. Berlin: Springer Verlag; 2007. pp. 105–121.
    1. Bass DJ, Delpech V, Beard J, Bass P, Walls RS. Ragweed in Australia. Aerobiologia. 2000;16:107–111.
    1. McFadyen R. Ambrosia species in Australia and their control. First International Ragweed Conference: 10-13 Sept. 2008; Budapest, Hungary. 2008. Abstract available at .
    1. Shin H-D. Present situation of ragweed problems and potential biological control in Korea. First International Ragweed Conference: 10-13 Sept. 2008; Budapest, Hungary. 2008. Abstract available at .
    1. Chauvel B, Dessaint F, Cardinal-Legrand C, Bretagnolle F. The historical spread of Ambrosia artemisiifolia L. in France from herbarium records. J Biogeogr. 2006;33:665–673.
    1. Chun YJ, Fumanal B, Laitung B, Bretagnolle F. Gene flow and population admixture as the primary post-invasion processes in common ragweed (Ambrosia artemisiifolia) populations in France. New Phytol. 2010;185:1100–1107.
    1. Genton BJ, Shykoff JA, Giraud T. High genetic diversity in French invasive populations of common ragweed, Ambrosia artemisiifolia, as a result of multiple sources of introduction. Mol Ecol. 2005;14:4275–4285.
    1. McNeely JA. As the world gets smaller, the chances of invasion grow. Euphytica. 2006;148:5–15.
    1. Tatem AJ. Global traffic and disease vector dispersal. P Natl Acad Sci USA. 2006;103:6242–6247.
    1. Pysek P, Prach K. Research into plant invasions in a crossroads region: history and focus. Biol Inv. 2003;5:337–348.
    1. Török K, Botta-Dukat Z, Dancza I, Németh I, Kiss J, et al. Invasion gateways and corridors in the Carpathian Basin: Biological invasions in Hungary. Biol Inv. 2003;5:349–356.
    1. Gladieux P, Giraud T, Kiss L, Genton B, Jonot O, et al. Distinct invasion sources of common ragweed (Ambrosia artemisiifolia) in Eastern and Western Europe. Biol Inv. In press. DOI 10.1007/s10530-010-9880-y.
    1. Jakobsson M, Torbjörn S, Lind-Halldén C, Halldén C. Evolution of chloroplast mononucleotide microsatellites in Arabidopsis thaliana. Theor Appl Genet. 2007;114:223–235.
    1. Molecular Ecology Resources Primer Development Consortium. Permanent genetic resources added to Molecular Ecology Resources database 1 January 2009-30 April 2009. Mol Ecol Resour. 2009;9:1375–1429.
    1. Bryan GJ, McNicoll J, Ramsay G, Meyer RC, De Jong WS. Polymorphic simple sequence repeat markers in chloroplast genomes of Solanaceous plants. Theor Appl Genet. 1999;99:859–867.
    1. Goudet J. FSTAT, version 1.2. A computer program to calculate Fstatistics. Journal of Heredity. 1995;86:485–486.
    1. El Mousadik A, Petit RJ. Chloroplast DNA phylogeography of the argan tree of Morocco. Mol Ecol. 1996;5:547–555.
    1. Cornuet JM, Luikart G. Description and power analysis of genetic differentiation between populations. Genetics. 1996;163:367, 374. Software Bottleneck available at .
    1. Raymond M, Rousset F. GENEPOP (version 1.2): population genetics software for exact tests and ecumenicism. J Hered. 1995;86:248–249.
    1. Rousset F. Genepop'007: a complete reimplementation of the Genepop software for Windows and Linux. Mol Ecol Resour. 2003;8:103–106.
    1. Rannala B, Mountain JL. Detecting immigration by using multilocus genotypes. P Natl Acad Sci USA. 1997;94:9197–9201.
    1. Paetkau D, Slade R, Burden M, Estoup A. Direct, real-time estimation of migration rate using assignment methods: a simulation-based exploration of accuracy and power. Mol Ecol. 2004;13:55–65.
    1. Piry S, Alapetite A, Cornuet J-M, Paetkau D, Baudouin L, et al. GeneClass2: a software for genetic assignment and first generation migrants detection. J Hered. 2004;95:536–539.
    1. Rohlf F. NTSYS-PC. 1990. Numerical Taxonomy and Multivariate Analysis System, Version 2.02. Exeter Software, Setauket, New York.
    1. Excoffier L, Laval G, Schneider S. Arlequin ver. 3.0: An integrated software package for population genetics data analysis. Evol Bioinform. 2005;1:47–50.
    1. Pritchard JK, Stephens M, Donnelly P. Inference of population structure using multilocus genotype data. Genetics. 2000;155:945–959.
    1. Falush D, Stephens M, Pritchard JK. Inference of population structure using multilocus genotype data: linked loci and correlated allele frequencies. Genetics. 2003;164:1567–1587.
    1. Gao H, Williamson S, Bustamante CD. An MCMC Approach for joint inference of population structure and inbreeding rates from multi-locus genotype data. Genetics. 2007;176:1635–1651.
    1. Huelsenbeck JP, Andolfatto P. Inference of population structure under a Dirichlet process model. Genetics. 2007;175:1787–1802.
    1. Hubisz MJ, Falush D, Stephens M, Pritchard JK. Inferring weak population structure with the assistance of sample group information. Mol Ecol Resour. 2009;9:1322–1332.
    1. Evanno G, Regnault S, Goudet J. Detecting the number of clusters of individuals using the software STRUCTURE: a simulation study. Mol Ecol. 2005;14:2611–2620.
    1. Ehrich D. AFLPdat: a collection of R functions for convenient handling of AFLP data. Mol Ecol Notes. 2006;6:603–604.
    1. Rosenberg N. DISTRUCT: a program for the graphical display of population structure. Mol Ecol Notes. 2004;4:137–138.
    1. Bandelt H-J, Forster P, Röhl A. Median-joining networks for inferring intraspecific phylogenies. Mol Biol Evol. 1999;16:37–48. Software NETWORK available at .
    1. Bandelt H-J, Forster P, Sykes BC, Richards MB. Mitochondrial portraits of human populations using median networks. Genetics. 1995;141:713–753.
    1. Hardy OJ, Vekemans X. SPAGeDi: a versatile computer program to analyse spatial genetic structure at the individual or population levels. Mol Ecol Notes. 2002;2:618–620.
    1. Pons O, Petit RJ. Measuring and testing genetic differentiation with ordered versus unordered alleles. Genetics. 1996;144:1237–1245.
    1. Thuillet A-C, Bru D, David J, Roumet P, Santoni S, et al. Direct estimation of mutation rate for 10 microsatellite loci in Durum wheat, Triticum turgidum (L.) Thell. ssp. durum desf. Mol Biol Evol. 2002;19:122–125.
    1. Wilson JRU, Dormontt EE, Prentis PJ, Lowe AJ, Richardson DM. Something in the way you move: dispersal pathways affect invasion success. Trends Ecol Evol. 2009;24:136–144.
    1. Zayed A, Constantin SA, Packer L. Successful biological invasion despite a severe genetic load. Plos One. 2007;9:e868.
    1. Marrs RA, Sforza R, Hubauer RA. When invasion increases population genetic structure: a study with Centaurea diffusa. Biol Inv. 2008;10:561–572.
    1. Jahodova S, Trybush S, Pysek P, Wade M, Karp A. Invasive species of Heracleum in Europe: an insight into genetic relationships and invasion history. Div Distrib. 2007;13:99–114.
    1. Martin MD, Chamecki M, Brush GS, Meneveau C, Parlange MB. Pollen clumping and wind dispersal in an invasive angiosperm. Am J Bot. 2009;96:1703–1711.
    1. Barrett SCH, Richardson BJ. Genetic attributes of invading species. In: Groves RH, Burdon JJ, editors. Ecology of Biological Invasions. Cambridge University Press; 1986. pp. 21–33.
    1. Jones KL. Studies on Ambrosia. I. The inheritance of floral types in the ragweed, Ambrosia elatior L. Am Midl Nat. 1936;17:673–699.
    1. Li X-M, Liao W-J, Zhang D-Y. Evolutionary changes in reproductive systems during invasion of common ragweed, Ambrosia artemisiifolia. 2009. International Congress of Biological Invasions (ICBI) - Managing Biological Invasions under Global Change: 2 – 6 Nov. 2009, Fuzhou, China. Abstract available at .
    1. Muirhead JR, Gray DK, Kelly DW, Ellis SM, Heath DD, et al. Identifying the source of species invasions: sampling intensity vs. genetic diversity. Mol Ecol. 2008;17:1020–1035.
    1. Colautti RI, Eckert CG, Barrett SCH. Evolutionary constraints on adaptive evolution during range expansion in an invasive plant. Proc Roy Soc Lond B. 2010;277:1799–1806.
    1. Genton BJ, Kotanen PM, Cheptou P-O, Adolphe C, Shykoff JA. Enemy release but no evolutionary loss of defence in a plant invasion: an inter-continental reciprocal transplant experiment. Oecologia. 2005;146:404–414.
    1. Skjøth CA, Petersen H, Sommer J, Smith M. Copenhagen: a harbinger for ragweed (Ambrosia) in Northern Europe under climate change? IOP Conf. Series: Earth Environ Sci. 2009;6:142031.

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