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<art><ui>1471-2148-11-210</ui><ji>1471-2148</ji><fm>
<dochead>Research article</dochead>
<bibl>
<title>
<p>Introgression and rapid species turnover in sympatric damselflies</p>
</title>
<aug>
<au ca="yes" id="A1"><snm>S&#225;nchez-Guill&#233;n</snm><mi>A</mi><fnm>Rosa</fnm><insr iid="I1"/><email>rguillen@uvigo.es</email></au>
<au id="A2"><snm>Wellenreuther</snm><fnm>Maren</fnm><insr iid="I2"/><email>maren.wellenreuther@zooekol.lu.se</email></au>
<au id="A3"><snm>Cordero-Rivera</snm><fnm>Adolfo</fnm><insr iid="I1"/><email>adolfo.cordero@uvigo.es</email></au>
<au id="A4"><snm>Hansson</snm><fnm>Bengt</fnm><insr iid="I2"/><email>bengt.hansson@zooekol.lu.se</email></au>
</aug>
<insg>
<ins id="I1"><p>Department of Ecology and Animal Biology, E. U. E. T. Forestry, Vigo University, 36005 Pontevedra, Spain</p></ins>
<ins id="I2"><p>Department of Biology, Lund University, SE-22362 Lund, Sweden</p></ins>
</insg>
<source>BMC Evolutionary Biology</source>
<issn>1471-2148</issn>
<pubdate>2011</pubdate>
<volume>11</volume>
<issue>1</issue>
<fpage>210</fpage>
<url>http://www.biomedcentral.com/1471-2148/11/210</url>
<xrefbib><pubidlist><pubid idtype="pmpid">21767355</pubid><pubid idtype="doi">10.1186/1471-2148-11-210</pubid></pubidlist></xrefbib>
</bibl>
<history><rec><date><day>17</day><month>2</month><year>2011</year></date></rec><acc><date><day>18</day><month>7</month><year>2011</year></date></acc><pub><date><day>18</day><month>7</month><year>2011</year></date></pub></history>
<cpyrt><year>2011</year><collab>S&#225;nchez-Guill&#233;n et al; licensee BioMed Central Ltd.</collab><note>This is an Open Access article distributed under the terms of the Creative Commons Attribution License (<url>http://creativecommons.org/licenses/by/2.0</url>), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.</note></cpyrt>
<abs>
<sec>
<st>
<p>Abstract</p>
</st>
<sec>
<st>
<p>Background</p>
</st>
<p>Studying contemporary hybridization increases our understanding of introgression, adaptation and, ultimately, speciation. The sister species <it>Ischnura elegans </it>and <it>I. graellsii </it>(Odonata: Coenagrionidae) are ecologically, morphologically and genetically similar and hybridize. Recently, <it>I. elegans </it>has colonized northern Spain, creating a broad sympatric region with <it>I. graellsii</it>. Here, we review the distribution of both species in Iberia and evaluate the degree of introgression of <it>I. graellsii </it>into <it>I. elegans </it>using six microsatellite markers (442 individuals from 26 populations) and five mitochondrial genes in sympatric and allopatric localities. Furthermore, we quantify the effect of hybridization on the frequencies of the genetically controlled colour polymorphism in females of both species.</p>
</sec>
<sec>
<st>
<p>Results</p>
</st>
<p>In a principal component analysis of the microsatellite data, the first two principal components summarised almost half (41%) of the total genetic variation. The first axis revealed a clear separation of <it>I. graellsii </it>and <it>I</it>. <it>elegans </it>populations, while the second axis separated <it>I. elegans </it>populations. Admixture analyses showed extensive hybridization and introgression in <it>I. elegans </it>populations, consistent with <it>I. elegans </it>backcrosses and occasional F<sub>1</sub>-hybrids, suggesting hybridization is on-going. More specifically, approximately 58% of the 166 Spanish <it>I. elegans </it>individuals were assigned to the <it>I. elegans </it>backcross category, whereas not a single of those individuals was assigned to the backcross with <it>I. graellsii</it>. The mitochondrial genes held little genetic variation, and the most common haplotype was shared by the two species.</p>
</sec>
<sec>
<st>
<p>Conclusions</p>
</st>
<p>The results suggest rapid species turnover in sympatric regions in favour of <it>I. elegans</it>, corroborating previous findings that <it>I. graellsii </it>suffers a mating disadvantage in sympatry with <it>I. elegans</it>. Examination of morph frequency dynamics indicates that hybridization is likely to have important implications for the maintenance of multiple female morphs, in particular during the initial period of hybridization.</p>
</sec>
</sec>
</abs>
</fm><bdy>
<sec>
<st>
<p>Background</p>
</st>
<p>Hybridization and introgression are increasingly recognized as important factors in the evolution of plants, animals <abbrgrp>
<abbr bid="B1">1</abbr>
<abbr bid="B2">2</abbr>
</abbrgrp> and prokaryotes <abbrgrp>
<abbr bid="B3">3</abbr>
</abbrgrp>, and can lead to the creation of novel genotypes and phenotypes. Thus, the study of contemporary hybridization between species and the extent of genomic introgression between them provides an excellent opportunity to examine evolutionary processes such as adaptation, gene flow and, ultimately, speciation <abbrgrp>
<abbr bid="B4">4</abbr>
<abbr bid="B5">5</abbr>
<abbr bid="B6">6</abbr>
</abbrgrp>. Determining the degree of genetic exchange between species may be of particular interest when studying recently diverged species, since they typically show incomplete reproductive barriers.</p>
<p>Hybridization has an inherent spatial component, as the process requires direct contact between populations of the different species. For this reason, the spatial setting is a crucial determinant of hybridization, and, in turn, the specific conditions under which hybridization occurs can, sometimes, be inferred from the geographical distribution of hybrids. Studies of hybrid zones have indicated that natural hybridization is most likely to take place in intermediate habitats, which are often found at the ecological limits of the species' distributional ranges, and where both taxa are found in close proximity to each other <abbrgrp>
<abbr bid="B5">5</abbr>
</abbrgrp>. When some of the interspecific matings lead to fertile first-generation (F<sub>1</sub>) hybrids, there is a possibility that these will backcross with at least one of the parental genotypes, with introgression as a consequence. If the resulting backcrossed individuals subsequently mate with the most similar parental genotype, novel genes and gene complexes can be particularly rapidly introduced into the new genetic background <abbrgrp>
<abbr bid="B7">7</abbr>
</abbrgrp>. In some cases, stable and long-lasting hybrid zones are formed as a consequence of spatial range overlap between two species <abbrgrp>
<abbr bid="B8">8</abbr>
<abbr bid="B9">9</abbr>
<abbr bid="B10">10</abbr>
</abbrgrp>. However, in the vast majority of cases, one of the two species, or possibly even the new hybrid cross, becomes more successful and displaces one or both of the original taxa <abbrgrp>
<abbr bid="B11">11</abbr>
</abbrgrp>.</p>
<p>In odonates (damselflies and dragonflies), a high level of hybridization between species is a rare phenomenon <abbrgrp>
<abbr bid="B12">12</abbr>
<abbr bid="B13">13</abbr>
</abbrgrp>. So far, only three molecular studies have investigated hybridization between closely related odonate species, namely between <it>Coenagrion puella </it>and <it>C. pulchellum </it>
<abbrgrp>
<abbr bid="B14">14</abbr>
</abbrgrp>, <it>Mnais costalis </it>and <it>M. pruinosa </it>
<abbrgrp>
<abbr bid="B15">15</abbr>
<abbr bid="B16">16</abbr>
</abbrgrp> and <it>Calopteryx splendens </it>and <it>C. virgo </it>
<abbrgrp>
<abbr bid="B17">17</abbr>
</abbrgrp>. All these studies failed, however, to detect extensive hybridization between the species. There was no evidence of hybridization between <it>Coenagrion puella </it>and <it>C. pulchellum </it>in any of the populations examined <abbrgrp>
<abbr bid="B14">14</abbr>
</abbrgrp>, i.e. no hybrids were found. In addition, between <it>Mnais costalis </it>and <it>M. pruinosa </it>only two F<sub>1 </sub>hybrid females were found among 900 individuals <abbrgrp>
<abbr bid="B15">15</abbr>
<abbr bid="B16">16</abbr>
</abbrgrp> and between <it>Calopteryx splendens </it>and <it>C. virgo </it>only seven hybrids out of 1600 putative hybrids were detected <abbrgrp>
<abbr bid="B17">17</abbr>
</abbrgrp>. Despite the lack of evidence from molecular studies, observational and experimental studies have found evidence for putative intrageneric hybrids in some additional species <abbrgrp>
<abbr bid="B18">18</abbr>
</abbrgrp>. For example, two of the best documented cases of hybridization among odonates are between <it>Ischnura gemina </it>and <it>I. denticollis </it>
<abbrgrp>
<abbr bid="B19">19</abbr>
</abbrgrp>, and <it>I. elegans </it>and <it>I. graellsii </it>
<abbrgrp>
<abbr bid="B20">20</abbr>
<abbr bid="B21">21</abbr>
</abbrgrp>.</p>
<p>The latter species pair consists of two closely related damselfly species that co-occur in southern Europe <abbrgrp>
<abbr bid="B18">18</abbr>
</abbrgrp>. Specifically, <it>I. graellsii </it>is a widespread species on the Iberian Peninsula (see Figure <figr fid="F1">1</figr>), while <it>I. elegans </it>is a species with a more northern and easterly distribution, which has recently spread into new regions within the Iberian Peninsula <abbrgrp>
<abbr bid="B20">20</abbr>
<abbr bid="B21">21</abbr>
</abbrgrp>. For example, the first record of <it>I. elegans </it>in north-west Spain was made in 1984, whereas <it>I. graellsii </it>is known from this area since 1917 <abbrgrp>
<abbr bid="B22">22</abbr>
</abbrgrp>. In addition, <it>I. elegans </it>is the dominant species in the coastal lagoons of Galicia (north-west Spain), a region where it was a very rare species less than 30 years ago. Furthermore, <it>I. elegans </it>is still rapidly expanding in the area, and in several coastal populations, that are dominated by <it>I. graellsii</it>, immigrant individuals of <it>I. elegans </it>are now starting to appear <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp>. In a literature revision, Monetti <it>et al</it>. <abbrgrp>
<abbr bid="B20">20</abbr>
</abbrgrp> have found that at least six Spanish localities that held both species simultaneously before the 1980's, had only <it>I. elegans </it>in 2002. Recent observations of <it>I. elegans </it>individuals in south Spain (personal observation), where only <it>I. graellsii </it>populations have been detected until now, and in western Spain, support that this species is gradually expanding its distribution in southern latitudes and western longitudes. <it>Ischnura elegans </it>has also expanded elsewhere; in the UK it has expanded its northern range by approximately 168 km in the last few decades, which is more than double than the average expansion distance of other odonates <abbrgrp>
<abbr bid="B23">23</abbr>
</abbrgrp>. Likewise, Parmesan <it>et al</it>. <abbrgrp>
<abbr bid="B24">24</abbr>
</abbrgrp> showed that 22 of 35 European butterfly species have shifted their ranges over the last century. The recent change in the climate has been suggested to drive changes in both phenology <abbrgrp>
<abbr bid="B25">25</abbr>
</abbrgrp> and distribution <abbrgrp>
<abbr bid="B23">23</abbr>
</abbrgrp> of odonates.</p>
<fig id="F1"><title><p>Figure 1</p></title><caption><p>Map showing spatial distribution of <it>I. elegans </it>and <it>I. graellsii </it>in Europe and northern Africa</p></caption><text>
   <p><b>Map showing spatial distribution of <it>I. elegans </it>and <it>I. graellsii </it>in Europe and northern Africa</b>. <it>I. elegans </it>(grey region) and <it>I. graellsii </it>(dark grey) in Europe and northern Africa, and the overlapping distribution of the two species in Spain (grey with stars). We sampled nine populations (166 samples) dominated by individuals that we phenotypically classified as <it>I. elegans </it>in three areas in Spain; north-west (1. Laxe, 2. Louro, 3. Doni&#241;os), north and central (4. Arreo, 5. Alfaro, 6. Baldajo) and east (Mediterranean coast: 7. Europa, 8. Amposta, 9. Marjal del Moro). Thirteen populations of allopatric <it>I. elegans </it>were sampled from Europe (10. Vigueirat, 11. Heuringhem, 12. Het Vinne, 13. Kaiserslautern, 14. Liverpool, 15. V&#228;rpinge, 16. Genarp, 17. Gran Sasso d'Italia, 18. Lublin-Zemborzyce, 19. Zwi&#281;czyca Resz&#243;w, 20. Breznica, 21. Suchoi Limon, 22. Enmakov Island; 220 samples). Finally, three populations of <it>I. graellsii </it>from the allopatric region in Iberia (23. Campus, 24. Ribeira de Cobres, 25. C&#243;rdoba) and one in northern Africa (26. Sa&#239;dia) (56 samples) were sampled.</p>
</text><graphic file="1471-2148-11-210-1"/></fig>
<p>
<it>Ischnura elegans </it>and <it>I. graellsii </it>are very similar ecologically and morphologically, but they can be unambiguously identified by the morphology of prothorax and anal appendages and by the comparatively small body and short wings of <it>I. graellsii </it>
<abbrgrp>
<abbr bid="B20">20</abbr>
</abbrgrp>. Furthermore, genetic analyses have shown that <it>I. elegans </it>and <it>I. graellsii </it>are very similar both at allozymes <abbrgrp>
<abbr bid="B26">26</abbr>
</abbrgrp>, and at the mitochondrial <it>Cytochrome b </it>and <it>Coenzyme II </it>genes [0.2% genetic distance, 21]. Previous work has documented that the two species hybridize in the laboratory <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp>, and hybrids (i.e. morphologically intermediate individuals) have been detected in one sympatric locality in north-western Spain <abbrgrp>
<abbr bid="B20">20</abbr>
</abbrgrp>.</p>
<p>Wirtz <abbrgrp>
<abbr bid="B27">27</abbr>
</abbrgrp> reviewed the factors promoting unidirectional or reciprocal hybridization and proposed a hypothesis based on sexual selection to explain unidirectional hybridization. He proposed that hybridization is more likely between the female of the rare species and the male of the common species. However, when the rare species is also the bigger species, hybridization can be impeded by mechanical incompatibility <abbrgrp>
<abbr bid="B28">28</abbr>
</abbrgrp>, and the outcome degree and direction of hybridization is difficult to predict. Previous findings from the field (one population) <abbrgrp>
<abbr bid="B20">20</abbr>
</abbrgrp> and laboratory <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp> indicate that <it>I. graellsii </it>(the common and smaller species in Iberia) suffers a mating disadvantage in sympatry with <it>I. elegans </it>(the less abundant and larger species in Iberia). In particular, males of <it>I. elegans </it>readily mate with females of <it>I. graellsii </it>in the laboratory but males of <it>I. graellsii </it>are mechanically incapable of mating with <it>I. elegans </it>females <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp>. The resulting F<sub>1</sub>-hybrid males can only mate with <it>I. graellsii </it>females, whereas the F<sub>1</sub>-hybrid females are mechanically incapable of mating with males of <it>I. graellsii </it>but can instead mate with <it>I. elegans </it>males <abbrgrp>
<abbr bid="B20">20</abbr>
</abbrgrp>. Furthermore, F<sub>1</sub>-hybrids (males and females) show a similar degree of reduced viability and fertility [S&#225;nchez-Guill&#233;n RA, Wellenreuther M and Cordero-Rivera A: Strong asymmetry in the relative strengths of prezygotic and postzygotic barriers between two damselfly sister species, submitted]. These conditions can be hypothesized to result in a directional bias in hybridization in favour of <it>I. elegans </it>that could explain the recently documented range expansion of <it>I. elegans </it>into areas that were previously only occupied by <it>I. graellsii </it>
<abbrgrp>
<abbr bid="B20">20</abbr>
<abbr bid="B21">21</abbr>
</abbrgrp>. This agrees with the colonization pattern of <it>I. elegans </it>in the area. Under the described scenario of introgressive hybridization, we hypothesize extensive introgression of <it>I. graellsii </it>genes into the Spanish <it>I. elegans </it>populations. Furthermore, introgression and interspecific competition are probably contributing to the fast range expansion of <it>I. elegans </it>and contraction of <it>I. graellsii </it>in Iberia.</p>
<p>Interestingly, several <it>Ischnura </it>species, including <it>I. elegans </it>and <it>I. graellsii</it>, are characterized by a conspicuous colour polymorphism that is limited to females <abbrgrp>
<abbr bid="B21">21</abbr>
<abbr bid="B29">29</abbr>
<abbr bid="B30">30</abbr>
<abbr bid="B31">31</abbr>
</abbrgrp>. Females exhibit three colour morphs; one androchrome 1] and two gynochromes colour morphs (the green-brown <it>infuscans </it>and the orange-brown <it>infuscans-obsoleta </it>(<it>I. elegans</it>) or <it>aurantiaca </it>(<it>I. graellsii</it>)) <abbrgrp>
<abbr bid="B21">21</abbr>
<abbr bid="B29">29</abbr>
</abbrgrp>. The colour polymorphism is controlled by a simple genetic system consisting of one gene with three alleles that are in a dominance hierarchy <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp>. How the colour polymorphism of <it>Ischnura </it>damselflies is maintained in space and time has been a much discussed subject. Indeed, hybridization was the first mechanism proposed for maintaining the colour polymorphism in this genus <abbrgrp>
<abbr bid="B32">32</abbr>
</abbrgrp>. For example, hybridization was hypothesized to maintain contrasting androchrome frequencies in nearby populations of <it>I. damula </it>and <it>I. demorsa</it>, and <it>I. elegans </it>and <it>I. graellsii</it>, respectively <abbrgrp>
<abbr bid="B21">21</abbr>
<abbr bid="B32">32</abbr>
</abbrgrp>. Under the aforementioned scenario of extensive introgressive hybridization of <it>I. graellsii </it>genes into the Spanish <it>I. elegans </it>populations, and the hypothesised role of the hybridization for the temporal maintenance of contrasting androchrome frequencies; female morph frequencies of <it>I. elegans </it>in nearby populations to <it>I. graellsii </it>must be more similar to <it>I. graellsii </it>frequencies, due to the absorption of the typical morph frequencies, than in populations of <it>I. elegans </it>located far away of <it>I. graellsii </it>populations. In fact, Gosden &amp; Svensson <abbrgrp>
<abbr bid="B33">33</abbr>
</abbrgrp> proposed that the contrasting androchrome frequencies observed in the Spanish populations of <it>I. elegans </it>could be a by-product of the hybridization in combination with a founder effect.</p>
<p>The objectives of the present study were to examine the spatial distribution of <it>I. graellsii </it>and <it>I. elegans </it>in the Iberian Peninsula, evaluate the extent of introgression of <it>I. graellsii </it>genes into the recently established <it>I. elegans </it>populations in Spain, and to understand the role of the hybridization on the temporal maintenance of female colour morph frequencies in both species. Therefore, we conducted a detailed reconstruction of the distribution of the two species in Spain to quantify the overlap in space between the species. Furthermore, we examined the degree of introgression in nine <it>I. elegans </it>populations within the zone of overlap using both nuclear microsatellite markers <abbrgrp>
<abbr bid="B34">34</abbr>
</abbrgrp> and mitochondrial genes <abbrgrp>
<abbr bid="B35">35</abbr>
</abbrgrp>. Previous studies have shown that analyses based on differentiated markers between parental species can be used to efficiently and accurately describe admixture proportions, i.e. the degree of introgression, in F<sub>1</sub>-hybrids and backcrosses see <abbrgrp>
<abbr bid="B36">36</abbr>
<abbr bid="B37">37</abbr>
<abbr bid="B38">38</abbr>
<abbr bid="B39">39</abbr>
</abbrgrp>. Furthermore, studies have also shown the usefulness of mitochondrial DNA in the study of introgressive hybridization because of their maternal inheritance <abbrgrp>
<abbr bid="B40">40</abbr>
</abbrgrp>. Specifically, with this method F<sub>1</sub>- and F<sub>2</sub>-hybrids may be assigned to a particular maternal species based on the mtDNA haplotype they carry. However, a prerequisite is that the species do not share haplotypes, which may happen because of hybridization and ancestral polymorphisms <abbrgrp>
<abbr bid="B41">41</abbr>
</abbrgrp>. Finally, in order to evaluate if the previously observed uncharacteristic morph frequencies of <it>I. elegans </it>populations in north-western Spain, where frequencies are broadly different between populations <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp>, extend into the sympatric area (northern, central and eastern Spain), we combined morph frequency data from previous studies <abbrgrp>
<abbr bid="B42">42</abbr>
</abbrgrp> with new data from this study, and discuss the proposed hypothesis about the role of hybridization in the temporal maintenance of the colour polymorphism.</p>
</sec>
<sec>
<st>
<p>Results</p>
</st>
<sec>
<st>
<p>Spatial distribution of <it>I. graellsii </it>and <it>I. elegans </it>in the Iberian Peninsula</p>
</st>
<p>Using the available distribution data of <it>I. elegans </it>and <it>I. graellsii </it>in Spain, we constructed two geographic maps to show their overall distributional range (Figure <figr fid="F2">2A</figr>, <it>Ischnura elegans</it>; 2B, <it>I. graellsii</it>). Species overlap in north and central Spain (from west to east). In particular, <it>I. graellsii </it>is found all over the Iberian Peninsula, while <it>I. elegans </it>is very rare in southern Spain (Figure <figr fid="F2">2</figr>).</p>
<fig id="F2"><title><p>Figure 2</p></title><caption><p>Geographic distribution of <it>I. elegans </it>(A) and <it>I. graellsii </it>(B) in Spain</p></caption><text>
   <p><b>Geographic distribution of <it>I. elegans </it>(A) and <it>I. graellsii </it>(B) in Spain</b>.</p>
</text><graphic file="1471-2148-11-210-2"/></fig>
</sec>
<sec>
<st>
<p>Introgressive hybridization</p>
</st>
<p>All population groups (Spanish <it>I. elegans </it>populations, European <it>I. elegans </it>populations excluding Spain and <it>I. graellsii </it>populations) exhibited a high degree of molecular diversity (see Table <tblr tid="T1">1</tblr>). Estimates of observed and expected heterozygosity were similar and ranged from 0.56-0.70 and 0.61-0.76, respectively (Table <tblr tid="T1">1</tblr>). In the Spanish <it>I. elegans </it>populations, we detected a total of 87 alleles, 11 less than in the other European <it>I. elegans </it>populations. In contrast to <it>I. elegans</it>, we found somewhat fewer (66) alleles for <it>I. graellsii</it>, perhaps due to the fact that the microsatellites were specifically developed for <it>I. elegans </it>which could cause an ascertainment bias. Estimates of allelic richness were comparable between the Spanish and the other European <it>I. elegans </it>populations (6.54 and 6.03, respectively), and were considerably higher than in <it>I. graellsii </it>(3.41; Table <tblr tid="T1">1</tblr>).</p>
<tbl id="T1"><title><p>Table 1</p></title><caption><p>Basic population genetic data by regions and for each population:</p></caption><tblbdy cols="8">
      <r>
         <c ca="center">
            <p>
               <b>Species</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>Populations</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>Region</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>N</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>H<sub>O</sub></b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>H<sub>E</sub></b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>Alleles</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>Richness</b>
            </p>
         </c>
      </r>
      <r>
         <c cspan="8">
            <hr/>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center" cspan="2">
            <p>All Europe (except Spain)</p>
         </c>
         <c ca="center">
            <p>220</p>
         </c>
         <c ca="center">
            <p>0.701</p>
         </c>
         <c ca="center">
            <p>0.764</p>
         </c>
         <c ca="center">
            <p>98</p>
         </c>
         <c ca="center">
            <p>6.031</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center" cspan="2">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>166</p>
         </c>
         <c ca="center">
            <p>0.705</p>
         </c>
         <c ca="center">
            <p>0.767</p>
         </c>
         <c ca="center">
            <p>87</p>
         </c>
         <c ca="center">
            <p>6.538</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center" cspan="2">
            <p>Iberia-Africa</p>
         </c>
         <c ca="center">
            <p>56</p>
         </c>
         <c ca="center">
            <p>0.577</p>
         </c>
         <c ca="center">
            <p>0.682</p>
         </c>
         <c ca="center">
            <p>64</p>
         </c>
         <c ca="center">
            <p>3.409</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Doni&#241;os</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>0.711</p>
         </c>
         <c ca="center">
            <p>0.700</p>
         </c>
         <c ca="center">
            <p>41</p>
         </c>
         <c ca="center">
            <p>6.591</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Laxe</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>14</p>
         </c>
         <c ca="center">
            <p>0.715</p>
         </c>
         <c ca="center">
            <p>0.805</p>
         </c>
         <c ca="center">
            <p>32</p>
         </c>
         <c ca="center">
            <p>6.146</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Louro</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>15</p>
         </c>
         <c ca="center">
            <p>0.712</p>
         </c>
         <c ca="center">
            <p>0.729</p>
         </c>
         <c ca="center">
            <p>32</p>
         </c>
         <c ca="center">
            <p>5.792</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Arreo</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>15</p>
         </c>
         <c ca="center">
            <p>0.631</p>
         </c>
         <c ca="center">
            <p>0.761</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>7.784</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Baldajo</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>17</p>
         </c>
         <c ca="center">
            <p>0.603</p>
         </c>
         <c ca="center">
            <p>0.795</p>
         </c>
         <c ca="center">
            <p>48</p>
         </c>
         <c ca="center">
            <p>7.673</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Alfaro</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>0.663</p>
         </c>
         <c ca="center">
            <p>0.758</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>7.046</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Europa</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>18</p>
         </c>
         <c ca="center">
            <p>0.671</p>
         </c>
         <c ca="center">
            <p>0.787</p>
         </c>
         <c ca="center">
            <p>48</p>
         </c>
         <c ca="center">
            <p>7.109</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Amposta</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>0.691</p>
         </c>
         <c ca="center">
            <p>0.770</p>
         </c>
         <c ca="center">
            <p>51</p>
         </c>
         <c ca="center">
            <p>7.156</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Marjal del Moro</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>0.671</p>
         </c>
         <c ca="center">
            <p>0.751</p>
         </c>
         <c ca="center">
            <p>44</p>
         </c>
         <c ca="center">
            <p>5.776</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Lublin-Zemborzyce</p>
         </c>
         <c ca="center">
            <p>East Europe</p>
         </c>
         <c ca="center">
            <p>14</p>
         </c>
         <c ca="center">
            <p>0.7505</p>
         </c>
         <c ca="center">
            <p>0.797</p>
         </c>
         <c ca="center">
            <p>60</p>
         </c>
         <c ca="center">
            <p>8.081</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Vigueirat</p>
         </c>
         <c ca="center">
            <p>South France</p>
         </c>
         <c ca="center">
            <p>16</p>
         </c>
         <c ca="center">
            <p>0.733</p>
         </c>
         <c ca="center">
            <p>0.804</p>
         </c>
         <c ca="center">
            <p>42</p>
         </c>
         <c ca="center">
            <p>6.252</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Gran Sasso d'Italia</p>
         </c>
         <c ca="center">
            <p>Central Italy</p>
         </c>
         <c ca="center">
            <p>19</p>
         </c>
         <c ca="center">
            <p>0.777</p>
         </c>
         <c ca="center">
            <p>0.813</p>
         </c>
         <c ca="center">
            <p>51</p>
         </c>
         <c ca="center">
            <p>7.461</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Liverpool</p>
         </c>
         <c ca="center">
            <p>Great Britain</p>
         </c>
         <c ca="center">
            <p>16</p>
         </c>
         <c ca="center">
            <p>0.624</p>
         </c>
         <c ca="center">
            <p>0.709</p>
         </c>
         <c ca="center">
            <p>38</p>
         </c>
         <c ca="center">
            <p>5.964</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Heuringhem</p>
         </c>
         <c ca="center">
            <p>North France</p>
         </c>
         <c ca="center">
            <p>19</p>
         </c>
         <c ca="center">
            <p>0.729</p>
         </c>
         <c ca="center">
            <p>0.781</p>
         </c>
         <c ca="center">
            <p>45</p>
         </c>
         <c ca="center">
            <p>7.380</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Kaiserslautern</p>
         </c>
         <c ca="center">
            <p>South Germany</p>
         </c>
         <c ca="center">
            <p>17</p>
         </c>
         <c ca="center">
            <p>0.765</p>
         </c>
         <c ca="center">
            <p>0.770</p>
         </c>
         <c ca="center">
            <p>53</p>
         </c>
         <c ca="center">
            <p>8.177</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Het Vinne</p>
         </c>
         <c ca="center">
            <p>Belgium</p>
         </c>
         <c ca="center">
            <p>18</p>
         </c>
         <c ca="center">
            <p>0.682</p>
         </c>
         <c ca="center">
            <p>0.795</p>
         </c>
         <c ca="center">
            <p>46</p>
         </c>
         <c ca="center">
            <p>7.248</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>H&#246;je &#197;</p>
         </c>
         <c ca="center">
            <p>Sweden</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>0.653</p>
         </c>
         <c ca="center">
            <p>0.717</p>
         </c>
         <c ca="center">
            <p>43</p>
         </c>
         <c ca="center">
            <p>7.010</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Genarp</p>
         </c>
         <c ca="center">
            <p>Sweden</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>0.680</p>
         </c>
         <c ca="center">
            <p>0.753</p>
         </c>
         <c ca="center">
            <p>44</p>
         </c>
         <c ca="center">
            <p>7.203</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Zwi&#281;czyca Resz&#243;w</p>
         </c>
         <c ca="center">
            <p>East Europe</p>
         </c>
         <c ca="center">
            <p>11</p>
         </c>
         <c ca="center">
            <p>0.668</p>
         </c>
         <c ca="center">
            <p>0.827</p>
         </c>
         <c ca="center">
            <p>52</p>
         </c>
         <c ca="center">
            <p>7.264</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Breznica</p>
         </c>
         <c ca="center">
            <p>East Europe</p>
         </c>
         <c ca="center">
            <p>18</p>
         </c>
         <c ca="center">
            <p>0.712</p>
         </c>
         <c ca="center">
            <p>0.796</p>
         </c>
         <c ca="center">
            <p>47</p>
         </c>
         <c ca="center">
            <p>6.678</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Suchoi Limon</p>
         </c>
         <c ca="center">
            <p>East Europe</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>0.719</p>
         </c>
         <c ca="center">
            <p>0.791</p>
         </c>
         <c ca="center">
            <p>45</p>
         </c>
         <c ca="center">
            <p>6.537</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Enmakov Island</p>
         </c>
         <c ca="center">
            <p>East Europe</p>
         </c>
         <c ca="center">
            <p>15</p>
         </c>
         <c ca="center">
            <p>0.713</p>
         </c>
         <c ca="center">
            <p>0.766</p>
         </c>
         <c ca="center">
            <p>49</p>
         </c>
         <c ca="center">
            <p>6.811</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Campus</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>17</p>
         </c>
         <c ca="center">
            <p>0.485</p>
         </c>
         <c ca="center">
            <p>0.694</p>
         </c>
         <c ca="center">
            <p>31</p>
         </c>
         <c ca="center">
            <p>3.249</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>C&#243;rdoba</p>
         </c>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>0.647</p>
         </c>
         <c ca="center">
            <p>0.653</p>
         </c>
         <c ca="center">
            <p>36</p>
         </c>
         <c ca="center">
            <p>3.466</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Ribeira de Cobres</p>
         </c>
         <c ca="center">
            <p>Portugal</p>
         </c>
         <c ca="center">
            <p>14</p>
         </c>
         <c ca="center">
            <p>0.684</p>
         </c>
         <c ca="center">
            <p>0.719</p>
         </c>
         <c ca="center">
            <p>31</p>
         </c>
         <c ca="center">
            <p>3.713</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Sa&#239;dia</p>
         </c>
         <c ca="center">
            <p>North Africa</p>
         </c>
         <c ca="center">
            <p>13</p>
         </c>
         <c ca="center">
            <p>0.490</p>
         </c>
         <c ca="center">
            <p>0.677</p>
         </c>
         <c ca="center">
            <p>25</p>
         </c>
         <c ca="center">
            <p>3.118</p>
         </c>
      </r>
   </tblbdy><tblfn>
      <p>observed (H<sub>O</sub>) and expected heterozygosity (H<sub>E</sub>), number of alleles and allelic richness. N represents number of individuals genotyped per population.</p>
   </tblfn></tbl>
<p>Analyses of the overall genetic structure showed that <it>I. elegans </it>populations were significantly differentiated from one another in Europe outside Spain (F<sub>ST </sub>= 0.031, <it>P </it>&lt; 0.0001) as well as within Spain (F<sub>ST </sub>= 0.049, <it>P </it>&lt; 0.0001). Moreover, populations of <it>I. graellsii </it>were also significantly differentiated from one another (F<sub>ST </sub>= 0.029, <it>P </it>&lt; 0.0001).</p>
<p>Four of 23 principal component axes accounted for a significant amount of genetic variation among samples, as indicated by a screen plot. The first axis contained 24% (F<sub>ST </sub>= 0.024, <it>P </it>= 0.11), the second axis 17% (F<sub>ST </sub>= 0.017, <it>P </it>= 0.08), the third axis 14% (F<sub>ST </sub>= 0.014, <it>P </it>= 0.07) and the fourth axis 11% (F<sub>ST </sub>= 0.011, <it>P </it>= 0.05) of the total variation (Figure <figr fid="F3">3</figr>). The first two principal components thus summarise almost half (41%) of the total variation inherent in all <it>I. elegans </it>and <it>I. graellsii </it>populations. The scores for the first principal component axis revealed a clear separation of <it>I. graellsii </it>and <it>I</it>. <it>elegans </it>populations, suggesting that major population differences were predominantly caused by species rather than geographic areas <it>per se</it>. Major population differences (nested inside species) were revealed by the second PCA axis, where two of the Spanish <it>I. elegans </it>populations (Louro and Laxe; Table <tblr tid="T2">2</tblr> and <tblr tid="T3">3</tblr>) were situated in the same quadrant that was occupied by all <it>I. graellsii </it>populations (Figure <figr fid="F3">3</figr>).</p>
<fig id="F3"><title><p>Figure 3</p></title><caption><p>Principal component analysis of allopatric <it>I. graellsii</it>, and allopatric and sympatric <it>I. elegans </it>populations</p></caption><text>
   <p><b>Principal component analysis of allopatric <it>I. graellsii</it>, and allopatric and sympatric <it>I. elegans </it>populations</b>. The first (PCA 1) and second (PCA 2) axes represent the first two factorial components and sum up to 41% of explained variation.</p>
</text><graphic file="1471-2148-11-210-3"/></fig>
<tbl id="T2"><title><p>Table 2</p></title><caption><p>Species, sampling locality, sample size for molecular analysis (N), ecology, sampling year, latitude and longitude.</p></caption><tblbdy cols="7">
      <r>
         <c ca="left">
            <p>
               <b>Species</b>
            </p>
         </c>
         <c ca="left">
            <p>
               <b>Locality</b>
            </p>
         </c>
         <c ca="left">
            <p>
               <b>Ecology</b>
            </p>
         </c>
         <c ca="left">
            <p>
               <b>N</b>
            </p>
         </c>
         <c ca="left">
            <p>
               <b>Year</b>
            </p>
         </c>
         <c ca="left">
            <p>
               <b>Latitude</b>
            </p>
         </c>
         <c ca="left">
            <p>
               <b>Longitude</b>
            </p>
         </c>
      </r>
      <r>
         <c cspan="7">
            <hr/>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="left">
            <p>C&#243;rdoba, southern Spain</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>37.8833</p>
         </c>
         <c ca="left">
            <p>-4.7666</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="left">
            <p>Universitary-Campus, north-western Spain</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>1999</p>
         </c>
         <c ca="left">
            <p>42.171</p>
         </c>
         <c ca="left">
            <p>-8.6778</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="left">
            <p>Sa&#239;dia, northern Africa</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>35.1217</p>
         </c>
         <c ca="left">
            <p>-2.35</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="left">
            <p>Ribeira de Cobres, southern Portugal</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2005</p>
         </c>
         <c ca="left">
            <p>37.496</p>
         </c>
         <c ca="left">
            <p>-7.52</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Both species</it>
            </p>
         </c>
         <c ca="left">
            <p>Arreo, north-central Spain</p>
         </c>
         <c ca="left">
            <p>sympatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>42.4775</p>
         </c>
         <c ca="left">
            <p>-2.5787</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Both species</it>
            </p>
         </c>
         <c ca="left">
            <p>Baldajo, central Spain</p>
         </c>
         <c ca="left">
            <p>sympatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>40.2426</p>
         </c>
         <c ca="left">
            <p>-3.4206</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Both species</it>
            </p>
         </c>
         <c ca="left">
            <p>Alfaro, north-central Spain</p>
         </c>
         <c ca="left">
            <p>sympatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2007</p>
         </c>
         <c ca="left">
            <p>42.1908</p>
         </c>
         <c ca="left">
            <p>-1.7423</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Doni&#241;os, north-western Spain</p>
         </c>
         <c ca="left">
            <p>sympatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2007</p>
         </c>
         <c ca="left">
            <p>43.2927</p>
         </c>
         <c ca="left">
            <p>-8.1855</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Laxe, north-western Spain</p>
         </c>
         <c ca="left">
            <p>sympatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2007</p>
         </c>
         <c ca="left">
            <p>43.2125</p>
         </c>
         <c ca="left">
            <p>-8.9554</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Louro, north-western Spain</p>
         </c>
         <c ca="left">
            <p>sympatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2007</p>
         </c>
         <c ca="left">
            <p>42.758</p>
         </c>
         <c ca="left">
            <p>-9.0953</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Europa, north-eastern Spain</p>
         </c>
         <c ca="left">
            <p>sympatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>42.2438</p>
         </c>
         <c ca="left">
            <p>3.1028</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Amposta, central-eastern Spain</p>
         </c>
         <c ca="left">
            <p>sympatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>40.2732</p>
         </c>
         <c ca="left">
            <p>0.2156</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Marjal del Moro, south-eastern Spain</p>
         </c>
         <c ca="left">
            <p>sympatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>39.0727</p>
         </c>
         <c ca="left">
            <p>-0.3135</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Liverpool, Great Britain</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>53.2439</p>
         </c>
         <c ca="left">
            <p>-2.584</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>V&#228;rpinge, southern Sweden</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2005</p>
         </c>
         <c ca="left">
            <p>55.7022</p>
         </c>
         <c ca="left">
            <p>13.1437</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Genarp, southern Sweden</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2005</p>
         </c>
         <c ca="left">
            <p>55.6075</p>
         </c>
         <c ca="left">
            <p>13.4042</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Het Vinne, Belgium</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2007</p>
         </c>
         <c ca="left">
            <p>50.833</p>
         </c>
         <c ca="left">
            <p>5.117</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Kaiserslautern, southern Germany</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>49.2641</p>
         </c>
         <c ca="left">
            <p>7.4674</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Heuringhem, northern France</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>50.4209</p>
         </c>
         <c ca="left">
            <p>2.164</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Vigueirat, southern France</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>43.5311</p>
         </c>
         <c ca="left">
            <p>4.3012</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Gran Sasso, central Italy</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2008</p>
         </c>
         <c ca="left">
            <p>42.5015</p>
         </c>
         <c ca="left">
            <p>13.4328</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Lublin-Zemborzyce, Poland</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2007</p>
         </c>
         <c ca="left">
            <p>51.15</p>
         </c>
         <c ca="left">
            <p>22.34</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Zwi&#281;czyca Resz&#243;w, Poland</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2007</p>
         </c>
         <c ca="left">
            <p>50.0167</p>
         </c>
         <c ca="left">
            <p>21.9167</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Breznica, Poland</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2007</p>
         </c>
         <c ca="left">
            <p>49.9696</p>
         </c>
         <c ca="left">
            <p>19.6429</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Suchoi Limon, Ukraine</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2006</p>
         </c>
         <c ca="left">
            <p>46.03</p>
         </c>
         <c ca="left">
            <p>30.047</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="left">
            <p>Enmakov Island, Ukraine</p>
         </c>
         <c ca="left">
            <p>allopatric</p>
         </c>
         <c ca="left">
            <p>20</p>
         </c>
         <c ca="left">
            <p>2006</p>
         </c>
         <c ca="left">
            <p>45.435</p>
         </c>
         <c ca="left">
            <p>29.525</p>
         </c>
      </r>
   </tblbdy></tbl>
<tbl id="T3"><title><p>Table 3</p></title><caption><p>Number of <it>I.elegans</it>, <it>I. graellsii </it>and hybrid males examined in each putative introgressed populations.</p></caption><tblbdy cols="6">
      <r>
         <c ca="left">
            <p>
               <b>Population</b>
            </p>
         </c>
         <c ca="left">
            <p>
               <b>Region</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>Year</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>
                  <it>I. elegans</it>
               </b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>
                  <it>I. graellsii</it>
               </b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>
                  <it>Hybrids</it>
               </b>
            </p>
         </c>
      </r>
      <r>
         <c cspan="6">
            <hr/>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>Doni&#241;os</p>
         </c>
         <c ca="left">
            <p>north-western Spain</p>
         </c>
         <c ca="center">
            <p>2007</p>
         </c>
         <c ca="center">
            <p>80</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>Laxe</p>
         </c>
         <c ca="left">
            <p>north-western Spain</p>
         </c>
         <c ca="center">
            <p>2007</p>
         </c>
         <c ca="center">
            <p>206</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>Louro</p>
         </c>
         <c ca="left">
            <p>north-western Spain</p>
         </c>
         <c ca="center">
            <p>2007</p>
         </c>
         <c ca="center">
            <p>136</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>Arreo</p>
         </c>
         <c ca="left">
            <p>north-central Spain</p>
         </c>
         <c ca="center">
            <p>2008</p>
         </c>
         <c ca="center">
            <p>160</p>
         </c>
         <c ca="center">
            <p>2</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>Alfaro</p>
         </c>
         <c ca="left">
            <p>north-central Spain</p>
         </c>
         <c ca="center">
            <p>2007</p>
         </c>
         <c ca="center">
            <p>38</p>
         </c>
         <c ca="center">
            <p>63</p>
         </c>
         <c ca="center">
            <p>4</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>Baldajo</p>
         </c>
         <c ca="left">
            <p>central Spain</p>
         </c>
         <c ca="center">
            <p>2008</p>
         </c>
         <c ca="center">
            <p>34</p>
         </c>
         <c ca="center">
            <p>2</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>Europa</p>
         </c>
         <c ca="left">
            <p>north-eastern Spain</p>
         </c>
         <c ca="center">
            <p>2008</p>
         </c>
         <c ca="center">
            <p>121</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>Amposta</p>
         </c>
         <c ca="left">
            <p>central-eastern Spain</p>
         </c>
         <c ca="center">
            <p>2008</p>
         </c>
         <c ca="center">
            <p>30</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>Marjal del Moro</p>
         </c>
         <c ca="left">
            <p>south-eastern Spain</p>
         </c>
         <c ca="center">
            <p>2008</p>
         </c>
         <c ca="center">
            <p>25</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
   </tblbdy></tbl>
<p>Analyses of the population structure in S<smcaps>TRUCTURE</smcaps> supported the molecular differentiation between the two <it>Ischnura </it>species, although the <it>&#916;K</it>-method suggested three clusters as the most likely population structure (Figure <figr fid="F4">4</figr>). More specifically, the results showed that one of the genetic clusters highly corresponded to the <it>I. graellsii </it>group, while the other two genetic clusters were best represented by <it>I. elegans </it>genotypes (one mainly corresponding to northern, central and southern European populations, and one to populations in eastern Europe), with the Spanish populations showing an intermediate assignment to each of these three genetic clusters (Figure <figr fid="F4">4</figr>).</p>
<fig id="F4"><title><p>Figure 4</p></title><caption><p>Estimated population structure of <it>I. elegans </it>from Bayesian structure analyses using the program S<smcaps>TRUCTURE</smcaps></p></caption><text>
   <p><b>Estimated population structure of <it>I. elegans </it>from Bayesian structure analyses using the program S<smcaps>TRUCTURE</smcaps></b>. <b>4.A</b>. <it>&#916;K</it>-values for different <it>K</it>; suggesting <it>K </it>= 3 as the most likely structure (<it>&#916;K </it>= m|L"(<it>K</it>)|/s[L(<it>K</it>)]; see <abbrgrp><abbr bid="B67">67</abbr></abbrgrp>. <b>4.B</b>. Mean likelihood (&#177; SD) of <it>K </it>for different numbers of clusters, <it>K</it>. <b>4.C</b>. Individual Bayesian assignment probabilities for <it>K </it>= 3 for 22 populations of <it>I. elegans </it>and 4 <it>I. graellsii </it>populations. Individuals are represented by thin vertical lines, which are partitioned into <it>K </it>shaded segments representing each individual's estimated membership fraction. The black lines separate sampling sites. <b>4.D</b>. The average Bayesian assignment probabilities for <it>K </it>= 3 for the four geographical areas; (1) eastern Europe, (2) northern, central and southern Europe, (3) Spanish <it>I. elegans </it>populations, and (4) <it>I. graellsii </it>populations.</p>
</text><graphic file="1471-2148-11-210-4"/></fig>
<p>Based on these results, we included all populations of <it>I. graellsii </it>and <it>I. elegans </it>in the S<smcaps>TRUCTURE</smcaps> runs (<it>K </it>= 2) to analyse the individual admixture proportions of <it>I. elegans </it>individuals in Spain (Table <tblr tid="T4">4</tblr>). These results showed that one genetic cluster clearly corresponded to <it>I. graellsii</it>, while the other cluster corresponded to <it>I. elegans </it>(European populations outside Spain; Table <tblr tid="T4">4</tblr>; Figure <figr fid="F5">5</figr>). The majority of individuals of the European <it>I. elegans </it>outside Spain (95%) and <it>I. graellsii </it>(88%) were assigned with a certainty of at least 90% to each of these clusters. However, only 27% of individuals of the Spanish <it>I. elegans </it>were strongly assigned to <it>I. elegans </it>(admixture proportions &#8805; 90%) and one individual (from the sympatric population Alfaro) was assigned to <it>I. graellsii </it>(admixture proportion to <it>I. elegans </it>&lt; 10%). The rest of the Spanish <it>I. elegans </it>individuals were intermediate between the two clusters (with a skew of admixture proportion towards <it>I. elegans</it>, see additional file <supplr sid="S1">1</supplr>), suggesting a significant degree of introgressed <it>I. graellsii </it>alleles (Table <tblr tid="T4">4</tblr>; Figure <figr fid="F5">5</figr>).</p>
<tbl id="T4"><title><p>Table 4</p></title><caption><p>Summary of the results from the Admixture models in S<smcaps>TRUCTURE</smcaps> for <it>Ischnura </it>populations.</p></caption><tblbdy cols="8">
      <r>
         <c ca="right" cspan="8">
            <p>
               <b>Admixture proportion to <it>I. elegans </it>cluster</b>
            </p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <b>Region/Locality</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>N</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>Species</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>&#8805; 90</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>(89-68)</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>(67-21)</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>(20-11)</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>&#8804; 10</b>
            </p>
         </c>
      </r>
      <r>
         <c cspan="8">
            <hr/>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Iberia-Africa</p>
         </c>
         <c ca="center">
            <p>56</p>
         </c>
         <c ca="center">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>3</p>
         </c>
         <c ca="center">
            <p>4</p>
         </c>
         <c ca="center">
            <p>49</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>All Europe (except Spain)</p>
         </c>
         <c ca="center">
            <p>220</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>209</p>
         </c>
         <c ca="center">
            <p>11</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Spain</p>
         </c>
         <c ca="center">
            <p>166</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>45</p>
         </c>
         <c ca="center">
            <p>97</p>
         </c>
         <c ca="center">
            <p>23</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>1</p>
         </c>
      </r>
      <r>
         <c cspan="8">
            <hr/>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <it>Spanish localities</it>
            </p>
         </c>
         <c>
            <p/>
         </c>
         <c>
            <p/>
         </c>
         <c>
            <p/>
         </c>
         <c>
            <p/>
         </c>
         <c>
            <p/>
         </c>
         <c>
            <p/>
         </c>
         <c>
            <p/>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Doni&#241;os</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>8</p>
         </c>
         <c ca="center">
            <p>10</p>
         </c>
         <c ca="center">
            <p>2</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Laxe</p>
         </c>
         <c ca="center">
            <p>14</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>5</p>
         </c>
         <c ca="center">
            <p>9</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Louro</p>
         </c>
         <c ca="center">
            <p>15</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>1</p>
         </c>
         <c ca="center">
            <p>12</p>
         </c>
         <c ca="center">
            <p>2</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Arreo</p>
         </c>
         <c ca="center">
            <p>17</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>7</p>
         </c>
         <c ca="center">
            <p>10</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Baldajo</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>4</p>
         </c>
         <c ca="center">
            <p>15</p>
         </c>
         <c ca="center">
            <p>1</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Alfaro</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>7</p>
         </c>
         <c ca="center">
            <p>9</p>
         </c>
         <c ca="center">
            <p>3</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>1</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Europa</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>8</p>
         </c>
         <c ca="center">
            <p>11</p>
         </c>
         <c ca="center">
            <p>1</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Amposta</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>6</p>
         </c>
         <c ca="center">
            <p>13</p>
         </c>
         <c ca="center">
            <p>1</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>Marjal del Moro</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>4</p>
         </c>
         <c ca="center">
            <p>12</p>
         </c>
         <c ca="center">
            <p>4</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
   </tblbdy></tbl>
<fig id="F5"><title><p>Figure 5</p></title><caption><p>Admixture analysis in S<smcaps>TRUCTURE</smcaps></p></caption><text>
   <p><b>Admixture analysis in S<smcaps>TRUCTURE</smcaps></b>. <b>A </b>and <b>B </b>panels show the admixture analysis in S<smcaps>TRUCTURE</smcaps> of 166 genotypes of nine Spanish populations of <it>I. elegans </it>(upper panel) and for the artificial hybrids genotypes generated with the program H<smcaps>YBRID-LAB</smcaps> (mid panel). The estimated admixture proportion of each individual is represented by the mean assignment (&#177; 90% credible intervals) to the <it>I. elegans </it>cluster. <b>C </b>panel shows admixture proportions of all 472 <it>I. elegans </it>and <it>I. graellsii </it>genotypes. Each individual is represented by a single vertical line broken into two segments which are proportional to the estimated membership in each of the two genetic clusters (Q<sub>1 </sub>for <it>I. graellsii </it>(black), and Q<sub>2 </sub>for <it>I. elegans </it>(grey)).</p>
</text><graphic file="1471-2148-11-210-5"/></fig>
<suppl id="S1">
<title>
<p>Additional file 1</p>
</title>
<text>
<p>
<b>Bayesian assignment probabilities</b>. The average Bayesian assignment probabilities in each of the two genetic clusters (Q<sub>1 </sub>for <it>I. graellsii </it>(grey), and Q<sub>2 </sub>for <it>I. elegans </it>(grey dark)), for the nine Spanish populations of <it>I. elegans</it>.</p>
</text>
<file name="1471-2148-11-210-S1.PDF">
   <p>Click here for file</p>
</file>
</suppl>
<p>The admixture proportions of the artificial hybrids and backcrosses ranged between 11-89% (Table <tblr tid="T5">5</tblr>; Figure <figr fid="F5">5</figr>). The F<sub>1 </sub>and F<sub>2 </sub>showed admixture proportions to <it>I. elegans </it>between 67 and 21%; the 1 GB (first <it>I. graellsii </it>backcross) between 67 and 11%; and the four <it>I. elegans </it>backcrosses (1-4 EB) between 89 and 21% (Table <tblr tid="T5">5</tblr>; Figure <figr fid="F5">5</figr>). Based on these results, we defined three conservative assignment groups: backcrosses with <it>I. elegans </it>with admixture between 89-68%; backcrosses with <it>I. graellsii </it>ranging between 20-11%; and a mixed group of F<sub>1</sub>, F<sub>2 </sub>and backcrosses ranging between 67-21%. When the Spanish <it>I. elegans </it>individuals (N = 166) were allocated by their admixture proportions in one of these three groups, a total of 97 individuals (admixture proportions to <it>I. elegans </it>between 89-68%) were assigned to backcrosses with <it>I. elegans </it>(1-4 EB), whereas not a single individual was assigned to the backcross with <it>I. graellsii </it>(1 GB) (Table <tblr tid="T5">5</tblr>). Finally, the rest of the Spanish <it>I. elegans </it>(i.e. 23 individuals with admixture proportions to <it>I. elegans </it>between 67-21%), excluding the single individual from Alfaro that was assigned to <it>I. graellsii</it>, were assigned to the mixed-hybrid group, including F<sub>1</sub>, F<sub>2 </sub>and backcrosses with the parental species (Table <tblr tid="T4">4</tblr>).</p>
<tbl id="T5"><title><p>Table 5</p></title><caption><p>Summary of the results from the Admixture models in S<smcaps>TRUCTURE</smcaps> for artificial hybrids and backcrosses:</p></caption><tblbdy cols="7">
      <r>
         <c ca="center" cspan="7">
            <p>
               <b>Admixture proportion to <it>I. elegans </it>cluster</b>
            </p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>
               <b>Type of cross</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>N</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>&#8805; 90</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>(90-68)</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>(67-21)</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>(20-11)</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>&#8804; 10</b>
            </p>
         </c>
      </r>
      <r>
         <c cspan="7">
            <hr/>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>F1</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>F2</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>1 GB</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>35</p>
         </c>
         <c ca="center">
            <p>15</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>1 EB</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>24</p>
         </c>
         <c ca="center">
            <p>26</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>2 EB</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>30</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>3 EB</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>40</p>
         </c>
         <c ca="center">
            <p>10</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>4 EB</p>
         </c>
         <c ca="center">
            <p>50</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>42</p>
         </c>
         <c ca="center">
            <p>8</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
      </r>
   </tblbdy><tblfn>
      <p>first-generation hybrid (F<sub>1</sub>; i.e. <it>I. graellsii </it>&#215; <it>I. elegans</it>), second-generation hybrid (F<sub>2</sub>; i.e. F<sub>1 </sub>&#215; F<sub>1</sub>), first backcross with <it>I. elegans </it>(1 EB; i.e. F<sub>1 </sub>&#215; <it>I. elegans</it>), first backcross with <it>I. graellsii </it>(1 GB; F<sub>1 </sub>&#215; <it>I. graellsii</it>), second backcross with <it>I. elegans </it>(2 EB; 1 EB &#215; <it>I. elegans</it>), third backcross with <it>I. elegans </it>(3 EB; 2 EB &#215; <it>I. elegans</it>), and forth backcross with <it>I. elegans </it>(4 EB; 3 EB &#215; <it>I. elegans</it>).</p>
   </tblfn></tbl>
</sec>
<sec>
<st>
<p>Low genetic variation and shared polymorphism at mitochondrial genes</p>
</st>
<p>The alignments for the <it>Cytochrome C Oxidase I </it>and <it>II </it>(COI-COII), <it>Cytochrome B </it>(CYTB), <it>12S rRNA </it>(12S) and <it>NADH Dehydrogenase 1 </it>(ND1) fragments included 591 bp, 673 bp, 457 bp, 370 bp and 591 bp, respectively (Table <tblr tid="T6">6</tblr>). All new sequences were deposited in GenBank (accession numbers: <ext-link ext-link-id="HQ834794" ext-link-type="gen">HQ834794</ext-link>-<ext-link ext-link-id="HQ834810" ext-link-type="gen">HQ834810</ext-link>). COI fragment showed no polymorphic sites, revealing a unique haplotype (H1) that was shared by the two species. COII showed one polymorphic site, revealing two haplotypes (haplotype diversity, H = 0.409 &#177; 0.133; nucleotide diversity, &#960; = 0.00122). Haplotype H2, the most abundant haplotype, was shared by the species in both allopatric and sympatric regions, while haplotype H3 appeared only in the three samples of <it>I. graellsii </it>from one allopatric region (Morocco). CYTB fragment showed two polymorphic sites revealing three haplotypes (H = 0.163 &#177; 0.099; &#960; = 0.00053). Each species showed one unique haplotype (H5 and H6), in a single sample from one allopatric region (Greece and Morocco), respectively, while the rest of the samples of both species shared a common haplotype (H4). The 12S fragment showed three polymorphic sites revealing four haplotypes (H = 0.087 &#177; 0.047; &#960; = 0.00024). <it>Ischnura elegans </it>showed three unique haplotypes (H7, H8, H9), each of which appeared in a unique sample (two haplotypes in samples from allopatric regions and one in a sample from a sympatric region), while the rest of the samples of both species shared the common haplotype H10. The last fragment, ND1, showed one polymorphic site, revealing two haplotypes (H = 0.250 &#177; 0.180; &#960; = 0.00042). The most abundant haplotype (H11) was shared by both species (from allopatric and sympatric regions), while the second haplotype (H12) appeared only in one sample of <it>I. graellsii </it>(from an allopatric population in Portugal).</p>
<tbl id="T6"><title><p>Table 6</p></title><caption><p>Number of individuals genotyped per gene (N), sequence length (bp), number of haplotypes (S), haplotype diversity (H) and nucleotide diversity (&#960;) for each of the five analysed mitochondrial genes.</p></caption><tblbdy cols="7">
      <r>
         <c ca="center">
            <p>
               <b>Mitochondrial gene</b>
            </p>
         </c>
         <c>
            <p/>
         </c>
         <c>
            <p/>
         </c>
         <c ca="center" cspan="4">
            <p>
               <b>Genetic measures</b>
            </p>
         </c>
      </r>
      <r>
         <c>
            <p/>
         </c>
         <c ca="center">
            <p>
               <b>N</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>bp</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>S (<it>I. elegans</it>)</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>S (<it>I. graellsii</it>)</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>H</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>&#960;</b>
            </p>
         </c>
      </r>
      <r>
         <c cspan="7">
            <hr/>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>COI</p>
         </c>
         <c ca="center">
            <p>13</p>
         </c>
         <c ca="center">
            <p>591</p>
         </c>
         <c ca="center">
            <p>H1</p>
         </c>
         <c ca="center">
            <p>H1</p>
         </c>
         <c ca="center">
            <p>0.000</p>
         </c>
         <c ca="center">
            <p>0.00000</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>COII</p>
         </c>
         <c ca="center">
            <p>12</p>
         </c>
         <c ca="center">
            <p>673</p>
         </c>
         <c ca="center">
            <p>H2</p>
         </c>
         <c ca="center">
            <p>H2, H3</p>
         </c>
         <c ca="center">
            <p>0.409 &#177; 0.133</p>
         </c>
         <c ca="center">
            <p>0.00122</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>CYTB</p>
         </c>
         <c ca="center">
            <p>24</p>
         </c>
         <c ca="center">
            <p>457</p>
         </c>
         <c ca="center">
            <p>H4, H5</p>
         </c>
         <c ca="center">
            <p>H5, H6</p>
         </c>
         <c ca="center">
            <p>0.163 &#177; 0.099</p>
         </c>
         <c ca="center">
            <p>0.00053</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>12S</p>
         </c>
         <c ca="center">
            <p>68</p>
         </c>
         <c ca="center">
            <p>370</p>
         </c>
         <c ca="center">
            <p>H7, H8, H9, H10</p>
         </c>
         <c ca="center">
            <p>H10</p>
         </c>
         <c ca="center">
            <p>0.087 &#177; 0.047</p>
         </c>
         <c ca="center">
            <p>0.00024</p>
         </c>
      </r>
      <r>
         <c ca="center">
            <p>ND1</p>
         </c>
         <c ca="center">
            <p>8</p>
         </c>
         <c ca="center">
            <p>591</p>
         </c>
         <c ca="center">
            <p>H11</p>
         </c>
         <c ca="center">
            <p>H11, H12</p>
         </c>
         <c ca="center">
            <p>0.250 &#177; 0.180</p>
         </c>
         <c ca="center">
            <p>0.00042</p>
         </c>
      </r>
   </tblbdy><tblfn>
      <p>The genes are <it>Cytochrome C Oxidase I </it>and <it>II </it>(COI-COII), <it>Cytochrome B </it>(CYTB), <it>12S rRNA </it>(12S) and <it>NADH Dehydrogenase 1 </it>(ND1). GenBank Accession numbers: <ext-link ext-link-id="HQ834794" ext-link-type="gen">HQ834794</ext-link>-<ext-link ext-link-id="HQ834810" ext-link-type="gen">HQ834810</ext-link>.</p>
   </tblfn></tbl>
</sec>
<sec>
<st>
<p>Colour morph frequencies</p>
</st>
<p>All populations showed all three female morphs, with the exception of Sa&#239;dia in northern Africa (where the <it>aurantiaca </it>morph was missing) (Table <tblr tid="T7">7</tblr>). In populations dominated by <it>I. elegans </it>from north-central, central and eastern Spain, androchrome, <it>infuscans </it>and <it>infuscans-obsoleta </it>frequencies were highly variable between populations (range of androchrome frequencies: 3.3-42.9%; <it>infuscans</it>: 6.7-68.8%; <it>infuscans-obsoleta</it>: 11.8-76.7%) which is consistent with what has previously been observed for the <it>I. elegans </it>populations from north-western Spain <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp>. In allopatric populations of <it>I. graellsii</it>, androchrome frequencies were always below 20% (3.0-18.8%); with the <it>infuscans </it>morph being the most abundant morph type (64.9-89.7%). The sympatric populations, O Vilar and Xu&#241;o, which have previously shown very high frequencies of androchromes for both species <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp>, also showed in our study high levels of androchrome frequencies (12.5-15.7% in <it>I. graellsii </it>and 40.0-47.6% in <it>I. elegans</it>). In addition, the sympatric populations Las Ca&#241;as and Alfaro from central Spain further showed high androchrome frequencies (13.0-17.1% in <it>I. graellsii </it>and 69.7-70.8% in <it>I. elegans</it>).</p>
<tbl id="T7"><title><p>Table 7</p></title><caption><p>Frequencies of female colour morphs of <it>Ischnura elegans </it>and <it>I. graellsii</it>.</p></caption><tblbdy cols="9">
      <r>
         <c ca="left">
            <p>
               <b>Species</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>Ecology</b>
            </p>
         </c>
         <c ca="left">
            <p>
               <b>Locality</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>Date</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>N</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>A</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>O</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>I</b>
            </p>
         </c>
         <c ca="center">
            <p>
               <b>Source</b>
            </p>
         </c>
      </r>
      <r>
         <c cspan="9">
            <hr/>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Allopatric</p>
         </c>
         <c ca="left">
            <p>Sa&#239;dia, northern Africa</p>
         </c>
         <c ca="center">
            <p>Jun-09</p>
         </c>
         <c ca="center">
            <p>29</p>
         </c>
         <c ca="center">
            <p>10.3</p>
         </c>
         <c ca="center">
            <p>89.7</p>
         </c>
         <c ca="center">
            <p>0</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Allopatric</p>
         </c>
         <c ca="left">
            <p>Puente de los Arenales, southern Spain</p>
         </c>
         <c ca="center">
            <p>Sep-08</p>
         </c>
         <c ca="center">
            <p>33</p>
         </c>
         <c ca="center">
            <p>3</p>
         </c>
         <c ca="center">
            <p>78.8</p>
         </c>
         <c ca="center">
            <p>18.2</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Allopatric</p>
         </c>
         <c ca="left">
            <p>Do&#241;ana, southern Spain</p>
         </c>
         <c ca="center">
            <p>Jun-03</p>
         </c>
         <c ca="center">
            <p>77</p>
         </c>
         <c ca="center">
            <p>10.4</p>
         </c>
         <c ca="center">
            <p>76.6</p>
         </c>
         <c ca="center">
            <p>13</p>
         </c>
         <c ca="center">
            <p>21</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Allopatric</p>
         </c>
         <c ca="left">
            <p>Granjuela, southern Spain</p>
         </c>
         <c ca="center">
            <p>Sep-08</p>
         </c>
         <c ca="center">
            <p>35</p>
         </c>
         <c ca="center">
            <p>11.4</p>
         </c>
         <c ca="center">
            <p>77.1</p>
         </c>
         <c ca="center">
            <p>11.4</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Allopatric</p>
         </c>
         <c ca="left">
            <p>Jaraiz de la Vera, central Spain</p>
         </c>
         <c ca="center">
            <p>Jun-07</p>
         </c>
         <c ca="center">
            <p>67</p>
         </c>
         <c ca="center">
            <p>13.5</p>
         </c>
         <c ca="center">
            <p>64.9</p>
         </c>
         <c ca="center">
            <p>21.6</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Allopatric</p>
         </c>
         <c ca="left">
            <p>Ribeira de Cobres, southern Portugal</p>
         </c>
         <c ca="center">
            <p>Apr-2003</p>
         </c>
         <c ca="center">
            <p>48</p>
         </c>
         <c ca="center">
            <p>18.8</p>
         </c>
         <c ca="center">
            <p>72.9</p>
         </c>
         <c ca="center">
            <p>8.3</p>
         </c>
         <c ca="center">
            <p>21</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Troi, northern Spain</p>
         </c>
         <c ca="center">
            <p>Jul-08</p>
         </c>
         <c ca="center">
            <p>54</p>
         </c>
         <c ca="center">
            <p>14.8</p>
         </c>
         <c ca="center">
            <p>72.2</p>
         </c>
         <c ca="center">
            <p>13</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Sympatric-I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>O Vilar, north-western Spain</p>
         </c>
         <c ca="center">
            <p>May-Jul 2006</p>
         </c>
         <c ca="center">
            <p>121</p>
         </c>
         <c ca="center">
            <p>15.7</p>
         </c>
         <c ca="center">
            <p>33.06</p>
         </c>
         <c ca="center">
            <p>51.24</p>
         </c>
         <c ca="center">
            <p>This study</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Sympatric-I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>O Vilar, north-western Spain</p>
         </c>
         <c ca="center">
            <p>May-Jul 2007</p>
         </c>
         <c ca="center">
            <p>21</p>
         </c>
         <c ca="center">
            <p>47.62</p>
         </c>
         <c ca="center">
            <p>47.62</p>
         </c>
         <c ca="center">
            <p>4.76</p>
         </c>
         <c ca="center">
            <p>This study</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Sympatric-I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Xu&#241;o, north-western Spain</p>
         </c>
         <c ca="center">
            <p>Jun-Sept 2006</p>
         </c>
         <c ca="center">
            <p>48</p>
         </c>
         <c ca="center">
            <p>12.5</p>
         </c>
         <c ca="center">
            <p>33.33</p>
         </c>
         <c ca="center">
            <p>54.17</p>
         </c>
         <c ca="center">
            <p>This study</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Sympatric-I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Xu&#241;o, north-western Spain</p>
         </c>
         <c ca="center">
            <p>Jun-Sept 2007</p>
         </c>
         <c ca="center">
            <p>15</p>
         </c>
         <c ca="center">
            <p>40</p>
         </c>
         <c ca="center">
            <p>40</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>This study</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Sympatric-I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Las Ca&#241;as, north-central Spain</p>
         </c>
         <c ca="center">
            <p>Jul-07</p>
         </c>
         <c ca="center">
            <p>23</p>
         </c>
         <c ca="center">
            <p>17.4</p>
         </c>
         <c ca="center">
            <p>69.6</p>
         </c>
         <c ca="center">
            <p>13</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Sympatric-I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Las Ca&#241;as, north-central Spain</p>
         </c>
         <c ca="center">
            <p>Aug-07</p>
         </c>
         <c ca="center">
            <p>24</p>
         </c>
         <c ca="center">
            <p>70.83</p>
         </c>
         <c ca="center">
            <p>25</p>
         </c>
         <c ca="center">
            <p>4.17</p>
         </c>
         <c ca="center">
            <p>This study</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Sympatric-I. graellsii</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Alfaro, north-central Spain</p>
         </c>
         <c ca="center">
            <p>Jul-07</p>
         </c>
         <c ca="center">
            <p>23</p>
         </c>
         <c ca="center">
            <p>13</p>
         </c>
         <c ca="center">
            <p>60.9</p>
         </c>
         <c ca="center">
            <p>26.1</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>Sympatric-I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Alfaro, north-central Spain</p>
         </c>
         <c ca="center">
            <p>Aug-07</p>
         </c>
         <c ca="center">
            <p>33</p>
         </c>
         <c ca="center">
            <p>69.7</p>
         </c>
         <c ca="center">
            <p>27.3</p>
         </c>
         <c ca="center">
            <p>3</p>
         </c>
         <c ca="center">
            <p>This study</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Arreo, north Spain</p>
         </c>
         <c ca="center">
            <p>Jul-08</p>
         </c>
         <c ca="center">
            <p>30</p>
         </c>
         <c ca="center">
            <p>6.3</p>
         </c>
         <c ca="center">
            <p>68.8</p>
         </c>
         <c ca="center">
            <p>25</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Almoquera, central Spain</p>
         </c>
         <c ca="center">
            <p>Aug-2008</p>
         </c>
         <c ca="center">
            <p>28</p>
         </c>
         <c ca="center">
            <p>42.9</p>
         </c>
         <c ca="center">
            <p>42.9</p>
         </c>
         <c ca="center">
            <p>14.3</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Baldajo, central Spain</p>
         </c>
         <c ca="center">
            <p>Aug-2008</p>
         </c>
         <c ca="center">
            <p>34</p>
         </c>
         <c ca="center">
            <p>29.4</p>
         </c>
         <c ca="center">
            <p>58.8</p>
         </c>
         <c ca="center">
            <p>11.8</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Europa, north-eastern Spain</p>
         </c>
         <c ca="center">
            <p>Jul-08</p>
         </c>
         <c ca="center">
            <p>30</p>
         </c>
         <c ca="center">
            <p>16.7</p>
         </c>
         <c ca="center">
            <p>6.7</p>
         </c>
         <c ca="center">
            <p>76.7</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Amposta, north-eastern Spain</p>
         </c>
         <c ca="center">
            <p>Jul-08</p>
         </c>
         <c ca="center">
            <p>30</p>
         </c>
         <c ca="center">
            <p>3.3</p>
         </c>
         <c ca="center">
            <p>33.3</p>
         </c>
         <c ca="center">
            <p>63.3</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Barranco de Caixanet, south-eastern Spain</p>
         </c>
         <c ca="center">
            <p>Sep-08</p>
         </c>
         <c ca="center">
            <p>27</p>
         </c>
         <c ca="center">
            <p>25.9</p>
         </c>
         <c ca="center">
            <p>25.9</p>
         </c>
         <c ca="center">
            <p>48.1</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
      <r>
         <c ca="left">
            <p>
               <it>I. elegans</it>
            </p>
         </c>
         <c ca="center">
            <p>Sympatric</p>
         </c>
         <c ca="left">
            <p>Marjal del Moro, south-eastern Spain</p>
         </c>
         <c ca="center">
            <p>Sep-08</p>
         </c>
         <c ca="center">
            <p>25</p>
         </c>
         <c ca="center">
            <p>36</p>
         </c>
         <c ca="center">
            <p>20</p>
         </c>
         <c ca="center">
            <p>44</p>
         </c>
         <c ca="center">
            <p>39</p>
         </c>
      </r>
   </tblbdy><tblfn>
      <p>The number of mature female examined in each locality is indicated (N). A: <it>androchrome</it>, I: <it>infuscans </it>and O: <it>infuscans-obsoleta </it>(<it>I. elegans</it>) or <it>aurantiaca </it>(<it>I. graellsii</it>).</p>
   </tblfn></tbl>
</sec>
</sec>
<sec>
<st>
<p>Discussion</p>
</st>
<p>Hybridization and genomic introgression are repeatedly suggested to be important elements in evolutionary processes such as maintenance of genetic variation, adaptation and speciation <abbrgrp>
<abbr bid="B4">4</abbr>
<abbr bid="B5">5</abbr>
<abbr bid="B6">6</abbr>
</abbrgrp>. Determining the degree of genetic exchange between recently diverged species may be of particular interest in this sense since they typically show incomplete reproductive barriers. Moreover, the pattern and extent of hybridization and introgression can have important conservation implications because it may lead to the replacement of one of the hybridizing taxa <abbrgrp>
<abbr bid="B10">10</abbr>
<abbr bid="B43">43</abbr>
<abbr bid="B44">44</abbr>
<abbr bid="B45">45</abbr>
</abbrgrp>.</p>
<p>In the present study, we have revealed extensive hybridization and introgression in <it>I. elegans </it>populations in Iberia where it co-occurs sympatrically with its closely related sister species <it>I. graellsii</it>. Distribution maps for both species show an extended area of overlap in northern and central Spain. <it>Ischnura graellsii </it>is generally very abundant all along the Iberian Peninsula, while <it>I. elegans </it>has a patchy distribution. For example, <it>I. elegans </it>is very rare in southern Spain. In the sympatric regions, <it>I. elegans </it>is also less abundant than <it>I. graellsii </it>(with the exception of the area around Valencia) and is not present at all in some provinces (Figure <figr fid="F2">2</figr>). Consequently, <it>I</it>. <it>graellsii </it>occurs allopatrically in southern Iberia (Figure <figr fid="F2">2</figr>), whereas <it>I. elegans </it>is exclusively found in areas that are also occupied by <it>I. graellsii</it>. Our admixture analyses in S<smcaps>TRUCTURE</smcaps> revealed clear evidence of past and present hybridization and introgression between <it>I. elegans </it>and <it>I. graellsii </it>over a large geographic area in northern Spain. The degree of introgression in the populations is consistent with <it>I. elegans </it>backcrosses and occasional F<sub>1</sub>-hybrids. Thus, hybridization between these two damselfly species is a relatively recent and widespread phenomenon. Interestingly, the studied populations have been going through a recent species turn-over and are now dominated by <it>I. elegans </it>individuals that appear to carry introgressed <it>I. graellsii </it>genetic material. These kinds of dramatic demographic and genetic effects have not previously been documented in odonates, although it is known from other taxa. For instance, over the past century, the blue-winged (<it>Vermivora pinus</it>) warbler has rapidly replaced the golden-winged warbler (<it>V. chrysoptera</it>) over an extensive part of their hybrid zone in eastern north America. Marker-based analyses show asymmetric and rapid introgression from blue-winged warbler into golden-winged warbler in some areas and bidirectional maternal gene flow in others <abbrgrp>
<abbr bid="B46">46</abbr>
<abbr bid="B47">47</abbr>
</abbrgrp>. Rapid introgression has also been detected in other taxa, e.g. in pocket gophers (<it>Geomys bursarius major </it>and <it>G. knoxjonesi</it>) <abbrgrp>
<abbr bid="B48">48</abbr>
</abbrgrp>.</p>
<sec>
<st>
<p>Extent of hybridization and direction of introgression</p>
</st>
<p>In vertebrates, hybridization is particularly common in fish, where several hundred interspecific and intergeneric crosses have been reported, and in birds, with roughly 10% of all species known to have bred in nature with another species e.g. <abbrgrp>
<abbr bid="B5">5</abbr>
<abbr bid="B27">27</abbr>
<abbr bid="B46">46</abbr>
<abbr bid="B47">47</abbr>
<abbr bid="B48">48</abbr>
<abbr bid="B49">49</abbr>
<abbr bid="B50">50</abbr>
</abbrgrp>. In comparison, detailed genetic studies of hybridization and introgression, and thus the knowledge about these phenomena, are lacking for most odonates <abbrgrp>
<abbr bid="B12">12</abbr>
<abbr bid="B13">13</abbr>
</abbrgrp>. As mentioned above, three previous genetic studies failed in detecting extensive hybridization between different pairs of odonate species <abbrgrp>
<abbr bid="B14">14</abbr>
<abbr bid="B15">15</abbr>
<abbr bid="B16">16</abbr>
<abbr bid="B17">17</abbr>
</abbrgrp>. Our admixture analysis in S<smcaps>TRUCTURE</smcaps> showed that the <it>I. elegans </it>populations Louro and Laxe in north-western Spain had the highest degree of introgression of <it>I. graellsii </it>alleles. This is not surprising, given that north-western Spain is the region where hybridization between <it>I. elegans </it>and <it>I. graellsii </it>was most recently detected <abbrgrp>
<abbr bid="B20">20</abbr>
</abbrgrp>. In 1990, <it>I. elegans, I. graellsii </it>and hybrids were found in Foz (north-western Spain), which is geographically close to Louro and Laxe. However, after only ten years, the population was dominated by individuals that were phenotypically classified as <it>I. elegans</it>, although morphological intermediate and <it>I. graellsii </it>males were occasionally detected <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp>. The population Laxe was visited for the first time in June 2001 (two visits) and only <it>I. elegans </it>were detected, although at a low densities (between 0.2 to 1.3 captured males/minute). At a visit in June 2002, <it>I. elegans </it>were found at a similar density (0.5 males/minute). Five years later (in 2007), we revisited the population and the density had reached the highest value in the region. A total of seven visits were conducted in 2007, between June and August, and the density ranged between 3.3 and 14.7 males/minute; and neither <it>I. graellsii </it>nor putative hybrids were detected. Nevertheless, the admixture analyses showed that none of the 14 examined individuals at Laxe could be genetically assigned to pure <it>I. elegans </it>status. Nine individuals were assigned to F<sub>1</sub>, F<sub>2</sub>, or backcrosses with <it>I. elegans </it>(admixture proportion between 67-21%), and five individuals were assigned to backcrosses with <it>I. elegans </it>(admixture proportion between 89-68%). In 1980, Louro was visited for first time by Ocharan <abbrgrp>
<abbr bid="B22">22</abbr>
</abbrgrp> and mainly <it>I. graellsii </it>individuals were observed. However, Torralba and Ocharan <abbrgrp>
<abbr bid="B51">51</abbr>
</abbrgrp> reviewed Ocharan's samples from Louro (sampled in 1980) and have now identified both species in the sample; nevertheless, <it>I. graellsii </it>species still remains the dominant species. However, on our first visit in 2000 and on subsequent visits, <it>I. elegans </it>individuals completely dominated in numbers (a couple of <it>I. graellsii </it>individuals were detected among hundreds of <it>I. elegans</it>). Only one out of the 15 Louro individuals that were molecularly examined in the present study was assigned to be pure <it>I. elegans</it>. In addition, the vast majority of the individuals (93%) showed an assignment proportion between 89-68%, suggesting that these individuals were backcrosses, and not F<sub>1 </sub>or F<sub>2 </sub>hybrids.</p>
<p>These results are corroborated by the PCA-analysis. Both Laxe and Louro were placed within the <it>I. graellsii </it>quadrant, indicating a significant degree of molecular similarity between these <it>I. elegans </it>populations and <it>I. graellsii</it>. Analyses of the remaining Spanish <it>I. elegans </it>populations showed that only 31% of the individuals were pure <it>I. elegans</it>, and that the remaining 69% showed admixture proportions expected for hybrids and backcrosses with <it>I. elegans</it>. In the Alfaro population in the north-central Spain where both species co-occur in equal numbers, one individual classified as <it>I. elegans </it>had a very high proportion of <it>I. graellsii </it>alleles. This either suggest that this individual was misclassified despite the fact that we only collected males to minimise misidentifications <abbrgrp>
<abbr bid="B20">20</abbr>
</abbrgrp>, or that it is a backcross that has inherited a very high proportion of <it>I. graellsii </it>alleles at the few markers analysed.</p>
<p>Our suggest that hybridization between <it>I. elegans </it>and <it>I. graellsii </it>is asymmetric and largely unidirectional. This corroborates previous findings in the field <abbrgrp>
<abbr bid="B20">20</abbr>
</abbrgrp> and laboratory <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp> showing that <it>I. graellsii </it>has a mating disadvantage in sympatry with <it>I. elegans</it>. Heterospecific matings, and matings between the F<sub>1</sub>-hybrids and the parental species, rarely take place with <it>I. elegans </it>females, but occur more frequently among <it>I. graellsii </it>females, <it>I. elegans </it>males and hybrids [S&#225;nchez-Guill&#233;n RA, Wellenreuther M and Cordero-Rivera A: Strong asymmetry in the relative strengths of prezygotic and postzygotic barriers between two damselfly sister species, submitted]. The reason for the almost complete lack of hybridization between <it>I. graellsii </it>males and <it>I. elegans </it>females is that males cannot grasp the female by their protothorax <abbrgrp>
<abbr bid="B20">20</abbr>
</abbrgrp>, a mechanical handicap that appears to be a very efficient prezygotic isolation mechanism. Previous work on plants <abbrgrp>
<abbr bid="B52">52</abbr>
<abbr bid="B53">53</abbr>
</abbrgrp> and animals <abbrgrp>
<abbr bid="B27">27</abbr>
</abbrgrp> has suggested that unidirectional hybridization usually occurs between the females of the rare species and the males of a common species, but not <it>vice versa</it>. Wirtz <abbrgrp>
<abbr bid="B27">27</abbr>
</abbrgrp> reviewed the factors promoting unidirectional or reciprocal hybridization and proposed a sexual selection hypothesis for unidirectional hybridization based on the fact that females normally invest more in offspring and, therefore, are more discriminating than males. When heterospecific males are less abundant than conspecific males, females rarely mate with heterospecific males. Consequently, under such a condition, the rare species is usually the maternal parent of the hybrids. However, this is not the case in our study where the more abundant species is initially <it>I. graellsii</it>. <it>Ischnura elegans</it>, on the other hand, appears to be the intruding species and is hence initially the rare species, which has been expanding its range in Spain and is now displacing <it>I. graellsii </it>from some populations and regions. Thus, the direction of hybridization between these two <it>Ischnura </it>species is opposite that expected based on the rare female hybridization hypothesis just outlined e.g. <abbrgrp>
<abbr bid="B27">27</abbr>
</abbrgrp>, but follows the prediction proposed by Grant and Grant <abbrgrp>
<abbr bid="B28">28</abbr>
</abbrgrp>, namely that when the rare species is also the bigger species (in our study <it>I. elegans</it>), hybridization can be impeded by mechanical incompatibility. Laboratory tests have detected that <it>I. elegans </it>females and <it>I. graellsii </it>males are mechanically impaired to form a tandem, preventing over 93% of all matings, while only 13% of the matings between <it>I. graellsii </it>females and <it>I. elegans </it>males are mechanically prevented [S&#225;nchez-Guill&#233;n RA, Wellenreuther M and Cordero-Rivera A: Strong asymmetry in the relative strengths of prezygotic and postzygotic barriers between two damselfly sister species, submitted].</p>
</sec>
<sec>
<st>
<p>The role of hybridization in the maintenance of colour polymorphisms</p>
</st>
<p>Johnson <abbrgrp>
<abbr bid="B33">33</abbr>
</abbrgrp> proposed that the colour polymorphisms in odonates could be maintained due to hybridization between closely related species and balanced by differential predation pressure. According to this hypothesis, androchrome females benefit from avoiding matings with heterospecific males, while gynochromes females are involved in heterospecific matings (usually sterile); the relative fitness of the colour morphs is balanced by a higher probability of predation of the androchrome females. In a recent study on <it>I. elegans </it>and <it>I. graellsii </it>
<abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp>, a role of hybridization for the temporal maintenance of contrasting androchrome frequencies in nearby populations in north-western Spain was suggested. The relatively low androchrome frequencies in <it>I. elegans </it>populations located close to <it>I. graellsii </it>populations, and the relatively high androchrome frequencies in <it>I. graellsii </it>populations adjacent to <it>I. elegans </it>populations, were hypothesized to be caused by the absorption of the, in other circumstances, typical morph frequency <abbrgrp>
<abbr bid="B21">21</abbr>
</abbrgrp>. <it>Ischnura elegans </it>data from other sympatric regions in the Iberian Peninsula now shows that the substantial variation in female morph frequencies between different populations in north-western Spain is not unique to this region; also in other parts of Iberia morph frequencies are drastically variable between populations (androchrome: 3.3-70.8%; <it>infuscans</it>: 6.7-72.9%; <it>infuscans-obsoleta</it>: 3.0-76.7%). Furthermore, other recent studies have revealed that disparate morph frequencies are not restricted to Iberian populations <abbrgrp>
<abbr bid="B53">53</abbr>
<abbr bid="B54">54</abbr>
</abbrgrp>, although androchrome frequencies are typically more abundant in northern latitudes and show less variation between populations than in Iberia [with the exception of Iberia, 53]. In our study, the highest frequencies of androchromes were found in the four populations with both species present (Xu&#241;o, O Vilar, Alfaro and Las Ca&#241;as; Table <tblr tid="T7">7</tblr>); in <it>I. graellsii </it>androchrome frequencies ranged between 12.5 and 17.4% and in <it>I. elegans </it>between 40.0 and 70.8%. Nevertheless, the <it>I. graellsii </it>population Ribeira de Cobres had androchrome frequencies of 18.8%, for this species an atypically high level. However, this comparatively high androchrome frequency cannot be explained by the influence of nearby <it>I. elegans </it>populations, because this population is located in the allopatric region (southern Portugal). Furthermore, in <it>I. elegans </it>the lowest androchrome frequencies were found in north-central Spain (population named Arreo) where the nearest <it>I. graellsii </it>population (named Troi) had higher androchrome frequencies (14.8%) than the <it>I. elegans </it>population (3.3%), and in a coastal population near the Mediterranean coast (eastern Spain) (Amposta; 3.3% androchromes), but here we lack data of <it>I. graellsii </it>morph frequencies in nearby populations.</p>
<p>In conclusion, hybridization is likely to have important implications for the maintenance of multiple female morphs, but only during the short period when two species with contrasting morph frequencies start to hybridize.</p>
<p>The evolution, maintenance and adaptive function of genetic colour polymorphism have received very much attention in a broad range of organisms, e.g. in birds <abbrgrp>
<abbr bid="B55">55</abbr>
</abbrgrp>, reptiles <abbrgrp>
<abbr bid="B56">56</abbr>
</abbrgrp> and insects <abbrgrp>
<abbr bid="B57">57</abbr>
</abbrgrp>. However, the role of hybridization in this context has received little attention, which may simply reflect the fact that only a few suitable study systems are available to study; one being the presently described <it>Ischnura </it>damselfly complex in Spain. Another case is the hybrid zone of the land snails <it>Mandarina mandarina </it>and <it>M. chichijimana </it>in the oceanic Bonin Islands <abbrgrp>
<abbr bid="B58">58</abbr>
</abbrgrp>. In that system, the variability of the colour polymorphism in the hybrid population was substantially higher than that in the pure populations, suggesting that morphological variation was maintained by hybridization <abbrgrp>
<abbr bid="B58">58</abbr>
</abbrgrp>. These results highlight the importance of hybridization as a source of morphological variation, diversity and evolutionary novelty.</p>
</sec>
</sec>
<sec>
<st>
<p>Conclusions</p>
</st>
<p>When hybrids are fertile and backcross with one of the parental species, hybridization will inevitably result in introgression, thereby increasing the genetic variability of the introgressed species <abbrgrp>
<abbr bid="B59">59</abbr>
</abbrgrp>. Even at low levels, introgression of novel genetic material could be an important factor as a source of new genetic and phenotypic variability, and subsequent evolution. Thus a certain degree of hybridization could create favourable conditions for new adaptations <abbrgrp>
<abbr bid="B4">4</abbr>
<abbr bid="B5">5</abbr>
<abbr bid="B6">6</abbr>
</abbrgrp>. In contrast, extensive hybridization and introgression can, as mentioned above, sometimes have important conservation implications when leading to the replacement of one of the hybridizing taxa <abbrgrp>
<abbr bid="B10">10</abbr>
<abbr bid="B42">42</abbr>
<abbr bid="B43">43</abbr>
<abbr bid="B44">44</abbr>
</abbrgrp>. We have documented a unique case of hybridization and unidirectional introgression in polymorphic <it>Ischnura </it>damselflies, where hybridization is likely to having important implications on the temporal maintenance of multiple female morphs. The potential adaptive significance of introgression in the system, and whether this <it>per se </it>has contributed to the rapid species turn-over in sympatric populations in the region, remains to be evaluated.</p>
</sec>
<sec>
<st>
<p>Methods</p>
</st>
<sec>
<st>
<p>Spatial distribution of <it>I. graellsii </it>and <it>I. elegans </it>in the Iberian Peninsula</p>
</st>
<p>We conducted a revision of the distribution data of the two species along the Iberian Peninsula from 1866-2008 using data from Baixeras <it>et al</it>. <abbrgrp>
<abbr bid="B60">60</abbr>
</abbrgrp>, J&#246;dicke <abbrgrp>
<abbr bid="B61">61</abbr>
</abbrgrp> and Ocharan <abbrgrp>
<abbr bid="B22">22</abbr>
<abbr bid="B62">62</abbr>
</abbrgrp>, in the region around la Rioja using data from Tom&#225;s Latasa (personal communication) and along the Iberia using data from Jean Pierre Boudot (personal communication). Using DMAP (Distribution mapping software, Version 7.0) we constructed two geographic maps showing the distribution of both species in Iberia (Figure <figr fid="F2">2</figr>).</p>
</sec>
<sec>
<st>
<p>Study populations and sample collection</p>
</st>
<p>Samples of <it>I. elegans </it>and <it>I. graellsii </it>were collected from 26 populations from Europe and northern Africa (see Table <tblr tid="T2">2</tblr> for details of sampling locations). In particular, all European populations, except the populations from Spain, were classified as allopatric <it>I. elegans </it>populations and included a total of 220 individuals from 13 <it>I. elegans </it>populations. In depth sampling of both <it>I. elegans </it>and <it>I. graellsii </it>was carried out in the sympatric region in Spain; in the north-western corner, the central parts and along the east coast (Figure <figr fid="F1">1</figr>). In these areas, nine sympatric populations (166 individuals) were sampled, and these were, with the exception of Alfaro, dominated by individuals that were phenotypically classified as <it>I. elegans </it>(see Table <tblr tid="T3">3</tblr> for details of species proportions in the sampled populations). In addition, four allopatric <it>I. graellsii </it>populations (56 <it>I. graellsii </it>individuals) from the north, central and south Iberia, and northern Africa were sampled.</p>
<p>At each allopatric and sympatric <it>I. elegans </it>population (see Table <tblr tid="T2">2</tblr>), and at the four allopatric <it>I. graellsii </it>populations, a minimum of 20 adult males were collected during the flight season between 1999-2008 using hand nets. Captured individuals were stored in 100% ethanol until DNA extraction. Only males were sampled because the identification of male <it>I. elegans</it>, <it>I. graellsii </it>and hybrids is more reliable than that of females. Note that the few individuals classified as <it>I. graellsii </it>and hybrids in the Spanish <it>I. elegans </it>populations, mainly found in Alfaro in north-central Spain (Table <tblr tid="T3">3</tblr>), were not included in the genetic analyses because the aim of this study was to test for introgression in <it>I. elegans </it>populations.</p>
</sec>
<sec>
<st>
<p>DNA extraction and microsatellite genotyping</p>
</st>
<p>To extract DNA from the samples, the head of each damselfly was removed, dried and then homogenized using TissueLyser (Qiagen). DNA was extracted by proteinase K digestion followed by a standard phenol/chloroform-isoamylalcohol extraction <abbrgrp>
<abbr bid="B63">63</abbr>
</abbrgrp>. The purified DNA was re-suspended in 50-100 &#956;l of sterile water. The genotypes of all damselflies were assayed at six microsatellite loci previously isolated for this species [I-002, I-015, I-041, I-053, I-095, I-134, for details see 33]. These loci did not deviate statistically from Hardy-Weinberg expectations and linkage equilibrium, and showed no evidence for presence of common null-alleles (using Micro-Checker; <abbrgrp>
<abbr bid="B64">64</abbr>
</abbrgrp>, within populations of both species <abbrgrp>
<abbr bid="B34">34</abbr>
</abbrgrp>. One primer of each pair was 5'-labelled with 6-FAM, HEX or NED florescent dyes. Polymerase chain reactions (PCRs) were carried out in 10 &#956;L volumes on a GeneAmp PCR System 9700 (Applied Biosystems) and contained 4 pmol of each primer, 15 nmol MgCl<sub>2</sub>, 1.25 nmol dNTP, 0.5 U Ampli-taq polymerase and 10-20 ng template. The conditions were: denaturation step of 94&#176;C for 2 minutes, then 35 cycles at 94&#176;C for 30 s, touch-down from 62-58&#176;C for 30 s, 72&#176;C for 30 s followed by 72&#176;C for 10 minutes. Multiplex primer reactions were performed for combinations of primers with matching annealing temperatures but differing size ranges and dye labels, then mixed with a labelled size standard and electrophoresis was conducted on an ABI PRISM 3730 Genetic Analyzer (Applied Biosystems). GeneMapper 3.0 (Applied Biosystems) was used for fragment size determination and allelic designations.</p>
</sec>
<sec>
<st>
<p>Microsatellite DNA Analyses</p>
</st>
<p>The program F<smcaps>STAT </smcaps>
<abbrgrp>
<abbr bid="B65">65</abbr>
</abbrgrp> was used to calculate several basic population genetic measures, namely, the expected heterozygosity (H<sub>E</sub>), observed heterozygosity (H<sub>o</sub>), number of alleles, and the allelic richness for each population. These aforementioned measures as well as the genetic differentiation between populations (F<sub>ST</sub>) were also calculated for three regions, namely the Spanish populations of <it>I. elegans</it>, the European populations of <it>I. elegans </it>(excluding Spain), and the entire sample of <it>I. graellsii</it>.</p>
<p>Principal component analysis (PCA) was used to reduce the variation in the multivariate data set (consisting of 117 alleles at six loci) to two linear combinations. The analysis was done using <smcaps>PCA-GEN </smcaps>
<abbrgrp>
<abbr bid="B66">66</abbr>
</abbrgrp>. The significance of each principal component was assessed from 5000 randomisations of genotypes. The allocation of each species across the two principal components provides a quantitative measure of the degree of the genetic dissimilarity among the populations/species <abbrgrp>
<abbr bid="B18">18</abbr>
</abbrgrp>.</p>
<p>The Bayesian statistical framework provided by the program S<smcaps>TRUCTURE</smcaps> [version 2.2.3, 67] was used to understand the genetic structure among populations and to determine which individuals from the allopatric and sympatric populations of <it>I. elegans </it>and <it>I. graellsii </it>can be classified to a high degree as pure species. S<smcaps>TRUCTURE</smcaps> applies a Bayesian Markov chain Monte Carlo (MCMC) approach that uses model-based clustering to partition individuals into groups. The model accounts for the presence of Hardy-Weinberg and linkage disequilibrium by introducing group structure and attempts to find groupings that (as far as possible) are in equilibrium <abbrgrp>
<abbr bid="B68">68</abbr>
</abbrgrp>. We applied the 'admixture model' with 'correlated allele frequencies' for more details <abbrgrp>
<abbr bid="B69">69</abbr>
</abbrgrp>. For the model, a 'burn-in' period of 20,000 MCMC replicates and a sampling period of 100,000 replicates were used. We performed runs for a number of genetic clusters (<it>K</it>), ranging from one to ten; and for each <it>K</it>, 20 iterations were run. In this way, multiple posterior probability values (log likelihood (lnL) values) for each <it>K </it>were generated, and the most likely <it>K </it>was evaluated by the <it>&#916;K</it>-method following Evanno <it>et al</it>. <abbrgrp>
<abbr bid="B66">66</abbr>
</abbrgrp>.</p>
<p>Admixture analyses in S<smcaps>TRUCTURE</smcaps> were also used to assign all individuals of the Spanish <it>Ischnura </it>populations into each of two genetic clusters, one representing <it>I. graellsii </it>genotypes and one <it>I. elegans</it>. We used the 'prior population information' option in the models to (i) facilitate the clustering process of the reference individuals (i.e. pure <it>I. elegans </it>from central and eastern Europe, and <it>I. graellsii</it>, respectively), and (ii) to calculate the admixture proportions (and &#177; 90% credible regions) of each individual in the Spanish <it>I. elegans </it>populations. This approach was hence used to measure of the degree of introgression of <it>I. graellsii </it>genetic material into the genome of <it>I. elegans </it>in Spain. The model was run for <it>K </it>= 2, where one cluster corresponded to <it>I. graellsii </it>and the other to <it>I. elegans</it>. We used the 'population flag' option to exclude Spanish <it>I. elegans </it>as reference individuals, which implied that the clustering process was based on only <it>I. graellsii </it>samples and <it>I. elegans </it>samples collected outside of Spain. The model was run for 100,000 MCMC replicates, after an initial burn-in period of 20,000 replicates, using the admixture model and correlated frequencies for five iterations <abbrgrp>
<abbr bid="B32">32</abbr>
<abbr bid="B33">33</abbr>
<abbr bid="B34">34</abbr>
<abbr bid="B63">63</abbr>
</abbrgrp>. To generate simulated genotypes of hybrids and backcrosses, we applied the program <smcaps>HYBRID-LAB&#160;</smcaps>
<abbrgrp>
<abbr bid="B70">70</abbr>
</abbrgrp> using the genotypes of 66 individuals of <it>I. graellsii </it>and 240 genotypes of <it>I. elegans </it>collected outside of Spain as initial genotypes. We generated 50 genotypes of each of the following crosses: first-generation hybrid (F<sub>1</sub>; i.e. <it>I. graellsii </it>&#215; <it>I. elegans</it>), second-generation hybrid (F<sub>2</sub>; i.e. F<sub>1 </sub>&#215; F<sub>1</sub>), first backcross with <it>I. elegans </it>(1 EB; i.e. F<sub>1 </sub>&#215; <it>I. elegans</it>), first backcross with <it>I. graellsii </it>(1 GB; F<sub>1 </sub>&#215; <it>I. graellsii</it>), second backcross with <it>I. elegans </it>(2 EB; 1 EB &#215; <it>I. elegans</it>), third backcross with <it>I. elegans </it>(3 EB; 2 EB &#215; <it>I. elegans</it>), and forth backcross with <it>I. elegans </it>(4 EB; 3 EB &#215; <it>I. elegans</it>). We then evaluated the admixture proportions (&#177; 90% credible intervals) of these artificial crosses with S<smcaps>TRUCTURE</smcaps> in the same way as done for the <it>I. elegans </it>samples from Spain (above). To determine the level of introgression of <it>I. graellsii </it>into the Spanish <it>I. elegans </it>populations, the individual admixture proportions of the <it>I. elegans </it>samples from Spain were compared to the admixture proportion for the artificial hybrids and backcrosses.</p>
</sec>
<sec>
<st>
<p>Mitochondrial sequencing</p>
</st>
<p>Three to six damselflies from sympatric and allopatric localities were amplified by polymerase chain reaction (PCR) for part of the mitochondrial <it>Cytochrome C Oxidase I </it>and <it>II </it>genes (COI-COII), part of the mitochondrial <it>Cytochrome B </it>(CYTB) gene and part of the mitochondrial <it>12S rRNA </it>(12S) and <it>NADH Dehydrogenase 1 </it>(ND1). The amplification was done using universal primers: 591 bp of the COI with the primers COI-H (5'-TCAGGGTGACCAAAAAATCA-3') and COI-L (5'-GGTCAACAAATC ATAAAGATATTGG-3') (Marina Maga&#241;a Ramos, personal communication), 673 pb of the COII with the primers TL2-J-3037 (5'- ATGGCAGATTAGTGCAATGG-3') and C2-N-3494 (5'-GGTAAAACTACTCGATTATCAAC-3') and C2-J-3400 (5'-ATTGGACATCAATGATATTGA-3') and TK-N-3785 (5'-GTTTAAGAGACCAGTACTTG-3') <abbrgrp>
<abbr bid="B34">34</abbr>
</abbrgrp>, 457 pb of the CYTB with the primers CB-J-10933 (5'-TATGTACTACCATGAGGACAAATATC-3') and TS1-N-11683 (5'-TATTTCTTTATTATGTTTTCAAAAC-3') <abbrgrp>
<abbr bid="B34">34</abbr>
</abbrgrp>, 370 bp of the 12S with the primers SR-J-14233 (5'-AAGAGCGACGGGCGATGTGT-3') and SR-N-14588 (5'-AAACTAGGATTAGATACCCTATTAT-3') <abbrgrp>
<abbr bid="B30">30</abbr>
</abbrgrp>, and 591 bp of the ND1 gene with CB-J-11545 (5'ACATGAATTGGAGCTCGACCAGT-3') and N1-N-12051 (5'-GATTTTGCTGAAGGTGAATCAGA-3') <abbrgrp>
<abbr bid="B34">34</abbr>
</abbrgrp>. DNA amplification was done in a total reaction volume of 20 &#956;l. The amplification conditions were as follows: 50 ng of DNA (1 &#956;L), 1 unit (0.2 &#956;L) of Taq DNA polymerase (Ecogen), 2 &#956;L 10x of reaction buffer (Ecogen), 0.5 &#956;L of MgCl<sub>2 </sub>(50 mM) (Ecogen), 0.5 &#956;L of dNTPs Mix Sigma (200 &#956;M), and 1 &#956;L of each primer (10 pmol). All PCR reactions were completed in a "GeneAmp PCR system 2700" thermocycler (Applied Biosystems). The PCR program had an initial cycle of 95&#176;C for 3 min, the annealing temperature for 1 min, and an elongation period at 72&#176;C for 45 s, followed by 34 cycles at 95&#176;C for 30 s, with annealing for 45 s, and an elongation phase at 72&#176;C for 45 s, and a final extension phase at 72&#176;C for 10 min. PCR products were sent to an external sequencing service (University of Valencia) where bidirectional sequencing reactions were conducted using Bigdye&#8482;terminator cycle sequencing kit (Applied Biosystems) using automatic sequencer ABI3100 (Applied Biosystems). Forward and reverse sequences were edited in Codon Code Aligned (CodonCode, Dedham, MA, USA) and consensus sequences were aligned with Clustal X <abbrgrp>
<abbr bid="B71">71</abbr>
</abbrgrp> implemented in MEGA v. 4.0 <abbrgrp>
<abbr bid="B72">72</abbr>
<abbr bid="B73">73</abbr>
</abbrgrp>. Variable positions were revised by eye, and only high quality sequences were considered.</p>
</sec>
<sec>
<st>
<p>Mitochondrial data analyses</p>
</st>
<p>Samples of both species were pooled in two groups, depending on the sympatric or allopatric origin. For each gene, genetic diversity was assessed in terms of number of haplotypes (S), and haplotype diversity (H) and nucleotide diversity (&#960;) according to Nei <abbrgrp>
<abbr bid="B74">74</abbr>
</abbrgrp> with D<smcaps>NA</smcaps>SP V4.10 <abbrgrp>
<abbr bid="B74">74</abbr>
</abbrgrp>. Further analyses could not be done because overall low genetic diversity and shared haplotype frequencies.</p>
</sec>
<sec>
<st>
<p>Colour morph frequencies</p>
</st>
<p>We reviewed female morph frequencies from the literature in seven <it>I. graellsii </it>populations from Iberia and northern Africa and seven <it>I. elegans </it>populations from Iberia <abbrgrp>
<abbr bid="B41">41</abbr>
</abbrgrp>. In addition, we estimated female colour morph frequencies in four sympatric populations; Xu&#241;o and O Vilar from north-western Spain, and Alfaro and Las Ca&#241;as from north-central Spain. Populations were visited between June and September during sunny days, in two different years (2006 and 2007) and the sampling was done with entomological nets. Only single, solitary and mature females were used, and colour morph frequencies were estimated from the number of each morph divided by the total number of females.</p>
</sec>
</sec>
<sec>
<st>
<p>Authors' contributions</p>
</st>
<p>RSG designed the study, collected genetic samples, did laboratory work, analysed data and wrote the paper. MW designed the study, did laboratory work, analysed data and wrote the paper. ACR designed the study and wrote the paper. BH designed the study, analysed data and wrote the paper. All authors approved the final version of the manuscript.</p>
</sec>
</bdy><bm>
<ack>
<sec>
<st>
<p>Acknowledgements</p>
</st>
<p>We would like to thank for help with fieldwork I&#241;aki Mezquita, Tom&#225;s Latasa, Mario Garc&#237;a-Par&#237;s, Bernat Garrig&#243;s, Pere Luque, Xoaqu&#237;n Baixeras, Francisco Cano, Jean Pierre Boudot, J&#252;rgen Ott, Cedrick Vanappelghem, Philippe Lambret, and Phill Watts. We would like to thank Geert de Knijf, Tom Kompier, Martin Waldhauser, Xoaqu&#237;n Baixeras, Tom&#225;s Latasa and Jean Pierre Boudot for help with the distribution maps. This research was funded by the Spanish Ministry of Science and Innovation (grant CGL2008-02799 and CGL2008-03197-E to ARC) and the Swedish Research Council (grant 621-2007-5381 and 621-2009-4945 to BHN). RSG is supported by a grant (Formaci&#243;n de Personal Investigador) from Spanish Ministry of Science and Innovation, and MW by postdoctoral scholarships from the Wenner-Gren Foundation, Tryggers Foundation and the Swedish Research Council. Permits to capture damselflies in Spain were issued by each Regional Government to RSG.</p>
</sec>
</ack>
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