Genetic variation and phylogeo n rri hio ral epte 6 N Swordtail ?sh have been studied extensively in relation to diverse aspects of biology; however, little attention has been paid to the Quanti?cation of genetic variation within and among migration of individuals between populations include the phylogenetic relationships among species have been exam- ined extensively (Rosen, 1979; Rauchenberger et al., 1990; Meyer et al., 1994; Borowski et al., 1995; Meyer, 1997; Morris et al., 2001), little attention has been paid to pat- terns of genetic variation within and among populations of swordtails, particularly in a phylogenetic and geographic * Corresponding author. Present address: Departamento de Biolog??a Evolutiva, Instituto de Ecolog??a, A.C. Km 2.5 antigua carretera a Coatepec No. 351, Congregacio?n El Haya Xalapa, Veracruz 91070, Me?xico. Fax: +52 228 818 7809. E-mail address: carla.gutierrez@inecol.edu.mx (C. Gutie?rrez-Rodr??- guez). Molecular Phylogenetics and Evolutpopulations is crucial to understanding the evolutionary processes that promote and maintain their biodiversity (Moritz, 2002) as well as establishing genetic relationships among populations in order to reconstruct their evolution- ary history. Within a species, the distribution of genetic variation within and among populations is in?uenced by several factors such as gene ?ow and genetic drift. Limited dispersal of individuals among populations due to the presence of natural barriers translates into restricted gene topography of the streams, habitat fragmentation and patterns of ?ow from one stream to another (Carvalho, 1993). In this study, we investigate the genetic variation of the swordtail Xiphophorus cortezi, a freshwater ?sh species endemic to the Pa?nuco river system of Mexico. Swordtails and platy?shes (Xiphophorus) have been studied extensively in relation to their systematics, biogeography, genetics, oncology, and behavior (reviewed in Me?e and Snelson, 1989) and are considered a model system for studies in behavioral ecology (Ryan and Rosenthal, 2001). Whilepatterns of genetic variation within and among populations of swordtails. In this study, we sequenced the mtDNA control region from 65 individuals and 10 populations of Xiphophorus cortezi to investigate the genetic variation within and among populations, including tests for correlations between genetic and geographic distances and tests for species monophyly. We found low gene and nucleotide diver- sity within populations and high degrees of genetic di?erentiation among populations. Signi?cant and positive correlations between genetic distance and both river and straight-line geographic distance indicate that genetic di?erentiation among X. cortezi populations can be explained, to some extent, by an isolation-by-distance model and provide evidence of stream capture. Phylogenetic analyses sug- gest that X. cortezi is paraphyletic relative to X. malinche, raising questions concerning the status of these taxa as separate species.  2006 Elsevier Inc. All rights reserved. Keywords: Genetic di?erentiation; Gene ?ow; Monophyletic; Mitochondrial DNA; Swordtail; Xiphophorus cortezi 1. Introduction ?ow and can result in genetic di?erentiation among popu- lations. In river systems, factors that can in?uence theXiphophorus cortezi (Cypri Carla Gutie?rrez-Rodr??guez a,*, Molly R. Mo a Department of Biological Sciences, O b Department of Vertebrate Zoology, National Museum of Natu Received 17 March 2006; revised 27 S Available online Abstract1055-7903/$ - see front matter  2006 Elsevier Inc. All rights reserved. doi:10.1016/j.ympev.2006.10.022graphy of the swordtail ?sh odontiformes, Poeciliidae) s a, Natalie S. Dubois a, Kevin de Queiroz b University, Athens, OH 45701, USA History, Smithsonian Institution, Washington, DC 20560, USA mber 2006; accepted 20 October 2006 ovember 2006 www.elsevier.com/locate/ympev ion 43 (2007) 111?123 hylocontext. Morris et al. (2001) included several populations of X. cortezi in their phylogenetic study of the northern swordtails, and in some of their analyses, these populations did not form a monophyletic group. However, relation- ships among X. cortezi populations were not speci?cally addressed or well supported by their allozyme data. Xiphophorus cortezi is distributed throughout the south- ern portion of the Pa?nuco river basin of eastern Mexico. This river enters the Gulf of Mexico at Tampico and drains the Sierra Madre Oriental. X. cortezi inhabits relatively still pools in small streams with rocky bottoms but is missing from larger rivers with sandy bottoms (Rauchenberger et al., 1990). The physical distribution of X. cortezi in small streams across three larger river drainages suggests that the populations might have evolved independently from each other. Because the rivers that connect the populations become quite large and therefore are not suitable habitat for this ?sh, the river habitats downstream may act as physical and ecological barriers among the populations in the headwater streams. Therefore, we expect X. cortezi populations to be genetically di?erentiated. In addition, some of the populations found in the headwaters of di?er- ent rivers are geographically closer than the populations found within the same river system. As the river systems in this area are known to be relatively instable (Rauchen- berger et al., 1990), we suspect that stream capture (i.e., the process by which a river or stream erodes through a divide so that its ?ow is diverted into a neighboring drain- age system) may have played a role in the current distribu- tion of this species. The purpose of our study is to assess the distribution of genetic variation within and among pop- ulations of X. cortezi, establish the geographical relation- ships among populations, test for cases of stream capture, and test the hypothesis of monophyly for this species. 2. Materials and methods 2.1. Samples We collected 65 individuals from 10 di?erent sites locat- ed in three drainages of the Pa?nuco River system in Mexi- co, thereby sampling the known distribution of the species (Fig. 1 and Table 1). A ?n-clip was collected from the cau- dal ?n of each ?sh and preserved in salt-saturated 20% dimethyl sulphoxide solution (Seutin et al., 1991). Fin-clips from single individuals of swordtail species X. birchmanni, X. malinche, X. montezumae and X. multilineatus from Atlapexco, Soyatla, R??o Fr??o, and R??o Coy, respectively, were included as presumptive outgroups for the phyloge- netic analyses. 2.2. Ampli?cation, sequencing and alignment Total DNA was extracted from ?n-clips using the 112 C. Gutie?rrez-Rodr??guez et al. / Molecular PDNeasy tissue kit (Qiagen Inc.) following the manufactur- er?s instructions. The entire mitochondrial control regionwas ampli?ed in 25 or 50 ll reactions using the polymerase chain reaction (PCR) and the previously published primers K (50 AGCTCAGCGCCAGAGCGCCGGTCTTGTAAA 30) and G (50 CGTCGGATCCCATCTTCAGTGTTAT GCTT 30) (Lee et al., 1995) according to standard methods. Reactions were performed on a MJ Research PTC-100 thermocycler (MJ Research Inc.) under the following conditions: 2 min at 94C, followed by 35 cycles at 90 or 94 C for 30 s, 55?63 C for 30 s and 72 C for 45 s, with a ?nal extension period of 7 min at 72 C. PCR products were puri?ed using the UltraClean PCR Clean-up DNA Puri?cation Kit (MoBio Laboratories Inc.) or the QIAquick Gel Extraction Kit (Qiagen Inc.) and sequenced in both directions to check the validity of the sequence data using the BigDye terminator cycle sequencing kit. Sequences were visualized with an ABI 310 or 3730 automated sequencers (Applied Biosystems) at the DNA Analysis Facility at Ohio University and the Plant-Microbe Genomics Facility at Ohio State University respectively. We aligned the forward and reverse sequences using the computer software SeqMan II (DNAStar Inc.). Contigu- ous sequences were initially aligned using Clustal X (Thompson et al., 1997) with the default settings, followed by manual alignment with the program Sequence Align- ment Editor v2.0a11. All sequences were deposited in Gen- bank (Table 1). 2.3. Population genetics analyses All population genetic analyses were performed using ARLEQUIN (Schneider et al., 2000). Levels of intra-pop- ulation variation were estimated by calculating the mean gene diversity (h), the probability that two randomly cho- sen haplotypes are di?erent (Nei, 1987) and the nucleotide diversity (p), the average number of di?erences between all pairs of haplotypes (Tajima, 1983; Nei, 1987). An analysis of molecular variance (AMOVA) (Exco?er et al., 1992) was used to test whether sequences from previously de?ned groups were signi?cantly di?erent from each other. We de?ned groups corresponding to the three drainages (Tam- peon, Moctezuma and Tempoal) from which the samples were collected (Table 1). An AMOVA without de?ned groups was also conducted. We used 16,000 permutations to test for statistical signi?cance of both AMOVAs. AMOVA compares the similarity within and among groups using genetic distance as the measure of similarity. We used the Tamura-Nei (TrN) model (Tamura and Nei, 1993) with the transition/transvertion (ti/tv) ratio = 3.0232 and the gamma shape parameter (a) = 0.8982 (see below) to calculate the genetic distance between the di?erent sequences. HKY, which is the model that best ?tted our data (see below), is not an option in ARLEQUIN 2.0 and TrN is the closest available approximation to HKY. We calculated the degree of genetic di?erentiation between all the sampled populations with pairwise F-statistics (Weir genetics and Evolution 43 (2007) 111?123and Cockerham, 1984) and their signi?cance by performing 1000 permutations. hyloC. Gutie?rrez-Rodr??guez et al. / Molecular PTwo Mantel tests with 10,000 permutations were per- formed to test for a correlation between genetic and geo- graphic distance using the computer program IBD (Bohonak, 2002). Genetic distances were calculated using the method of Nei and Li (1979) and 1000 permutations in both tests. Nei and Li?s measure of genetic distance (1979) is an estimate of the number of nucleotide di?erenc- es between populations that incorporates information on both haplotype frequencies and the number of substitu- tional di?erences between haplotypes. Geographic distanc- es were measured using river distances (the paths along the water courses connecting two localities) and straight-line distances (the minimum great circle distance between two localities). Both distances were calculated using the soft- ware ExpertGPS 1.3.7 (Topogra?x, 2003). Fig. 1. Map showing the di?erent collection sitesgenetics and Evolution 43 (2007) 111?123 1132.4. Relationships among haplotypes We assessed genetic di?erences between pairs of haplo- types using both the total number of base di?erences and maximum-likelihood distances (HKY model, ti/tv ratio and base frequencies estimated from the data, values for proportion of invariant sites and gamma shape parameter as obtained from MODELTEST software, see below). Dis- tance calculations were performed using PAUP* 4.0b10 (Swo?ord, 2002). We analyzed the phylogenetic relationships among the haplotypes using a variety of inference methods. Phyloge- netic trees of the X. cortezi and outgroup haplotypes were inferred using PAUP* 4.0b10 (Swo?ord, 2002) under parsimony, maximum-likelihood and least-squares distance of X. cortezi (d) and four outgroup taxa (m). dive ean hylocriteria. For the parsimony analysis, we conducted a branch and bound search, treating gaps as a ???fth base??. For the likelihood analyses, we selected a nucleotide substi- tution model using hierarchical likelihood ratio tests as implemented in MODELTEST 3.06 (Posada and Crandall, 1998). We estimated the optimal tree using a successive approximation approach (Swo?ord et al., 1996; Sullivan et al., 2005) with PAUP* 4.0b10 (Swo?ord, 2002). This method consists of a series of successive likelihood analy- ses, with the parameter values used in a given analysis esti- mated on the optimal tree from the previous analysis and reiterated until the topology, the likelihood score for the tree, and the parameter values match those from the previ- ous analysis. Each iteration used a heuristic search with starting trees obtained by random stepwise addition (100 replicates) and TBR branch swapping. For the distance analysis, we used unweighted least squares as the optimal- ity criterion and maximum-likelihood (HKY85 + G + I) distances, with the parameters estimated from the neigh- Table 1 Populations of X. cortezi sampled in this study, measures of their genetic Locality Species Abbreviation Drainage Oxitipa X. cortezi OXI Tampao?n Caldera X. cortezi CAL Tampao?n Tambaque X. cortezi TAM Tampao?n Tanute X. cortezi TAN Tampao?n La Conchita X. cortezi CON Moctezuma Amacuzac X. cortezi AMA Moctezuma San Mart??n X. cortezi SAM Tempoal Chalpuhuacanita X. cortezi CHA Tempoal Tecolutlo X. cortezi TEC Tempoal Xiliatl X. cortezi XIL Tempoal Atlapexco X. birchmanni ATL Tempoal Soyatla X. malinche SOY Tempoal R??o Fr??o X. montezumae FRI Tampao?n R??o Coy X. multilineatus COY Tampao?n N = number of sequences (individuals), Nh = number of haplotypes, h = m because only one sample was collected from the site. 114 C. Gutie?rrez-Rodr??guez et al. / Molecular Pbor-joining tree used in the hierarchical likelihood ratio tests. Gaps were treated as missing data in a heuristic search with starting trees obtained by random stepwise addition (100 replicates) and TBR branch swapping. Nodal support was assessed under the likelihood criterion using non-parametric bootstrap resampling (1000 replicates) and heuristic searches with starting trees obtained by ran- dom stepwise addition (10 replicates) and TBR branch swapping. Relationships among the haplotypes were also inferred using the statistical parsimony method of Templeton et al. (1992). Unlike the previous methods, relationships inferred by the statistical parsimony method are not con- strained to take the form of a tree (minimally connected graph), allowing them to take the form of more extensively connected graphs in which additional connections repre- sent alternative, equally parsimonious, mutational path- ways from one haplotype to another. TCS v1.21 (Clement et al., 2000) was used to estimate the statistical parsimony network (SPN), with the default 0.95 probabil-ity connection limit and treating gaps both as a ?fth state and as missing data. Because di?erent outgroups suggested two di?erent root positions, we conducted three analyses to determine whether our data could distinguish between the alternative root placements with con?dence. First, we constrained the X. cortezi plus X. malinche haplotypes to form a monophy- letic group and used the Kishino-Hasegawa (KH; Kishino and Hasegawa, 1989) and Shimodaira-Hasegawa (SH; Shi- modaira and Hasegawa, 1999) tests to determine whether the maximum-likelihood trees in the presence versus absence of this constraint were signi?cantly di?erent in their ability to explain the data. Second, we searched for optimal trees (1) using only X. montezumae and X. birch- manni as outgroups (excluding X. multilineatus) and (2) using only X. mulitlineatus as the outgroup (excluding X. montezumae and X. birchmanni). We compared the maxi- mum-likelihood trees inferred in each of these analyses (using the successive approximation approach described rsity and GenBank Accession Nos. N Nh h p GenBank Accession Nos. 3 1 0.000 0.0000 DQ445674 5 1 0.000 0.0000 DQ445674 5 1 0.000 0.0000 DQ445674 8 1 0.000 0.0000 DQ445674 12 2 0.530 0.0006 DQ445669-70 1 1 ? ? DQ445671 10 1 0.000 0.0000 DQ445671 10 2 0.467 0.0005 DQ445672-73 4 1 0.000 0.0000 DQ445675 7 2 0.476 0.0011 DQ445676-77 1 1 ? ? DQ445678 1 1 ? ? DQ445679 1 1 ? ? DQ445680 1 1 ? ? DQ445681 gene diversity, p = nucleotide diversity, ? = calculations are not possible genetics and Evolution 43 (2007) 111?123above) with the trees using the same outgroup(s) attached to the branch identi?ed as the root by the alternative out- group(s) using the KH and SH tests. For these tests, we used PAUP* 4.0b10 with the same model as in the maxi- mum-likelihood tree searches, estimating the transition/ transversion ratios, the nucleotide base frequencies, the proportion of variable sites and the shape parameter (a), and using RELL bootstrap resampling (1000 replicates). To assess the strength of the support for the derivation of X. malinche from within X. cortezi, we constrained X. cortezi to be monophyletic and, because of the di?erent root positions suggested by the di?erent outgroups, we conducted two separate analyses. We estimated maxi- mum-likelihood trees using the successive approximations approach described above with the same model, ?rst using only X. montezumae and X. birchmanni as outgroups (excluding X. multilineatus) and then using only X. multi- lineatus as the outgroup (excluding X. montezumae and X. birchmanni). We then compared the maximum-likeli- hood trees inferred in these analyses with those inferred for the same set of taxa in the absence of the monophyly constraint using KH and SH tests. For these tests, we used PAUP* 4.0b10 with the same model as in the maximum- likelihood tree searches, estimating the transition/transver- sion ratios, the nucleotide base frequencies, the proportion of variable sites and the shape parameter (a), and using RELL bootstrap resampling (1000 replicates). 3. Results 3.1. Sequence variation We obtained 881 bp sequences for the mitochondrial DNA control region of 65 X. cortezi individuals from 10 populations as well as of four individuals of closely related species. For the X. cortezi and four outgroup haplotypes (69?72) could not be aligned unambiguously, we retained both the most widespread (four localities) and the most common (21 individuals). The remainder of the haplotypes were only shared by individuals from the same locality (Table 2). Three of the populations (Chalpuhuacanita, La Conchita, Xiliatl) exhibited two di?erent haplotypes; all other populations exhibited only a single haplotype. Mean gene diversity (h) was very low to moderate among X. cor- tezi populations (Table 1). Nucleotide diversity (p) was very low in all populations, ranging from 0 to 0.0011 (Table 1) indicating a high degree of similarity of sequences within populations. The analysis of variance, in which we speci?ed three dif- ferent groups based on river drainages (Tampao?n, Moc- tezuma and Tempoal), showed signi?cant genetic structure at all hierarchical levels. Most of the variation (53.71%) was explained by di?erences among the three drainages. Dif- ferences among the populations within each drainage were ur p 5 X. cortezi CON 5 7 C. Gutie?rrez-Rodr??guez et al. / Molecular Phylogenetics and Evolution 43 (2007) 111?123 115X. cortezi AMA 1 X. cortezi SAM 10 X. cortezi CHA 7 3 X. cortezi TEC X. cortezi XIL X. birchmanni ATL X. malinche SOY X. montezumae FRI X. multilineatus COYthem in our analyses. Three of the haplotypes (H7, H8, and H9) di?er only in the ambiguously aligned region yet are clearly di?erent from one another. We thought that it was preferable to retain the information present in the identi?cation of three distinct haplotypes even though the speci?c substitutions separating those haplotypes are ambiguous. In any case, analyses excluding these positions yielded qualitatively similar results (not presented). 3.2. Genetic diversity and population structure Nine haplotypes were identi?ed among the 65 sequenced X. cortezi individuals and four among the outgroup taxa (Table 2). Haplotypes H3 and H6 were shared by individ- uals from di?erent populations, and haplotype H6 was Table 2 Number and geographic distribution of haplotypes from X. cortezi and fo Species Location Haplotype H1 H2 H3 H4 H X. cortezi OXI X. cortezi CAL X. cortezi TAM X. cortezi TANtogether, 67 variable sites out of the 881 were detected (7.6%) and for the X. cortezi haplotypes alone, 16 variable sites were detected (1.8%). The minimum number of muta- tions for the X. cortezi haplotypes alone was 16 (none of the variable sites for the nine haplotypes observed in this species had more than two bases). Although four sitesTotal 5 7 11 7 3also large and explained 42.07% of the variance. Only 4.22% of the variance was attributed to di?erences among individuals within populations (Table 3). The AMOVA per- formed without groupings also showed high and signi?cant degrees of genetic structure (Table 3). Most of the variation (95.03%) was explained by di?erences among populations, and only 4.97% by di?erences within populations. Genetic di?erentiation between pairs of populations is presented in Table 4. The majority of the FST values were high (P0.4232) and signi?cantly di?erent from zero. The main exceptions were the comparisons between pairs of populations located in the Tampao?n drainage, which were all zero and thus not signi?cant. FST values between popu- lations from di?erent drainages were generally higher than values between populations from the same drainage, although San Mart??n and Chalpuhuacanita (Tempoal drainage) exhibited low values in comparison to La Conch- ita (Moctezuma drainage) relative to other between-drain- age comparisons and relatively high values in comparison with Tecolutlo and Xiliatl (Tempoal drainage) relative to other within-drainage comparisons. utative outgroup species H6 H7 H8 H9 H10 H11 H12 H13 3 5 5 8 4 5 2 1 1 1 121 4 5 2 1 1 1 1 uares Variance components Percentage of variation Among groups 2 99.700 1.82654(Va) 53.71* Among populations within groups 7 57.428 1.43058(Vb) 42.07* 0.14362(Vc) 4.22* 3.40074 2.74359(Va) 95.03* 0.14362(Vb) 4.97 etic distances (above the diagonal) among X. cortezi populations CON AMA SAM CHA TEC 19.7771 19.1938 19.1938 22.5261 31.323 19.7771 19.1938 19.1938 22.5261 31.323 19.7771 19.1938 19.1938 22.5261 31.323 19.7771 19.1938 19.1938 22.5261 31.323 2.2833 2.5833 5.3156 18.7771 0.6657 0 3.3323 20.1938 0.8186* 0.0000 3.3323 20.1938 0.7809* 0.6412 0.8206* 22.9261 0.9381* 1.0000 1.0000* 0.9554* * * * * hylogenetics and Evolution 43 (2007) 111?123Within populations 55 7.899 Total 64 165.028 AMOVA without grouping Among populations 9 157.129 Within populations 55 7.899 Total 64 165.028 * Signi?cant values at P < 0.05. Table 4 Pairwise FST comparisons (below the diagonal) and Nei and Li (1979) gen OXI CAL TAM TAN OXI 0 0 0 CAL 0.0000 0 0 TAM 0.0000 0.0000 0 TAN 0.0000 0.0000 0.0000 CON 0.9421* 0.9497* 0.9497* 0.9578* AMA 1.0000 1.0000 1.0000 1.0000 SAM 1.0000* 1.0000* 1.0000* 1.0000* CHA 0.9487* 0.9565* 0.9565* 0.9644* TEC 1.0000* 1.0000* 1.0000* 1.0000* * * * *Table 3 Hierarchical analysis of molecular variance (AMOVA) for X. cortezi Source of variation df Sum of sq AMOVA with drainage grouping 116 C. Gutie?rrez-Rodr??guez et al. / Molecular PMantel tests revealed signi?cant and positive correla- tions between genetic distance and river distance (Fig. 2A, r = 0.766, P = 0.0004) as well as between genetic distance and straight-line geographic distance (Fig. 2B, r = 0.769, P = 0.0003). All population comparisons fell within the 95% con?dence intervals for both regressions, although eight comparisons in the analysis using river dis- tances were much further than the others from the line of best ?t. Four of these represent pairs of populations whose genetic distances are substantially greater than expected given their geographic distances; they involve comparisons between San Mart??n and Chalpuhuacanita, and compari- sons between Tecolutlo and Xiliatl, all from the Tempoal drainage. The other four comparisons represent pairs of populations whose genetic distances were substantially smaller than expected given their geographic distances; they involve comparisons between San Mart??n and Chal- puhuacanita from the Tempoal drainage and La Conchita and Amacuzac from the Moctezuma drainage. 3.3. Relationships among haplotypes Hierarchical likelihood ratio tests identi?ed HKY85 + I + G with the following initial parameter esti- mates as the appropriate model for our data: transition/ transversion (ti/tv) ratio = 3.0323, proportion of invariable XIL 0.9301 0.9437 0.9437 0.9563 0.9031 0.8727 0.9486 0.9190 0.4232 The signi?cance of the FST values between R??o Amacuzac and the rest of populations is not reported because only a single individual was sampled from the R??o Amacuzac. * P < 0.05 signi?cance level. Fig. 2. Plots of (A) Nei and Li (1979) genetic distance compared to river distance for all possible pairs of populations, (B) Nei and Li (1979) genetic distance compared to straight-line geographic distance for the same pairs of populations. The regression line and the lines that bound the 95% con?dence intervals are shown and were calculated only for the X. cortezi data. Comparisons between all X. cortezi populations to the X. malinche population are included and are denoted with a di?erent symbol. sites (i) = 0.8015, gamma shape parameter (a) = 0.8982, and base frequencies A = 0.3091, C = 0.2274, G = 0.1391, T = 0.3243. The optimal trees derived from parsimony, distance and likelihood analyses were generally similar, although the strict consensus of the maximum-likelihood trees exhibited greater resolution (8/11 possible nodes) than those derived from distance (7/11) and parsimony (6/11) analyses. The maximum-likelihood tree with nodal support (bootstrap) values is presented in Fig. 3. The only group present in this tree that is contradicted by the results of analyses based on other optimality criteria is H3, H4, H6, H10 and H12. In the parsimony tree H3 and H4 group with H5, while in the least squares distance tree they group with H1, H2 and H5. None of these con?icting relationships is strongly supported (bootstrap proportions all 655%). Details of the results of all three analyses are presented in Appendix A. In all optimal trees inferred by likelihood and distance analyses and some of those inferred by parsimony analysis, the trees cannot be rooted so that the haplotypes found in X. cortezi (and X. malinche) form a monophyletic group because di?erent outgroups suggest di?erent root positions (Fig. 3). The X. mulitlineatus haplotype roots the tree between the group H7?H9 + H11 (found in X. cortezi and X. malinche populations from the Tempoal river drain- age) and the remaining haplotypes (Fig. 3A); whereas the X. birchmanni plus X. montezumae haplotypes root the tree Tampao?n drainage) (Fig. 3B). The ?rst root position (Fig. 3A) is inferred in those parsimony trees that can be rooted without disrupting monophyly of the X. cortezi (and X. malinche) haplotypes. Regardless of root position, the X. malinche haplotype (H11) falls out within those of X. cortezi and is most closely related to haplotypes from the Tempoal drainage (H7?9). In the trees resulting from all of these analyses, the X. cortezi haplotypes fall into groups that correspond roughly to the river drainages in which they are found. All populations from the Tampao?n drainage exhibit a sin- gle haplotype (H6). The haplotypes from the Moctezuma drainage (H1?3) form a para- or polyphyletic group rela- tive to those from the Tempoal drainage, or the Tempoal and Tampao?n drainages, depending on the position of the root. Finally, some of the haplotypes from the Tempoal drainage (H7?9) form a monophyletic group while the oth- ers (H3?5) are intermixed with haplotypes from the Moc- tezuma drainage (H1?3). Branch lengths leading to the various X. cortezi haplotypes are generally short, and only four groups in the maximum-likelihood tree are supported by bootstrap values >50% (Fig. 3). The statistical parsimony networks (Fig. 4) postulate a number of hypothetical unsampled haplotyes (which di?er depending on whether gaps are treated as a ?fth state or as missing data) in addition to the nine X. cortezi and one X. malinche sampled haplotypes that were connected with l reg ite. C. Gutie?rrez-Rodr??guez et al. / Molecular Phylogenetics and Evolution 43 (2007) 111?123 117on the branch to H6 (found in four populations from the Fig. 3. Maximum-likelihood bootstrap tree for mitochondrial DNA contro 13). Branch lengths are proportional to the number of substitutions per s Names of the outgroup species and drainage name for the X. cortezi haplotyp Rooted with the outgroups X. montezumae and X. birchmanni.probabilitiesP0.95 (ignoring the outgroup X. multilineatus ion haplotypes from X. cortezi (H1?9) and four putative outgroups (H10? Numbers above branches indicate bootstrap support if greater than 50%. es are also indicated. (A) Rooted with the outgroup X. multilineatus. (B) in the network in which gaps were treated as missing data, Fig. 4B). Outgroup weights (Castelloe and Templeton, 1994) based on both haplotype frequencies and positions in the graph (internal versus terminal) suggest that either haplotype H4, found in the Chalpuhuacanita population, or H1, found in the La Conchita population, is ancestral (Fig. 4), depending on the interpretation of gaps. The X. cortezi haplotypes form three groups of closely connected haplotypes (1?2 mutations between nearest neighbors) that are separated from one another by more distant connections (at least ?ve mutations when treating gaps as a ?fth state). One contains haplotypes from the Tampao?n drainage (H6), a second has haplotypes from the Moctezuma and Tempoal drainages (H1?5), and a third is formed by haplotypes from the Tempoal drainage (H7?9). The haplotype from X. malinche (H11) is posi- tioned in the networks 1 or 2 mutational steps from X. cor- tezi haplotype (H9) from the Tempoal drainage. In contrast, the X. birchmanni (H10) and X. montezumae (H12) haplotypes, and, when gaps are treated as a ?fth base, that of X. multilineatus (H13), are not linked to the networks, indicating that the number of nucleotide di?er- ences between those Xiphophorus species and X. cortezi exceeds the connection limit of 12 steps, which corresponds cant di?erences. The maximum-likelihood tree in the absence of any constraints did not exhibit a signi?cantly better ?t to the data than the maximum-likelihood tree constrained so that the X. cortezi plus X. malinche haplo- types formed a monophyletic group according to both the KH test (P = 0.552) and the SH test (P = 0.309). This constrained tree (not shown) was rooted in the position indicated by X. multilineatus (see Fig. 3A). In addition, the maximum-likelihood tree including only X. montezu- mae and X. birchmanni as outgroups did not exhibit a sig- ni?cantly better ?t to the data than a tree in which these two outgroups were attached in the position where X. mul- tilineatus was attached in the analysis including all three outgroups (KH test, P = 0.532; SH test, P = 0.246). Simi- larly, the maximum-likelihood tree including only X. multi- lineatus as the outgroup did not exhibit a signi?cantly better ?t to the data than a tree in which X. multilineatus was attached in the position where X. montezumae and X. birchmanni were attached in the analysis including all three outgroups (KH test, P = 0.156; SH test, P = 0.097). Although derivation of X. malinche from within X. cor- tezi (paraphyly of X. cortezi relative to X. malinche) is implied by the optimal trees from phylogenetic analyses under diverse optimality criteria (Fig. 3 and Appendix mit rec 118 C. Gutie?rrez-Rodr??guez et al. / Molecular Phylogenetics and Evolution 43 (2007) 111?123to a probability of 0.95 that the number of mutations is accurately estimated by parsimony. For the X. cortezi hap- lotypes alone, 19 mutations were estimated by both tree and network methods that treated gaps as a ?fth state (20 when the X. malinche haplotype is included). Tests of the alternative root placements suggested by di?erent outgroups (Fig. 3A and B) did not reveal signi?- Fig. 4. Statistical parsimony network based on X. cortezi sequences of the treating gaps as missing data. Haplotype designations are from Table 1. The rectangles is proportional to the haplotype?s frequency. Small black circles are h network. Each of the lines between observed and/or hypothetical haplotypesA), our data do not reject the alternative hypothesis of monophyly for the X. cortezi haplotypes. Comparison of the maximum-likelihood trees in the absence of any con- straints to the maximum-likelihood trees under a con- straint of X. cortezi monophyly did not reject the hypothesis of X. cortezi monophyly whether X. montezu- mae and X. birchmanni were used as outgroups (KH test, ochondrial DNA control region. (A) Treating gaps as a ?fth state and (B) tangles represent the inferred ancestral haplotype. The size of the ovals and ypothetical haplotypes necessary to connect the observed haplotypes in the represents one mutational step. hyloP = 0.532; SH test, P = 0.246) or X. multilineatus was used as the outgroup (KH test, P = 0.783; SH test, P = 0.649). 4. Discussion 4.1. Genetic variation The results of this study indicate a low degree of genetic variation in the mtDNA control region of X. cortezi com- pared to other teleostean ?shes (i.e., Fajen and Breden, 1992; Lee et al., 1995; Salzburger et al., 2003; Stefanni and Thorley, 2003; Aboim et al., 2005). Out of 881 aligned positions 16 (1.8%) were variable (the numbers are the same if the X. malinche sample is included) and out of 65 sequences nine (13.8%) distinct haplotypes were found (10 if the X. malinche sample is included). Gene diversity (h) was low to moderate and nucleotide diversity (p) was very low in X. cortezi populations. Although the number of genotypes found in each population should be interpret- ed with caution because of the limited sample sizes, similar low levels of within population variation in the mtDNA control region have been found in other poeciliids, such as the guppy species Poecilia reticulata (Fajen and Breden, 1992; Carvalho et al., 1996; Shaw et al., unpublished data) and the swordtail species X. birchmanni (Shearer et al., unpublished data). The low genetic diversity within populations may re?ect founder e?ects, as reductions in genetic polymorphisms have been observed in introduced populations of guppies (Shaw et al., 1992; Carvalho et al., 1996). Alternatively, the low values of nucleotide diversity (p) combined with moderate haplotype diversity (h) may suggest recent popu- lation expansion after a bottleneck or a founder event. However, a Tajima?s D-test (Tajima, 1989) indicated this is not the case in X. cortezi, as all populations had positive D values that were not signi?cantly di?erent from zero (results not shown). These patterns of low genetic diversity within population are most likely the consequence of con- sistently small population sizes, which might have resulted in genetic drift and inbreeding (Nei et al., 1975; Wishard et al., 1984). Small population size could be a consequence of human activities, as there are indications of human con- tamination in these areas that are likely to contribute to ?sh mortality. In contrast to the low variation within populations, we found high degrees of genetic di?erentiation among X. cor- tezi populations. The AMOVA with drainage grouping showed that the variation among populations within drain- ages explained a large proportion of the total variance, indicating genetic structure among populations located in the same drainage. This was supported by the signi?cance of the AMOVA performed without groupings and by the high and signi?cant values of the FST comparisons between most pairs of populations. High levels of genetic di?erenti- ation among populations have been reported in other C. Gutie?rrez-Rodr??guez et al. / Molecular Pfreshwater ?shes (Carvalho et al., 1991; Shaw et al., 1991, 1994; Fajen and Breden, 1992; Alves and Coelho, 1994;Coelho et al., 1997; Ha?n?ing and Brandl, 1998a,b,c; Mesq- uita et al., 2001) and could be the result of discontinuities in suitable habitat. As a result, genetic di?erentiation might re?ect the physical subdivision of populations (Carvalho, 1993). Sections of the streams where X. cortezi and other swordtails species are distributed dry seasonally and may be contaminated by human activities, resulting in destruc- tion of suitable habitat. In addition, X. cortezi only occurs in small rivers, which are often more subdivided by barriers to ?sh movement than larger rivers. The populations from the Tampao?n drainage (Oxitipa, Caldera, Tambaque and Tanute) constitute an exception to the pattern of high genetic di?erentiation among popu- lations from the same drainage. All the populations in Tampao?n shared the same single haplotype (H6). Such genetic homogeneity among the sampling sites in this drainage suggests recent and/or historical migration throughout the streams of the drainage and could re?ect the absence of barriers to gene ?ow. Alternatively, it could re?ect the geographic proximity of the collection sites in this drainage. The geographic distances between the popu- lations sampled from the Tampao?n drainage are, in gener- al, smaller than those between populations in the other drainages and do not include stretches of larger rivers with unsuitable X. cortezi habitat. The patterns of low intra- population genetic diversity combined with high genetic di?erentiation among populations found in this investiga- tion have also been reported in studies of other freshwater ?shes based on allozymes (Carvalho et al., 1991; Shaw et al., 1994; Ha?n?ing and Brandl, 1998b,c) and mtDNA (Carvalho et al., 1996; Mesquita et al., 2001; Shaw et al., unpublished data). 4.2. Geographic patterns of genetic variation and evidence of stream capture Our data exhibited signi?cant correlations between genetic and geographic distances, regardless of whether geographic distance was measured along watercourses or as straight lines. These ?ndings suggest that genetic di?er- entiation among X. cortezi populations can be explained, to some extent, by an isolation-by-distance model. A strong geographic e?ect on genetic variation is also implied by the results of the AMOVA with drainage grouping, in which a signi?cant amount of the total genetic variation was attributable to di?erences among groups of popula- tions from di?erent drainages. On the other hand, there does not appear to be a one-to-one correspondence between groups of related haplotypes and drainage groups. Neither the haplotype trees nor the haplotype networks exhibit groups that correspond precisely to the three drain- age groups. In both cases, some haplotypes from the Tem- poal drainage (H4?5) are closer to those from the Moctezuma drainage (H1?3), in terms of both common ancestry and mutational steps, than they are to other hap- genetics and Evolution 43 (2007) 111?123 119lotypes from the Tempoal drainage (H7?9). Moreover, one of the haplotypes (H3) is found in both drainages. hyloSeveral of our results provide evidence of stream cap- ture. First, the Mantel tests revealed that genetic distance between populations is more strongly correlated with straight-line geographic distance than with geographic dis- tance measured along river courses, suggesting that genetic di?erentiation is more strongly in?uenced by gene ?ow between populations in adjacent drainages (as might occur through stream capture) than by gene ?ow up and down river courses. Second, in the comparison of genetic distanc- es versus river distances, the eight most obvious outliers all represent comparisons involving populations from the northwestern part of the Tempoal drainage. The popula- tions in this drainage (represented in our study by San Mart??n and Chalpuhacanita) exhibit substantially larger genetic distances to the other populations in the Tempoal drainage (Tecolutlo and Xiliatl) and substantially smaller genetic distances to the populations in the Moctezuma drainage (La Conchita and Amacuzac) than expected given their river course geographic distances suggesting that these two streams may have drained into the Moctezuma in the past. Third, in both the haplotype trees and the statistical parsimony networks, the haplotypes from San Mart??n (H3) and Chalpuhuacanita (H4 and H5) from the Tempoal drainage are more closely related to haplotypes from the Moctezuma drainage (H1, H2 and H3, which is shared with San Mart??n) than they are to other haplotypes from the Tempoal drainage (H7, H8, and H9). The above ?ndings, in conjunction with the fact that the northwestern branches of the Tempoal drainage are located geographi- cally between the Moctezuma drainage and the southeast- ern branches of the Tempoal drainage, are consistent with a scenario in which the current northwestern branches of the Tempoal drainage were formerly part of the Moc- tezuma drainage and were later captured by the Tempoal drainage. The low elevation (less than 100 m) separating parts of the drainages also suggests the possibility of stream capture. 4.3. Root of the haplotype tree and ancestral haplotype Although tests designed to establish the placement of the root of the haplotype tree could not conclusively distin- guish between the alternatives, two lines of evidence favor the root position indicated by the outgroup X. multilineatus over that suggested by X. birchmanni and X. montezumae. First, some of the optimal trees under parsimony as well as the maximum-likelihood tree under the constraint of monophyly of the X. cortezi plus X. malinche haplotypes (trees not shown) were rooted in the position (branch) sug- gested by X. multilineatus on the maximum-likelihood tree in the absence of any constraints. Second, trees rooted using X. birchmanni and X. montezumae as outgroups were far from approaching signi?cance in distinguishing between alternative root positions (P = 0.246?0.532), sug- gesting that these taxa are not particularly informative 120 C. Gutie?rrez-Rodr??guez et al. / Molecular Pfor discriminating between the two alternatives, while trees rooted using only X. multilineatus as the outgroup werecloser to approaching signi?cance in favoring the root posi- tion implied by that species over the position suggested by X. birchmanni and X. montezumae (P = 0.097?0.156). The statistical parsimony networks indicated that either haplotype H4 (when gaps treated as ?fth state) or H1 (when gaps treated as missing) is ancestral among the hap- lotypes from X. cortezi and X. malinche, an inference based on both the relative haplotype frequencies and numbers of connections to other haplotypes (Castelloe and Templeton, 1994; Clement et al., 2000). If the root position is assumed to occur at the node at which X. multilineatus attaches to the tree (see above), then the optimal phylogenetic tree sug- gests that the ancestral haplotype is located along the branch separating X. cortezi haplotypes H7?9 from haplo- types H1?6, which is only a few mutational steps from the haplotypes identi?ed as ancestral by the analyses using TCS, particularly when gaps are treated as missing data (H1). In the results of that analysis (Fig. 4B) the outgroup X. multilineatus (H13) connects to the rest of the network in the same area. In addition to using di?erent kinds of information to infer the ancestral haplotype (position and frequency versus outgroup) the minor di?erences between the results of these analyses may be attributable to the fact that the TCS analyses only identify observed haplotypes as ancestral while the phylogenetic analyses can identify an inferred haplotype as ancestral. 4.4. Monophyly versus paraphyly of X. cortezi haplotypes and the status of X. malinche The phylogenetic analyses suggest that X. cortezi is not monophyletic. Regardless of the root position, X. cortezi haplotypes from the Tempoal drainage (H7?9) appear to be more closely related to the X. malinche haplotype (H11) than they are to otherX. cortezi haplotypes (H1?6). In addi- tion, the number of substitutions separating the X. malinche haplotype from the X. cortezi haplotypes are within the range for comparisons involving the X. cortezi haplotypes alone. Moreover, our sample of X. malinche (from Soyatla) and the haplotypes of X. cortezi to which it appears most closely related (from Xiliatl and Tecolutlo) all come from the Tempoal drainage. Although our data cannot reject the alternative hypothesis that the X. cortezi haplotypes form a monophyletic group exclusive of X. malinche, based on the phylogenetic relationships and geographic proximity of the X. malinche haplotypes to the X. cortezi haplotypes from Tecolutlo and Xiliatl we suspect that these haplotypes (and the populations in which they occur) are closely related and that failure to demonstrate this relationship with a high degree of con?dence is a result of the limited power of the tests resulting from the small number of mutational di?erences between the haplotypes in question. The use of a more polymorphic marker would be necessary to conclusively resolve these relationships. The ?nding that X. cortezi may be paraphyletic relative genetics and Evolution 43 (2007) 111?123to X. malinche raises several issues concerning the status of these taxa as separate species. One possibility is that the two taxa are separate species, with X. cortezi ancestral to X. malinche. Alternatively, X. malinche may not be a separate species but rather a group of X. cortezi populations that has evolved some distinctive features. This second possibil- ity is supported by the fact that the genetic versus geo- graphic distance comparisons between the X. malinche population and the various X. cortezi populations lie very close to (and below rather than above) the best ?tting line representing the comparisons among the X. cortezi popula- tions (see Fig. 2). A third possibility is that the taxon cur- rently recognized as X. cortezi consists of several di?erent species (from which X. malinche may or may not be specif- ically distinct). Although a large component of the total genetic variation is attributable to di?erentiation between the populations from di?erent drainages, the di?erences also conform closely to an isolation-by-distance model, related outgroup (X. montezumae) and the entire set of haplotypes from X. cortezi and X. malinche. Moreover, in both the haplotype trees and networks, the X. cortezi and X. malinche haplotypes form a tight group whose members are separated by relatively short branches. In contrast, the X. birchmanni haplotype connects to the trees via a much longer branch and is so divergent that is not connected to the statistical parsimony network of X. cortezi and X. malinche haplotypes. As noted above, there is ambiguity concerning the root of the haplotype trees and the relationships of X. birchman- ni and X. montezumae to the rest of the taxa in our study (see Section 4 of alternative root positions). However, if the tree root position indicated by the outgroup X. multi- lineatus is correct, then the X. malinche and X. birchmanni haplotypes are most closely related to di?erent X. cortezi haplotypes (H7?9 versus H6, respectively). This result is KY 11, 77 42 42 55 11 55 37 C. Gutie?rrez-Rodr??guez et al. / Molecular Phylogenetics and Evolution 43 (2007) 111?123 121suggesting the possibility of ongoing gene ?ow. Moreover, genetic divergence within X. cortezi (Table 5) is not nearly as great as divergence between X. cortezi and populations that clearly represent di?erent species. Nonetheless, it is possible that sets of populations in the di?erent drainages are no longer exchanging genes but have not been isolated long enough for greater di?erentiation to have occurred. 4.5. Relationship of X. cortezi and X. malinche to X. birchmanni Contrary to previous ?ndings (Rauchenberger et al., 1990), which placed X. malinche and X. birchmanni as sister species, with X. cortezi as their sister group, the results of our phylogenetic analyses suggest that X. malinche is more closely related to X. cortezi than to X. birchmanni. In our phylogenetic trees and networks, the haplotype from X. malinche (H11) is very closely related to the X. cortezi hap- lotypes in general, and to those from the southeastern branches of the Tempoal drainage (H7?9) in particular (see previous section). In contrast, the X. birchmanni haplo- type connects to the phylogenetic trees between a distantly Table 5 Pairwise total base di?erences (above diagonal) and maximum-likelihood (H in X. cortezi (H1?H10) and four outgroup species (H10, X. birchmanni; H H1 H2 H3 H4 H5 H6 H1 ? 1 1 2 1 7 H2 0.00115 ? 2 3 2 8 H3 0.00116 0.00235 ? 1 2 6 H4 0.00233 0.00356 0.00114 ? 1 7 H5 0.00114 0.00233 0.00233 0.00116 ? 8 H6 0.00849 0.00988 0.00715 0.00841 0.00979 ? H7 0.00713 0.00847 0.00848 0.00976 0.00839 0.013 H8 0.00838 0.00975 0.00976 0.01106 0.00966 0.012 H9 0.00590 0.00721 0.00721 0.00848 0.00714 0.012 H10 0.05526 0.05818 0.05253 0.05062 0.05338 0.052 H11 0.00469 0.00597 0.00597 0.00721 0.00590 0.011 H12 0.05214 0.05502 0.04681 0.04495 0.04755 0.047 H13 0.01850 0.02022 0.02025 0.02176 0.02000 0.023Estimates for the number of mutational di?erences between pairs of haplotypes multiplying the maximum-likelihood distances (number of substitutions/site) bcongruent with the results obtained from several di?erent analyses of allozyme data for the northern swordtails, which place X. malinche and X. birchmanni populations closest to di?erent populations of X. cortezi (Morris et al., 2001; esp. Fig. 4). Alternatively, if the root position indicated by the outgroup X. montezumae is correct, then the X. malinche haplotypes are once again closest to some of the X. cortezi haplotypes from the Tempoal drainage (H7?9), but the X. birchmanni haplotype is outside of a monophyletic group composed of the X. malinche and all the X. cortezi haplotypes. This result is congruent with those of a previous analysis of Xiphophorus DNA sequence data (Meyer et al., 1994), which placed either X. birchmanni (when analyzed by neighbor-joining) or a group composed of X. birchmanni and X. pygmaeus (when analyzed by par- simony) as the sister group to all the rest of the northern swordtails. Sequence divergence corroborates the results obtained from the phylogenetic analyses (Table 5). Maximum-likeli- hood (HKY + I + G) distances between the X. cortezi and X. malinche haplotypes (0.0012?.0111) are substantially + I + G model) distances (below diagonal) for mitochondrial haplotypes X. malinche; H12, X. montezumae; H13, X. multilineatus) H7 H8 H9 H10 H11 H12 H13 6 7 5 34 4 32 14 7 8 6 35 5 33 15 7 8 6 33 5 30 15 8 9 7 32 6 29 16 7 8 6 33 5 30 15 11 10 10 33 9 30 17 ? 1 1 31 2 34 14 0.00114 ? 2 32 3 33 13 0.00114 0.00231 ? 30 1 33 13 0.04938 0.05121 0.04746 ? 30 37 38 0.00231 0.00349 0.00115 0.04753 ? 31 12 0.05611 0.05400 0.05410 0.06692 0.04941 ? 36 0.01849 0.01701 0.01704 0.06770 0.01563 0.06414 ?that correct for multiple substitutions at individual sites can be obtained by y the number of sites (in this case 881). is the sister to a group composed of X. malinche and X. cor- (Research Incentive) to MRM. Collecting methods comply The branch and bound search found 12 optimal trees of Marked genetic divergence revealed by allozymes among populations variance inferred from metric distances among DNA haplotypes: hylolength 86, the strict consensus of which had the following topology: (H13,H6,(H4,H5,H3),H1,H2,(((H7,H8),H9),H11), (H10,H12)). A.2. Likelihood analyses Of 881 characters, 49 distinct character patterns were observed. The successive approximation heuristic search required three iterations, and although it identi?ed two trees as maximum-likelihood estimates of the phylogeny under ?xed parameter values, only one of these trees (Fig. 2) was identi?ed as optimal when the parameters were estimated for that tree (ln L = 1632.18538). The parameter estimates from the ?nal iteration of the successive approximation analysis on the optimal tree were ti/tv = 3.663520, i = 0.783835, and a = 0.792371,with the Animal Care Guidelines of Ohio University (Ani- mal Care and Use approval No. L01-01). Appendix A. Results of phylogenetic analyses A.1. Parsimony analyses Of 881 unordered characters, 814 were constant, 67 were variable, and 25 were informative (42 uninformative) under the parsimony criterion with gaps treated as a ?fth state.tezi. Regardless, of whether these three species form a clade, X. birchmanni seems to be much more distantly relat- ed to X. cortezi and X. malinche than these two taxa are to each other. Acknowledgments We are grateful to the Mexican government for permis- sion to collect the ?shes. We would like to thank Oscar Rios-Cardenas and Abby Darrah for their help in the ?eld. This research was supported by funding from the National Science Foundation (IBN 9983561) and Ohio Universitysmaller than those between both the X. cortezi and X. birchmanni haplotypes (0.0475?0.0582) and the X. malinche and X. birchmanni haplotypes (0.0475). In contrast, dis- tances between the X. cortezi and X. malinche haplotypes and the haplotypes from X. birchmanni (0.0475?0.0582) are similar to the distances of the former two taxa from one relatively distantly related outgroup (X. montezumae 0.0450?0.0561), and smaller than those from another (X. multilineatus 0.0156?0.0234). Because of limited sampling of other swordtail species and ambiguities concerning the position of the root, our results cannot rule out the possibility that X. birchmanni 122 C. Gutie?rrez-Rodr??guez et al. / Molecular Pfrequency of A = 0.308990, C = 0.227496, G = 0.138244, T = 0.325269. The strict consensus of the two trees identi-application to human mitochondrial DNA restriction data. Genetics 131, 479?491. Fajen, A., Breden, F., 1992. Mitochondrial DNA sequence variation among natural populations of the Trinidad guppy, Poecilia reticulata. Evolution 46, 1457?1465. Ha?n?ing, B., Brandl, R., 1998a. Genetic and morphological variation in aof the guppy Poecilia reticulata (Poeciliidae), in Trinidad. Biol. J. Linn. Soc. 57, 219?234. Carvalho, G.R., 1993. Evolutionary aspects of ?sh distribution: genetic variability and adaptation. J. Fish Biol. 43, 53?73. Carvalho, G.R., Shaw, P.W., Hauser, L., 1996. Arti?cial introductions, evolutionary change and population di?erentiation in Trinidadian guppies (Poecilia reticulata: Poeciliidae). Biol. J. Linnean Soc. 57, 219? 234. Castelloe, J., Templeton, A.R., 1994. Root probabilities for intraspeci?c gene trees under neutral coalescent theory. Mol. Phylogenet. Evol. 3, 102?113. Clement, M., Posada, D., Crandall, K.A., 2000. TCS: a computer program to estimate gene genealogies. Mol. Ecol. 9, 1657?1659. Coelho, M.M., Alves, J., Rodrigues, E., 1997. Patterns of genetic divergence in Chondrostoma lusitanicum Collares-Pereira, in intermit- tent Portuguese rivers. Fish Manage. Ecol. 4, 223?232. Exco?er, L., Smouse, P., Quattro, J., 1992. Analysis of molecular?ed as optimal under ?xed parameter estimates had the fol- lowing topology: (H13,(((H6,(H10,H12)),H4,H3),H5,H1,H2),(((H7,H8), H9),H11)). A.3. Distance analyses Using HKY85 + G + I distances (with the same param- eter estimates used in the ?rst iteration of the likelihood analysis) and an unweighted least squares optimality crite- rion, the heuristic search found 12 optimal trees with a score of 0.00026. The strict consensus of the 12 trees had the following topology: (H13,((H6,(H10,H12)),(H4,H5,H1,H2,H3)),((H7,H8),- H9),H11). In the individual optimal trees, the haplotype from Xiphophorus malinche (H11) always grouped with one group (H1?6) or the other (H7?9) of the X. cortezi hap- lotypes, resulting in an unresolved position in the strict consensus tree. References Aboim, M.A., Menezes, G.M., Schlitt, T., Rogers, A.D., 2005. Genetic structure and history of populations of the deep-sea ?sh Helicolenus dactylopterus (Delaroche, 1809) inferred form mtDNA sequence analysis. Mol. Ecol. 14, 1343?1354. Alves, J., Coelho, M.M., 1994. Genetic variation and population subdivision of the endangered Iberian cyprinid Chondrostoma lusitan- icum. J. Fish Biol. 44, 627?636. Bohonak, A.J., 2002. IBD (Isolation by Distance): a program for population genetic analyses of isolation by distance. J. Hered. 93, 153?154. Borowski, R.L., McClelland, M., Cheng, R., Welsh, J., 1995. Arbitrarily primed DNA ?ngerprinting for phylogenetic reconstruction in verte- brates: the Xiphophorus model. Mol. Biol. Evol. 12, 1022?1032. Carvalho, G.R., Shaw, P.W., Magurran, A.E., Sehers, B.H., 1991. genetics and Evolution 43 (2007) 111?123common European cryprinid, Leuciscus cepahlus within and across Central European drainages. J. Fish Biol. 52, 706?715. Ha?n?ing, B., Brandl, R., 1998b. Genetic variability, population size and isolation of distinct populations in the freshwater ?sh Cottus gobio L. Mol. Ecol. 7, 1625?1632. Ha?n?ing, B., Brandl, R., 1998c. Genetic di?erentiation of the bullhead Cottus gobio L. across watersheds in Central Europe: evidence for two taxa. Heredity 80, 110?117. Kishino, H., Hasegawa, M., 1989. Evaluation of the maximum likelihood estimate of the evolutionary tree topologies from DNA sequence data, and the branching order in Hominoidea. J. Mol. Evol. 29, 170? 179. Lee, W-J., Conroy, J., Howell, W.H., Kocher, T.D., 1995. Structure and evolution of teleost micochondrial control regions. J. Mol. Evol. 41, Schneider, S., Roessli, D., Exco?er, L., 2000. ARLEQUIN, Version 2.00: a Software for Population Genetics Data Analysis. University of Geneva, Geneva. Seutin, G., White, B.N., Boag, P.T., 1991. Preservation of avian blood and tissue samples for DNA analyses. Can. J. Zool. 69, 82?92. Shaw, P.W., Carvalho, G.R., Magurran, A.E., Seghers, B.H., 1991. Population di?erentiation in Trinidad guppies (Poecilia reticulata): patterns and problems. J. Fish Biol. 39 (suppl. A), 203?209. Shaw, P.W., Carvalho, G.R., Seghers, B.H., Magurran, A.E., 1992. Genetic consequences of an arti?cial introduction of guppies (Poecilia reticulata) in N. Trinidad. Proc. R. Soc. B. 248, 111?116. C. Gutie?rrez-Rodr??guez et al. / Molecular Phylogenetics and Evolution 43 (2007) 111?123 12354?66. Me?e, G.K., Snelson, F.F., 1989. An ecological overview of poeciliid ?shes. In: Me?e, G.K., Snelson, F.F. (Eds.), Ecology and Evolution of Livebearing Fishes (Poeciliidae). Prentice Hall, Englewood Cli?s, pp. 13?31. Mesquita, M., Carvalho, G., Shaw, P., Crespo, E., Coelho, M.M., 2001. River basin-related genetic structuring in an endangered ?sh species, Chondrostoma lusitanicum, based on mtDNA sequencing and RFLP analysis. Heredity 86, 253?264. Meyer, A., Morrissey, J., Shartl, M., 1994. Recurrent evolution of a sexually selected trait in Xiphophorus ?shes inferred from a molecular phylogeny. Nature 368, 539?542. Meyer, A., 1997. The evolution of sexually selected traits in male swordtail ?shes (Xiphophorus: Poeciliidae). Heredity 79, 329?337. Moritz, C., 2002. Strategies to protect biological diversity and the evolutionary process that sustain it. Syst. Biol. 51, 238?254. Morris, M.R., de Queiroz, K., Morizot, D.C., 2001. Phylogenetic relationships among populations of northern swordtails (Xiphophor- ous) as inferred form allozyme data. Copeia 1, 65?81. Nei, M., Maruyama, T., Chakraborty, R., 1975. The bottleneck e?ect and genetic variability in populations. Evolution 29, 1?10. Nei, M., Li, W.H., 1979. Mathematical model for studying genetic variation in terms of restriction endonucleases. Proc. Natl. Acad. Sci. USA 76, 5269?5273. Nei, M., 1987. Molecular Evolutionary Genetics. Columbia University Press, New York. Posada, D., Crandall, K.A., 1998. Modeltest: testing the model of DNA substitution. Bioinformatics 14, 817?818. Rauchenberger, M., Kallman, K.D., Morizot, D.C., 1990. Monophyly and geography of the R??o Pa?nuco basin swordtails (Genus Xipho- phorus) with descriptions of four new species. Am. Mus. Nov. 2975, 1?41. Rosen, D.E., 1979. Fishes from the uplands and intermontane of Guatemala: reversionary studies and comparative geography. Bull. Am. Mus. Nat. Hist. 162, 268?375. Ryan, M.J., Rosenthal, G.G., 2001. Variation and selection in swordtails. In: Dugatkin, L.A. (Ed.), Model Systems in Behavioral Ecology. Princeton University Press, New Jersey, pp. 133?148. Salzburger, W., Branda?stter, A., Gilles, A., et al., 2003. Phylogeography of the vairone (Leuciscus sou?a, Risso 1826) in Central Europe. Mol. Ecol. 12, 2371?2386.Shaw, P.W., Carvalho, G.R., Magurran, A.E., Seghers, B.H., 1994. Factors a?ecting the distriution of genetic variability in the guppy, Poecilia reticulata. J. Fish Biol. 45, 875?888. Shimodaira, H., Hasegawa, M., 1999. Multiple comparisons of log- likelihoods with applications to phylogenetic inference. Mol. Biol. Evol. 16, 1114?1116. Stefanni, S., Thorley, J., 2003. Mitochondrial DNA phylogeography reveals the existence of an evlutionary signi?cant unit of the sand goby Pomatoschistus minutus in the Adriatic (Eastern Mediterranean). Mol. Phylogenet. Evol. 28, 601?609. Sullivan, J., Abdo, Z., Joyce, P., Swo?ord, D.L., 2005. Evaluating the performance of a successive approximations approach to parameter optimization in maximum-likelihood phylogeny estimation. Mol. Biol. Evol. 22, 1386?1392. Swo?ord, D.L. 2002. PAUP*. Phylogenetic Analysis Using Parsimony (*and Other Methods). Version 4b10. Sinauer Associates, Sunderland, MA. Swo?ord, D.L., Olsen, G.J., Waddell, P.J., Hillis, D.M., 1996. Phyloge- netic inference. In: Hillis, D.M., Moritz, C., Mable, B.K. (Eds.), Molecular Systematics. Sinauer Associates, MA, pp. 407?514. Tajima, F., 1983. Evolutionary relationship of DNA sequences in ?nite populations. Genetics 105, 437?460. Tajima, F., 1989. Statistical method for testing the neutral mutation hypothesis by DNA polymorphism. Genetics 123, 585?595. Tamura, K., Nei, M., 1993. Estimation of the number of nucleotide substitutions in the control region of mitochondrial DNA in humans and chimpanzees. Mol. Biol. Evol. 10, 512?526. Templeton, A.R., Crandall, K.A., Sing, C.F., 1992. A cladistic analysis of phenotypic associations with haplotypes inferred from restriction endonuclease mapping and DNA sequence data. III. Cladogram estimation. Genetics 132, 619?633. Thompson, J.D., Gibson, T.J., Plewniak, F., Jeanmougin, F., Higgins, D.G., 1997. The ClustalX windows interface: ?exible strategies for multiple sequence alignments aided by quality analysis tools. Nucleic Acids Res. 24, 4876?4882. Topogra?x 2003. ExpertGPS, Copyright 2000?2006, TopoGra?x, Stow MA. Weir, B.S., Cockerham, C., 1984. Estimating F-statistics for the analysis of population structure. Evolution 38, 1358?1370. Wishard, L.N., Seeb, J.E., Utter, F.M., Stefan, D., 1984. A genetic investigation of suspected redband trout populations. Copeia 1984, 120?132.