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J21. .il..:. 21:2 . t. 117.4139 1:»l .L . lth .C 1: .aaz‘ls...‘ I13: ll..- E1351. a : . ,1... i. i. 2... .hfi... ‘ ‘ p 1 .3 DD’L/ LIBRARY Michigan State University This is to certify that the dissertation entitled Importance of Hybridization and Ecological Differentiation in the success of Lithrum Salicaria in North America. presented by Jaimie Melissa Houghton—Thompson has been accepted towards fulfillment of the requirements for Doctoral degree in Genetics Major professor Date December Q, 2991 MS U is an Affirmative Action/Equal Opportunity Institution 0-12771 PLACE IN RETURN BOX to remove this checkout from your record. TO AVOID FINES return on or before date due. MAY BE RECALLED with earlier due date if requested. DATE DUE DATE DUE DATE DUE iii a 75605 6/01 c:/CIRC/DateDue.p65-p.15 IMPORTANCE OF HYBRIDIZATION AND ECOLOGICAL DIFFERENTIATION IN THE SUCCESS OF LY THRUli/I SALICARIA IN NORTH AMERICA By Jaimie Melissa Houghton-Thompson A DISSERTATION Submitted to Michigan State University in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY Program in Genetics 2001 ABSTRACT IMPORTANCE OF HYBRIDIZATION AND ECOLOGICAL DIFFERENTIATION IN THE SUCCESS OF LY THRUA/I SALICARIA IN NORTH AMERICA By Jaimie Melissa Houghton-Thompson Lythrum salicaria is much more invasive in North America than its native Europe (Batra et al.1986). One possibility for how it became more invasive is that it hybridized with a close relative in North America, such as L. alatum, and gained genes that made it better adapted to its new environment. This hypothesis was first tested by searching for morphological evidence of hybridization. By examining a variety of purple loosestrife populations across the northeastern United States, several traits were found that are not present in European populations of purple loosestrife but are found in North American winged loosestrife. These unique morphs found in North American purple loosestrife suggest hybridization between the two species. In support of this, we identified intermediate sized L. salicaria where the two species grow sympatrically and could have hybridized. Amplified fragment length polymorphism (AFLP) markers were then used to further analyze the relationship between L. salicaria and L. alatum, and search for evidence of hybridization. Twenty-seven North American and eleven European populations of L. salicaria and L. alatum were screened with 5 primer pairs, and then eight Michigan populations (selected for allopatry or sympatry between the two species) were screened with an additional 18 primer pairs. When the resulting patterns of molecular diversity were examined, North American L. salicaria clustered more closely to European L. salicaria than to North American L. alatum, and no evidence of inter- species hybridization was found. However, a considerable amount of differentiation was observed among the North American L. salicaria. This differentiation may be the real reason why L. salicaria became so successfiil in North America. I dedicate this work to my parents, William and Jean Houghton, who have always believed I could do anything I set my mind to, and my fiance, Matthew Thompson, who was always there to listen when I thought I couldn't go on. iv ACKNOWLEDGEMENTS First, I would like to thank my advisor, Dr. Jim Hancock. Without his tremendous knowledge, support, belief in my ability, and more than occasional push in the right direction, this never would have been accomplished. I would also like to thank the members of my committee: Dr. Harold Prince, Dr. Barbara Sears, Dr. James Smith, and Dr. Patrick Venta, who have always been willing to guide my work and help me find direction. None of this would ever been accomplished without the help, support, and humor of the members of the Hancock lab, past and present, including Pete Callow, Chad Osborn, Sedat Serce (including his enormous knowledge of statistics and computer formattingl), Cholani Webadde, Rebekah F leis, Chris Owens, Joan Stroher, and Chrislyn Drake. Fellow students in the Genetics Program, especially Sheldon Leung and Ribka Bedilu, have also made this journey a more interesting, and sometimes even productive one. Finally, I would like to thank my closest friends, Sarah Byers and Megan Nunez-Lane, and my family, including my parents, William and Jean Houghton, my brothers Cory and Patrick Houghton, members of my extended family including June, Buddy, Brian and Ryan Horr, Willard Blaisdell, and Arlene Tebbetts, and my fiance, Matthew Thompson. Without all of your love and support, this would not have been nearly as fun! TABLE OF CONTENTS LIST OF TABLES ........................................................................................................... viii LIST OF FIGURES ............................................................................................................. x CHAPTER 1 THE IMPLICATIONS OF POLYPLOIDY 1N LY T HR UM SALICARIA ............................ 1 Introduction .............................................................................................................. 1 Lythrum in North America ....................................................................................... 3 Type of polyploidy in Lythrum ................................................................................ 5 Role of hybridization and polyploidy in Lythrum .................................................. 1 1 CHAPTER 2 MORPHOLOGICAL DIVERSITY IN NORTH AMERICAN LY THR W ..................... 14 Introduction ............................................................................................................ 14 Materials and Methods ........................................................................................... 16 Population surveys ..................................................................................... 16 Common garden experiment ...................................................................... 21 Results .................................................................................................................... 22 Discussion .............................................................................................................. 37 CHAPTER 3 MOLECULAR DIVERSITY IN EUROPEAN AND NORTH AMERICAN LY T HRW ................................................................................................ 41 Introduction ............................................................................................................ 41 The utility of AF LP analysis .................................................................................. 42 Materials and Methods ........................................................................................... 44 Plant collection ........................................................................................... 44 DNA extraction .......................................................................................... 45 DNA preparation for AF LP analysis ......................................................... 46 AFLP reactions .......................................................................................... 47 Polyacrylamide gel electrophoresis ........................................................... 48 Silver staining technique ............................................................................ 48 Exposure of film ........................................................................................ 49 Scoring the gel ........................................................................................... 49 Statistical Analyses .................................................................................... 49 Results .................................................................................................................... 50 Study with all populations ......................................................................... 50 Further study of Michigan populations ...................................................... 54 Discussion .............................................................................................................. 59 APPENDIX ........................................................................................................................ 63 LITERATURE CITED ...................................................................................................... 88 vii LIST OF TABLES Table 1: Taxonomic characteristics that separate North American winged loosestrife (Lythrum alatum) and Eurasian purple loosestrife (Lythrum salicaria) (Graham, 1975)..15 Table 2: Location and species found at each study site ................................................... 18 Table 3: Loosestrife population size and type of environment at each study site ........... 19 Table 4: Prevalence of L. alatum diagnostic traits in populations of L. salicaria and L. alatum surveyed in North America. For qualitative traits, the percentage of L. salicaria carrying L. alatum traits is reported. For quantitative traits, the mean and range of each trait are denoted .................................................................................................................. 23 Table 5: ANOVA of plant height in 14 populations of Lythrum alatum and 16 populations of L. salicaria in North America .................................................................... 24 Table 6: ANOVA of leaf length, width, and length/width ratio in 9 populations of Lythrum alatum and 12 populations of L. salicaria in North America ............................. 24 Table 7: ANOVA of seedlings produced per flower in four populations of Lythrum salicaria in Michigan. Two of the populations were sympatric to L. alatum, two were allopatric. Number of seedlings was determined for 10 flowers each of 10 clones from each population .................................................................................................................. 33 Table 8: Height and leaf characteristics of four populations of Lythrum salicaria grown from seed in a common greenhouse at Michigan State University, East Lansing, MI. Two of the populations were sympatric with L. alatum [Harsen's Island (HIS) and Sheep Farm B (SFB)], and two were allopatric [Lake Lansing (LLA) and Quanicassee B (QWB)]. Values are given for natural populations and seedlings grown in a greenhouse. Mean values were compared using SAS (Cary, NC). Bold values are significant at P<0.05 ..... 33 Table 9: Summary of AFLP variation in 15 populations of Lythrum salicaria and 12 populations of L. alatum in North America, 11 European populations of L. salicaria, and 6 cultivars. Included are number of fragments for each primer, with numbers unique to each species and number shared between species ............................................................. 51 Table 10: Summary of AFLP variation in four populations of Lythrum salicaria and four populations of L. alatum in Michigan. Included are number of fragments for each primer, with numbers unique to each species and number shared between species ...................... 55 Table 11: AFLP data for global experiment. Msel primer for all combinations is CAG, EcoRl primer is indicated. Molecular weight of fragment is indicated after primer name. Presence of fragment is indicated with 1, absence with 0. North American purple viii loosestrife is bold, European purple loosestrife is italicized, and cultivars are underlined ............................................................................................ 63 Table 12: AFLP data for extended Michigan experiment. Population is indicated, and primer pair is indicated in the following manner: the first two letters of the primer indication is the last two letters of the Msel primer, the last two letters of the primer indication is the last two letters of the EcoRI primer (the first letter of all Msel primers is C, the first letter of all EcoRl primers is 0). For example, ACAG is M-CAC/E-AAG...79 ix LIST OF FIGURES Figure l: Crossing evidence for type of tetraploidy of purple loosestrife. A is the result of crosses if purple loosestrife is an allotetraploid, B is the case when it is an autotetraploid. Experimental findings of full fertility of hybrids indicates that purple loosestrife rs an autopolyploid ........................................................................................... .9 Figure 2: Inheritance patterns in purple x winged loosestrife hybrids where there is little or extensive chromosomal divergence. With little chromosomal divergence, the hybrid exhibits tetrasomic inheritance and backcrosses easily to purple loosestrife. With extensive divergence, meiotic irregularities develop and backcrossing is difficult ........... 10 Figure 3: Locations of Lythrum salicaria, L. alatum, and mixed populations surveyed in this study. L. salicaria is denoted with a diamond, L. alatum with a circle, and mixed sites with a triangle. States are indicated by abbreviation .............................................. 20 Figure 4: Distribution in height of Lythrum salicaria and L. alatum from 30 North American populations. L. salicaria is denoted in black, L. alatum in white ................... 25 Figure 5: Mean heights of Lythrum salicaria and L. alatum populations in Massachusetts, Michigan, Ohio, and Wisconsin. Populations from the same state are placed next to each other. L. salicaria is denoted in black, L. alatum in white, and states are denoted along the x-axis. Striped bars indicated sympatric populations of L. salicaria and L. alatum ..................................................................................................................... 26 Figure 6: Distribution of leaf length of Lythrum salicaria and L. alatum from 30 North American populations surveyed. L. salicaria is denoted in black, L. alatum in white ..... 27 Figure 7: Mean leaf length of Lythrum salicaria and L. alatum in different populations in Michigan and Wisconsin. Populations from the same state are placed next to each other. L. salicaria is denoted in black, L. alatum in white, and states are denoted along the x-axis. Striped bars indicate sympatric populations of L. salicaria and L. alatum ..... 28 Figure 8: Distribution of leaf ratios (length/width) of Lythrum salicaria and L. alatum from 21 North American populations surveyed. L. salicaria is denoted in black, L. alatum in white .................................................................................................................. 29 Figure 9: Mean leaf ratios (length/width) of Lythrum salicaria and L. alatum in 12 Michigan and 9 Wisconsin populations. Populations from the same state are placed next to each other. L. salicaria is denoted in black, L. alatum in white, and states are denoted along the x-axis. Striped bars indicate sympatric populations of L. salicaria and L. alatum ................................................................................................................................ 30 Figure 10: Distribution in height of all allopatric Lythrum salicaria and L. alatum populations (bottom panels) compared to four sympatric populations of L. salicaria (Harsen's Island, Sheep Farm B, Ottawa National Wildlife Refuge, and Kildeer) skewed towards L. alatum morphology .......................................................................................... 34 Figure 11: Distribution in leaf length in all allopatric L. salicaria and L. alatum (top and bottom times) compared to two sympatric populations of L. salicaria (Harsen's Island, Sheep Farm B) skewed towards L. alatum morphology ................................................... 35 Figure 12: Distribution in leaf length/width ratios in all allopatric Lythrum salicaria and L. alatum (top and bottom frames) compared to leaf length/width ratios in two sympatric populations of L. salicaria (Harsen's Island and Sheep Farm B) skewed towards L. alatum morphology ............................................................................................................ 36 Figure 13: Principle component analysis of L. salicaria and L. alatum populations. All variable morphological traits were included in this analysis (leaf placement, length, width, length/width ratio, plant height, and flower number per leaf axil). Region of origin, species, and sympatry vs. allopatry are denoted. Two populations which appear intermediate are labeled by name ...................................................................................... 37 Figure 14: Principle Component Analysis for all populations included in study. North American L. salicaria is indicated by filled circles, European L. salicaria by filled triangles, cultivars of L. salicaria by open triangles, and L. alatum by open circles. Percentage that each principle component contributed to overall variation is indicated in parentheses on the appropriate axis ................................................................................... 52 Figure 15: Cluster analysis of L. salicaria and L. alatum, including all populations studied in analysis. The top cluster includes all L. salicaria, and the lower cluster includes all L. alatum. The top cluster can be firrther broken into North American L. salicaria, cultivars, and European L. salicaria. Abbreviation for state of origin is listed before each North American population name... . .. .......................................................... 53 Figure 16: Principle component analysis of the 8 Michigan populations more extensively studied. L. salicaria populations are on the lefi, L. alatum populations on the right. Percentage that each principle component contributed to overall variation is indicated in parentheses on the appropriate axis ................................................................ 56 Figure 17: Cluster analysis of the eight Michigan populations of L. salicaria and L. alatum more intensively studied. The top cluster includes all L. salicaria populations, the lower cluster includes all L. alatum populations ............................................................... 57 Figure 18: An example of a polyacrylamide gel run in the Michigan experiment. Purple loosestrife is on the lefi, winged loosestrife is on the right. Some markers are present in purple loosestrife and not winged loosestrife, and vice versa, and some markers are present in both species ............................................................................ 58 CHAPTER 1 THE MPLICATIONS OF POLYPLOIDY 1N L YTHRUM SALICARIA Introduction It has been suggested that some exotic species are preadapted to become invasive if they are released from natural predators in their new environment (Blossey et al., 1992). As a result, the control of invasives has moved more and more into the arena of biological control, operating under the assumption that if a critical natural control agent can be found, the fecundity of the invasive species, and their ability to invade, will be severely hampered if not eliminated. Recent studies, however, ask if invasives are truly ‘born’ and become invasive in a new environment simply because of the lack of natural enemies, or if they are ‘made’ and their invasive ability evolves after colonization (Ellster and Schierenbeck, 2000). There is support for both of these hypotheses. Some invasive species have been controlled by the introduction of a biological control agent (Dodd, 1959; Huffaker and Kennett, 1959), suggesting that the release from biotic pressure was the main factor allowing invasion to occur. However, only a small fraction of species, when taken out of their natural environment and introduced to a new ecosystem, do develop invasiveness, and even for species that do become invasive, there is often a considerable lag time between their first introduction and their becoming invasive (Ewel et al., 1999). If release from biotic pressure was the only prerequisite to invasiveness, the spread of the species should occur quickly after the release from predators. Ellstrand and Schierenbeck (2000) have proposed that the reason for this delay may often be that interspecific hybridization with native species must occur, allowing invasiveness to evolve after the introduction of new genes. Abbott (1992) observed that interspecific hybridization involving a non-native and a native or non-native species has led to the development of numerous new sexually reproducing species. The models of Ellstrand and Schierenbeck extend this idea to include previously-isolated, allopatric populations of sexually reproducing species as well. However, species can also evolve invasiveness without an influx of genes via hybridization. Considerable ecological differentiation has been observed in many native species, and it is certainly conceivable that such differentiation could occur in an introduced species if its founders carried sufficient genetic variability. Polyploidy may be an excellent way for this variability to be stored. Several aspects of polyploidy contribute to their success as a whole, including their polyphyletic origin, which incorporates high levels of genetic diversity into the species from recurrent formation from multiple parent populations (Soltis and Soltis, 2000). As a result, polyploids have higher levels of heterozygosity than their diploid progenitors and less inbreeding depression. The genetic variability found in polyploids can be further assorted through genomic rearrangement, and in the case of autopolyploids, tetrasomic inheritance. An underlying theme in our laboratory is the investigation of how polyploidy, especially autopolyploidy, plays a role in a species’ survival and evolutionary history. In my project, that question was addressed by testing for interactions between an introduced, invasive autopolyploid, Lythrum salicaria (purple loosestrife) and a closely related native diploid species to explore if introgression has occurred, which could explain the increased invasiveness of the introduced autopolyploid. The alternative hypothesis was that genetic variability already present in L. salicaria reassorted and allowed previously unrevealed characteristics to be expressed, expanding its ability to adapt and invade. L. salicaria (purple loosestrife) is a highly invasive, exotic, autotetraploid plant that has been the focus of recent attention because of its ability to become the dominant species in wetlands, replacing many native species (Cutright, 1986; Batra et al., 1986). Lyth_r_ym in North America Purple loosestrife is a tall, perennial, autotetraploid plant found in wetland habitats. It is native to Eurasia, but was introduced into North America in the early 1800’s (Pursh, 1814) both accidentally through ship ballast and purposely through seed sales (Mack, 1991). It is considered invasive and a noxious weed in several states due to its ability to eliminate pre-existing native species in wetlands (Cutright, 1986). Over the last century, its range has spread westward from New England and it has now successfully established itself as far west as the Pacific Northwest (Stuckey, 1980). Although it is aggressive in North America, it is not in its native Eurasia (Batra et al., 1986) Purple loosestrife was initially introduced to North America in the early 1800’s, specifically in New England, but it was not recognized as invasive until the 1930’s, when it began to form monospecific stands in the floodplain pastures of the St. Lawrence River in Quebec (Louis-Marie, 1944). Since that time, it has followed a distinct pattern of invasion across the US. Typically, it remains unobtrusive for a long period (at least 20 years) followed by a brief period (of less than 3 years) in which it becomes dominant in many parts of that region (Stuckey, 1980). One possibility why purple loosestrife is much more dominant in North America than Eurasia may be that favorable genes have introgressed from a close relative native in North America. If this is the case, the most likely candidate is Lythrum alatum (winged loosestrife), a widespread diploid species that is closely related to purple loosestrife, not found in Eurasia, and has habitat overlap at its outer edges with purple loosestrife, but is typically found in drier areas. There are 11 known species of Lythrum native to North America, but L. alatum is the most widespread. Winged loosestrife is a shorter, less showy species than purple loosestrife (Blackwell, 1970), and grows in wet meadows as a sub-dominant (Cody, 1978). There is evidence that the genomes of winged and purple loosestrife are compatible, as some cultivars of purple loosestrife were generated by breeders by crossing the two species (Anderson and Ascher, 1993). Most of these cultivars are self- sterile, but recent work has shown that these cultivars are fiilly fertile when crossed with the wild species of purple loosestrife (Lindgren and Clay, 1993; Anderson and Ascher, 1993; Ottenbreit and Staniforth, 1994). Purple loosestrife is self incompatible and heterostylous (Darwin, 1877) and as a result the cultivars are self-sterile. While no direct evidence of hybridization in the wild has been documented between winged and purple loosestrife, bees and butterflies have been observed to move between these species when they grow sympatrically (Levin, 1970), and hybridization could occur between the two species via unreduced gametes (Anderson and Ascher, 1993). Morphological characters thought to be unique to winged loosestrife have also been observed in purple loosestrife populations (Anderson and Ascher, 1994) and the hybrids produced by breeders have been shown to be highly fertile tetraploids, which can readily backcross to the tetraploid purple loosestrife. Type of polyploidy in Lythrum There are two major types of polyploids: autopolyploids and allopolyploids. Autopolyploidy arises when only one type of chromosome set is doubled, while allopolyploidy occurs when two nonhomologous genomes are united. Most polyploids are thought to originate through unreduced gametes (Harlan and deWet, 1975). Until recently (Soltis and Soltis, 1993, 1995), autopolyploidy was considered to be much rarer in natural populations than allopolyploidy. The traditional view of autopolyploidy was that it is generally maladaptive: that there would be multivalent pairing of chromosomes and this would lead to reduced pollen and seed fertility because of unbalanced chromosome segregation at meiosis (Stebbins, 1950, 1971). Successful establishment of an autopolyploid was therefore seen as unlikely, particularly since their adaptations were predicted to be very similar to their parent species (Levin, 1983; Soltis and Rieseberg, 1986). These assumptions have now been tested in a wide range of polyploid species using molecular markers, and segregation ratios have indicated the reverse — autopolyploids are often highly fertile. In many autopolyploids, multiple homologues actually pair in random assortments of bivalents rather than in multivalents, and as a result pairing relationships are normal (Soltis and Rieseberg, 1986; Krebs and Hancock, 1989; Samuel et al. 1990; On et al., 1998). Autopolyploidy is much more common than previously thought because many autopolyploids were misidentified as allopolyploids, based on bivalent pairing, but this bivalent pairing is random with tetrasomic inheritance. Molecular studies of autopolyploid species have revealed three important characters that may confer an evolutionary advantage over their diploid progenitors: enzyme multiplicity, increased heterozygosity, and increased allelic diversity (Soltis and Soltis, 1993). This increased biochemical diversity may confer a fitness advantage to polyploids (Levin, 1983), especially autotetraploids because of the tetrasomic inheritance they exhibit. Fertility is high in many autopolyploid species because the multiple homologues pair in random assortments of bivalents rather than in multivalents (Qu et al., 1998). A number of studies comparing genetic variation (as a function of polymorphic loci and mean observed heterozygosity) have shown autotetraploids to be more genetically variable than related diploid species (Shore, 1991; Soltis and Soltis, 1989; Lumaet, 1986). Autopolyploidy could contribute greatly to the success of an introduced autotetraploid species if its diploid progenitor (or close relative) is located in the area of introduction. An alien autotetraploid species can cross with a closely related diploid species with little chromosomal divergence if the diploid produces unreduced gametes, since the unification of the reduced gamete from the tetraploid with the unreduced one from the diploid would result in tetraploid F1 progeny with normal tetrasomic pairing association, as shown in Figure 18. Through backcrossing, advantageous genes from the diploid genome could become incorporated into the tetraploid genome. Over time, this could allow genes to be injected into the tetraploid genome that allow the alien species to further adapt to the new environment. Alternatively, autopolyploidy in L. salicaria may have allowed unique adaptions to arise via reassortment once exposed to a new environment. The increased level of heterozygosity generally observed in polyploids may have given some traits the plasticity needed to adapt to a new habitat. Heterozygosity is fixed in allopolyploids, due to the fact that the two ancestral genomes do not pair with each other in the polyploid. In autopolyploidy, with pairing freely allowed among all chromosome sets, reassortment into new ecotypes suited for a wider range of habitats is possible. Genetic variability already present in L. salicaria may have reassorted without hybridization into new morphologies and adaptive types. Several species of Lythrum in Europe are diploid, and some carry similar traits to L. alatum (Tutin et al., 1968). Some of these species could be the natural progenitors of L. salicaria, although this possibility has not been tested. If these species are the original progenitors to the tetraploid L. salicaria, seemingly new traits in L. salicaria could actually have lain hidden in the ancient polyploid genome and reassorted when L. salicaria encountered new habitats in North America. The presence of new habitats in North America may have presented the opportunity for these genes to reassort and become phenotypically expressed. Researchers have referred to L. salicaria as an allotetraploid because it is thought to be an interspecific hybrid (Strefeler et al. 1996), but at the chromosome level, it probably acts as an autopolyploid. This is supported by the discovery that the inheritance patterns of style length are tetrasomic (Fisher, 1949). Breeding evidence that purple and winged loosestrife can intercross, and the fact that these cultivar hybrids can backcross to purple loosestrife (Ottenbreit and Staniforth, 1994), are also compelling evidence that purple loosestrife is an autopolyploid. If, chromosomally, it acted as an allopolyploid, the two sets of chromosomes in the purple loosestrife gametes would be incompatible and would cause significant fertility reductions in an interspecific cross (Figure 2). The most conclusive evidence that the hybrid acts as an autotetraploid comes from crossing studies where tetraploid purple loosestrife was hybridized with diploid winged loosestrife, and the resulting tetraploid F1 hybrids produced via unreduced gametes (in the diploid) were completely fertile (Ottenbreit and Staniforth, 1994). A known purple and winged loosestrife hybrid, the cultivar Morden Gleam, was crossed with purple loosestrife and no significant reduction in the fertility of progeny was found when compared to crosses among purple loosestrife. Therefore, several lines of evidence support the hypothesis that L. salicaria is an autopolyploid. The F1 hybrid between purple and winged loosestrife must be an autopolyploid rather than an allopolyploid, as the unification of a purple loosestrife gamete with an unreduced winged loosestrife gamete in the case of allopolyploidy would result in an unfertile hybrid that had two chromosome sets from the winged gamete that could freely pair, but two sets of chromosomes from the purple gamete that could not pair with each other. Depending on chromosomal divergence between winged and purple loosestrife, either one or none of the purple loosestrife chromosomes could pair with the winged chromosomes (Figure 1). This would result in reduced fertility of the hybrid due to meiotic irregularities, leading to the production of numerous partially aneuploid and/or triploid gametes with poor viability, and backcross hybrids would likely have low vigor and meiotic irregularities. The only way for a hybrid between purple and winged loosestrife to be fiilly fertile when backcrossed to a purple loosestrife plant is if all four chromosomes of each set in the hybrid can interchangeably pair with each other at meiosis (Figure 2). This would result in tetrasomic inheritance (four alleles at a locus) (Fisher, 1944, 1949). In the case of an autopolyploid, there would be little chromosomal divergence between winged and purple loosestrife, and the chromosomes could pair in a balanced fashion at meiosis resulting in high fecundity. If there is as little chromosomal divergence between the two species, as illustrated by this example, it is not hard to imagine a pathway for the movement of information fiom one genome to the other. A: If purple loosestrife is an allotetraploid: Purple loosestrife gamete x unreduced winged loosestrife gamete = Hybrid In hybrids: L3 can pair with L3, but L1 and L2 cannot pair with each other. L1 or L2 may be able to pair with L3, depending on how divergent the chromosomes are. Some hybrids would have meiotic irregularities (partially aneuploid and/or triplo id gametes). B: If purple loosestrife is an autotetraploid: 69 Purple loosestrife gamete xunreduced winged loosestrife gamete = Hybrid In hybrids: L3 can pair with L3, and L1 can pair with L]. Forms balanced L1 L3 gametes. L1 may be able to pair with L3, depending on how diverged the chromosomes are. If there is little divergence, gametes can backcross to purple loosestrife (L1 L1) gametes to form L1 L1 L1 L3 hybrids. Figure 1: Crossing evidence for type of tetraploidy of purple loosestrife. A is the result of crosses if purple loosestrife is an allotetraploid, B is the case when it is an autotetraploid. Experimental findings of full fertility of hybrids indicates that purple loosestrife is an autopolyploid. Extensive Chromosomal Divergence Little Chromosomal Divergence 6) Purple gamete Winged Garnete Purple Garnete Winged Garnete (unreduced) (unreduced) Resultant Hybrid Resultant Hybrid Gametes formed Gametes formed Backcross to Purple Loosestrife (L1 L1) lBackcross to Purple Loosestrife (L1 L1) L1 L1 . Some of the Gametes Formed Gametes Formed (Reduced fertility due to pairing (Full fertility) irregularities) Figure 2: Inheritance patterns in purple x winged loosestrife hybrids where there is little or extensive chromosomal divergence. With little chromosomal divergence, the hybrid exhibits tetrasomic inheritance and backcrosses easily to purple loosestrife. With extensive divergence, meiotic irregularities develop and backcrossing is difficult. 10 Role of hybridization ananolyploidy in Lythrum In recent years, the role of interspecific hybridization in plant evolution has received renewed attention. The importance of interspecific hybridization was long suspected utilizing morphological markers (Anderson, 1949; Riley, 193 8; Heiser, 1947 and 1949), and with the advent of molecular markers, considerable direct evidence has accumulated that genes have been exchanged between closely related species of the same ploidy (Arnold et al., 1990, 1992 and 1993; Rieseberg and Warner, 1987; Rieseberg et al., 1988; Rieseberg and Ellstrand, 1993). In some cases, substantial genomic reorganizations have occurred after hybridization resulting in speciation (Arnold, 1993; Rieseberg et al., 1993; Rieseberg, 1995). Recently, a number of plant families were identified as “hotspots” for hybridization (Ellstrand et al. , 1996). Although Lythraceae, the family that includes Lythrum, was not included in this discussion, its closest relative, Onagraceae, was, and this family was identified as one of the families with an unusually high level of natural hybridization. Lythrum also fits all three criteria that were identified to increase the likelihood of hybridization: perennial habit, outcrossing breeding system, and reproductive modes that can stabilize hybridity (e. g. clonal reproduction). Our original hypothesis was that there was hybridization occurring between winged and purple loosestrife as it moved across North America, via unreduced gametes, that allowed genes from the winged loosestrife genome to be incorporated into purple loosestrife populations. These incorporated genes then allowed purple loosestrife to more rapidly adapt to North American habitats. We based this hypothesis on previous 11 morphological (Anderson and Ascher, 1994) and isozyme (Strefeler eta1., 1996a, 1996b) studies conducted in Minnesota that indicated that there had been movement of traits fiom winged loosestrife into purple loosestrife populations. The alternative hypothesis was that the appearance of new traits and adaptation to new habitats of purple loosestrife in North America was due to genetic reassortment in the polyploid, unveiling previously untapped invasive potential. My project addressed these hypotheses in three ways. First, by characterizing both purple loosestrife and winged loosestrife on both a regional level and species level, using genetic [amplified fragment length polymorphism (AFLP)] and morphological markers, and searching for evidence of either movement of genetic material from winged to purple loosestrife or extensive differentiation without hybridization. Second, by observing putative hybrid populations in a controlled environment and determining if the morphological patterns observed in the field have a genetic basis. Third, by obtaining plant material from European populations and discovering whether North American populations of purple loosestrife have diverged from European ones. This project allowed us to study whether autopolyploidy and interspecific hybridization can play a critical evolutionary role in a species’ adaptation to a new environment. To date, ecotypic variation in an autopolyploid species that arose through sexual interaction with a diploid carrying the same genome has not been documented, and levels of genetic differentiation in autopolyploids have only rarely been described, with or without interspecific hybridization. Showing that polyploidy and natural hybridization can be a dynamic process in evolutionary change, especially as a mechanism for 12 increasing invasiveness, would further our understanding of how plants evolve invasive properties such as weediness, and can help in developing strategies to control them. Understanding the mechanism of invasion of a polyploid alien species can also be critical to determining methods of biological control, particularly when natural hybridization could lead to the transfer of resistance. Many studies have been performed to determine methods for biological control of purple loosestrife, specifically looking at herbivores that feed on purple loosestrife in its native Eurasia (Blossey, 1995). Based on host specificity, three herbivore species have been chosen: Galerucella calmariensis (L.) and G. pusiIIa (Dull), leaf feeding beetles, and Hylobius transversovittatus Goeze, a root feeding weevil (Kok et al. 1992a, b). In no-choice tests, the leaf feeding beetles were found to oviposition as well as feed on winged loosestrife, although in choice tests, purple loosestrife was preferred (Kok et al., 1992). If hybridization has taken place between purple and winged loosestrife, that could have an significant effect on the susceptibility of both purple and winged loosestrife to Eurasian predators. Two effects are possible: 1) the hybrid could be less susceptible to Eurasian predators than purple loosestrife is in Eurasia, or 2) the hybrid could provide an evolutionary “bridge” for the Eurasian predators to adapt to feeding on winged loosestrife. Documentation of hybridization occurring in the wild between these species will allow environmental managers to make more informed decisions about biological control agents. If purple loosestrife in North America becomes more resistant to Eurasian predators than the Eurasian purple loosestrife, much time and money could be wasted breeding and releasing insects that will have little or no effect. Additionally, if the Eurasian predators are more effective predators of F1 hybrids, our native species may be put at risk. 13 CHAPTER 2 MORPHOLOGICAL DIVERSITY IN NORTH AMERICAN LY 1' HR UM Introduction Lythrum salicaria, purple loosestrife, was introduced to North America from Eurasia in the early 1800’s and now ranges from New England to the Pacific Northwest. Its closest relative is L. alatum, more commonly known as winged loosestrife, a shorter, less showy diploid species that is native to North America and is not present in Eurasia (Blackwell, 1970). Winged loosestrife grows in wet meadows as a sub-dominant (Cody, 1978), and its preferred habitat overlaps extensively with purple loosestrife. Purple and winged loosestrife can intercross, and they probably share a common genome. Purple loosestrife has been identified as an autotetraploid by previous researchers (Fisher, 1949) by determining that inheritance patterns of style length were tetrasomic. Purple and winged loosestrife have been successfully hybridized by breeders, and these cultivar hybrids can be successfully backcrossed to purple loosestrife (Ottenbreit and Staniforth, 1994). Winged loosestrife is a diploid species, therefore the most likely way for these two species to intercross is through an unreduced gamete in winged loosestrife fertilizing a natural diploid gamete in purple loosestrife. The resultant hybrid would be tetraploid, and could backcross to purple loosestrife. Unreduced gametes have been shown to be important in the evolution of numerous autopolyploid species including blueberry (Qu et al., 1998), potato (Lam, 1974) and alfalfa (V eronesi et aL,1986) l4 There are several taxonomic characters that are found in winged loosestrife that are not present in European populations of purple loosestrife (Graham, 1975; Table 1). All of these morphological characters have been anecdotally observed in purple loosestrife populations in Minnesota (Anderson and Aster, 1994), but similar searches have not been made across the entire range of purple loosestrife. The research described herein sought to determine whether winged loosestrife traits occur elsewhere in purple loosestrife populations across the northeastern United States, following its original invasion pattern. We found that winged loosestrife traits do appear in purple loosestrife all across its North American range, and that some purple loosestrife populations which are sympatric with winged loosestrife have heights and leaf lengths intermediate to most other winged and purple populations. These observations are consistent with the possibility that purple and winged loosestrife have hybridized in North America, although the possibility can not be excluded that purple loosestrife has evolved traits similar to those found in winged loosestrife without hybridization. Table 1: Taxonomic characteristics that separate North American winged loosestrife (Lythrum alatum) and Eurasian purple loosestrife (Lythrum salicaria) (Graham, 1975). Lythrum alatum Lythrum salicaria 1 to 2 flowers per leaf axil 4 or more flowers per leaf axil leaves alternately placed leaves placed opposite or whorled glabrous, oblong calyx Pubescent calyx distylous Tristylous dwarf, less than 3 feet tall 4 feet tall or more Oblong-Ovate to Linear-Lanceolate Leaves Lanceolate leaves 15 Materials and Methods Population surveys Lythrum salicaria and L. alatum populations were surveyed afier flowering in the months of July and August. Michigan populations were surveyed in August, 1997, Ohio populations in July, 1998, and Massachusetts and Wisconsin populations in July, 1999. Distribution of collection sites by map location are outlined in Figure 3, and details for each population (region, species, name, abbreviation) are found in Table 2. Population _ size estimates and short descriptions of the habitats of each population are listed in Table 3. The main difference in population habitats was water depth. Populations ranged from permanent flooding at depths greater than 30 cm, to no history of flooding whatsoever, with all available water determined by rainfall. L. salicaria clones were surveyed in a transect across the width of each population, at a distance of ten meters from each other, to minimize the possibility of repeat sampling of the same clone. In general, individual clones were distinct, forming colonies of 20 - 25 individual shoots. An attempt was made to sample at least 50 clones from each population, although some populations were too limited to collect this many samples without duplication. L. alatum clones were also surveyed 10 meters apart in the larger populations, but in the smaller populations, plants were examined as close as 1 m, as L. alatum plants do not exhibit the same degree of vegetative underground growth as L. salicaria, so distinguishing between different plants was much easier. In the large populations, 50 clones were surveyed at regular intervals, but in the small populations, all 16 distinct clones were surveyed. Total numbers of clones surveyed in both L. salicaria and L. alatum populations are listed in Table 3. A total of six taxonomic traits (Table 1) were surveyed in each clone. Flower number was counted in each leaf axil along a random shoot in each clone and the average number of flowers per leaf axil was recorded. Placement of leaves along the stem was also noted as either alternate, opposite, or whorled. The calyx was rated as either glabrous or pubescent, by examining all calyxes along another random shoot in each clone. Style length was recorded on 10 randomly selected flowers on each clone to determine if there was deviation from distyly in Lythrum alatum or tristyly in Lythrum salicaria. The height of the tallest shoot of each clone was also measured. Leaf length and width of two to three randomly selected leaves on each plant was measured for use in determining leaf shape, via ratios (length / width). 17 Table 2: Location and species found at each study site. State Species Site Abbr. Latitude Longitude Michigan Lsalicaria Lake Lansing LLA 42:44:59 N 084:24:02 W Michigan L.salicaria Crow Island St. Game Area CIA 43:28:11 N 083:54: 14 W Michigan L.salicaria Shiawassee R. St. Game Area SRA 43:23: 13 N 083:57:58 W Michigan L.salicaria Quanicassee Wildlife Area B QWB 43:35:00 N 083:40:51 W Michigan Lsalicaria Quanicassee Wildlife Area A QWA 43:35:00 N 083:40:51 W Michigan Lsalicaria Sheep Farm B SFB 43:39:13 N 083:27z58 W Michigan Lsaltbaria Harsen's Island HIS 42:35:22 N 082:35:]9 W Michigan L.alatum Sheep Farm A SFA 43:39:13 N 083:27z58 W Michigan L. alatum Algonac State Park ASP 42:37:06 N 082:31:52 W Michigan L. alatum Wildfowl Bay WFB 43:53:00 N 083:22:00 W Michigan Lalatum Rose Island Railroad RIR 43:46:58 N 083:25253 W Michigan L. alatum Harsen's Island I-IIW 42:35:22 N 082:35: 19 W Wisconsin Lsalicaria Wee Know School WKS 43:06:18 N 0882031 W Wisconsin L.salicaria Bark River BR] 43:04:50 N 088:15:40 W Wisconsin Lsalicaria Duck Creek DCR 44:33:43 N 088:04:09 W Wisconsin Lsalicaria Senior Citizen Center SCC 42:54:38 N 087:5]:38 W Wisconsin Lsalicaria Tichigan Lake TLP 42:49:44 N 088:11:51 W Wisconsin Lalatum Janesville JAN 42:40:58 N 089:0]:07 W Wisconsin Lalatum Herbarium Preserve HPR 43:04:53 N 088:54z42 W Wisconsin Lalatum Tichigan Lake TLW 42:49:44 N 088:11:51 W Wisconsin L. alatum Nature Conservancy NCO 42:30:44 N 087:48:33 W Ohio L.salicaria Ottawa Natl Wildlife Refuge ONP 41:36:56 N 083: 12:58 W Ohio Lsalicaria Kildeer KIL 41:02:39 N 083:39:00 W Ohio Lalatran Kitty Todd A KTA 41:34:46 N 083:37:02 W Ohio Lalatum Kitty Todd B KTB 41:34:46 N 083:37:02 W Ohio Lalatwn Kildeer KIW 41 :02:39 N 083:39:00 W Ohio Lalatum Ottawa Natl Wildlife Refuge ONW 41:36:56 N 083:12:58 W Massachusetts L.salicaria Field Farm FFA 42:42:43 N 073:12: 15 W Massachusetts Lsalicaria West Pittsfield WPI 42:25:51 N 073:18:37 W Massachusetts L. alatum Sheflield SHE 42:06:37 N 073:21z20 W l8 888» :8 .eteomfi 833 8:888 oz 878 5:884 28888 =88 85882 288 88A 8588 .883 8-8 88884 288: 83 8:88 :8 .88 .888 :8 .8888_ 2&8 58v :5 88 28:8 88.88 88.8884 88 28: 88.8 .88 .885888_ 8853 28 288 8888 O2 878 .8884 8x 8883 82 $80 8888 =8 .888 .88 .88888_ 8853 8588 oz 878 3:884 88. 88. :88 858 .888» :8 .8355 88882 8853 8.. 2&8 8888 oz 8v 88884 888. :88 858 .8888 :8 .8388 88882 8853 28 2&8 8888 oz 878 .538 4 8828 8888 88 .883 :8 88882 885 8.. 2&8 8.88: oz 88-8_ 88884 8.3 8:83 82 88:0 8888 :8 88888. 8883 8888 oz 878 5884 888880 9882 88 .882. as .8888 88882 8853 9888 oz 8-8 .5884 83 5888 838 .88 .8888 :3 883823 .8888. 8853 8.888 oz 878 $884 3888 8:88: 828 :88... .8888 :8 88.88. 8853 8888 oz 878 .5884 8:885: 888 88882 2&8 :8? 8588 .588 878 888884 8.3 8888 88 .8888 :8 88882 298 8588 oz 8-8 888884 8880 886 88m 888» e8... .82. 88882 298 88A 8588 .888 878 58884 :86 88 8888 .88. .8888... 2&8 88-88 3888.883 878 8889.4 8.5. c.8. 888 98 88888. 2.5.. 8888 02 8883 88884 888 329 83 8888 .88 .2888 88882 833 ea 2&8 88v .8 88 2888 8-8 2:884 822 8.88.8: 882» .888 83 .83 .8888... 8853 988: oz 8v 8.884 8888. 882 83. 8888 =3 28 88882 833 88v 5.. 88 88288 878 5:884 :8 768.3 883825 888 .888» .8888... .8853 8888 oz 88-2: 2:884 8.88 3.8 8:82 828 as. 888» 88882 8853 8888 oz 878 .8884 < Sam 888 888 .88 .2888 88882 8853 88 2&8 88v :5 88 288: 8-8 88884 882 888: 88.8 .88 88882 2&8 8888 oz 878 88884 m 85 82m 88358 883 .83 80783 .888 .8888... 298 88-88 88 288“. 8? 8883.4 < 883 8885.0 88585 8883 .888 88-33 .888 88882 2&8 as? 8588 2883 878 888.884 m 88.3 §§_§o 83w 9:8 woo.— .85-8 30.5 .83 50.8: dab-682 295m EoomA mfivoou 8.6m comA 8.8.4.4384 8.2. 0:80 cow-833$ 8.88 88882 2&8 88? 8888 .888 822 88884 82 280 283 320 88w 38:8 32 6me £5882 295A— Eoom-Eom wfivoocébm comA etc-4:84 mama—3 8.3-— £8858 589 883 88 .83 88% 8m .88 3:8 some 8 «cogobéomo cab 98 on? cote—smog £58895 an 933—. 19 d8§>o£nm .3 828%”: 08 $85 .0355 a :33 m8?- ?me was .226 a 5? 5533 d 6.8888 a £3» @883 mm 3.8.53. .4 .358 m3“ 5 608035.0- maouwwaoa 358 was .5533 d 6.4.8323 535.3% 88803 um 0.5»:— -...-. a. .. .r‘. «Id: 21 .882 4 95842.4 9 EBaBd . 20 Common garden experiment Seed was collected from 8 Michigan populations ( 4 L. salicaria and 4 L. alatum) in late September of 2000. Four purple loosestrife and four winged loosestrife populations were selected (HIS, SFB, LLA, QWB, HIW, SFA, ASP, and WFB). These populations were chosen to represent two allopatric and two sympatric populations of each species. The sympatric populations of purple loosestrife chosen (HIS and SFB) were previously determined to have intermediate heights and leaf lengths in the field studies. A randomly selected shoot from each of 20 random clones was collected along a transect across each population. Ten flowers were chosen fiom each shoot, and their seed were spread onto moistened soil in a covered tray and allowed to germinate under artificial light. After germination, seedlings were transplanted to 10 cm. pots and grown in a single greenhouse at Michigan State University, East Lansing MI, under 12 hour day lengths supplemented with artificial light. They were each fertilized with 2 tablespoons Osmocote (The Scotts Company, Marysville, OH) after transplantation and watered daily. Plants were arranged on three benches in a completely randomized block design (bench being the blocking factor), and allowed to grow until flowering (approximately 8 weeks). At flowering, the same traits were measured that varied in the field (height, flower number, style length, and leaf size). Height was recorded for the tallest shoot in each plant. Number of flowers per leaf axil were counted for 10 - 20 axils in each plant and the most common number was recorded. Styly was measured on a random shoot and recorded as long, mid, or short. Leaf size was measured on a randomly selected fully expanded leaf of each plant. 21 Univariate statistics, Analysis of Variance (AN OVA), and Principle Component Analysis on all data were performed using the SAS statistical software package (Cary, NC). Results All the L. alatum clones had the taxonomic traits considered diagnostic for L. alatum. Among the L. salicaria clones, the calyx and stny traits were always true for L. salicaria; however, the height of L. salicaria clones varied widely on a population level, from x=74.8 to 173.6 cm. The purple loosestrife populations HIS (x=107.5 cm), ONP (109.5 cm), KIL (74.8 cm) and SF B (96.7 cm) had mean heights significantly closer to typical L. alatum (x= 50.4 - 68.1 cm) than L. salicaria (Table 4, Figure 5). All four of these purple loosestrife populations were also sympatric to winged loosestrife. Similarly, leaf length in the L. salicaria populations HIS (x= 26.4 mm) and SFB (41.4 cm) were also much closer to the typical mean leaf length of L. alatum (x= 8.0 - 22.4 mm) than L. salicaria (x= 26.4 - 78.9 mm) (Figures 6 and 7). Length/width ratios were significantly smaller in L. alatum (x= 3.33 - 3.93) than L. salicaria (x= 3.26 - 5.63), but there were no significant differences among the individual species populations (Figures 8 and 9). 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Table 5: AN OVA of plant height in 14 populations of Lythrum alatum and 16 populations of L. salicaria in North America. Source DF SS MS F P Var. Comp1 % Var.2 Replication 50 91129.365 1822.587 4.91 <.0001 81.08681 2 Species 1 1009008099 1009008099 2718.42 <.0001 3069.6 78 Pop(Species) 28 346023 .656 123 57.988 33 .29 <.0001 547.67895 14 Error 915 339624.253 371.174 218.3909 6 Total 994 2344528.422 3916.7567 100 1Variance in each component 2 % of variance in each component Table 6: AN OVA of leaf length, width, and length/width ratio in 9 populations of Lythrum alatum and 12 populations of L. salicaria in North America. Length: Source DF SS MS F P Var. Comp] % Var.2 Replication 49 7509 153 1.04 0.4104 -2.33 0.0 Species 1 185761 187561 1267.62 <0.001 978.02 77.0 Pop(Species) 19 83526 4396 29.71 <0.001 161.63 12.7 Error 571 84487 147 132.69 10.4 Total 640 453791 1270.01 100.0 Width: Source DF SS MS F P Var. 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D £28m; Ea .3332 s 23m 523235: .33 ed o; o.~ o.m o6 o.m o6 o8 snug A 0111211 30 Each of the ‘intermediate’ populations of purple loosestrife was compared to allopatric purple and winged loosestrife individually for height (Figure 10), leaf length (Figure 11), and leaf length/width ratio (Figure 12). Principle component analysis was then used to look at all traits simultaneously, and the Harsen's Island (HIS) and Sheep Farm B (SFB) populations of L. salicaria appeared to be intermediate between all the other L. salicaria and L. alatum populations (Figure 13). There were significant differences (P< 0.05) in the rate of germination of seeds from the population LLA, which was significantly higher than the other purple loosestrife populations collected from seed. Unfortunately, none of the L. alatum populations produced seed that germinated at all. This may be due to a dormancy requirement for L. alatum that was not met. However, germination of HIS was still lower than the other purple loosestrife populations collected, as in the field, with some families having germination rates that averaged less than 1 seedling per flower, but this trend was non- significant when compared to the other populations. ANOVA of germination is in Table 7. HIS and SFB had significantly shorter heights and smaller leaf values than the other two purple loosestrife populations in the greenhouse (Table 8). Although absolute values of traits differed significantly between naturally occurring and greenhouse grown plants from the same populations, the overall trend of relationships between populations for each trait was preserved. However, few L. salicaria plants carried the other two L. alatum traits found in the field. All four purple loosestrife populations exhibited overwhelming numbers of plants (>95%) with opposite leaf placement vs. either alternate 31 (the diagnostic for winged loosestrife) or whorled, and four or more flowers per leaf axil compared to fewer than two flowers (the diagnostic for winged loosestrife). Table 7: AN OVA of seedlings produced per flower in four populations of Lythrum salicaria in Michigan. Two of the populations were sympatric to L. alatum, two were allopatn'c. Number of seedlings was determined for 10 flowers each of 10 clones from each population. Source DF SS MS F P Replication 9 5016 557 1.05 0.4285 Population 3 46308 15436 29.08 <0.001 Error 27 14332 530 Total 39 65657 32 Table 8: Height and leaf characteristics of four populations of Lythrum salicaria grown fiom seed in a common greenhouse at Michigan State University, East Lansing, MI. Two of the populations were sympatric with L. alatum [Harsen's Island (HIS) and Sheep Farm B (SFB)], and two were allopatric [Lake Lansing (LLA) and Quanicassee B (QWB)]. Values are given for natural populations and seedlings grown in a greenhouse. Mean values were compared using SAS (Cary, NC). Bold values are significant at P=0.05. Natural populations: Greenhouse populations: Height: Mean LLA QWB SFB Mean LLA QWB SFB 107.5 HIS <.0001 0.0118 0.151 67.9 HIS <.0001 <.0001 0.508 173.6 LLA <.0001 <.0001 87.7 LLA <.0001 <.0001 126.3 QWB <.0001 77.3 QWB <.0001 96.7 SFB 69.2 SFB Leaf Length: Mean LLA QWB SFB Mean LLA QWB SFB 26.4 HIS <.0001 <.0001 0.0028 69.5 HIS 0.0005 0.0064 0.0185 48 LLA 0.0003 0.0547 76.2 LLA 0.3043 <.0001 62.1 QWB <.0001 74.6 QWB <.0001 41.4 SFB 65 SFB Leaf Width: Mean LLA QWB SFB Mean LLA QWB SFB 8.2 H18 0.4939 <.0001 0.3485 21.1 HIS 0.0929 0.0022 0.2828 8.8 LLA <.0001 0.7029 19.9 LLA <.0001 0.4563 11.7 QWB <.0001 23.4 QWB <.0001 9 SFB 20.4 SFB Leaf Length/Width Ratio: Mean LLA QWB SFB Mean LLA QWB SFB 3.3 HIS <.0001 <.0001 0.0006 3.4 HIS <.0001 0.7588 0.9574 5.5 LLA 0.9139 0.0079 4.1 LLA <.0001 <.0001 5.4 QWB 0.0236 3.3 QWB 0.7596 4.7 SFB 3 .4 SFB 33 (Bo—0:39: £556 Q £538 3387. C329 93 .owaom 0.525» 3.232 «385 .m scam aoonm .933 «.0835 330:9. 4&0 3033300 ocean—Sm 50m 3 339:8 3050 50308 macaw—smog £533 .4 EH 3.28:3. 5.25.3 2530:“ :0 mo Emma: E cousntuma "an 0.5!..— Einua .5553. e a a I I I In». 94? Iac I». IoI IAI IeI oI0I I». p I... I». I 0II5 0IACOIIOO II§ I0II9 0II.A 0II..60II0I 01/»v II9 QIIA II». II 8% a 0J9? 9 I0I IOI I9I 008/ II_0%0I p. I 099 0591.60 I o o 0 0o. 0.. 00a on. 09 a. a o wewafiuoaewvezeeao a... 09 a. a». o # # o w. 8~ I. .d 8m M w- m 0 8m 9. u§m§4§§< o c N # M N an e w. v w. m m e a 2 w l n a S m Sketch 4. 38.35.4- . Q 9. ., 3 $29 one“... £35» 3522 :55 .820— m .. .. v w. w. w u u 2 m n . n n _ n 3.50230. NI organ». 4' m =5... 325 an: .52: “has: Allopatric L. salicaria 8O 3 a 60 E A: 40 ~a at 20 ._ 0 Harsen's Island (HIS) IL. salicaria # of Plants leaflnigdl: SheepFarmB 2 a. ‘5 at 80 '3 60 a Ga 40 "5 at: 20 0 s§§§§=§§v®¢§ leaf length (mm) Figure 11: Distribution in leaf length in all allopatric L. salicaria and L. alatum (top and bottom frames) compared to two sympatric populations of L. salicaria (Harsen's Island, Sheep Farm B) skewed towards L. alatum morphology. 35 Allopatric L. salicaria 80 O E 60 _ .2 ‘, 9- 40 ~52 at 0 a 0 Harsen'slsland 10 J1 I L. salicaria L— 3 8 fl 2 6 A. 4 l ‘6 2 I- * 0 n I... I Sheep Farm B (SFB) 510 E 3 ; V 9: a a: o 3 fl 5 fl: «- 0 3t G). b. I\ . Leaf Ratio Figure 12: Distribution in leaf length/width ratios in all allopatric Lythrum salicaria and L. alatum (top and bottom fi'ames) compared to leaf length/width ratios in two sympmc populations of L. salicaria (Harsen‘s Island and Sheep Farm B) skewed towards L. alatum morphology. 36 3 o Allopatric L salicaria I Sympatfic L salicaria 2 _ o Allopatn'c L alatum c1 Sympatn'c L alatum . o 1 — ,‘o <9 SFB I 3'5 a: 3 o — 0. 0 ° 0 '1 ‘ D HIS I .2 _ o ‘3 l l l l l -3 -2 -1 0 1 2 3 PC1 (96%) Figure 13: Principle component analysis of L. salicaria and L. alatum populations. All variable morphological traits were included in this analysis (leaf placement, length, width, length/width ratio, plant height, and flower number per leaf axil). Region of origin, species, and sympatry vs. allopatry are denoted. Two populations which appear intermediate are labeled by name. Discussion Most of the North American L. salicaria carried at least a few L. alatum traits that have not been described in Eurasian L. salicaria. This suggests that the two species may have hybridized in North America, supporting the morphological evidence in Minnesota 37 described by Anderson and Ascher (1994), but on a much larger geographic scale. None of the L. alatum populations carried any of the L. salicaria traits, which is not surprising, since the theoretical hybrid would be tetraploid and only capable of backcrossing to purple loosestrife populations, unless triploids exist (which is rare in plant species). Screening 20 random winged loosestrife plants, unreduced gametes were produced at a rate of 0.35% (70 unreduced gametes in 20,000 pollen grains screened, data not shown). Because the L. alatum traits appear across the entire range of L. salicaria, such a hybridization would have had to occur several times throughout the history of the two species, or the hybridization occurred early in the establishment of purple loosestrife and spread across North America. The possibility of multiple hybridizations is supported by the two L. salicaria populations (HIS and SFB) which were intermediate in height and leaf ratio between the typical L. salicaria and L. alatum populations in both the native field and common greenhouse. This intermediacy may be evidence that they are hybrid swarms, suggesting that interspecific hybridization is ongoing, although it remains possible that purple loosestrife is evolving a more xeric ecotype favoring winged loosestrife habitats. Interestingly, most of the purple loosestrife plants grown in the common greenhouse had the leaf placement and flower numbers typical of purple loosestrife, even though plants of both typical purple and typical winged loosestrife traits were collected in the field for use in this study. These traits must have a strong environmental component. Purple loosestrife was not considered invasive until well after its establishment in North America, specifically when it began to form monospecific stands in the floodplain pastures of the St. Lawrence River in Quebec in the 1930’s (Louis-Marie, 1944). The 38 subsequent invasions of purple loosestrife have followed a distinct pattern, a few plants appear in a region, the plant stays a very minor member of the community for 20 - 40 years, then in a very short interval (approximately 5 years) becomes the dominant member of the wetland community (Stuckey, 1980). Ellstrand and Schierenbeck (2000) have suggested that some exotic invasive plants only become invasive afier hybridization with a native species, and one of the examples they site is L. salicaria, using isozyme evidence provided by Strefeler et al. (1996). This isozyme evidence was not conclusive, which is why I chose to do further, more in depth studies. My morphological data lends further support to the hybridization hypothesis. The delays in invasion may occur because purple loosestrife must gain and reassort genetic material from winged loosestrife to help it adapt to new North American habitats. Not knowing the genetic basis for any of the morphological traits studied, it remains possible that invasiveness in purple loosestrife arose through genetic divergence without interspecific hybridization, or new mutations have arisen in purple loosestrife genetic material after its arrival in North America. It is also possible that an ecotype is evolving in purple loosestrife that is better adapted to the drier habitats of winged loosestrife through reassortment of its own genetic variability. In the next chapter, we will use AFLP markers to show that, indeed, ecological differentiation without interspecific hybridization is the most likely basis of L. salicaria's ecological success in North America. Knowing whether hybridization or ecological differentiation has played the primary role in purple loosestrife’s success in North America could be critical to determining methods of control. Much interest has been devoted to methods for 39 biological control of purple loosestrife, specifically searching for herbivores that feed on purple loosestrife in its native Eurasia (Blossey, 1995). Based on host specificity, three herbivore species have been chosen: Galerucella calmariensis (L) and G. pusilla (Duff), leaf feeding beetles, and Hylobius transversovittatus Goeze, a root feeding weevil (Kok et al. 1992a, b). In no-choice tests, the leaf feeding beetles were found to oviposition as well as feed on winged loosestrife, although in choice tests, purple loosestrife was preferred (Kok et al., 1992). If hybridization has taken place between purple and winged loosestrife, it could have altered the susceptibility of purple loosestrife to Eurasian predators. Two effects are possible. First, the hybrid could be less susceptible to Eurasian predators than purple loosestrife is in Eurasia and pass that resistance on to purple loosestrife populations. Alternatively, the hybrid could provide an evolutionary “bridge” for the Eurasian predators to adapt to feeding on winged loosestrife. Documentation of hybridization occurring in the wild between these species will allow environmental managers to make more informed decisions about biological control agents. If purple loosestrife in North America becomes more resistant to Eurasian predators than the Eurasian purple loosestrife, much time and money could be wasted breeding and releasing insects that will have little or no effect. Additionally, if the Eurasian predators are more effective predators of F1 hybrids, our native species may be put at risk. 40 CHAPTER 3 MOLECULAR DIVERSITY IN EUROPEAN AND NORTH AMERICAN LYTHRUM Introduction Lythrum salicaria became an invasive, noxious weed after arriving in North America, but it is not considered invasive in its native environment (Batra et 01.1986). One possibility for how it became invasive is that it hybridized with a close relative in North America, such as L. alatum, and gained genes that made it better adapted to this new environment. In Chapter 2, I tested this hypothesis by searching for morphological evidence of hybridization. By examining a variety of purple loosestrife populations across the northeastern United States, I found several traits that are not present in European populations of purple loosestrife but are found in North American winged loosestrife. These unique morphs found in North American purple loosestrife suggest hybridization between the two species (Chapter 2; Anderson and Ascher, 1994; Strefeler et al., 1996). In support of this, I identified intermediate sized L. salicaria where the two species grow sympatrically and could have hybridized (Chapter 2). However, it is also possible that the genetic variability already present in L. salicaria has reassorted without hybridization into new morphologies and adaptive types. This might have been enhanced by its polyploid nature. There are several aspects of polyploids that can contribute to their success. They can hybridize with their diploid progenitors via unreduced gametes, or form recurrently fiom multiple parent populations. 41 Their polyphyletic origin also can lead to the incorporation of high levels of genetic diversity (Soltis and Soltis, 2000). As a result, polyploids have higher levels of heterozygosity than their diploid progenitors and less inbreeding depression. The high level of genetic variability found in polyploids can be fithher assorted through genomic rearrangement, and in the case of autopolyploids, tetrasomic inheritance. All of these factors are quite applicable to L. salicaria and may have contributed its success as it encountered new habitats across North America. We used amplified fragment length polymorphism (AFLP) markers to fiirther analyze the relationship between L. salicaria and L. alatum, and search for evidence of hybridization. We screened all of our North American and European populations of L. salicaria and L. alatum with 5 primer pairs, and then evaluated eight Michigan populations (selected for allopatry or sympatry between the two species) with an additional 18 primer pairs, to determine the genetic relationship between L. salicaria and L. alatum in North America, and North American L. salicaria to European L. salicaria. We found that there is no molecular evidence of hybridization in North America between the two species. However, we did find that North American L. salicaria has differentiated from European L. salicaria, and this differentiation may be the real reason that L. salicaria has been so successful in North America. The utility of AFLP analysis Molecular markers are useful in determining genetic evolution and changes within an organism. Morphological traits are controlled by a wide range of gene numbers and frequently have large environmental components, making them often misleading in 42 evolutionary studies. By using molecular markers, the changes across an entire genome can be studied with no extra weight assigned to any single trait or change (Tohme et al., 1996) Amplified fiagment length polymorphism (AFLP) analysis, as developed by Vos et al. (1995), has fast become a favored method of DNA marker analysis. This technique combines the reliability of RFLP markers with the time efficiency of PCR—based markers and yields at least 10 times more genetic loci per primer pair than RFLP or RAPD analysis in many crop species (Tohme et al., 1996). The resulting DNA fingerprint yields a large number of genetic markers, and the multiplex ratio (the number of information points analyzed per experiment) is higher than for other commonly used markers (RFLPs, RAPDs, or SSRs) (Powell et al., 1996). AFLPs have been used in many species to study evolution and genetic relationships, with some examples including soybean (Maughan et al., 1996), lettuce (Hill et al., 1996), tea (Paul et al., 1997), tef (Bai et al., 1999), olive (Angiolillo etal., 1999), and cassava (Roa et al., 1997). AFLP analysis has been used to determine both genetic similarity and average amount of polymorphism in a number of different species groups. Comparing difl‘erent cultivated and natural olive species, Angiollio et a1. (1999) found the average percentage of polymorphism to be between 51% for one primer combination and 83% for another. Vroh et al. (1999) compared upland cotton to the wild species and found that genetic similarity between the two groups ranged from 29.5% to 43.2%. Within closely related tef accessions, however, Bai et al. (1999) detected a very low level of polymorphism (18%), but still detected differentiation within these closely related individuals. One common denominator for AFLP analysis is its ability to discern relationships in even the 43 closest of related individuals; this made it ideal for searching for hybridization between L. salicaria and L. alatum, because the closeness of the relationship between the two species was not previously known, and could be quite high. Materials and Methods Plant collection Plant tissue was collected from each clone of L. salicaria and L. alatum surveyed in the previous morphological studies. Approximately 10 young green leaves were collected from every clone in early to late June before full growth and flowering occurred. The leaves were placed in a ziploc bag with enough silica gel to completely cover the leaf tissue. Bags were then labeled as to population and individual, sealed, and stored at room temperature for several months until the DNA was extracted. Number of individuals collected from each population corresponds with numbers surveyed in the previous morphological study, outlined in Table 4. European samples of L. salicaria were obtained from Dr. Bernd Blossey at Cornell University. Seed had been collected from 11 European populations and grown in a common garden at Cornell University. These populations originated from Germany, England, Ireland, Austria, and Finland. Four to six leaves were collected from five clones in each European population, covered with silica gel, and shipped to Michigan State University. Six cultivars of L. salicaria were purchased based on availability. Three clones each of Robert, Roseum Superbaurn, and Purple Spires were purchased from Wrenwood 44 of Berkeley Springs (Berkeley Springs, WV). Three clones each of Happy, Morden's Gleam, and Morden's Pink were purchased from Bluestone Perennials (Madison, OH). New leaves were collected from each plant the morning that DNA was to be extracted. DNA extraction DNA was extracted following the protocol of Doyle and Doyle (1990) with modification. Three to four leaves from each clone (approximately 1 g) were placed in a sterile mortar, liquid nitrogen was added, and the leaves were then ground to a fine powder. CTAB buffer [2% w/v hexadecyltrimethylammonium bromide (CTAB), 1.4 M NaCl, 0.2% v/v 2-mercaptoethanol, 20 mM EDTA, 100 mM Tris-HCl (pH 8.0)] was added 800 uL at a time twice for a total of 1600 uL, and the material was ground into a slurry. The resulting homogenate was poured into two 1.6 mL tubes and gently mixed by inversion. The tubes were placed in a water bath at 60°C for 30 — 60 minutes, with periodic mixing by inversion. The tubes were then removed fi'om the water bath and allowed to return to room temperature. Equal volumes of Chloroform: Isoamyl alcohol (24: 1) were added to each tube (approximately 800 uL), and the tubes were inverted to gently mix them. The tubes were centrifuged at 14,000 x g for 5 minutes, and then the top aqueous layer was transferred to a new tube. Equal volume (approximately 800 uL) of ethanol acetate (4 % 3 M NaAc and 96 % EtOH) was added to each tube, gently mixed, then the DNA was allowed to precipitate for 10 to 30 minutes at room temperature. The tubes were centrifirged at 14,000 x g for 5 minutes, and the supernatant was gently poured or pipetted off, saving the pellet. The pellet was washed in 70% EtOH, and then spun for 5 minutes at 14,000 x g. The tube was then left open 45 overnight in a sterile laminar flow hood, to allow the pellet to dry thoroughly, before being resuspended in 50 uL TE. DNA preparation for AFLP analysis Gibco BRL-Life Technology (Rockville, MD) reagents were used for all digestions, ligations, and other AFLP preparations and experiments. First, 200 ng of DNA were digested in 5 uL of 5X Restriction digest buffer, 2 uL of EcoRl/Mse I restriction enzyme solution, and an appropriate amount of autoclaved ddI-120 to bring the final volume to 20 uL per reaction. This solution was held at 37°C for 2 hours, then the enzymes were deactivated at 70°C for 15 minutes. Next, ligations were performed by adding 19.2 uL of the Adaptor/Ligation solution (containing Gibco patented extensions to ligate to the sticky ends of our digested DNA) and 0.8 uL of T4 DNA ligase directly to each digestion. This was incubated at 20°C for 3 hours. Afier ligations, 10 uL of each solution was pipetted into a new tube and diluted 1:10 with 90 uL of 0.1 M Tris/EDTA (TE). The remaining ligation solution was stored at —20°C. The diluted ligation solution was then used for the pre-amplification reaction. For each preamplification reaction, 20.0 uL of Pre Amp Primer Mix 1, 2.5 uL 10X PCR Buffer, 1.0 uL 50 mM MgC12, 0.5 uL Taq DNA polymerase, and 0.5 uL of the diluted template DNA from the ligation reaction were mixed together in a tube, and then held in a Perkin Elmer 9600 PCR machine for 20 cycles of the following program: 94°C for 30 seconds, 56°C for 1 minute, and 72°C for 1 minute. The program finished with 72°C for 10 minutes and then a 4°C soak. 5 uL of the preamplified reaction was then run on a 2% Tris, Boric Acid, and EDTA (TBE) gel, and photographed to score for relative 46 DNA concentration. The brightness of the DNA smear was used to determine the final dilution of the sample. Bright, clearly visualized pre-amplified reactions were diluted 1:20; while faint, identifiable but not clearly visualized pre-amplified reactions were diluted 1:10, and absent smears were lefi undiluted. These diluted samples were then stored at —20°C pending AFLP amplification reactions. AFLP reactions Initial screens included 10 individuals from each of the North American purple and winged populations, as well as 5 individuals fiom each European population and 3 samples of each cultivar. The 320 samples were divided into four sets of 80, with two positive controls (Arabidopsis and Tomato DNA) and two negative controls (ddH20) included. Five primer pairs were selected to use in this study, which are listed in Table 9. Each reaction consisted of 0.5 uL EcoRl primer, 4.5 uL Msel primer and dNTP mixture, 2.5 uL 10X PCR buffer, 0.8 uL 50 mM MgC12, 0.5 uL Taq polymerase, 13.7 uL ddH20, and 2.5 uL diluted template DNA for a total reaction volume of 25 uL. Reactions were performed in a Perkin Elmer 9600 PCR thermocycler set with the following parameters: 35 cycles of 94°C for 30 seconds, 56°C for 30 seconds, 72°C for 1 minute, then 72°C for 10 minutes and a 4°C soak. The reaction solutions were then stored at —20°C until being run on a gel. Eight populations of Lythrum in Michigan were selected for fithher analysis: 1) four populations of L. salicaria, two sympatric with L. alatum and two allopatric, and 2) four populations of L. alatum, two sympatric with L. salicaria and two allopatric. The sympatric populations of L. salicaria were chosen because they were shorter and had 47 smaller leaves than the other L. salicaria populations, even in the greenhouse. Five samples fiom each of the species populations were analyzed with 18 primer pairs (Table 10) following the above protocol. Polyacrylamide gel electrophoresis A 5% acrylamide gel (12% acrylamidezbis, 1X TBE, 40X Urea w/v) was poured into a BioRad Sequi-Gen GT Sequencing Cell (Hercules, CA) and polymerized by adding 700 uL 10X ammonium persulfate and 200 uL TEMED per 150 mL acrylamide solution. Formamide buffer containing xylenol and bromphenol indicators were added to the DNA reaction solutions, and the samples were denatured by heating to 96°C for 5 minutes, then stored on ice to preserve denaturization while loading into the gel. The gel was loaded through a 96 well 0.4 mm comb, with Gibco 10 bp and 25 bp ladders on both ends. The gel was run at 85 W with a variable voltage (1500 — 1700 average) for approximately 3 hours (when the xylenol color marker was approximately 10 cm from the bottom of the gel). One glass plate was then removed from the gel, and the gel was fixed, stained and developed on the other glass plate. Silver staining technique Fix/Stop (10% acetic acid), staining (1% silver nitrate and 0.6% forrnaldhyde), and developing (0.03g/mL sodium carbonate, 0.6% fonnaldhyde, and 0.002 mg/ml sodium thiosulfate) solutions were prepared from the protocol in the Promega kit (Madison, WI). The gel was placed in the fix/stop solution for 20 minutes (until the dye band disappeared), and washed three times in ddH20 for 2 minutes each. The gel was 48 then shaken in the staining solution for 1 hour, washed in ddH20 for 10 seconds, and placed in ice cold developing solution for 5 minutes, until bands appeared and were clearly identifiable, but background staining was still low. The reaction was then stopped by the addition of the fix/ stop solution, the gel was shaken for 5 minutes, and rinsed in ddH20 for 5 minutes. The gel was air dried overnight. Exposure of APC Film The gel was placed face up on a light box. Under red light, the film was aligned on the gel. The white light box was then turned on for 50 — 180 seconds, depending the darkness of the gel bands and background staining. The film was developed using the Kodak X-omat processor (Rochester, NY). Scoring the gel The gel was placed on a white light box and bands were scored for presence or absence in each lane. Results were compiled for every band that was clearly scorable, based on intensity of the band and smearing of the gel samples. This process was repeated for every primer combination run in both experiments. Statistical Analyses SAS (Cary, NC) and NTSYSpc (Setauket, NY) were used for all statistical analyses, including Cluster Analysis and Principle Component Analysis. The first three principle components were then represented graphically (Figures 14 and 16). Cluster analysis was performed with UPGMA similarity coefficients. 49 mm Study with all populations Five primer pairs were used to study 10 individuals fi'om each population, as well as five individuals from each European population and three samples from each cultivar. Sixty-four total fi'agments were observed, with 17 of those unique to L. salicaria and 12 unique to L. alatum. Of the remaining 35 fi'agments, 23 were monomorphic in all species, and 12 were polymorphic. However, no fragment appeared in both North American L. salicaria and L. alatum that was not also present in some proportion of the European L. salicaria (Table 9). Three distinct groups were observed in the principle component analysis (Figure 14): L. salicaria from North America, L. salicaria from Europe, and L. alatum. The cultivars formed a distinct subgroup within the European L. salicaria. This result was borne out by cluster analysis (Figure 15), where two major clusters were evident, one of L. salicaria and one of L. alatum. The native North American L. salicaria cluster monophyletically, forming a distinct cluster separate from the European L. salicaria and the cultivars of L. salicaria, suggesting that the evolutionary relationships between the North American L. salicaria are more recent than to the European L. salicaria. For the most part, individuals from the same North American populations clustered together. There was a clinal trend within the North American L. salicaria, with many of the populations from the same region clustering together; however, this relationship was violated with the Ohio and Massachusetts populations. 50 Table 9: Summary of AFLP variation in 15 populations of Lythrum salicaria and 12 populations of L. alatum in North America, 11 European populations of L. salicaria, and 6 cultivars. Included are number of fragments for each primer, with numbers unique to each species and number shared between species. # Frag. Unique to Primer Comb. L. salicaria L. alatum # Frag. in both Total # Frag. M-CAG/E-ACT 0 l 6 7 M-CAG/E-AGG 5 14 21 M-CAG/E-AAG 2 3 6 11 M-CAG/E-ACG 5 1 6 12 M-CAG/E-ACC 5 5 3 13 Total 17 12 35 64 51 .mp8 baggage 05 do 33:32am 5 3329: mm :oflatg 3205 3 Engage". E8388 03655 :30 «an: owflnoocom .mofiho some 3 £556 4 Ba .8359 none 3 558:3 4 mo magmas“. 6,233.5 v23 ,3 316.55. .N 539:5 629:0 82¢ E @88me mm 5.86:5. d 5053 5.82 .353 3 39:2: £83333 =m 8m mam—SQ. “unconfioo barium u: 9.53% or- ml VI (%6) 80d 93:30 €83va mtmoamm .4 £53m 4 EmoroE< :tozv atmoamw 4 OODD 52 .083 823389 528:2 5.82 :03 0.8.23 com: mm 538 .8 28m 8m 823305.? .3833“. {N 528:5 Ea 6.83:3 .3538. d 802.522 5.82 35 coo—05 85:: on :8 .5620 .29 2:. .5536 d z» mug—2: 8620 .532 on“ can Stanza d an mug—2: 8526 no“ 2:. $ng 5 BEE.“ macaw—smog =u memes—05 .5536 ..~ Ea 3.86:3. :20 $9333 .8620 "3 9...»:— 830880 «hum has...” Nuan— DD.— 6” D . ”Hang—TI”- . . . . — (HUQBZOH 30 II Samba?» :N 53 Further stuajr of Michigan populations Eighteen additional primer pairs were selected to study five individuals from each of eight Michigan populations. Using the additional eighteen primer pairs, 216 total fragments were observed, with 76 of those unique to L. salicaria and 86 unique to L. alatum. Of the remaining 54 fragments, all were monomorphic in both species (Table 10). Both principle component analysis and cluster analysis split the populations into two separate groups based solely on species (Figures 16 and 17). The sympatric populations of L. salicaria that appeared morphologically intermediate to L. alatum did not appear intermediate using the molecular markers. They clustered within L. salicaria, separate from L. alatum. Individuals from the same population always clustered together. An example of a gel run in this experiment is in Figure 18. 54 Table 10: Summary of AFLP variation in four populations of Lythrum salicaria and four populations of L. alatum in Michigan. Included are number of fragments for each primer, with numbers unique to each species and number shared between species. # Frag. Unique to: Primer Combination L. salicaria L. alatum # Frag. In both Total # Frag. 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