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Systematics |
2Department of Higher Plant Systematics and Evolution, Institute of Botany, University of Vienna, Rennweg 14, A-1030 Vienna, Austria; and 3Department of Chorology and Vegetation Science, Institute of Botany, University of Vienna, Rennweg 14, A-1030 Vienna, Austria
Received for publication February 26, 2002. Accepted for publication July 12, 2002.
| ABSTRACT |
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Key Words: alpine plants amplified fragment length polymorphism (AFLP) Caryophyllaceae ice age refugia long-distance dispersal phylogeography Pleistocene Saponaria pumila
| INTRODUCTION |
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The climatic situation during the coldest stages of the ice ages was very harsh in the Alps (Lister et al., 1998
). Large areas were covered by a continuous ice sheet, with only nunataks protruding from the glaciers. Outside the ice sheet, the temperature decrease was also dramatic. Whereas north of the Alps discontinuous permafrost with tundra-like vegetation predominated (Huijzer and Vandenberghe, 1998
), south of the Alps, under less severe climatic conditions, even oak forest survived in sheltered places (Paganelli, 1996
). In Central Europe mean annual temperatures are estimated to have been around 1317°C lower than at present (Frenzel, 1992a
, b
). As a consequence, the snowline decreased approximately 1200 m in the Eastern Alps (Nagl, 1972
). A shift of the vegetation belts of the same extent can be expected. During the Holocene there were also stages slightly warmer (
2°C) than at present (Prentice et al., 1998
), moving the timberline and thus vegetation belts 100300 m higher (Bortenschlager, 1991
; Burga, 1993
; Lang, 1993
).
The dramatic climate and habitat changes during the ice ages have caused diverging evolutionary lineages within species (Hewitt, 2000
). Various molecular methods offer the possibility to track these diverging tendencies (Schaal et al., 1998
; Newton et al., 1999
). Genetic structure, as revealed in phylogeographic studies in plants in recent years (reviewed in, e.g., Comes and Kadereit, 1998
; Schaal et al., 1998
), can be very different, ranging from high geographic variance within small areas (e.g., Travis, Maschinski, and Keim, 1996
; Bauert et al., 1998
; Stehlik, Schneller, and Bachmann, 2001
) to weak structural patterns in large areas due to high levels of (long-distance) migration and gene flow (e.g., Gabrielsen et al., 1997
; Hagen, Giese, and Brochmann, 2001
).
We selected Saponaria pumila (Caryophyllaceae) as a system of choice to track the impact of the ice ages in Europe on the fate of an alpine plant species. It is taxonomically isolated and occurs disjunctly in the Eastern Alps (Austria, Italy) and in the southern parts of the Eastern Carpathians in Romania (Simmler, 1910
; Meusel and Mühlberg, 1979
). Saponaria pumila is a perennial herb forming dense, large cushions only a few centimeters high. Flowers are large and pink with a balloon-like synsepalous calyx. As typical for Caryophyllaceae, they are proterandrous. Seeds are quite large (1.01.5 mm diameter) and have no adaptations for dispersal over long distances. After seed ripening, the capsules open only under dry conditions and sometimes the seeds remain in the capsule for several months (A. Tribsch, personal observation). It is likely that the balloon-like calyx containing capsule and seeds functions as a diaspore with good dispersal abilities, especially during periods of continuous snow cover (late autumn, winter), but that has not been tested experimentally.
Within the Alps, the distribution of Saponaria pumila shows strong affinities to presumptive refugial areas. The species' range includes formerly unglaciated easternmost parts of the central Eastern Alps (Fig. 1), where it is very abundant, and extends to adjacent, formerly glaciated, ranges. Saponaria pumila is restricted to acidic, siliceous bedrock and exposed, open, but stable habitats within alpine grassland communities. Disjunct populations are found in the Sarntaler Alpen, in siliceous parts of the Southern Alps (southern Dolomites: Lagorai, Cima d'Asta), and in Adamello (Pedrotti, 1988
). The altitudinal distribution ranges from 1800 to 2800 m.
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| MATERIALS AND METHODS |
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500 ng) was digested with Mse I (New England BioLabs, Beverly, Massachusetts, USA) and EcoR I (Promega, Madison, Wisconsin, USA) and ligated (T4 DNA-Ligase; Promega, Madison, Wisconsin, USA) to double-stranded adapters and preamplified using the AFLP ligation and preselective amplification module for regular genomes following the manufacturer's instructions (PE Applied Biosystems, 1996
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(pi ln[pi]), where pi is the relative frequency of the ith fragment (Legendre and Legendre, 1998
| RESULTS |
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Genetic variation
The intrapopulational diversity expressed in the Shannon diversity index (HSh) and in the percentage of polymorphic fragments (%Ppop) increases from west to east (Table 1, Fig. 2). Extremely low diversity (HSh, %Ppop, fr) is found only in populations in the western and northwestern portions of the distributional range (populations 1, 4, 5, 6, 7, 8, 9, 11). Private fragments (14 per population, see Table 1) and rare fragments (Fig. 3) are present especially in populations in the eastern part of the range. The number of fragments private to one of the four regions or shared by only two regions is given in Table 3.
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The PCoA of all individuals (Fig. 5) allows definition of E, CE, D, and CW as more or less discontinuous groups. Some individuals of population 15 (Hocheck, CE) are close to D (Fig. 5A). A PCoA with populations from E only (data not shown) shows no clear structure within this group along the first axis. Along axes 2, 3, and 4 (the four axes explain 15.4, 13.6, 13.4, and 13.3% of the overall variation), populations 30 (Saualpe), 33 (Gleinalpe), and 31 (Koralpe), respectively, are clearly separated.
Geographic relationships
Analyses of molecular variance (AMOVA) were assessed with different groupings of populations (2 to 5 groups, see Table 4). In all combinations about 50% of the overall diversity is assigned to variation within populations. When four regional groups (E, CE, D, CW) of populations are considered, 22.6% of the overall genetic diversity is found among populations within regions and 27.2% among regions.
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| DISCUSSION |
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The deepest split in the phylogeography of S. pumila is found within the large unglaciated area in the easternmost Central Alps. Mantel Tests (Fig. 7) support only this splitting (E/CE + D + CW). Even if the geographic distances between E and CE are very short, there are several possible geological as well as biological causes that might have prevented the amalgamation of the two groups. (1) Limestone, on which the species does not grow, dominates in the Radstädter Tauern and functions as a barrier in the west (Figs. 1, 9). (2) The deep Mur valley kept the populations separated and prevented geneflow. (3) Woodland areas nowadays separate the southern parts of regions CE (population 20) and E (population 29). During cold periods, however, due to the downshift of vegetation belts, these areas were possibly populated. However, if contact was not hindered for geomorphological reasons, the two ancestral groups might have been intermixing. The hybrid populations would have been extirpated during warmer periods due to the upshift of vegetation belts and the reduction of alpine vegetation to the present extent (or even less due to temperatures higher than today; cf. Lang, 1993
). Another possibility could be that a hybrid zone (Hewitt, 2001
) was possibly established between E and CE, preventing the amalgamation of genotypes over larger distances as exemplified by Martinsen et al. (2001)
. During warmer periods this presumed Pleistocene hybrid zone would have been eliminated.
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Geographic grouping
Region East (E) exhibits a high level of internal diversity (Table 1, Figs. 2, 3) and also a high number of unique markers (Table 3), which characterize this refugium. Within region E three peripheral populations are genetically isolated as indicated by higher bootstrap values in the neighbor-joining tree and by separation in the PCoA (data not shown). These are the presently (see Fig. 1) geographically isolated populations 31 (Koralpe), 30 (Saualpe), and 33 (Gleinalpe). Population 33 shows the highest fr value in the entire data set, but low HSh, making it a typical example of an "old" depauperate population. Isolation during warm periods restricting gene flow is a likely reason for the genetic distinctiveness of these populations.
Within Center-East (CE) the pattern is not clear. As a group it is significantly different from E as indicated by Mantel tests (Fig. 7). The moderate to high level of genetic diversity, especially in the more southern populations (Table 1, Figs. 2, 3), and the presence of nine unique fragments (Table 3) suggest a refugium in this area rather than a postglacial recolonization. As mentioned above, only a very small area in the east of CE (easternmost Gurktaler Alpen, around population 20, see Fig. 1) was situated outside the ice sheet, but south-exposed slopes and ridges of the central Gurktaler Alpen (surroundings of population 19), southeastern Hohe Tauern (Reisseckgruppe, surroundings of population 15; Kreuzeckgruppe, surroundings of population 13), and Goldeck (population 14) were not glaciated. The high level of genetic diversity and divergence might indicate that S. pumila did not only survive in a small peripheral refugium but also on these peripheral nunataks.
The fact that all populations of Center-West (CW) are genetically depauperate, lack unique fragments (Table 1), and possess no or very few rare fragments is clear evidence for recent colonization via long-distance dispersal. This is also indicated by a positive correlation of Mantel RM values of CW with CE and D (Fig. 7) in the Mantel tests. Even if UPGMA (Fig. 4) and PCoA (Fig. 5A) support CW, this group is only characterized by the shared absence of AFLP markers. The UPGMA shows that the genetic distances between populations 6, 7, and 8 are very low, even though the geographic distances are more than 50 km. If these isolated populations resulted from fragmentation of a formerly continuous distribution and of survival on nunataks during the last ice age, a higher level of genetic distinctiveness would be expected. Clear proof for recent or subrecent natural long-distance dispersal and establishment of viable populations as exemplified here is very rare (Ouborg, Piquot, and Van Groenendael, 1999
; Cain, Milligan, and Strand, 2000
), although the detection of processes involving long-distance dispersal are crucial in understanding the dynamics of populations and their distribution in space and time.
Even if Mantel tests (Fig. 7) do not support a separation of Dolomites (D) from CE and CW, it is very likely that these populations of S. pumila survived in a separate glacial refugium. Four unique fragments (Table 3), one present in nearly all investigated individuals, are confined to this region and the values of HSh (Fig. 2) and %Ppop (Table 1) in populations 2, 3, and 4 are moderately high compared to the highly depauperated populations from CW. Furthermore, the population most closely related to D is population 15 (Hocheck, CE; see Fig. 5A), which is geographically not the closest. Thus, colonization of D before the last glacial maximum appears more likely than postglacial spread. Glacial survival in situ in the southern Dolomites seems possible, as only the valleys were filled with glaciers and southern slopes remained unglaciated (Van Husen, 1987
). Periglacial survival in the small siliceous region further south (Fig. 9A), or postglacial colonization would involve several long-distance dispersals to explain these genetic characteristics. The genetically extremely depauperate disjunct population in Adamello (population 1) originated from recent long-distance dispersal from the southern Dolomites and is thus a typical example of a "young" depauperate population. All fragments detected in this population are also present in the Dolomites.
Limits of migration
Why S. pumila did not migrate further westward is of particular interest. In contrast to the situation at the western border of E, there are no migration obstacles like limestone areas or deep valleys. There are also no obvious changes in mesoclimate in the adjacent westerly regions. Three possible explanations must be considered. (1) The dispersal ability of the species is so poor that the migration distance per year is very short. Even dispersal over several hundreds of meters is exceptional and, as a consequence, establishment of new viable populations over larger distances is extremely rare. Moreover, the westward migration is opposed by the (at least presently) prevailing winds from west/northwest or from the southwest/south. If this is the case, it is only a matter of time before larger areas will be colonized. (2) There is a vicariant species preventing the colonization of areas further west. There is no evidence for this. (3) Strong genetic depauperation accompanied by reduced population viability in the marginal populations is resulting in the inability to recolonize new areas. This hypothesis is opposed by the fact that genetically depauperated plant populations are abundant in northern Europe (e.g., Reinhammar, 1999
) due to leading edge migration (Hewitt, 1996
), where they recolonized large areas after the Pleistocene.
Hypothetical preglacial, glacial, and postglacial history of Saponaria pumila
We can only speculate about the early stages of the evolutionary history of S. pumila. There are no closely related taxa (Simmler, 1910
), so the species may be ancient and perhaps has originated somewhere else. The history of the disjunction between Eastern Alps and the Southern Carpathians in Romania remains unclear. In the Alps it probably had been centered in the eastern Central Alps for a long time where it is still abundant. As this region was only locally glaciated during the whole Pleistocene (Voges, 1995
), recurrent glacial survival was possible more or less in situ for a long period. Reacting to climatic fluctuations, S. pumila had only to migrate vertically up and down the same mountain slopes. As a result, we find these populations with high levels of diversity and identity. The importance of this area as a glacial refugium is also emphasized by the occurrence of some endemic and many relict taxa of arctic-alpine or Alpic-Carpathic distribution (Schneeweiss and Schönswetter, 1999
). The divergence of E and CE occurred in this region probably several glacial cycles ago. Why the two regions could retain their genetic integrity at such a high level until today is not easy to see. Several possible explanations must be considered (see Geographic pattern and Pleistocene refugia). Possibly before the Würm glaciation the southern Dolomites were colonized from CE via long-distance dispersal.
The presumed situation during the coldest period of the last glaciation is outlined in Fig. 9A: S. pumila survived in the large eastern peripheral refugium (mainly E) and probably also on peripheral nunataks in the southeastern Hohe Tauern, western Gurktaler Alpen (CE), and also in the southern Dolomites (D). We favor the view that survival of alpine silicophilous plants on peripheral refugia was possible, and this is also supported by the presence of some endemics in the latter region (e.g., Saxifraga depressa, see Prosser, 2000
). A refugium "jumping" between the Dolomites and small siliceous regions at the southern border of the Alps, which do not exceed 1000 m asl, seems less likely as several long-distance dispersal events are necessary for this scenario (Fig. 9A, dotted arrow). Outside these regions, especially in the forelands of the Alps, the lack of favorable siliceous bedrock made survival impossible. After deglaciation, the remigration to the interior parts of the Alps began. The "leading edge" (Soltis et al., 1997
) of the refugial populations recolonized areas adjacent to the west by dispersal only over short distances without significant loss of genetic diversity (Fig. 9B). Within E the migration was stopped by the limestone massif of Radstädter Tauern. In the easternmost Alps at the same time fragmentation and reduction of the distributional area started. Some isolated populations retained high levels of genetic diversity. It is very likely that extinction of populations on low mountains took place during the warmest periods. The westernmost part of the present distributional area was colonized via long-distance dispersal leading to severe bottlenecks and genetic depauperation (Fig. 9B). The few locations in Adamello originate from those in the Dolomites, while the westermost populations in the interior Alps originate from adjacent Hohe Tauern populations. These were the most recent events completing the puzzle of the phylogeography of S. pumila in the Alps.
| FOOTNOTES |
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4 Author for reprint request (andreas.tribsch{at}univie.ac.at
) ![]()
| LITERATURE CITED |
|---|
|
|
|---|
Bennett K. D. 1997 Evolution and ecology. The pace of life. Cambridge University Press, Cambridge, UK
Bortenschlager S. 1991 Die Waldgrenze im Postglazial. In J. Kovar-Eder [ed.], Palaeovegetational development in Europe, 913. Museum of Natural History, Vienna, Austria
Brochmann C. T. M. Gabrielsen A. Hagen M. M. Tollefsrud 1996 Seed dispersal and molecular phylogeography: glacial survival, tabula rasa, or does it really matter?. Det Norske Videnskaps-Akademi. I. Matematisk-Naturvitenskapelig Klasse, Avhandlinger, Ny Serie 18: 53-67
Broyles S. B. 1998 Postglacial migration and the loss of allozyme variation in northern populations of Asclepias exaltata (Aslepiadaceae). American Journal of Botany 85: 1091-1097[Abstract]
Burga C. A. 1993 Das mittelholozäne Klimaoptimum Europas: Palynologische Untersuchungen an einem ehemaligen hochgelegenen Moor am Rutor-Gletscher, 2510 m (Aosta-Tal, Italien). Dissertationes Botanicae 196: 335-346
Cain M. L. B. G. Milligan A. E. Strand 2000 Long-distance seed dispersal in plant populations. American Journal of Botany 87: 1217-1227
Casgrain P. P. Legendre 2001 The R package for multivariate and spatial analysis, version 4.0 d3: user's manual. Départment de sciences biologiques, Université de Montréal, Montréal, Quebec, Canada. Available at http://www.fas.umontreal.ca/BIOL/legendre/
Comes H. P. J. W. Kadereit 1998 The effect of Quaternary climatic changes on plant distribution and evolution. Trends in Plant Science 3: 432-438[CrossRef][ISI]
Doyle J. J. J. L. Doyle 1987 A rapid DNA isolation procedure for small amounts of fresh leaf tissue. Phytochemical Bulletin 19: 11-15
Dynesius M. R. Jansson 2000 Evolutionary consequences of changes in species' geographical distributions driven by Milankovitch climate oscillations. Proceedings of the National Academy of Sciences of the United States of America 97: 9115-9120
Frenzel B. 1992a February mean temperature. Maximum cooling of the last glaciation. In B. Frenzel, B. Pecsi, and A. A. Velichko [eds.], Atlas of palaeoclimates and palaeoenvironments of the Northern Hemisphere, 39. International Union for Quaternary Research (INQUA)/Hungarian Academy of Sciences, Budapest, Hungary
Frenzel B. 1992b August mean temperature. Maximum cooling of the last glaciation. In B. Frenzel, B. Pecsi, and A. A. Velichko [eds.], Atlas of palaeoclimates and palaeoenvironments of the Northern Hemisphere, 41. International Union for Quaternary Research (INQUA)/Hungarian Academy of Sciences, Budapest, Hungary
Gabrielsen T. M. K. Bachmann K. S. Jakobsen C. Brochmann 1997 Glacial survival does not matter: RAPD phylogeography of Nordic Saxifraga oppositifolia. Molecular Ecology 6: 831-842[CrossRef]
Hagen A. R. H. Giese C. Brochmann 2001 Trans-Atlantic dispersal and phylogeography of Cerastium arcticum (Caryophyllaceae) inferred from RAPD and SCAR markers. American Journal of Botany 88: 103-112
Harold A. S. R. D. Mooi 1994 Areas of endemism: definition and recognition criteria. Systematic Biology 43: 261-266[CrossRef]
Hewitt G. M. 1996 Some genetic consequences of ice ages, and their role in divergence and speciation. Biological Journal of the Linnean Society 58: 247-276[CrossRef]
Hewitt G. M. 2000 The genetic legacy of the Quaternary ice ages. Nature 405: 907-913
Hewitt G. M. 2001 Speciation, hybrid zones and phylogeographyor seeing genes in space and time. Molecular Ecology 10: 537-549[CrossRef][Medline]
Huijzer B. J. Vandenberghe 1998 Climatic reconstruction of the Weichselian Pleniglacial in northwestern and central Europe. Journal of Quaternary Science 13: 391-417
Lang G. 1993 Holozäne Veränderung der Waldgrenze in den Schweizer AlpenMethodische Ansätze und gegenwärtiger Kenntnisstand. Dissertationes Botanicae 196: 317-327
Legendre P. L. Legendre 1998 Numerical ecology. Elsevier, Amsterdam, The Netherlands
Lister G. S. D. M. Livingstone B. Ammann D. Ariztegui W. Haeberli A. F. Lotter C. Ohlendorf C. Pfister J. Schwander F. Schweingruber B. Stauffer M. Sturm 1998 Alpine palaeoclimatology. In P. Cebon, U. Dahinden, H. Davies, D. M. Imboden, and C. C. Jaeger [eds.], Views from the Alps. Regional perspectives on climate change, 73169. MIT Press, Cambridge, Massachusetts, USA
Martinsen G. D. T. G. Whitham R. W. Turek P. Keim 2001 Hybrid populations selectively filter gene introgression between species. Evolution 55: 1325-1335[CrossRef][ISI][Medline]
Merxmüller H. 1952 Untersuchungen zur Sippengliederung und Arealbildung in den Alpen. Teil 1. Jahrbuch des Vereins zum Schutze der Alpenpflanzen und -Tiere 17: 96-133
Merxmüller H. 1953 Untersuchungen zur Sippengliederung und Arealbildung in den Alpen. Teil 2. Jahrbuch des Vereins zum Schutze der Alpenpflanzen und -Tiere 18: 135-158
Merxmüller H. 1954 Untersuchungen zur Sippengliederung und Arealbildung in den Alpen. Teil 3. Jahrbuch des Vereins zum Schutze der Alpenpflanzen und -Tiere 19: 97-139
Meusel H. H. Mühlberg 1979 Unterfamilie Silenoideae (Lindl.) A. Br. In G. Hegi [ed.], Illustrierte Flora von Mitteleuropa, vol. III/2, 9471182. Parey, Berlin, Germany
Mueller U. G. L. Wolfenbarger 1999 AFLP genotyping and fingerprinting. Trends in Ecology and Evolution 14: 389-394
Nagl H. 1972 Zur pleistozänen Vergletscherung Österreichs. Österreich in Geschichte und Literatur 16: 163-176
Nei M. 1972 Genetic distance between populations. American Naturalist 106: 283-292[CrossRef][ISI]
Nei M. W.-H. Li 1979 Mathematical model for studying genetic variation in terms of restriction endonucleases. Proceedings of the National Academy of Sciences of the United States of America 186: 5269-5273
Newton A. C. T. R. Allnutt A. C. M. Gillies A. J. Lowe R. A. Ennos 1999 Molecular phylogeography, intraspecific variation and the conservation of tree species. Trends in Ecology and Evolution 14: 140-145
Nordal I. 1987 Tabula rasa after all? Botanical evidence for ice-free refugia in Scandinavia reviewed. Journal of Biogeography 14: 377-388[CrossRef][ISI]
Norusis M. J. 1992 SPSS for Windows. Professional Statistics, Release 6.0. SPSS, Chicago, Illinois, USA
Ouborg N. J. Y. Piquot J. M. Van Groenendael 1999 Population genetics, molecular markers and the study of dispersal in plants. Journal of Ecology 87: 551-568[CrossRef]
Ozenda P. 1995 Endemism at the level of the whole European Alpine System. Acta Botanica Gallica 142: 753-762[ISI]
Paganelli A. 1996 A palynological study of forest vegetation in the Veneto-Po plain. Allionia 34: 189-217
Pawlowski B. 1970 Remarques sur l'endémisme dans la flore des Alpes et des Carpates. Vegetatio 21: 181-243[CrossRef]
PE Applied Biosystems. 1996 AFLP plant mapping protocol. PE Applied Biosystems, Foster City, California, USA
Pedrotti F. 1988 Senecio-Saponarietum pumilae, associazione nuova del Caricion curvulae del Trentino. Documents Phytosociologiques 11: 555-559
Prentice I. C. S. P. Harrison D. Jolly J. Guiot 1998 The climate and biomes of Europe at 6000 yr BP: comparison of model simulations and pollen-based reconstructions. Quaternary Science Reviews 17: 659-668[CrossRef][ISI]
Prosser F. 2000 La distribuzione delle entità endemiche "strette" in Trentino alla luce delle più recenti esplorazioni floristiche. Annali dei Musei Civici di Rovereto, Sezione: Archeologia, Storia, Scienze Naturali suppl 14: 31-64
Reinhammar L.-G. 1999 Allozyme differentiation between the lowland Carex capitata and the alpine Carex arctogena (Cyperaceae) in Scandinavia. Biological Journal of the Linnean Society 67: 377-389
Schaal B. A. D. A. Hayworth K. M. Olsen J. T. Rauscher W. A. Smith 1998 Phylogeographic studies in plants: problems and prospects. Molecular Ecology 7: 465-474[CrossRef]
Schneeweiss G. M. P. Schönswetter 1999 Feinverbreitung, Ökologie und Gesellschaftsanschluß reliktischer Gefäßpflanzen der Niederen Tauern östlich des Sölkpasses (Steiermark, Österreich). Stapfia 61: 1-242
Shapcott A. 1998 The patterns of genetic diversity in Carpentaria acuminata (Arecaceae), and rainforest history in northern Australia. Molecular Ecology 7: 833-847
Simmler G. 1910 Monographie der Gattung Saponaria. Denkschriften der Mathematisch-Naturwissenschaftlichen Klasse der Kaiserlichen Akademie der Wissenschaften 85: 433-509
Soltis D. E. M. A. Gitzendanner D. D. Strenge P. S. Soltis 1997 Chloroplast DNA intraspecific phylogeography of plants from the Pacific Northwest of North America. Plant Systematics and Evolution 206: 353-373[CrossRef][ISI]
Stehlik I. 2000 Nunataks and peripheral refugia for alpine plants during quaternary glaciation in the middle part of the Alps. Botanica Helvetica 110: 25-30
Stehlik I. J. J. Schneller K. Bachmann 2001 Resistance or emigration: response of the high-alpine plant Eritrichium nanum (L.) Gaudin to the ice age within the Central Alps. Molecular Ecology 10: 357-370[CrossRef][Medline]
Stehlik I. A. Tribsch P. Schönswetter 2001 Erstes gemeinsames Meeting zur Phylogeographie von arktischen und alpinen Pflanzen in Zürich, 1.3. Juni 2001. Bauhinia 15: 69-90
Taberlet P. L. Fumagalli A.-G. Wust-Saucy J.-F. Cosson 1998 Comparative phylogeography and postglacial colonization routes in Europe. Molecular Ecology 7: 453-464[CrossRef][Medline]
Travis S. E. J. Maschinski P. Keim 1996 An analysis of genetic variation in Astragalus cremnophylax var. cremnophylax, a critically endangered plant, using AFLP markers. Molecular Ecology 5: 735-745[Medline]
Van de Peer Y. R. De Wachter 1994 TREECON for Windows: a software package for the construction and drawing of evolutionary trees for the Microsoft Windows environment. Computer Application for Bioscience 10: 569-570
van Husen D. 1987 Die Ostalpen in den Eiszeiten. Geologische Bundesanstalt, Vienna, Austria
Voges A. [ed.] 1995 International Quaternary map of Europe. Bundesanstalt für Geowissenschaften und Rohstoffe (Unesco), Hannover, Germany
Vos P. R. Hogers M. Bleeker M. Reijans T. Van-De-Lee M. Hornes A. Frijters J. Pot J. Peleman M. Kuiper M. Zabeau 1995 AFLP: a new technique for DNA fingerprinting. Nucleic Acids Research 23: 4407-4414
Yeh F. C. T. J. B. Boyle 1997 Population genetic analysis of co-dominant and dominant markers and quantitative traits. Belgian Journal of Botany 129: 157.
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