|
|
||||||||
Systematics |
Plant and Microbial Sciences, University of Canterbury, Private Bag 4800, Christchurch, New Zealand
Received for publication March 20, 2003. Accepted for publication August 5, 2003.
| ABSTRACT |
|---|
|
|
|---|
Key Words: Asteraceae cpDNA hawkweed Hieracium pilosella hybrid introduced New Zealand reticulate variation weed
| INTRODUCTION |
|---|
|
|
|---|
The genus Hieracium (Asteraceae) is among the most species rich of plants with more described species than any other genus in Europe (Sell and West, 1976
). The systematics of the hawkweed genus is extremely complex and contentious, with much disagreement among systematists even with respect to numbers of species (Gadella, 1991
). The instability of the taxonomy is probably a reflection of the polyphyletic origin of many Hieracium taxa (Krahulcova et al., 2000
), though there is little direct evidence for this (but see Shi et al., 1996
). Many Hieracium species comprise a complex of ploidal levels, and in at least some instances, putative species may be composites of several independent hybridization events (Krahulcova et al., 2000
). Interestingly, reproductive systems vary among ploidal levels even within species; for example, in H. pilosella even ploidal numbers (e.g., 2, 4) are generally obligate sexuals while those with odd ploidal numbers (e.g., 3, 5) are usually facultative apomicts (Gadella, 1987
, 1991
). In related taxa such as H. praealtum, this is not the case; tetraploid and pentaploid plants are known, but all are apomictic.
The Hieracia of New Zealand comprises a minute, and thus manageable, fraction of the full diversity of the genus. The 10 species reported from the field are all accidental introductions from Europe first reported in New Zealand over 100 years ago (Travers, 1884
). These plants are generally thought to have arrived as contaminants of imported grass seed. The most likely source was the United Kingdom because this was the origin of most human and agricultural colonists. In addition, British colonialists founded acclimatization societies for the purpose of introducing plants and animals to New Zealand. Subgenus Pilosella is represented in South Island New Zealand by five species (H. pilosella, H. praealtum, H. caespitosum, H. aurantiacum, H. x stoloniflorum; Webb et al., 1988
). Of these, H. pilosella has, perhaps with the aid of human habitat modification, become a successful and troublesome weed among high country grasslands that predominate in the South Island (Treskonova, 1991
; Jenkins and Jong, 1997
). Hieracium is much scarcer in North Island and, so far, of little ecological significance. Hieracium pilosella forms small, prostrate leaf rosettes and, like other members of the subgenus, spreads vegetatively via stolons. In New Zealand, H. pilosella often forms dense mats that exclude other plants, but it is not a significant weed in Europe, where it occurs as a component of mixed grassland floras.
In Europe, five cytopes of Hieracium pilosella have been identified in the field, ranging from diploid to heptaploid (Gadella, 1991
). The range is dominated by sexual tetraploids and apomictic pentaploids, with higher ploidies occurring mostly in the north (United Kingdom, Scandinavia) and montane areas of central Europe. Morphologically too, H. pilosella is extremely variable. For instance, Gadella (1987)
reports that Zhan (1923)
recognized 624 variants of the species.
In New Zealand, initial cytological studies of H. pilosella indicated that populations were predominantly, if not entirely, pentaploid (Makepeace, 1981
; Jenkins, 1991
). However, subsequent studies have found aneuploids (Chapman and Lambie, 2000
) and hybrids (Morgan-Richards et al., in press
), which may reflect the presence of obligate sexuals. Tetraploid sexual plants have been confirmed in a number of populations, and these may have evolved in situ (Chapman et al., 2003
) through residual sex of facultatively apomictic pentaploids (Houliston and Chapman, 2001
). There is also considerable morphological variation (Chapman and Brown, 2001
) and evidence of high genetic diversity (Chapman et al., 2000
). Considering the recent, probable small size and apomictic reproduction of the initial introduction, H. pilosella in New Zealand is surprisingly variable. The degree to which this variability reflects initial introduced diversity vs. postcolonization changes remains unresolved (Chapman and Brown, 2001
) and is the subject of ongoing research.
We undertook a study of chloroplast DNA (cpDNA) sequence variation to further our understanding of the extent and origin (pre- or postintroduction) of genetic diversity of H. pilosella introduced to New Zealand. Our rationale was that any variants encountered were extremely unlikely to have evolved since colonization and could not be the result of recombination (unlike nuclear markers). We surveyed all other species of Hieracium subgenus Pilosella in New Zealand to seek evidence of hybridization, introgression, or reticulate evolution since colonization. To facilitate this and to shed light on the possible European source(s) of New Zealand lineages, we examined samples representing the same and closely related species sourced directly from European populations, in the first cpDNA survey of the group.
| MATERIALS AND METHODS |
|---|
|
|
|---|
European specimens were obtained as leaf samples, dried and stored with silica gel, and in some cases additional samples were provided as DNA sequences by collaborators. Our sampling in Europe reflects the availability of collectors and the distribution of taxa (e.g., H. praealtum in the United Kingdom is a localized garden escape and thus not in our sample). The provenance of our specimen of H. auricula is not known because it has been in culture for some time; however, we retained it in the study because it was the sole representative of a haplotype that forms an internal node in our tree.
Taxonomy
The systematics and nomenclature of the Hieracia is far from stable and several competing systems are in current use in Europe. For plants collected in New Zealand, we have followed Webb et al. (1988)
and as far as possible accommodated material from Europe within this system. To do this, we have relied on local expertise, and we acknowledge that without comparison of morphological and cytogenetic data some question as to placement of individuals may exist. However, we believe the determination of H. pilosella specimens is reliable and can be accommodated within all current taxonomic systems.
Ploidy
The ploidy of New Zealand specimens was determined using a combination of flow-cytometry and direct counts of chromosomes (Morgan-Richards et al., in press
). For European material for which DNA was extracted from silica-gel-dried specimens or from herbarium specimens or was obtained as raw DNA, we were not able to determine ploidy.
DNA extraction
Each sample was ground using a hot (60°C) ceramic pestle and mortar with preheated extraction buffer comprising 1000 µL 2% hexadecyltrimethylammonium bromide (CTAB) buffer in 100 mmol/L Tris-HCl pH 8.0, 1.4 mol/L NaCl, 20 mmol/L EDTA, and 2 µL ß-mercaptoethanol. Homogenates were incubated at 60°C for 3060 min. An equal volume of 24 : 1 chloroform : isoamyl alcohol was added, and the mixture vigorously shaken and centrifuged at 16 060 g for 5 min. Supernatants were pipetted into fresh tubes and combined with a two-thirds volume of cold 100% isopropanol. DNA was pelleted after 1560 min by spinning at 16 060 g for 10 min and then washed with 500 µL 70% ethanol by spinning briefly. The 70% ethanol was discarded and the pellet dried and dissolved in 30 µL of water.
DNA amplification and sequencing
We targeted noncoding regions of cpDNA as described by Taberlet et al. (1991)
. Polymerase chain reaction (PCR) was used to amplify the trnL-trnF chloroplast gene fragment (Taberlet et al., 1991
). Primers c and f (Taberlet et al., 1991
) were used to amplify the trnL intron and trnL/trnF intergenic spacer. The polymerase chain reactions were carried out in 25-µL volumes containing 2.5 mmol/L MgCl2, 200 µmol/L dNTPs, 1x PCR buffer, 0.625 units Taq (Roche Diagnostics, Mannheim, Germany) and 1.5 µL of diluted (1 : 201 : 100) DNA template. Thermal cycling conditions were: 2 min at 94°C, 35 cycles of 15 s at 94°C, 30 s at 48°C, and 90 s at 72°C, followed by 3 min at 72°C. The PCR products were purified using High Pure spin columns (Roche Diagnostics, Mannheim, Germany). Cycle sequencing utilized Dyenamic chemistry (Amersham Biosciences, Freibury, Germany) and the Taberlet et al. (1991)
primers c, e, and f following the manufacturer's protocols. Cycle sequencing products were electrophoresed on an ABI automated sequencer (PE Biosystems, Foster City, California, USA). Confirmation of base calls by comparison with chromatograms and alignment of sequences was achieved by eye using SeqEd version 3.01. We constructed a minimum spanning tree of the haplotypes identified manually.
| RESULTS |
|---|
|
|
|---|
12 species were surveyed from
72 locations in Europe (Table 1, Appendix 1) in 36 regions (Fig. 2). In total, 285 plants were sequenced.
|
|
|
|
|
Only two other haplotypes (D, G) were present in more than one taxon (Table 1, Appendix 1). Most samples of haplotype D came from H. aurantiacum (NZ and Europe), but also from H. glaciale (Europe) and H. praealtum (Europe and NZ). The two instances of haplotype D in New Zealand H. praealtum were in rare pentaploid individuals (Hope Saddle, Fig. 1); other pentaploid and all tetraploid H. praealtum in New Zealand had haplotype A. Haplotype G was found in H. x stoloniflorum (NZ), H. aurantiacum, H. florentinum, and H. pilosella from Europe.
New Zealand Hieracium pilosella
In New Zealand, haplotype A was the most frequent (70%) in both our total sample and within H. pilosella alone (Table 1, Table 3). A was present in representatives of all three ploidal levels of H. pilosella encountered (Table 4). Conversely, the other haplotypes found in New Zealand H. pilosella (B, C, and M) were restricted to pentaploids, tetraploids, and hexaploids, respectively (excluding F1 hybrids, see later). C was restricted to three adjacent locations (Drac Flat, Lyndon, and Rakaia), and M was found at just one location (Twizel) (Fig. 1, Table 4). All the tetraploid individuals in our New Zealand sample came from three intensively surveyed locations (Drac Flat, Lyndon, and Rakaia), but because we sequenced all tetraploids that we found, but not all the pentaploids, the ratio in our sample is skewed. However, the dominance of one haplotype (C) at Drac Flat is informative. Across the majority of locations, only pentaploids were found and these were either haplotype A or B (Fig. 1). At seven of 20 locations where more than one individual was examined, both A and B were found (Table 3).
|
|
European taxa
Haplotype A was also encountered with high frequency in Europe, being present in 53% of all plants and 50% of H. pilosella examined (Table 1). Of 12 taxa sampled, eight had Haplotype A and four of these had at least one other haplotype (Appendix 1). The actual extent of haplotype sharing is almost certainly much higher than this because our sample of most taxa was very small. In Europe, rare haplotypes were found in a number of taxa: I in two H. caespitosum (of eight), J in a single H. lactucella, and H in a single H. auricula.
Phylogeny
The relationship among these haplotypes was inferred using a fully resolved parsimony spanning tree. Many of the haplotypes we encountered appear as internal nodes in our tree, consistent with shallow or recent splitting (Fig. 3a). Interestingly, four of the five internal nodes consisted of haplotypes found in H. pilosella.
|
| DISCUSSION |
|---|
|
|
|---|
Reticulate evolution
We found six haplotypes within H. pilosella and extensive sharing among ploidal levels and sharing among species. Despite the predominance of apomixis the sharing of haplotypes can be explained by reticulate evolution. In New Zealand Hieracium pilosella, a low level of residual sex has been demonstrated in pentaploid apomicts (Houliston and Chapman, 2001
) and a breakdown in microspecies boundaries has been observed (Chapman and Brown, 2001
). Furthermore, sex between pentaploid apomicts not only results in pentaploids of mixed parentage but can also yield tetraploids, some of which are obligate sexuals (Chapman and Bicknell, 2000
; Chapman et al., 2003
). These and the sexual progeny of interspecies hybrids (Morgan-Richards et al., in press
; see Invasion later) may further contribute to reticulation. Nuclear markers have revealed genetic variation in apomictic microspecies of Hieracium (hawkweeds, Shi et al., 1996
; Chapman et al., 2000
) and Taraxacum (dandelions). In contrast, Wittzel (1999)
found no cpDNA variation within apomictic species of Taraxacum, the expected result for true clonal lineages (Richards, 1996
). The presence of multiple haplotypes (or other genetic variation) within apparently apomictic species could result from the failure to correctly identify microspecies (i.e., different lineages) as Wittzel (1999)
suggested for the Taraxacum data of King (1993)
. However, failure to correctly identify microspecies could be attributed to morphological instability, which would be likely if microspecies/species hybridized. It has become increasingly apparent that many (and perhaps all) apomicts are not in fact obligate apomicts but have some potential for sexual reproduction (Nogler, 1984
; Bayer et al., 1990
; Briggs and Walters, 1997
). Gene flow in predominantly selfing polyploids could result in exchange of chloroplast and other markers among lineages (microspecies, e.g., Doyle et al., 1999
) and thus inconsistent morphology.
Origins of New Zealand Hieracium
Hieracium pilosella and presumably the other species of the genus found today in New Zealand arrived sometime in the mid-1800s (Travers, 1884
). Introduction probably resulted from seed accidentally harvested with European grass seed used for development of New Zealand pastureland. It is assumed that the United Kingdom was the source of this seed but this is not supported by our data. We found more cpDNA haplotypes in New Zealand H. pilosella than in the United Kingdom. The two haplotypes in the United Kingdom (A, B) were ubiquitous throughout Europe. In particular, we did not find haplotype C in the United Kingdom, despite sampling from several populations. However, haplotype C was present in our smaller sample from eastern/northern Europe (Czech Republic, Finland). Also in our central European sample were H. pilosella and H. aurantiacum with haplotype G (Austria). Although G was not found in either of these species sampled in New Zealand, it was present in samples of the hybrid taxon derived from these parentals (H. x stoloniflorum). We note, too, that New Zealand H. x stoloniflorum, which are evidently derived from introduced hybrids rather than arising here, are hexaploid (Jenkins and Jong, 1997
; Morgan-Richards et al., in press
), and this ploidy is reported from Bavaria (Germany) and the Czech Republic but not the United Kingdom (Krahulcova et al., 2000
). It is significant too that all of the subgenus Pilosella taxa in New Zealand, except H. pilosella, exist only as garden escapes in the United Kingdom (Stace, 1997
). The combined evidence unexpectedly indicates that some, if not all, extant New Zealand Hieracium taxa came from central Europe rather than the United Kingdom.
Invasion
Why some introduced taxa succeed in founding persistent populations is not well understood. Acclimatization societies in New Zealand actively introduced foreign organisms and thus supplemented the large number that arrived accidentally (Travers, 1884
). A study of bird introductions to New Zealand revealed that colonization success might have as much to do with management as ecological characteristics of individual species (Veltman et al., 1996
). In the case of Hieracium pilosella, it cannot be known which, and in what relative frequencies, lineages (genotypes) were initially introduced. Initial studies of H. pilosella ploidy in New Zealand indicated most plants were pentaploids and tetraploids were absent (Makepeace, 1981
; Jenkins and Jong, 1997
). Sexual tetraploids have since been found (Chapman et al., 2003
), but so has evidence that apomict pentaploids are able to generate other ploidies through residual sex (Chapman and Bicknell, 2000
; Houliston and Chapman, 2001
). It has been inferred that tetraploid sexuals may have evolved in New Zealand (Chapman et al., 2003
).
The present study indicates that at least one sexual tetraploid lineage (4x C) was introduced directly from Europe. To have evolved in New Zealand would require a population of haplotype C pentaploids and given that the level of residual sex in apomicts is low (up to 2.3%; Houliston and Chapman, 2001
), a rather large population would be predicted. No haplotype C pentaploids have been found in New Zealand. All H. pilosella with haplotype C come from a small area in central South Island, and most individuals come from <25 m2 of one site (Drac Flat). It is not surprising therefore that earlier surveys did not encounter these tetraploids. This scenario might also apply to haplotype A tetraploids, and it is interesting to note that all sexual tetraploids found so far come from sites in the vicinity of the earliest record of Hieracium in New Zealand (Travers, 1884
). From our cpDNA and ploidy data, we can conservatively estimate that at least four different lineages (A, B, C, M) were introduced to New Zealand. There would have been a minimum of six lineages if shifts in ploidal level observed in plants with haplotype A occurred prior to colonization.
Although tetraploid H. pilosella are rather abundant in Europe and may have been relatively abundant in the introduced seed, it is likely that many features of pentaploids (e.g., facultative apomixis, more and longer stolons, more seeds; Gadella, 1987
) gave them advantages as colonizers. Pentaploids have the potential to colonize from single seeds, whereas isolated tetraploids might soon fail as they are self-incompatible (Krahulcova et al., 2000
). A rapid spread of pentaploids and localization of tetraploid sexuals can easily be visualized.
However, sexual tetraploids (whether introduced or derived) may be having a greater impact than previously realized. In New Zealand, H. pilosella unlike other related species (H. caespitosum and H. praealtum) appears to have rapidly increased in abundance since the 1960s (Connor, 1991
; Treskonova, 1991
; Scott, 1993a
, b
; Rose et al., 1995
; Svavarsdóttir et al., 1999
). Evidence from flow cytometry and crossing experiments indicate that this may be the result of interspecies hybridization (Morgan-Richards et al., in press
). We have observed tetraploid interspecies hybrids (probably H. pilosella x H. praealtum) at five different sites, and sequences indicate that three different cpDNA lineages have been involved in the formation of H. pilosella hybrids (Table 4). Many of the hybrids are sexual and able to back cross to parentals, and morphological and flow cytometric data indicate that many putative pentaploid H. pilosella individuals throughout New Zealand are probably pentaploid hybrids (Morgan-Richards et al., in press
). It is possible that interspecies hybridization has resulted in especially invasive lineages (Doyle et al., 1999
; Ellstrand and Schierenbeck, 2000
).
|
|
|
| FOOTNOTES |
|---|
2 Current address: Allan Wilson Centre for Molecular Ecology and Evolution, Massey University, Private Bag 11-222, Palmerston North, New Zealand (s.trewick{at}massey.ac.nz
) ![]()
| LITERATURE CITED |
|---|
|
|
|---|
Abbott R. J. L. C. Smith R. I. Milne R. M. M. Crawford K. Wolff J. Balfour 2000 Molecular analysis of plant migration and refugia in the Arctic. Science 289: 1343-1346
Bayer R. J. K. Ritland B. G. Purdy 1990 Evidence of partial apomixis in Antennaria media (Asteraceae: Inuleae) detected by segregation of genetic markers. American Journal of Botany 77: 1078-1083[CrossRef][ISI]
Briggs D. S. M. Walters 1997 Plant variation and evolution, 3rd ed. Cambridge University Press, Cambridge, UK
Chapman H. M. R. Bicknell 2000 Recovery of a sexual and an apomictic hybrid from crosses between facultative apomicts Hieracium caespitosum and H. praealtum. New Zealand Journal of Ecology 24: 81-85
Chapman H. M. J. Brown 2001 Thawing of frozen variation in an adventive, facultatively apomictic, clonal weed. Plant Species Biology 16: 107-118
Chapman H. M. S. C. Lambie 2000 Chromosome numbers in New Zealand populations of Pilosella officinarum F. W. Shultz. & Sch. Bip. International Organzation for Plant Biosystematics Newsletter 31: 12.
Chapman H. M. D. Parh H. Oraguzie 2000 Genetic structure and colonizing success of a clonal, weedy species, Pilosella officinarum (Asteraceae). Heredity 84: 401-409
Chapman H. M. B. Robson I. Ilene 2003 A case of reversal: the evolution and maintenance of sexuals from parthenogenetic clones in Hieracium pilosella. International Journal of Plant Sciences 164: 719-728.[CrossRef]
Comes H. P. R. J. Abbott 2001 Molecular phylogeography, reticulation, and lineage sorting in Mediterranean Senecio sect. Senecio (Asteraceae). Evolution 55: 1943-1962[ISI][Medline]
Connor H. E. 1991 Hawkweeds, Hieracium spp., in tussock grasslands of Canterbury, New Zealand, in the 1960s. New Zealand Journal of Botany 30: 219-282
Doyle J. J. J. L. Doyle H. D. Brown 1999 Origins, colonization, and lineage recombination in a widespread perennial soybean polyploidy complex. Proceedings of the National Academy of Sciences, USA 96: 10741-10745
Ellstrand N. C. K. A. Schierenbeck 2000 Hybridization as a stimulus for the evolution of invasiveness in plants?. Proceedings of the National Academy of Sciences, USA 97: 7043-7050
Gadella T. W. J. 1987 Sexual tetraploid and apomictic pentaploid populations of Hieracium pilosella, Compositae. Plant Systematics and Evolution 157: 219-246[CrossRef][ISI]
Gadella T. W. J. 1991 Variation, hybridization and reproductive biology of Hieracium pilosella L. Proceedings, Koninklijke Nederlandse Akadamie van Wetenschappen, Series C 94: 455-488
Hewitt G. 1996 Some genetic consequences of ice ages, and their role in divergence and speciation. Biological Journal of the Linnean Society 58: 247-276[CrossRef]
Houliston G. J. H. M. Chapman 2001 Sexual reproduction in field populations of the facultative apomict, Hieracium pilosella. New Zealand Journal of Botany 39: 141-146[ISI]
Jenkins T. A. 1991 A review of characteristics of mouse-ear hawkweed (Hieracium pilosella). New Zealand Ecological Society Occasional Publication 2: 15-23
Jenkins T. A. K. Jong 1997 Significance of polyploid variation in New Zealand Pilosella and Hieracium (Asteraceae). Botanical Journal of Scotland 49: 75-87
King L. M. 1993 Origins of genotypic variation in North American dandelions inferred from ribosomal DNA and chloroplast DNA restriction enzyme analysis. Evolution 47: 136-151[CrossRef][ISI]
Krahulcova A. F. Krahulec H. M. Chapman 2000 Variation in Hieracium subgen. Pilosella (Asteraceae): what do we know about its sources?. Folia Geobotanica and Phytotaxonomica 35: 319-338
Lee C. E. 2002 Evolutionary genetics of invasive species. Trends in Ecology and Evolution 17: 386-391[CrossRef]
Makepeace W. 1981 Polymorphism and chromosomal number in Hieracium pilosella L. in New Zealand. New Zealand Journal of Botany 19: 255-257[ISI]
Morgan-Richards M. S. A. Trewick H. M. Chapman A. Krahulcova In press Interspecific hybridization among Hieracium species in New Zealand: evidence from flow cytometry. Heredity
Neuffer B. H. Hurka 1999 Colonization history and introduction dynamics of Capsella bursa-pastoris (Brassicaceae) in North America: isozymes and quantitative traits. Molecular Ecology 8: 1667-1681[CrossRef][Medline]
Nogler G. A. 1984 Gametophytic apomixis. In B. M. Johri [ed.], Embryology of angiosperms, 475518. Springer-Verlag, Berlin, Germany
O'Hanlon P. C. R. Peakall D. T. Briese 1999 Amplified fragment length polymorphism (AFLP) reveals introgression in weedy Onopordum thistles: hybridization and invasion. Molecular Ecology 8: 1239-1246[CrossRef][Medline]
Raybould A. F. A. J. Gray M. J. Lawrence D. F. Marshall 1991 The evolution of Spartina anglica C. E. Hubbard (Gramineae): origin and genetic variability. Biological Journal of the Linnean Society 43: 111-126[CrossRef]
Richards A. J. 1996 Breeding systems in flowering plants and the control of variability. Folia Geobotanica and Phytotaxonomica 31: 283-293
Rose A. B. S. K. Wiser K. H. Platt C. M. Frampton 1995 Vegetation change over 25 years in a New Zealand short-tussock grassland: effects of sheep grazing and exotic invasion. New Zealand Journal of Ecology 19: 163-174[ISI]
Scott D. 1993a Response of Hieracium in two long term manipulative agricultural trials. New Zealand Journal of Ecology 17: 41-46[ISI]
Scott D. 1993b Time segment analysis of permanent quadrat data: changes in Hieracium cover in the Waimakariri in 35 years. New Zealand Journal of Ecology 17: 53-57[ISI]
Sell P. D. C. West 1976 Hieracium L. In T. G. Tutin, V. H. Hewood, N. A. Burges, D. M. Moore, D. H. Valentine, S. M. Walters, and D. A. Webb [eds.], Flora Europaea, vol. 4, Plantaginaceae to Compositae (and Rubiacieae), 358410. Cambridge University Press, Cambridge, UK
Shi Y. R. J. Gornall J. Draper C. A. Stace 1996 Intraspecific molecular variation in Hieracium sect. Alpina (Asterasceae), an apomictic group. Folia Geobotanica and Phytotaxonomica 31: 305-313
Stace C. 1997 New flora of the British Isles, 2nd ed. Cambridge University Press, Cambridge, UK
Stebbins G. L. 1985 Polyploidy, hybridization, and the invasion of new habitats. Annals of the Missouri Botanical Gardens 72: 824-832[CrossRef][ISI]
Svavarsdóttir K. J. G. Palmer J. J. H. White 1999 Distribution of three Hieracium species in the Mt Possession area, mid Canterbury, New Zealand. New Zealand Journal of Botany 37: 469-477[ISI]
Taberlet P. L. Fumagalli A.-G. Wust-Saucy J.-F. Cossons 1998 Comparative phylogeography and postglacial colonization routes in Europe. Molecular Ecology 7: 453-464[CrossRef][Medline]
Taberlet P. L. Gielly G. Pautou J. Bouvet 1991 Universal primers for amplification of three non-coding regions of chloroplast DNA. Plant Molecular Biology 17: 1105-1109[CrossRef][ISI][Medline]
Travers W. T. L. 1884 Acclimatisation in Canterbury. New Zealand Country Journal 8: 408-412 (and continued in vol. 8: 496500, vol. 9: 259264, vol. 10: 131136)
Treskonova M. 1991 Changes in the structure of tall tussock grasslands and infestation by species of Hieracium in the MacKenzie country, New Zealand. New Zealand Journal of Ecology 15: 65-78[ISI]
Veltman C. J. S. Nee M. J. Crawley 1996 Correlates of introduction success in exotic New Zealand birds. American Naturalist 147: 542-557[CrossRef][ISI]
Webb C. J. W. R. Sykes P. J. Garnock-Jones 1988 Flora of New Zealand, vol. IV, Naturalised pteridophytes, gymnosperms, dicotyledons. Botany Division, Department of Scientific and Industrial Research, Christchurch, New Zealand
Wittzell H. 1999 Chloroplast DNA variation and reticulate evolution in sexual and apomictic sections of dandelions. Molecular Ecology 8: 2023-2035[CrossRef][Medline]
Zhan K. H. 1923 Hieracium. In A. Engler [ed.], Das Pflanzenreich IV/280: 11471705
This article has been cited by other articles:
![]() |
P. Mraz, B. Singliarova, T. Urfus, and F. Krahulec Cytogeography of Pilosella officinarum (Compositae): Altitudinal and Longitudinal Differences in Ploidy Level Distribution in the Czech Republic and Slovakia and the General Pattern in Europe Ann. Bot., January 1, 2008; 101(1): 59 - 71. [Abstract] [Full Text] [PDF] |
||||
| ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| HOME | HELP | FEEDBACK | SUBSCRIPTIONS | ARCHIVE | SEARCH | TABLE OF CONTENTS |