Despite their complex evolutionary histories, aquatic plants are highly underrepresented in contemporary biosystematic studies. Of them, the genus Callitriche is particularly interesting because of such evolutionary features as wide variation in chromosome numbers and pollination systems. However, taxonomic difficulties have prevented broader investigation of this genus. In this study we applied flow cytometry to Callitriche for the first time in order to gain an insight into evolutionary processes and genome size differentiation in the genus. Flow cytometry complemented by confirmation of chromosome counts was applied to an extensive dataset of 1077 Callitriche individuals from 495 localities in 11 European countries and the USA. Genome size was determined for 12 taxa. The results suggest that many important processes have interacted in the evolution of the genus, including polyploidization and hybridization. Incongruence between genome size and ploidy level, intraspecific variation in genome size, formation of autotriploid and hybridization between species with different pollination systems were also detected. Hybridization takes place particularly in the diploid – tetraploid complex C. cophocarpa – C. platycarpa, for which the triploid hybrids were frequently recorded in the area of co-occurrence of its parents. A hitherto unknown hybrid (probably C. hamulata × C. cophocarpa) with a unique chromosome number was discovered in the Czech Republic. However, hybridization occurs very rarely among most of the studied species. The main ecological preferences were also compared among the taxa collected. Although Callitriche taxa often grow in mixed populations, the ecological preferences of individual species are distinctly different in some cases. Anyway, flow cytometry is a very efficient method for taxonomic delimitation, determination and investigation of Callitriche species, and is even able to distinguish homoploid taxa and identify introduced species.
Citation: Prančl J, Kaplan Z, Trávníček P, Jarolímová V (2014) Genome Size as a Key to Evolutionary Complex Aquatic Plants: Polyploidy and Hybridization in Callitriche (Plantaginaceae). PLoS ONE9(9): e105997. https://doi.org/10.1371/journal.pone.0105997
Editor: Maharaj K. Pandit, University of Delhi, India
Received: May 15, 2014; Accepted: July 26, 2014; Published: September 11, 2014
Copyright: © 2014 Prančl et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: The authors confirm that all data underlying the findings are fully available without restriction. All relevant data are within the paper and its Supporting Information files.
Funding: The research was supported by the Czech Science Foundation (project no. 14-36079G, Centre of Excellence PLADIAS), with additional support provided by the Academy of Sciences of the Czech Republic (long-term research development project no. RVO 67985939), institutional resources of Ministry of Education, Youth and Sports of the Czech Republic for the support of science and research, and by the Postdoc USB project (no. CZ.1.07/2.3.00/30.0006 to PT) realized through the EU Education for Competitiveness Operational Programme (funded by the European Social Fund and the Czech State Budget). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Aquatic plants are characterized by several specific adaptations to the water environment, including considerable morphological reduction, prolific clonal propagation and extensive phenotypic plasticity (e.g. –). These characteristics can make classification of these plants particularly difficult, with this difficulty increased by the frequent parallel evolution of traits in unrelated taxa –. Indeed, aquatic plants are regarded as being among the most taxonomically challenging angiosperms.
Aquatic plants play a key ecological role in aquatic ecosystems and often exhibit complex evolutionary histories. Polyploidy and hybridization have been crucial to the evolution of many aquatic plant groups , namely in Ranunculus subg. Batrachium , –, Potamogeton , , –, Lemnaceae –, Nymphaea –, Elodea , Myriophyllum  and many others. Intrageneric chromosome number variation has been reported from 80% and hybridization from 20% of all aquatic plant genera . Newly established polyploids and hybrids can be fixed by frequent clonal growth, with sterile primary hybrid genotypes persisting hundreds or even thousands of years without the presence of the parental species , –. However the new taxa that arise through these processes are often morphologically undetectable. Indeed, in general, a substantial part of the variation in aquatic plants is undoubtedly cryptic and detectable only using molecular techniques.
Despite the interesting evolutionary scenarios posed by aquatic plants, they are markedly underrepresented in contemporary biosystematic studies  – likely due in large part to the daunting challenges associated with these scenarios, as well as the difficulty in detecting taxonomic differences. Thus, our overall knowledge of the principal processes that have driven evolution of aquatic taxa is limited, especially in comparison with the information developed regarding terrestrial plants. This has limited our potential to understand the wider context of evolution and systematics of these plants.
In the current study, we examine the aquatic genus Callitriche (water-starwort) which comprises about 60 species throughout the world. In Europe, about 15 native and 4 rare, introduced species have been reported –. Callitriche is notoriously considered one of the most difficult aquatic plants to identify. Taxonomy of Callitriche is based mostly on the generative features, particularly fruits. Unfortunately, these characters are very small, difficult to observe and often not available due to the frequent occurrence (or even prevalence) of solely vegetative plants. Virtually all vegetative characters of water-starworts are extremely variable and mostly unusable without extensive experience. Therefore, although many detailed morphological studies on water-starworts have been published (e.g. , –), their reliable determination is still restricted to just a few specialists, with several taxa recognizable only in the case of well-developed, adult individuals.
Water-starworts, among the most common aquatic plants throughout Europe, inhabit almost all types of standing and running waters, even including small puddles on forest paths. Despite this, they are generally overlooked by field biologists, even though individual Callitriche species can differ substantially in their ecology and may serve as diagnostic taxa of various phytosociological units , . Water-starworts may also represent suitable model organisms for the study of phenotypic plasticity –, physiological processes associated with growth –, metabolism in aquatic environments –, plant patch formation in streams , , phytoremediation of polluted watercourses , and some taxa may even serve as a potential antioxidant-rich diet supplement , . Pollination biology of water-starworts is strikingly diversified and among the most remarkable of all the angiosperms , –. However, Callitriche is still only rarely a subject of scientific research due to taxonomic and methodological difficulties (e.g., observation, scoring, cultivation, and experimentation). Finding a method that allows easy and reliable determination of water-starworts in various developmental stages would therefore promote exploration of many aspects of aquatic and wetland ecosystems.
Evolution of the genus has featured recurrent polyploidization and aneuploid reduction of chromosome numbers in various lineages . Therefore, chromosome counting has often been used for the genus, especially in Europe. To date, chromosome numbers for 35 taxa are available (summarized in Table S1) and 11 different chromosome counts are known, ranging from 2n = 6 to 2n = 40. The most common diploid chromosome number is 2n = 10, but the diploids 2n = 6 and 2n = 8 have also been found in some species.
In Europe, all three diploid chromosome numbers are known, and at least four polyploid species occur (C. palustris 2n = 20, C. platycarpa 2n = 20, C. brutia 2n = 28, C. hamulata 2n = 38). Callitriche platycarpa is considered to be an allotetraploid that has arisen through the hybridization of the diploid species C. cophocarpa and C. stagnalis , , confirmed by allozyme analysis of plants from north-western Poland . The origin of other European polyploids is unknown.
Recent hybridization has also been detected in the genus: the triploid (2n = 15) Callitriche ×vigens (C. cophocarpa × C. platycarpa), the sole primary hybrid currently known and validly described, has repeatedly been found in areas of co-occurrence of the parental species (e.g. , , , ). However, to-date this hybrid has never been confirmed by molecular studies. More generally, the lack of molecular investigation of this genus leaves open the possibility of undiscovered hybrids within it. In particular, the amount of hybridization between taxa with the same ploidy levels would have escaped detection by chromosome counting.
To date, however, chromosome counting has remained the exclusive cytogenetic method used. However, the potential utility of chromosome counting per se for taxa determination is limited, because only two European (C. brutia, C. hamulata) and a single African (C. vulcanicola) species possess unique chromosome numbers. The phylogenetic relationships between most of the taxa remain unclear because molecular techniques have been only sporadically applied to Callitriche. These include phylogenetic analysis of European and North American species (, unfortunately using rbcL as a marker, which is not sufficiently variable) as well as allozyme and RAPD analyses on a small geographic scale , –. The combination of rbcL and ITS applied to northern Italian Callitriche  was unfortunately not supported by adequate determination of plants, and the data interpretation in this study is largely questionable.
The variation in chromosome numbers in Callitriche encourages use of the genome size as a species-specific marker. Flow cytometry (FCM), which has undergone a boom in plant sciences over the last decade, represents an excellent tool for this purpose. FCM is a rapid, easy, statistically robust and relatively cheap method , , frequently and successfully applied to evolutionarily and taxonomically intricate plant groups such as polyploid complexes –. Due to the high accuracy of the measurements, FCM is often able to distinguish even closely related homoploid taxa (reviewed in ), and it is also frequently used for detection of hybrids –. An indisputable benefit of FCM is its facility to analyze a large number of individuals (e.g., at a population level) rapidly, even allowing detection of rarely occurring cytotypes, hybrids and aneuploids (–, etc.). Finally, flow cytometry permits analyses using a very small amount of plant material. This is extremely useful in the aquatic environment, where researchers often find only small vegetative fragments.
Unfortunately, flow cytometry has so far been only sporadically applied to research on aquatic plants (Nymphaeales , ; Nymphaea , ; Cabomba , ; Rorippa ; Nasturtium ; Lemnaceae ; Zannichellia ). To date, no studies using FCM are available for Callitriche. In fact, the genome size has been estimated only once for Western European water-starwort species, using photometric cytometry with the Feulgen staining method . However, this method cannot process large numbers of samples and is unable to reliably distinguish small differences in genome size among taxa with the same ploidy level.
In this study, we applied flow cytometry combined with chromosome counting to improve our understanding and identification of Central European water-starworts. The following aims were addressed: (1) testing flow cytometry as a method for reliable determination of the Central European Callitriche species; (2) determining the chromosome numbers based on cytometrically analysed samples; (3) comparing the new counts with previously published records; and (4) estimating the hybridization rate in the studied area.
Materials and Methods
Plant samples were collected in Belgium, Czech Republic (majority of samples), Denmark, Germany, Hungary, Italy, Netherlands, Norway, Poland, Slovakia and Sweden in 2007–2014. Our sampling included all seven Central European species, several specimens of hybrid origin (see below) and also the Mediterranean species C. lenisulca, which is apparently closely related to the Central European C. cophocarpa . In addition, we included seven samples of European species that were collected in the western USA (C. stagnalis and C. hamulata, both introduced, and C. palustris, native to both Europe and North America). In total, 1076 plants from 494 localities were obtained (for locality details, see Table S2). Voucher specimens are preserved in the herbarium of the Charles University in Prague (acronym PRC).
We put an emphasis on visiting the widest possible range of aquatic habitats, including small and commonly neglected biotopes (e.g., puddles on forest paths, eutrophic ditches). At each locality, sampling covered observed morphological variation. The sampling was carried out even in stands comprising only sterile plants. The fresh plant material was placed in plastic bags and transported rapidly to the FCM laboratory. In the cases of longer transport, plants were wrapped in moist paper towels (not too wet, in order to avoid rotting) and then sealed in plastic bags. Aquatic plants preserved in this way stay fresh for 2–3 weeks, enabling analysis of samples even from distant regions.
All 1077 plants were analysed using FCM. If multiple samples were collected from a population, these samples were first analysed simultaneously (approximately 5 samples in a single run) using 4′,6-diamidino-2-phenylindole (DAPI) fluorochrome to reveal the possible presence of multiple cytotypes. About 0.25 cm2 of leaf tissue was chopped together with an appropriate volume of the internal standard using a sharp razor blade in a Petri dish containing 0.5 ml of ice-cold Otto I buffer (0.1 M citric acid, 0.5% Tween 20, ). Bellis perennis L. was selected as a primary reference standard, as it has a similar, but non-overlapping genome size with the majority of the studied samples (2C = 3.96 pg, ; 2C-value was calibrated according to the following internal standard). Glycine max (L.) Merr. ‘Polanka’ (2C = 2.50 pg, ) served as a reference standard for Callitriche palustris and C. obtusangula, because the genome size of these taxa overlapped with Bellis. The crude suspension was filtered through a 42-μm nylon mesh and incubated for ca 5 min. at room temperature. After incubation, isolated nuclei were stained with 1 mL of Otto II buffer (0.4 M Na2HPO4.12H2O) supplemented with DAPI (4 µg/ml) and β-mercaptoethanol (2 µl/ml). Samples were run on the flow cytometer after about one minute of staining, using a Partec PA II flow cytometer (Partec GmbH, Münster, Germany) equipped with a mercury arc lamp as the UV light excitation source. The fluorescence intensity of 3000 particles was recorded. Histograms were evaluated using FloMax software, ver. 2.4d (Partec GmbH).
Subsequently, all detected cytotypes from all populations were analyzed separately using propidium iodide FCM in order to estimate the variation in genome size. To determine the genome sizes for particular taxa in absolute units (pg of DNA), 178 samples representing all cytotypes were measured at least three times on different days to account for occasional fluctuations. Because genome size generally differed substantially between taxa (see below), a further 416 samples were each measured only once as a single measurement was sufficient for reliable assignment. The staining solution consisted of 1 mL of Otto II buffer supplemented with propidium iodide (50 µg/ml), RNase A, type IIA (50 µg/ml) and β-mercaptoethanol (2 µl/ml). The fluorescence intensity of 5000 particles was recorded using a Partec CyFlow instrument equipped with a green diode-pumped solid-state laser (Cobolt Samba, 532 nm, 150 mW output power). If the range in variation of the three measurements exceeded the 2% threshold, the outlying value was discarded and the sample re-analysed.
Because DAPI FCM was not able to distinguish C. cophocarpa and C. stagnalis in simultaneous analyses, the samples were measured individually using propidium iodide staining when either of these species was suspected.
Sufficiently developed plants exhibiting essential morphological characters were identified based on recent morphological studies , , . These determinations were then compared with genome sizes obtained from FCM analysis, with discordance suggesting hybrid plants. Identification of juvenile and sterile samples was facilitated using FCM. Species for which overlapping or very similar 2C-values were found even when using propidium iodide staining (see below), were identified by the most relevant morphological characters: C. palustris and C. obtusangula were distinguished on the basis of conspicuously different fruits, and C. obtusangula by its remarkable elongate-ellipsoid and curved pollen grains. Sterile plants with 2C-values within the ranges of variation of these two species were cultivated until they produced characters necessary for unambiguous identification. Callitriche lenisulca was distinguished from Italian samples of C. obtusangula through its unique flower pattern (nodes with only male or female flowers alternating approximately regularly along the stem), small stamens and anthers, and spherical pollen grains , .
The chromosome number was counted in at least one sample of each detected cytotype. Selected plants were cultivated in a tank (depth about 20 cm) until they began to form adventive roots on the stem. These adventive roots were used for chromosome counting.
The root tips were pre-treated in a saturated water solution of p-dichlorbenzene for approximately two hours, then fixed in a 3∶1 mixture of 96% ethanol and acetic acid, macerated in a 1∶1 mixture of ethanol and hydrochloric acid for 30 s, washed in water and stained with lacto-propionic orcein. The number of chromosomes was determined under a Carl Zeiss Jena NU microscope equipped with an Olympus Camedia C-2000 Z camera and Olympus E – 510 Digital SRL Camera.
Altogether, chromosome numbers of seven taxa were determined. The remaining three taxa (C. hermaphroditica, C. lenisulca, autotriploid C. stagnalis) failed to grow in cultivation.
Differences in genome sizes between particular taxa were tested by Bonferroni (Dunn) t Test (α = 5%) using the SAS 9.2 statistical package (SAS Institute, Cary, NC, USA) and depicted as boxplots in STATISTICA. Distribution map was created using DMAP for Windows .
To compare the ecological preferences and co-occurrence of individual taxa, all localities were divided on the basis of habitat into the following seven categories (see Table S2): ditch (artificial depression/channel with muddy bottom and standing or almost standing eutrophic water), exposed bottom (of drained water body or from coastal zone), fishpond (artificial water body established for fish farming), lake (large natural water body), pool (small water body with standing water, natural or arising spontaneously after human disturbances), puddle (very small and shallow temporary accumulation of water, usually on paths, with substrate remaining wet after surface water disappearance), reservoir (moderate to large artificial water body, not for fish farming), river (flowing watercourse with high flow rates; subdivided into two subcategories: mud – muddy bottom, sand – sandy bottom) and stream (small to moderate flowing watercourse; subdivided the same as the previous category).
The categories “fishpond”, “lake” and “reservoir” were subsequently merged into the common category “reservoir”, due to the small number of lakes and reservoirs among the studied localities and the poor ecological differentiation between them.
Genome size variation
In total, 12 taxa of Callitriche were recorded, the overwhelming majority of these differing clearly and with statistical significance in nuclear DNA content (Table 1, Figs 1, 2, 3). Among the eight generally recognized species, six can be unambiguously defined by means of genome size (C. hermaphroditica, C. stagnalis, C. cophocarpa, C. lenisulca, C. platycarpa, C. hamulata). The diploid species C. stagnalis and C. cophocarpa have similar genome sizes (difference between means 7.0%), and simultaneous analyses of these species did not result in double-peaks. However, 2C-values of both these species are non-overlapping and differed significantly in a Bonferroni (Dunn) t Test.
Taxa with different chromosome numbers are separated by vertical lines. For C. obtusangula, values for samples from Italian (IT) and north-western Europe were plotted separately, due to significantly different genome sizes.
The species C. hamulata (2n = 38) and the hybrid from the Tichá Orlice River (2n = 29) were not included due to aneuploid chromosome counts.
Nuclei of all samples were isolated, stained with propidium iodide and analysed simultaneously.
The other taxa analysed from Central and Atlantic Europe, C. palustris and C. obtusangula, surprisingly exhibit very similar, overlapping genome sizes, although they differ in DNA-ploidy level (see below).
The situation regarding diploid taxa sampled in Italy is more complicated. The Mediterranean species C. lenisulca differs significantly in genome size from both C. cophocarpa (difference between means 12.2%) and C. obtusangula from north-western Europe (difference 7.8%). However, Italian plants, assigned to C. obtusangula on the basis of pollen shape and gross morphology, possess a genome size distinct from north-western European plants of this species, with their 2C-value exactly intermediate between C. lenisulca and NW C. obtusangula (difference from C. lenisulca 3.9%, from NW C. obtusangula 3.8%; differences are small but statistically significant). On FCM histograms, C. lenisulca exhibited a peak clearly distinct from the peak of the internal standard Bellis perennis (Fig. 4), whereas both types of C. obtusangula always overlapped with Bellis and had to be measured with the Glycine standard.
In the Czech Republic, Germany and Denmark, non-fertile plants with aborted, deformed, yellow pollen grains were repeatedly found (26 samples). The genome size of these plants lies between some diploid species (C. stagnalis, C. cophocarpa) and tetraploid C. platycarpa, which suggests a triploid DNA-ploidy level. These plants were assigned to the F1 hybrid C. cophocarpa × C. platycarpa (C. ×vigens, see Discussion). The exception was the sole plant (specimen C125-13) from northern Bohemia (Czech Republic), which strongly resembled C. stagnalis and was partially fertile (but with most mericarps deformed or poorly developed). This plant possessed a slightly (and not significantly) smaller genome size than other triploids, which would better fit an autotriploid of C. stagnalis. This inference was confirmed by means of allozyme analysis (J. Prančl et al., unpublished data).
Other plants most likely representing a product of interspecific hybridization (samples C061-12, C065-12, C066-12) were discovered at three sites in the Tichá Orlice River (eastern Bohemia). This hybrid had submerged aborted flowers and colourless, irregular pollen grains with shrunken protoplasts. Callitriche hamulata is considered to be one of the parental species, based on its large genome size. The tetraploid C. platycarpa (reduced gamete) and the diploids C. stagnalis and C. cophocarpa (unreduced gametes) are possible as the second parent.
Regarding the European species occurring in North America, C. palustris from USA (specimen C048-13) showed the same genome size as all the conspecific samples from Europe. Also C. stagnalis, which is naturalized in North America , does not differ in genome size from European conspecifics (C053-13, C054-13). Finally, the occurrence of C. hamulata on the Pacific coast of the USA  was confirmed by the samples from there having genome size identical to that of the European samples of this species (C049-13, C050-13, C051-13, C052-13).
The chromosome number was determined for 12 individuals of 8 taxa (see Table 2, Fig. 5). Chromosome numbers quoted in published sources were confirmed in all studied species. Callitriche obtusangula (2n = 10) and C. palustris (2n = 20) differ in DNA ploidy level, although they cannot be distinguished by genome size. Triploid chromosome number (2n = 15) was confirmed in plants assigned to the hybrid C. ×vigens. Non-fertile plants discovered in the Tichá Orlice River possess an extraordinary chromosome number 2n = 29.
a – C. stagnalis, specimen C013-12, 2n = 10; b – C. cophocarpa, C002-12, 2n = 10; c – C. obtusangula, C052-12, 2n = 10; d – C. ×vigens, C059-08, 2n = 15; e – C. ×vigens, C021-12, 2n = 15; f – C. palustris, C019-12, 2n = 20; g – probable hybrid C. hamulata × C. cophocarpa, C066-12, 2n = 29; h – C. hamulata, C050-13, 2n = 38. Scale bar identical for all figures = 10 µm.
Karyotypes of species with 2n = 10 are different. Callitriche cophocarpa has two pairs of slightly bigger acrocentric chromosomes (Fig. 5b). Callitriche stagnalis possesses one pair of large metacentric chromosomes; the dimensions of particular chromosomes are the most variable among all the studied diploids (Fig. 5a). Callitriche obtusangula has one pair of large acrocentric chromosomes (Fig. 5c).
Four species (Callitriche cophocarpa, C. hamulata, C. palustris and C. stagnalis) were recorded as common in Central Europe. Detailed screening performed in the Czech Republic revealed the limits of the distribution of the Subatlantic species C. platycarpa in the north-western part of Bohemia (see Fig. 6). Where the range of C. platycarpa overlaps that of the related but rather continental species C. cophocarpa, many populations were shown to be triploids and assigned to C. ×vigens. However, this hybrid was also abundant in the Otava River in southern Bohemia, where C. platycarpa has never been found (cf. ).
Two populations with co-occurrence of two taxa are shown as two-colour bisected symbols.
The occurrence of C. platycarpa in southern Italy (specimen C010-13) is also noteworthy, because this species was until recently known only from the northernmost Italian regions (cf. ). The Mediterranean-Atlantic species C. obtusangula was for the first time found in Denmark during this study (cf. ; specimens C034-12, C048-12) and the Subatlantic species C. hamulata was for the first time reliably recorded from Hungary (specimen C14-001).
The habitat preferences of Callitriche taxa from 495 investigated localities are summarized in Table 3. For C. cophocarpa, C. hamulata, C. palustris and C. stagnalis, the numbers of localities were sufficiently high (>75) to assess environmental preferences. The strongest relationship with a specific habitat type was recorded for C. stagnalis. In total, 78.8% of C. stagnalis localities were in puddles. Callitriche palustris was found almost exclusively in standing water or on moist, exposed bottoms, with only one locality (1.3%) in running water. In contrast, C. hamulata showed the strongest relation to running waters (53.8% of localities). In rivers and streams, bottom substrate can play an important role: streams with C. hamulata, predominantly had sandy bottoms (87.0%), whereas those with C. cophocarpa had mostly muddy bottoms (75.0%).
Callitriche taxa often occurred in mixed populations. Thus, 88 localities (17.8% of all localities, 31.5% of all samples) supported more than one taxon. Ten localities (2.0%) supported three taxa, and one locality (0.2%) supported four taxa. Generally, the proportion of mixed localities was highest in C. palustris (44.7% of all localities, compared to 34.7% for C. platycarpa, 33.9% for C. hamulata, 31.7% for C. stagnalis and 22.0% for C. cophocarpa). The most frequent co-occurrences were the pairs C. platycarpa and C. hamulata (14 populations, i.e. 28.6% of C. platycarpa localities) and C. palustris and C. stagnalis (17 populations, i.e. 22.7% of C. palustris localities).
This study represents the first application of flow cytometry to the genus Callitriche and the most comprehensive application of FCM to aquatic angiosperms (in terms of the number of plants collected as well as the number of populations). It has provided insights into methodological, evolutionary, taxonomic, and ecological issues, discussed below.
Genome size as a tool for identification of Callitriche species
Flow cytometry has proven to be a reliable, fast, inexpensive and easy tool to distinguish Central-European Callitriche taxa (Table 1, Figs 1, 2, 3). Even homoploid species are recognizable on the basis of genome size. Callitriche obtusangula and C. palustris are the only two species indistinguishable by this approach. Fortunately, both species differ markedly in fruit shape, size and colour, pollen grain shape, and floating leaf shape , and mostly also in the general appearance of the plants. In fact, these two taxa are probably the most distinctive species of Callitriche in Europe. Thus, confusion between them is unlikely. Due to the unique mode of self-pollination (internal geitonogamy; ), individuals of C. palustris are almost always abundantly fertile , greatly facilitating determination.
Despite the very similar genome sizes, both species differ in ploidy level (diploid C. obtusangula vs. tetraploid C. palustris). This striking fact is made possible by the large genetic distance between these species: the widespread C. palustris seems to be more closely related to American than European taxa , whereas C. obtusangula is an exclusively European and North African species . The species also have substantially different life strategies. Callitriche palustris is mostly an annual species with a rapid life cycle , ; therefore, evolutionary constraints leading to small genome size may play an important role in this species (cf. , ). On the other hand, C. obtusangula is typically perennial, often forming luxuriant vegetative stands. Several other examples of ecologically different congeners are currently known for which genome sizes ratios are incongruent with ploidy levels (e.g. Chenopodium ; Anthoxanthum – Chumová & Trávníček, unpublished data).
The main obstacle to research on water-starworts (and aquatic plants in general) lies in the enormous phenotypic plasticity of these plants and lack of prominent morphological characters. The absence of tools enabling unambiguous determination of particular taxa has resulted in frequent misidentifications and unreliable records. In many such morphologically challenging plant groups, flow cytometry has proven to be the first efficient tool for species and hybrid determination and served as the fundamental method for ensuing studies (e.g. Chenopodium album agg. ; Dryopteris carthusiana agg. ; Fallopia sect. Reynoutria ; Pilosella ). Likewise, easy identification of Callitriche species using FCM opens up great opportunities for further interdisciplinary research on this evolutionarily remarkable genus. We highly recommend FCM for taxa delimitation in forthcoming molecular studies on the genus. Genome size can also serve as an independent, species-specific character to define groups in taxonomic research.
Our results will be widely geographically applicable, as well, because many Callitriche species occur throughout Europe. Flow cytometry can be applied with equal success to species from Northern and Eastern Europe, where most of the Callitriche species represented were included in our study (with the exception of some unclear taxa close to C. hermaphroditica, e.g. C. transvolgensis in Russia; ). Only two species not covered by this study have been reported from north-western Europe: Callitriche truncata subsp. occidentalis from sect. Pseudocallitriche can perhaps be confused only with C. hermaphroditica in this region (both species have 2n = 6). Callitriche brutia, which is closely related and often indistinguishable from C. hamulata (, ; see comment in Table 1 footnote), has a unique chromosome number (2n = 28, in contrast with 2n = 38 in C. hamulata). Because exact genetic delimitation is necessary for further taxonomic assessment of these two problematic taxa, flow cytometry will be able to serve as a basic method for their delimitation.
The situation in the Mediterranean area is more complicated. Additional diploid species (2n = 6–10) are reported from that region, including C. lusitanica, C. pulchra, C. truncata subsp. truncata from sect. Pseudocallitriche and C. cribrosa, C. lenisulca, C. regis-jubae from sect. Callitriche. Our FCM results for C. lenisulca provide the foundation for further research on these species. Callitriche lenisulca, which is very similar and maybe closely related to C. cophocarpa or C. obtusangula , differs significantly in genome size from both these species. Both C. lusitanica and C. cribrosa have a different chromosome number (2n = 8) and it is likely that they will be distinct using FCM.
Two similar but significantly different 2C-values were identified in C. obtusangula. Italian plants have a smaller genome size than samples from north-western Europe. This differentiation may be associated with the several different karyotypes of this species described by Schotsman , . Two karyotypes were reported from France , one of which occurs in Atlantic region and the other in Mediterranean region and the Rhine Valley. These two karyotypes were described as somewhat different ecologically, although morphologically indistinguishable. Molecular approaches will be necessary to elucidate their evolutionary origins.
The genome size of the Italian C. obtusangula was intermediate between that of Subatlantic specimens of this species and C. lenisulca. However, pollen of the Italian C. obtusangula was normally developed, which makes it less probable that these plants are F1 hybrids. Additionally, hybridization between these taxa is less likely due to the presence of an effective self-pollination system in C. lenisulca ().
Evolution of polyploid Callitriche platycarpa
The origin of polyploid species is currently a widely studied phenomenon. In taxonomically difficult groups that include polyploids, repeated origins of polyploid taxa appears to be the rule rather than the exception –. Especially in aquatic plants, many of which have undergone considerable morphological reduction, the possibility that allopolyploids recognized as single species may actually be polyphyletic cannot be excluded (see, for example, Ranunculus penicillatus; , ). In water-starworts, the tetraploid C. platycarpa is believed to be an allotetraploid with the parental species C. cophocarpa and C. stagnalis (see above). The observed range of genome size for C. platycarpa is equal to the sum of these two diploid congeners (see Table 1, Figs 2 and 3), which may support this hypothesis. Anyway, a molecular approach will be necessary to elucidate the evolution of C. platycarpa, as autopolyploid origin of some populations cannot be excluded and multiple allopolyploid formation through reciprocal hybridization events is also possible.
Species-rich genera of aquatic plants may produce extremely high numbers of hybrids (e.g. 99 sufficiently recognized hybrids in Potamogeton; ). Many aquatic hybrid clones can occupy large areas, produce dominant stands , , , , or even exhibit invasive behaviour  or extensive introgression , . However, the results of this study suggest that hybridization between most Central-European Callitriche species is not common, despite the frequent co-occurrence of most taxa (see above). The different pollination biology of particular taxa, high proportions of selfing (geitonogamy) and in some cases also ecological differences between species are presumably the main reasons why water-starworts rarely hybridize. For example, C. hermaphroditica and C. hamulata are hypohydrogamous (pollinated through wettable exine-reduced pollen under the water surface), whereas the rest of the studied species have pollen with an exine, which is not adapted to spread freely underwater , . Some species have highly geitonogamous pollination, realized via contact between male and female flowers (“contacters”: C. hamulata , C. lenisulca ) or growth of pollen tubes through filaments and non-floral vegetative tissues (“internal geitonogamy”: C. palustris ). Therefore, in some cases, even though the stands of different species intermingle at a locality, transfer of pollen to the stigmas of the second species may be physically hardly possible.
The exception to the rule is the triploid hybrid taxon, which we assigned to the F1 hybrid C. cophocarpa × C. platycarpa (C. ×vigens). We consider this parental combination the most probable, because triploids were morphologically intermediate between C. cophocarpa and C. platycarpa (or indistinguishable from one or the other) and were detected almost exclusively in areas of co-occurrence of both species. The genome size of the triploids also best fits the hybrid combination of these two species. The hybrid was found at 25 localities; in some regions (northern and western Bohemia) it seems to be relatively abundant (see Fig. 6).
The hybrid is perennial, forming lush and highly viable vegetative stands, and was found occurring without the presence of parents in the overwhelming majority of localities. Triploid plants were also detected in the Otava River in southern Bohemia, where C. platycarpa is not known from the river basin. A similar case is known from Scandinavia  where Callitriche ×vigens is frequent in southernmost Sweden, although one of the parental species (C. cophocarpa) is fairly rare there. Occurrence of hybrids in different areas very long after the disappearances of their parents is well documented in Potamogeton and Stuckenia , , , –, and it is probable in Ranunculus subsp. Batrachium , .
We cannot yet, however, entirely rule out that some populations of triploids may be of different origin (including hybridization between C. platycarpa and C. stagnalis, hybridization of diploids C. stagnalis and C. cophocarpa involving unreduced gametes, or formation of autotriploids of both species). In any case, the combination C. cophocarpa × C. platycarpa is the most probable, because (i) unreduced gametes are much rarer than reduced gametes; (ii) the putative parental taxa also share pollination systems and ecological preferences, with both often occurring in permanent water bodies, where the newly established non-fertile hybrids can persist. In contrast, C. stagnalis prefers to grow in very shallow water or terrestrially, often remains non-flowering in deeper water, and probably possesses a higher rate of geitonogamous pollination . The single plant identified as autotriploid C. stagnalis is the very rare exception. This plant was found in a puddle on a forest path, unlike all the other triploids.
The most notable case of hybridization was detected in the Tichá Orlice River. All populations of the hybrid taxon were located in mixed populations with C. hamulata, from which they were morphologically indistinguishable without careful inspection of flowers. On the basis of the observed chromosome number (2n = 29), these plants probably represent a cross between C. hamulata (2n = 38) and a diploid (2n = 10) or tetraploid (2n = 20) species. The observed genome size (7.60–7.64 pg DNA) can be explained as the hybrid C. hamulata × C. platycarpa (expected 2C-value 7.40–7.70 pg), C. hamulata × unreduced gamete of C. cophocarpa (7.48–7.81 pg) or perhaps C. hamulata × unreduced gamete of C. stagnalis (7.32–7.59 pg). Thus, we hypothesize that this is a rather surprising hybrid between hypohydrogamous, underwater-flowering C. hamulata, and a non-hypohydrogamous species with (predominantly) aerial flowers. To date, an analogous case of hybridization has never been observed in angiosperms. The only other Callitriche species that has been observed in the Tichá Orlice River is C. cophocarpa. In one locality (C061-12), both C. hamulata and C. cophocarpa co-occurred with the hybrid. Therefore, the parental combination C. hamulata (reduced gamete) × C. cophocarpa (unreduced gamete) is most likely, but confirmation of this tentative identification by means of molecular markers would be necessary.
Flow cytometry does not enable us to confidently distinguish potential hybrids between homoploid species with similar genome sizes. In the present study, this limitation mainly involves the species C. stagnalis and C. cophocarpa, which are broadly sympatric in Central Europe. However, there is a clear (although narrow) gap between the genome sizes of the species, without any intermediate values. Many plants with extreme 2C-values and individuals appearing morphologically intermediate were cultivated but no reduced fertility or other indications of hybrid origin were ever observed. Based on these facts, we can exclude hybridization between these species occurring widely in nature. However, this crossing must have occurred at some point, due to the existence of the allopolyploid C. platycarpa, which has the same parental species.
Reliability of published chromosome records and genome sizes
Callitriche species have relatively large chromosomes which can be counted relatively easily. Errors arising directly during the counting process are apparently rare in this genus. Mistakes caused by misidentification are much more likely. Fortunately, the monographer and Callitriche expert H. D. Schotsman published reliable chromosome counts for most European species in the 1950s and 1960s. These data served as a reference for other researchers. However, confusion can often occur between species with the same chromosome number (in Europe, especially between the species with 2n = 10). Without examining original specimens, it is usually impossible to know whether the published data were based on accurate identification. Chromosome counting combined with genome size determination will allow elimination of most confusion in the future.
The genome sizes obtained by Pijnacker & Schotsman using photometric cytometry with the Feulgen staining method  possess somewhat different absolute values and lower accuracy, but the ratio between 2C-values of particular taxa are ± similar to that in our study. The most striking difference is in 2C–values of C. palustris and C. obtusangula, which appeared to be clearly distinct in the study by Pijnacker & Schotsman but overlapping in our study.
Geographical distribution of Callitriche taxa
Flow cytometry can fundamentally refine our understanding of the distribution of particular taxa (cf. , ). For example, the taxonomically difficult species C. platycarpa has been previously reported from various areas of the Czech Republic but not from the most northern and western parts of the country . In contrast, our study involving flow cytometry detected C. platycarpa only in these areas. Therefore, we conclude that the local limit of the distribution of this species passes through this region. In light of our findings, the occurrence of C. platycarpa in more eastern parts of Central Europe (e.g., in Slovakia; ) seems to be very unlikely.
We also detected C. hamulata for Hungary, C. ×vigens to the Czech Republic and recorded C. obtusangula in Denmark, which is its northernmost known occurrence in continental Europe.
Callitriche hermaphroditica has been recently referred to as very rare and close to extinction in Central Europe, and probably isolated from its continuous distribution range in Northern Europe . We found this species only in a single pond system in eastern Bohemia (C088-12, C089-12, C090-12). Callitriche hermaphroditica is very variable in fruit characters , and its intraspecific division needs clarification throughout its extensive distribution range. Based on the fruit size , Czech populations clearly belong to subsp. hermaphroditica. The additional sample (C127-13) obtained from Sweden was unfortunately sterile and failed to grow in cultivation.
FCM also enables easier identification of introduced taxa. On the west coast of North America, widespread occurrence of plants considered to be C. hamulata has recently been reported  and this was confirmed using flow cytometry.
Ecological properties and their consequences
Many Callitriche species show relatively broad ecological amplitude and often grow in mixed populations. Despite this, we found that the frequency of occurrence in different biotopes can vary substantially between species. Knowledge of the ecology of water-starworts may facilitate their identification in the field because some species have never been recorded in certain types of habitat in spite of an extensive field survey.
During this study, considerable differences were recorded in the frequency of flowering and fruiting among different species. Whereas mature plants of C. palustris almost inevitably produced flowers and fruits in each biotope from which it was recorded, C. cophocarpa and C. platycarpa remained sterile at most localities (other species were also often sterile, but with lower frequency). Although both C. cophocarpa and C. platycarpa often grow and form large stands in flowing water, they almost never develop fruits under these circumstances. Both taxa also rarely flower in shaded habitats. For these reasons, species that seldom fruit are highly under-recorded in field surveys. Flow cytometry allows estimation of the true abundances of Callitriche species in particular biotopes and also enables identification of mixed populations even in habitats where some species have never been observed to produce fruits or fruit very rarely.
This study represents the first application of flow cytometry to the genus Callitriche. FCM was shown to be the best analytical method for distinguishing Callitriche species. This technique also helped increase our knowledge of variation, hybridization, distribution and ecology of particular taxa.
This genus has been considered extremely difficult taxonomically and therefore has been an unpopular subject for research. Nevertheless, the water-starworts are quite intriguing in terms of the evolution of pollination mechanisms and the frequent incidence of polyploidy in different evolutionary lineages . We validated FCM as a powerful tool not only for determining Callitriche taxa, but also as a basic method for future multidisciplinary research on the genus. Moreover, applying this method also to other, similarly complex aquatic plant groups should be very promising.
Complete list of chromosome numbers published for the genus Callitriche.
Locality details and genome sizes of 494 Callitriche populations from 11 countries, including reference number, number of analysed samples, genome size (three times-measured values are in bold, containing mean and standard deviation), geographic coordinates, altitude, type of habitat (with categories described in Materials and Methods), other Callitriche taxa recorded on the same locality, date of collection and collector name(s) (JanR = Jan Rydlo, JarR = Jaroslav Rydlo, JP = Jan Prančl, KK = Klára Kabátová, PT = Pavel Trávníček, ZK = Zdeněk Kaplan).
We are grateful to Klára Kabátová, Jaroslav Rydlo, Jan Rydlo, Petr Koutecký, Jiří Hadinec, Magdalena Hrdinová, Soňa Píšová, Bjarne Moeslund, Jens Christian Schou, Richard Hrivnák, Attila Mesterházy and many others for their help during fieldwork and/or providing some Callitriche samples; to Jana Krejčíková and Magdalena Lučanová for their help with cytometric analysis; Daniele Saiani for providing some localities of C. leniculca; Anna Krahulcová for providing some unpublished chromosome counts, Richard V. Lansdown for his valuable and constructive suggestions to the manuscript and Jonathan Rosenthal for kindly improving our English.
Conceived and designed the experiments: JP ZK. Performed the experiments: JP PT VJ. Analyzed the data: JP PT ZK VJ. Contributed reagents/materials/analysis tools: JP ZK PT VJ. Contributed to the writing of the manuscript: JP ZK.
- 1. Sculthorpe CD (1967) The biology of aquatic vascular plants. London: Edward Arnold. 610 p.
- 2. Cook CDK (1988) Wind pollination in aquatic angiosperms. Ann Missouri Bot Gard 75: 768–777.
- 3. Les DH (1988) Breeding systems, population structure, and evolution in hydrophilous angiosperms. Ann Missouri Bot Gard 75: 819–835.
- 4. Philbrick CT (1988) Evolution of underwater outcrossing from aerial pollination systems: A hypothesis. Ann Missouri Bot Gard 75: 836–841.
- 5. Barrett SCH, Eckert CG, Husband BC (1993) Evolutionary processes in aquatic plant populations. Aquat Bot 44: 105–145.
- 6. Grace JB (1993) The adaptive significance of clonal reproduction in angiosperms: an aquatic perspective. Aquat Bot 44: 159–180.
- 7. Les DH, Philbrick CT (1993) Studies of hybridization and chromosome number variation in aquatic angiosperms: evolutionary implications. Aquat Bot 44: 181–228.
- 8. Philbrick CT, Les DH (1996) Evolution of aquatic angiosperm reproductive systems. Bioscience 46: 813–826.
- 9. Kaplan Z (2002) Phenotypic plasticity in Potamogeton. Folia Geobot 37: 141–170.
- 10. Les DH, Crawford DJ, Kimball RT, Moody ML, Landolt E (2003) Biogeography of discontinuously distributed hydrophytes: a molecular appraisal of intercontinental disjunctions. Int J Plant Sci164: 917–932.
- 11. Cook CDK (1970) Hybridization in the evolution of Batrachium. Taxon 19: 161–166.
- 12. Fiasson JL, Gluchoff-Fiasson K, Dahlgren G (1997) Flavonoid patterns in European Ranunculus L. Subgenus Batrachium (Ranunculaceae). Biochem Syst Ecol 25: 327–333.
- 13. Kaplan Z (2001) Potamogeton ×fluitans (P. natans × P. lucens) in the Czech Republic. I. Morphology and anatomy. Preslia 73: 333–340.
- 14. Kaplan Z, Štěpánek J (2003) Genetic variation within and between populations of Potamogeton pusillus agg. Plant Syst Evol 239: 95–112.
- 15. Kaplan Z, Fehrer J, Hellquist CB (2009) New hybrid combinations revealed by molecular analysis: The unknown side of North American pondweed diversity (Potamogeton). – Syst Bot 34: 625–642.
- 16. Kaplan Z, Fehrer J (2011) Erroneous identities of Potamogeton hybrids corrected by molecular analysis of plants from type clones. Taxon 60: 758–766.
- 17. Cook CDK (1966) A monographic study of Ranunculus subgenus Batrachium (DC.) A. Gray. Mitt Bot Staatssamml München 6: 47–237.
- 18. Turała K (1969) Cytotaxonomical studies in Ranunculus subgenus Batrachium (DC.) A. Gray from Poland. Acta Biol Cracov, Ser Bot 12: 9–20.
- 19. Dahlgren G (1991) Karyological investigations in Ranunculus subg. Batrachium (Ranunculaceae) on the Aegean Islands. Plant Syst Evol 177: 193–211.
- 20. Hong DY (1991) A biosystematic study of Ranunculus subgenus Batrachium in S. Sweden. Nord J Bot 11: 41–59.
- 21. Hollingsworth PM, Preston CD, Gornall RJ (1998) Euploid and aneuploid evolution in Potamogeton (Potamogetonaceae): a factual basis for interpretation. Aquat Bot 60: 337–358.
- 22. Wiegleb G, Kaplan Z (1998) An account of the species of Potamogeton L. (Potamogetonaceae). Folia Geobot 33: 241–316.
- 23. Kaplan Z, Fehrer J (2006) Comparison of natural and artificial hybridization in Potamogeton. Preslia 78: 303–316.
- 24. Kaplan Z, Fehrer J (2007) Molecular evidence for a natural primary triple hybrid in plants revealed from direct sequencing. Ann Bot 99: 1213–1222.
- 25. Kaplan Z, Jarolímová V, Fehrer J (2013) Revision of chromosome numbers of Potamogetonaceae: a new basis for taxonomic and evolutionary implications. Preslia 85: 421–482.
- 26. Kaplan Z (2010) Hybridization of Potamogeton species in the Czech Republic: Diversity, distribution, temporal trends and habitat preferences. Preslia 82: 261–287.
- 27. Urbanska-Worytkiewicz K (1980) Cytological variation within the family Lemnaceae. Veroff Geobot Inst ETH, Stift Rübel 70: 30–101.
- 28. Landolt E (1986) The family of Lemnaceae – a monographic study. Vol. 1: Morphology, karyology, ecology, geographic distribution, systematic position, nomenclature, descriptions. Veroff Geobot Inst ETH, Stift Rübel 71: 1–566.
- 29. Gupta PP (1978) Cytogenetics of aquatic ornamentals. II. Cytology of Nymphaeas. Cytologia 43: 477–484.
- 30. Gupta PP (1980) Cytogenetics of aquatic ornamentals. VI. Evolutionary trends and relationships in the genus Nymphaea. Cytologia 45: 307–314.
- 31. Cook CDK, Urmi-König K (1985) A revision of the genus Elodea. Aquat Bot 21: 111–156.
- 32. Moody ML, Les DH (2010) Systematics of the aquatic angiosperm genus Myriophyllum (Haloragaceae). Syst Bot 35: 121–139.
- 33. Wiegleb G, Herr W (1983) Taxonomie und verbreitung von Ranunculus subgenus Batrachium in Niedersächsischen Fliessgewässeren unter besonderer Berücksichtigung des Ranunculus penicillatus Komplexes. Gött Flor Rundbr 17: 101–175.
- 34. Martinsson K (1991) Natural hybridization within the genus Callitriche (Callitrichaceae) in Sweden. Nord J Bot 11: 143–151.
- 35. Preston CD, Hollingsworth PM, Gornall RJ (1998) Potamogeton pectinatus L. × P. vaginatus Turcz. (P. × bottnicus Hagstr.), a newly identified hybrid in the British Isles. Watsonia 22: 69–82.
- 36. King RA, Gornall RJ, Preston CD, Croft JM (2001) Molecular confirmation of Potamogeton ×bottnicus (P. pectinatus × P. vaginatus, Potamogetonaceae) in Britain. Bot J Linn Soc 135: 67–70.
- 37. Kaplan Z, Fehrer J (2009) An orphaned clone of Potamogeton ×schreberi in the Czech Republic. Preslia 81: 387–397.
- 38. Schotsman HD (1967) Les Callitriches. Espèces de France et taxa nouveaux d’Europe. In: Jovet P, editor. Flora de France, vol. 1 . Paris: Editions Paul Lechevalier, pp. 1–151.
- 39. Lansdown RV (2006) Notes on the water-starworts (Callitriche) recorded in Europe. Watsonia 26: 105–120.
- 40. Lansdown RV (2008) Water-starworts (Callitriche) of Europe. B.S.B.I. Handbook no. 11. London: Botanical Society of the British Isles. 184 p.
- 41. Fassett NC (1951) Callitriche in the New World. Rhodora 53: 137–222 –––
- 42. Schotsman HD (1954) A taxonomic spectrum of the section Eu-Callitriche in the Netherlands. Acta Bot Neerl 3: 313–384.
- 43. Schotsman HD (1958) Beitrag zur Kenntnis der Callitriche-Arten in Bayern. Ber Bayer Bot Ges 32: 128–140.
- 44. Schotsman HD (1977) Callitriches de la région Méditerranéenne. Nouvelles observations. Bull Cent Etud Rech Sci, Biarritz 11: 241–312.
- 45. Schotsman HD (1982) Biologie florale des Callitriche: étude sur quelques espèces d’Espagne méridionale. Bull Mus Natl His Natur, B, Adansonia 4: 111–160.
- 46. Mason R (1959) Callitriche in New Zealand and Australia. – Austr J Bot 7: 295–327.
- 47. Dersch G (1986) Zur Verbreitung der Callitriche-Arten (Wassersterne) in Niedersachsen. Gött Flor Rundbr 20: 79–100.
- 48. Hedberg O, Hedberg I (2001) Tropical African Callitriche (Callitrichaceae): A neglected and taxonomically difficult part of an evolutionary extremely interesting family. Biol Skr 54: 19–30.
- 49. Prančl J (2012) Rod Callitriche (hvězdoš) v České republice. I. Úvod a určování, druhy C. hermaphroditica, C. hamulata a C. palustris [The genus Callitriche (water-starwort) in the Czech Republic. I. Introduction and determination, the species C. hermaphroditica, C. hamulata and C. palustris]. Zprávy Čes Bot Společ 47: 209–290.
- 50. Prančl J (2013) Rod Callitriche (hvězdoš) v České republice. II. C. cophocarpa, C. stagnalis, C. platycarpa, C. × vigens [The genus Callitriche (water-starwort) in the Czech Republic. II. C. cophocarpa, C. stagnalis, C. platycarpa, C. × vigens]. Zprávy Čes Bot Společ 48: 179–262.
- 51. Jones H (1955) Heterophylly in some species of Callitriche, with special reference to C. intermedia. Ann Bot 19: 225–245.
- 52. Jones H (1955) Further studies on heterophylly in Callitriche intermedia: leaf development and experimental induction of ovate leaves. Ann Bot 19: 370–388.
- 53. Deschamp PA, Cooke TJ (1984) Causal mechanisms of leaf dimorphism in the aquatic angiosperm Callitriche heterophylla. Am J Bot 71: 319–329.
- 54. Deschamp PA, Cooke TJ (1985) Leaf dimorphism in the aquatic angiosperm Callitriche heterophylla. Am J Bot 72: 1377–1387.
- 55. McComb AJ (1965) The control of elongation in Callitriche shoots by environment and gibberellic acid. Ann Bot 29: 445–458.
- 56. Wong CH, McComb AJ (1967) An anatomical investigation into the effects of gibberellic acid on the expansion of Callitriche shoots. Austral J of Biol Sci 20: 1053–1062.
- 57. Musgrave A, Jackson MB, Ling E (1972) Callitriche stem elongation is controlled by ethylene and gibberellin. Nat New Biol 238: 93–96.
- 58. Madsen TV (1991) Inorganic carbon uptake kinetics of the stream macrophyte, Callitriche cophocarpa. Aquat Bot 40: 321–332.
- 59. Maberly SC, Madsen TV (2002) Use of bicarbonate ions as a source of carbon in photosynthesis by Callitriche hermaphroditica. Aquat Bot 73: 1–7.
- 60. Augustynowicz J, Grosicki M, Hanus-Fajerska E, Lekka M, Waloszek A, et al. (2010) Chromium(VI) bioremediation by aquatic macrophyte Callitriche cophocarpa Sendtn. Chemosphere 75: 1077–1083.
- 61. Augustynowicz J, Kołton AM, Baran AM, Kostecka-Gugała AM, Lasek WW (2013) Strategy of Cr detoxification by Callitriche cophocarpa. Centr Eur J Chem 11: 295–303.
- 62. Sand-Jensen K, Andersen K, Andersen T (1999) Dynamic properties of recruitment, expansion and mortality of macrophyte patches in streams. Int Rev Hydrobiol 84: 497–508.
- 63. Sand-Jensen K, Pedersen ML (2008) Streamlining of plant patches in streams. Freshwater Biol 53: 714–726.
- 64. Augustynowicz J, Tokarz K, Baran A, Płachno BJ (2014) Phytoremediation of water polluted by thallium, cadmium, zinc, and lead with the use of macrophyte Callitriche cophocarpa. Arch Environ Contam Toxicol 66: 572–581.
- 65. Dawson I (1998) New salad and vegetable crops. From Australia's sub-Antarctic Islands. A report fo the Rural Industries Research and Develpoment Corporation. Canberra: Rural Industries Research and Development Corporation. 35 p.
- 66. Augustynowicz J, Długosz-Grochowska OG, Kostecka-Gugała AM, Leja M, Kruczek MK, et al. (2014) Callitriche cophocarpa – a new rich source of active phenolic compounds. Centr Eur J Chem 12: 519–527.
- 67. Philbrick CT, Anderson GJ (1992) Pollination biology in the Callitrichaceae. Syst Bot 17: 282–292.
- 68. Philbrick CT, Bernardello LM (1992) Taxonomic and geographic distribution of internal geitonogamy in New World Callitriche (Callitrichaceae). Am J Bot 79: 887–890.
- 69. Martinsson K (1996) Growth forms and reproductive characters in six species of Callitriche (Callitrichaceae). Acta Univ Upsal, Symb Bot Upsal 31: 123–131.
- 70. Philbrick CT, Les DH (2000) Phylogenetic studies in Callitriche: implications for interpretation of ecological, karyological and pollination system evolution. Aquat Bot 68: 123–141.
- 71. Savidge JP (1960) The experimental taxonomy of European Callitriche. Proc Linn Soc London 171: 128–130.
- 72. Martinsson K (1985) Problem kring Callitriche platycarpa, plattlånke [Problems concerning Callitriche platycarpa, various-leaved Water-starwort]. Svensk Bot Tidskr 79: 165–174.
- 73. Bączkiewicz A, Szoszkiewicz K, Cichocka J, Celińsky K, Drapikowska M, et al. (2007) Isozyme patterns of Callitriche cophocarpa, C. stagnalis and C. platycarpa from 13 Polish rivers. Biol Lett 44: 103–114.
- 74. Savidge JP (1959) An interspecific hybrid in European Callitriche. Proc Bot Soc British Isles 3: 335.
- 75. Schotsman HD (1961) Contribution a l’étude des Callitriche du canton de Neuchatel. Bull Soc Neuchâteuloise Sci Nat 84: 89–101.
- 76. Demars BOL, Gornall RJ (2003) Identification of British species of Callitriche by means of isozymes. Watsonia 24: 389–399.
- 77. Triest L, Mannaert A (2006) The relationship between Callitriche L. clones and environmental variables using genotyping. Hydrobiologia 570: 73–77.
- 78. Buczkowska K, Szoszkiewicz K, Bączkiewicz A (2008) Genetic variation in Polish populations of Callitriche cophocarpa. Acta Biol Cracov, Ser Bot 50: 63–70.
- 79. Gomarasca S, Cicatelli A, Maggioni LA, Castiglione S (2012) The use of Callitriche for water quality determination can be misleading: An example from the Po Valley in Northern Italy. Pl Biosystems 147: 459–471.
- 80. Doležel J, Greilhuber J, Suda J (2007) Estimation of nuclear DNA content in plants using flow cytometry. Nature Protocols 2: 2233–2244.
- 81. Loureiro J, Doležel J, Greilhuber J, Santos C, Suda J (2008) Plant flow cytometry – far beyond the stone age. Cytom Part A 73A: 579–580.
- 82. Kolář F, Fér T, Štech M, Trávníček P, Dušková E, et al. (2012) Bringing together evolution on serpentine and polyploidy: spatiotemporal history of the diploid-tetraploid complex of Knautia arvensis (Dipsacaceae). PLoS ONE 7: e39988
- 83. Kolář F, Lučanová M, Vít P, Urfus T, Chrtek J, et al. (2013) Diversity and endemism in deglaciated areas: ploidy, relative genome size and niche differentiation in the Galium pusillum complex (Rubiaceae) in Northern and Central Europe. Ann Bot 111: 1095–1108.
- 84. Mandák B, Trávníček P, Paštová L, Kořínková D (2012) Is hybridization involved in the evolution of the Chenopodium album aggregate? An analysis based on chromosome counts and genome size estimation. Flora 7: 530–540.
- 85. Pellicer J, Clermont S, Houston L, Rich TC, Fay MF (2012) Cytotype diversity in the Sorbus complex (Rosaceae) in Britain: sorting out the puzzle. Ann Bot 110: 1185–1193.
- 86. Niketić M, Siljak-Yakovlev S, Frajman B, Lazarević M, Stevanović B, et al. (2013) Towards resolving the systematics of Cerastium subsection Cerastium (Caryophyllaceae): a cytogenetic approach. Bot J Linn Soc 172: 205–224.
- 87. Loureiro J, Trávníček P, Rauchová J, Urfus T, Vít P, et al. (2010) The use of flow cytometry in the biosystematics, ecology and population biology of homoploid plants. Preslia 82: 3–21.
- 88. Bennert HW, Horn K, Kauth M, Fuchs J, Jakobsen ISB, et al. (2011) Flow cytometry confirms reticulate evolution and reveals triploidy in Central European Diphasiastrum taxa (Lycopodiaceae, Lycophyta). Ann Bot 108: 867–876.
- 89. Kúr P, Štech M, Koutecký P, Trávníček P (2012) Morphological and cytological variation in Spergularia echinosperma and S. rubra, and notes on potential hybridization of these two species. Preslia 84: 905–924.
- 90. Winter S, Chizzola R, Kriechbaum M, Kropf M (2013) Hybridisation in Jacobaea – characterisation of hybrids between Jacobaea aquatica and J. vulgaris in Austria. Plant Ecol Divers 6: 217–229.
- 91. Hanušová K, Ekrt L, Vít P, Kolář F, Urfus T (2014) Continuous morphological variation correlated with genome size indicates frequent introgressive hybridization among Diphasiastrum species (Lycopodiaceae) in Central Europe. PLoS ONE, accepted
- 92. Vít P, Wolfová K, Urfus T, Tájek P, Suda J (2014) Interspecific hybridization between rare and common plant congeners inferred from genome size data: assessing the threat to the Czech serpentine endemic Cerastium alsinifolium. Preslia 86: 95–117.
- 93. Mráz P, Chrtek J, Fehrer J (2011) Interspecific hybridization in the genus Hieracium s. str.: evidence for bidirectional gene flow and spontaneous allopolyploidization. Plant Syst Evol 293: 237–245.
- 94. Trávníček P, Kubátová B, Čurn V, Rauchová J, Krajníková E, et al. (2011) Remarkable coexistence of multiple cytotypes of the Gymnadenia conopsea aggregate (the fragrant orchid): evidence from flow cytometry. Ann Bot 107: 77–87.
- 95. Trávníček P, Jersáková J, Kubátová B, Krejčíková J, Bateman RM, et al. (2012) Minority cytotypes in European populations of the Gymnadenia conopsea complex (Orchidaceae) greatly increase intraspecific and intrapopulation diversity. Ann Bot 110: 977–986.
- 96. Diao Y, Chen L, Yang G, Zhou M, Song Y, et al. (2006) Nuclear DNA C-values in 12 species in Nymphaeales. Caryologia 59: 25–30.
- 97. Pellicer J, Kelly LJ, Magdalena C, Leitch IJ (2013) Insights into the dynamics of genome size and chromosome evolution in the early diverging angiosperm lineage Nymphaeales (water lilies). Genome 56: 437–449.
- 98. Volkova PA, Trávníček P, Brochmann C (2010) Evolutionary dynamics across discontinuous freshwater systems: Rapid expansions and repeated allopolyploid origins in the Palearctic white water-lilies (Nymphaea). Taxon 59: 483–494.
- 99. Kabátová K, Vít P, Suda J (2014) Species boundaries and hybridization in central-European Nymphaea species inferred from genome size and morphometric data. Preslia 86: 131–154.
- 100. Vialette-Guiraud ACM, Alaux M, Legeai F, Finet C, Chambrier P, et al. (2011) Cabomba as a model for studies of early angiosperm evolution. Ann Bot 108: 589–598.
- 101. McCracken A, Bainard JD, Miller MC, Husband BC (2013) Pathways of introduction of the invasive aquatic plant Cabomba caroliniana. Ecol Evol 3: 1427–1439.
- 102. Stift M, Bregman R, Oostermeijer JGB, van Tienderen PH (2010) Other tetraploid species and conspecific diploids as sources of genetic variation for an autotetraploid. Am J Bot 97: 1858–1866.
- 103. Morozowska M, Czarna A, Jędrzejczyk I (2010) Estimation of nuclear DNA content in Nasturtium R. Br. by flow cytometry. Aquat Bot 93: 250–253.
- 104. Wang W, Kerstetter RA, Michael TP (2011) Evolution of genome size in duckweeds (Lemnaceae). Journal of Botany 2011 : ID 570319. doi:10.1155/2011/570319.
- 105. Tanaka N, Ito Y, Matsuyama R, Uehara K (2007) Chromosome numbers of Zannichellia L. (Zannichelliaceae) in Japan. Bull Natl Museum of Nature and Science, Series B 33: 133–136.
- 106. Pijnacker LP, Schotsman HD. 1988. Nuclear-DNA amounts in European Callitriche species (Callitrichaceae). Acta Bot Neerl 37: 129–135.
- 107. Schotsman HD, Andreas CH (1974) Callitriche lenisulca Clav. espèce méconnue. Bull Cent Etud Rech Sci, Biarritz 10: 285–316.
- 108. Otto F (1990) DAPI staining of fixed cells for high-resolution flow cytometry of nuclear DNA. In: Crisssman HA, Darzynkiewicz Z, editors. Methods in cell biology, vol. 33 . New York: Academic Press. pp. 105–110.
- 109. Leong-Škorničková J, Šída O, Jarolímová V, Sabu M, Fér T, et al. (2007) Chromosome numbers and genome size variation in Indian species of Curcuma (Zingiberaceae). Ann Bot 100: 505–526.
- 110. Morton A (2008) DMAP. Distribution mapping software. Available: http://www.dmap.co.uk/ Accessed 6 February 2013.
- 111. Philbrick CT, Aakjar RA, Stuckey RL (1998) Invasion and spread of Callitriche stagnalis (Callitrichaceae) in North America. Rhodora 100: 25–38.
- 112. Prančl J, Schou JC (2014) Butfrugtet Vandstjerne – Callitriche obtusangula Le Gall – ny art for Danmark [Blunt-fruited Water-starwort – Callitriche obtusangula Le Gall – a new species for Denmark]. URT 38: 29–33.
- 113. Philbrick CT (1984) Pollen-tube growth within vegetative tissues of Callitriche (Callitrichaceae). Am J Bot 71: 882–886.
- 114. Francis D, Davies MS, Barlow PW (2008) A strong nucleotypic effect on the cell cycle regardless of ploidy level. Ann Bot 101: 747–757.
- 115. Šímová I, Herben T (2012) Geometrical constraints in the scaling relationships between genome size, cell size and cell cycle length in herbaceous plants. Proc R Soc B 279: 867–875.
- 116. Ekrt L, Holubová R. Trávníček P, Suda J (2010) Species boundaries and frequency of hybridization in the Dryopteris carthusiana (Dryopteridaceae) complex: a taxonomic puzzle resolved using genome size data. Am J Bot 97: 1208–1219.
- 117. Suda J, Trávníček P, Mandák B, Berchová-Bímová K (2010) Genome size as a marker for the recognition of invasive alien taxa in Fallopia section Reynoutria. Preslia 82: 97–106.
- 118. Suda J, Krahulcová A, Trávníček P, Rosenbaumová R, Peckert T, et al. (2007) Genome size variation and species relationships in Hieracium subgen. Pilosella (Asteraceae) as inferred by flow cytometry. Ann Bot 100: 1323–1335.
- 119. Schotsman HD (1961) Races chromosomiques chez Callitriche stagnalis Scop. et Callitriche obtusangula Legall. Ber Schweiz Bot Ges 71: 5–17.
- 120. Soltis DE, Soltis PS (1993) Molecular data facilitate a reevaluation of traditional tenets of polyploid evolution. Crit Rev Plant Sci 12: 243–273.
- 121. Soltis DE, Soltis PS (1999) Polyploidy: Origins of species and genome evolution. Trends Ecol Evol 14: 349–351.
- 122. Soltis DE, Buggs RJA, Doyle JJ, Soltis PS (2004) What we still don’t know about polyploidy. Taxon 59: 1387–1403.
- 123. Webster SD (1988) Ranunculus penicillatus (Dumort.) Bab. in Great Britain and Ireland. Watsonia 17: 1–22.
- 124. Kaplan Z, Fehrer J (2013) Molecular identification of hybrids from a former hot spot of Potamogeton hybrid diversity. Aquat Bot 105: 34–40.
- 125. Moody ML, Les DH (2007) Geographic distribution and genotypic composition of invasive hybrid watermilfoil (Myriophyllum spicatum × M. sibiricum) populations in North America. Biol Invasions 9: 559–570.
- 126. Martinsson K (1993) The pollen of Swedish Callitriche – trends towards submergence. Grana 32: 198–209.
- 127. Kaplan Z, Fehrer J (2004) Evidence for the hybrid origin of Potamogeton ×cooperi (Potamogetonaceae): traditional morphology-based taxonomy and molecular techniques in concert. Folia Geobot 39: 431–453.
- 128. Kaplan Z, Wolff P (2004) A morphological, anatomical and isozyme study of Potamogeton ×schreberi: confirmation of its recent occurrence in Germany and first documented record in France. Preslia 76: 141–161.
- 129. Kaplan Z, Uotila P (2011) Potamogeton × exilis (P. alpinus × P. natans), a new hybrid pondweed from Finland. Nord J Bot 29: 477–483.
- 130. Letz DR, Dančák M, Danihelka J, Šarhanová P (2012) Taxonomy and distribution of Cerastium pumilum and C. glutinosum in Central Europe. Preslia 84: 33–69.
- 131. Ekrt L, Trávníček P, Jarolímová V, Vít P, Urfus T (2009) Genome size and morphology of the Dryopteris affinis group in Central Europe. Preslia 81: 261–280.
- 132. Husák Š (2000) Callitrichaceae Link – hvězdošovité. In: Slavík B, editor. Květena České republiky [Flora of the Czech Republic], vol. 6 . Praha: Academia. pp 709–718.
- 133. Zahradníková K (1982) Callitrichaceae L. Hviezdošovité. In: Futák J, Bertová L, editors. Flóra Slovenska [Flora of Slovakia], vol. 3 . Bratislava: Veda. pp. 463–470.