Abstract

Background and Aims

Compared with other plant lineages, bryophytes have very small genomes with little variation across species, and high levels of endopolyploid nuclei. This study is the first analysis of moss genome evolution over a broad taxonomic sampling using phylogenetic comparative methods. We aim to determine whether genome size evolution is unidirectional as well as examine whether genome size and endopolyploidy are correlated in mosses.

Methods

Genome size and endoreduplication index (EI) estimates were newly generated using flow cytometry from moss samples collected in Canada. Phylogenetic relationships between moss species were reconstructed using GenBank sequence data and maximum likelihood methods. Additional 1C-values were compiled from the literature and genome size and EI were mapped onto the phylogeny to reconstruct ancestral character states, test for phylogenetic signal and perform phylogenetic independent contrasts.

Key Results

Genome size and EI were obtained for over 50 moss taxa. New genome size estimates are reported for 33 moss species and new EIs are reported for 20 species. In combination with data from the literature, genome sizes were mapped onto a phylogeny for 173 moss species with this analysis, indicating that genome size evolution in mosses does not appear to be unidirectional. Significant phylogenetic signal was detected for genome size when evaluated across the phylogeny, whereas phylogenetic signal was not detected for EI. Genome size and EI were not found to be significantly correlated when using phylogenetically corrected values.

Conclusions

Significant phylogenetic signal indicates closely related mosses have more similar genome sizes and EI values. This study supports that DNA content in mosses is defined by small genomes that are highly endopolyploid, suggesting strong selective pressure to maintain these features. Further research is needed to understand the functional significance of DNA content evolution in mosses.

INTRODUCTION

Phylogenetic comparative methods provide a powerful tool to enhance our understanding of genome size (1C-value, the amount of DNA in a non-replicated chromosome complement; Greilhuber et al., 2005) evolution across land plants (Leitch et al., 2005; Soltis et al., 2018). Phylogenetic reconstructions indicate that the ancestral genome size of land plants was likely very small (Soltis et al., 2018), with larger genome sizes subsequently evolving in many plant lineages e.g. lycophytes (Bainard et al., 2011a); ferns (Clark et al., 2016), gymnosperms (Burleigh et al., 2012) and angiosperms (Leitch et al., 1998)]. In contrast, the three bryophyte lineages (hornworts, liverworts and mosses) predominantly retain the very small ancestral genome sizes with little variation across species (Temsch et al., 1998; Voglmayr, 2000; Bainard and Villarreal, 2013; Bainard et al., 2013). While considerable genome size data have been amassed for all three bryophyte lineages, a comprehensive analysis of genome size evolution using phylogenetic comparative methods is lacking for mosses.

Mosses (Bryophyta) are the most speciose bryophyte lineage, comprising ~13 000 species worldwide (Magill, 2010), compared with liverworts (Marchantiophyta) with 7271 species and hornworts (Anthocerotophyta) with 215 species (Söderström et al., 2016). These lineages share a dominant haploid generation in the course of alternation of generations, with an unbranched sporophyte that remains physically attached to and nutritionally dependent on the maternal gametophyte throughout its lifespan. Recent analyses of molecular data have confirmed the longstanding hypothesis of a sister relationship between liverworts and mosses (setaphyte hypothesis), which was first proposed based on morphological studies of spermatogenesis (Renzaglia and Garbary, 2001; Renzaglia et al., 2018), and have also supported the monophyly of the three bryophyte lineages (Morris et al., 2018; Puttick et al., 2018; de Sousa et al., 2019). Analysing the 1C-values present in mosses will broaden our understanding of genome size evolution in bryophytes and across land plants.

Overall, <1.5 % of known moss species have published genome size estimates (Plant DNA C-values Database; http://data.kew.org/cvalues/) and the need to better understand genome diversity in this lineage has often been noted (e.g. Leitch and Leitch, 2013). Voglmayr (2000) can be credited with the largest single survey of moss species to date, which contained 138 taxa. Genome sizes for Sphagnum (peat mosses) have been reported by Temsch et al. (1998), Greilhuber et al. (2003) and Karlin et al. (2014). A handful of other moss species have published genome size estimates (Reski et al., 1994; Renzaglia et al., 1995; Lamparter et al., 1998; Zouhair and Lecocq, 1998; Schween et al., 2003; Melosik et al., 2005; Bainard et al., 2010).

Bryophytes have both very small and more highly constrained genome sizes in comparison with other land plants (Soltis et al., 2018). The greatest variation in genome sizes is found in the angiosperms, which range in 1C-value from 61 Mbp (0.06 pg) in Genlisea tuberosa (Fleischmann et al., 2014) to 148 852 Mbp (152.23 pg) in Paris japonica (Pellicer et al., 2010). The monilophytes (ferns) show a similar wide range in genome sizes, from 750 Mbp (0.8 pg) in Azolla microphylla (Obermayer et al., 2002) to 147 297 Mbp (150.61 pg) in Tmesipteris obliqua (Hidalgo et al., 2017), while the lycophytes (fern allies) range from 81 Mbp (0.08 pg) in Selaginella selaginoides (Baniaga et al., 2016) to 11 704 Mbp (11.97 pg) in Isoetes lacustris (Hanson and Leitch, 2002). Gymnosperms tend to have larger genomes on average, ranging from 2201 Mbp (2.25 pg) in Gnetum ula (Ohri and Khoshoo, 1986) to 35 208 Mbp (36 pg) in Pinus ayacahuite (Grotkopp et al., 2004). Across bryophytes, 1C-values for hornworts range from only 160 Mbp (0.16 pg) in Leiosporoceros dussii to 719 Mbp (0.73 pg) in Nothoceros endiviifolius (Bainard and Villarreal, 2013), while liverworts have a wider variation of sizes, from 206 Mbp (0.21 pg) in Lejeunea cavifolia (Temsch et al., 2010) to 20 006 Mbp (20.46 pg) in Phyllothallia fuegiana (Bainard et al., 2013). The variation in moss genome sizes falls between the other two bryophyte lineages and spans from 170 Mbp (0.17 pg) in Holomitrium arboreum to 2004 Mbp (2.05 pg) in Mnium marginatum (Voglmayr, 2000).

DNA content varies within an individual plant when nuclei are found at varying ploidy levels in the same individual, termed endopolyploidy (Nagl, 1978). Endopolyploidy is the result of endoreduplication, which occurs when DNA replication is not followed by mitotic division, and is largely due to modification of cyclin-dependent kinase activity (De Veylder et al., 2011). The prevalence of endopolyploidy varies widely across plant lineages. It is common in angiosperms and mosses, appears to be rare in both gymnosperms and ferns, and is entirely lacking in liverworts (Barlow, 1978; Barow and Jovtchev, 2007; Bainard and Newmaster, 2010). High levels of endopolyploidy are often associated with small genome sizes in plants (Nagl, 1978; De Rocher et al., 1990; Barow and Meister, 2003; Bainard et al., 2012). The implications of this relationship may have far-reaching consequences, as the amount of DNA (the ‘nucleotype’) directly impacts nuclear and cell volume, which in turn affects other morphological and ecological features (Bennett, 1971, 1972; Cavalier-Smith, 1978). Barow and Meister (2003) speculated that endopolyploidy in angiosperms may allow species with small genomes to combine the advantages of a small genome (such as shorter cell cycles and shorter generation times) with those of a large genome (such as the ability for cell growth and expansion in low temperatures). All mosses surveyed to date, except for members of the genus Sphagnum, demonstrate high levels of endopolyploidy (Bainard and Newmaster, 2010). Understanding whether there is a relationship between genome size and endopolyploidy in mosses will help us determine if this pattern is limited to broad differences within the angiosperm lineage, or if it occurs in other taxonomic groups as well.

We tested the following hypotheses using the most comprehensive dataset of 1C-values and endopolyploidy data assembled to date from a broad phylogenetic sample of moss species. (1) We tested the genetic obesity hypothesis (Bennetzen and Kellogg, 1997), which postulates that genome size evolution is unidirectional, resulting in species with larger genomes occupying derived positions within the phylogeny. (2) We examined whether there is phylogenetic signal for genome size and/or endopolyploidy, which is the tendency of closely related species to resemble each other more than a random set of species from the same tree (Harvey and Pagel, 1991). (3) We tested the hypothesis that high levels of endopolyploidy are correlated with small genome sizes (Nagl, 1978; De Rocher et al., 1990; Barow and Meister, 2003), using phylogenetic comparative methods that account for the non-independence of data collected across species (Felsenstein, 1985).

MATERIALS AND METHODS

Plant material

Moss specimens were collected from three main localities in Canada in the summer of 2009: various sites in Ontario, the Gulf Islands in British Columbia, and Churchill, Manitoba. Species were identified by the authors using floras appropriate for each region (Lawton, 1971; Crum and Anderson, 1981). Voucher specimens of all collected materials are deposited in the Biodiversity Institute of Ontario Herbarium (OAC/BIO, University of Guelph; Supplementary Data Table S1). Sampling for this study was limited to field-collected populations. Laboratory-cultured populations for additional Funariaceae species were originally included in the sampling; however, Schween et al. (2003) found that cultured mosses have a majority of nuclei in the G2/M phase in the juvenile chloronema cells, and very few (sometimes lacking) nuclei in G1/S phase in caulonema cells. This made it very difficult to determine the 1C nuclei in a flow cytometry histogram and thus these laboratory cultures of Funariaceae were excluded from this study. Before analysis, the moss gametophyte tissue was air-dried, which does not significantly affect DNA content estimates (Bainard et al., 2010; Bainard et al., 2011b). Leaf and stem tissue that was green and healthy was selected for analysis. After mosses were determined suitable for analysis by flow cytometry, there was a total of 60 samples: 39 from Ontario, 14 from British Columbia and seven from Manitoba (Table 1).

Table 1.

DNA content estimates for moss species collected at various locations in Canada (BC, British Columbia; MB, Manitoba; ON, Ontario). Taxa are classified according to the Taxonomic Name Resolution Service (http://tnrs.iplantcollaborative.org) and are arranged alphabetically by family. Genome size is reported as average 1C-value ± standard error of the mean in picograms (pg) as well as average Mbp (1 pg = 0.978 × 109 bp; Doležel et al., 2003). Degree of endopolyploidy is reported as the endoreduplication index (EI) ± s.e.m.

TaxonCollection locality1C-value ± s.e.m. (pg)1C-value (Mbp)StandardEI ± s.e.m.
Amblystegiaceae
Campylium chrysophyllum (Brid.) LangeON1.00 ± 0.022982Solanum lycopersicum0.64 ± 0.057
Sanionia uncinata (Hedw.) LoeskeMB0.37 ± 0.007358Raphanus sativus1.53 ± 0.023
Aulacomniaceae
Aulacomnium androgynum (Hedw.) Schwägr.ON0.34 ± 0.007336Raphanus sativus0.64 ± 0.076*
Brachytheciaceae
Brachythecium acuminatum (Hedw.) AustinON1.02 ± 0.022999Glycine max0.54 ± 0.045*
Brachythecium salebrosum (Hoffm. ex F.Weber and D.Mohr) Schimp.BC0.55 ± 0.004534Glycine max1.01 ± 0.037
Brachythecium salebrosum (Hoffm. ex F.Weber and D.Mohr) Schimp.ON0.97 ± 0.057952Glycine max0.14 ± 0.018*
Brachythecium velutinum (Hedw.) Schimp.ON0.46 ± 0.004§449Raphanus sativus0.51 ± 0.071*
Cirriphyllum piliferum (Hedw.) GroutMB1.04 ± 0.0091021Glycine max0.63 ± 0.056
Eurhynchium pulchellum (Hedw.) Jenn.ON0.52 ± 0.024507Raphanus sativus0.27 ± 0.044*
Homalothecium aeneum (Mitt.) E. Lawton BC0.26 ± 0.006257Glycine max1.63 ± 0.114
Pohlia wahlenbergii (F. Weber and D. Mohr) A.L. AndrewsON0.49 ± 0.006481Raphanus sativus1.13 ± 0.125*
Bruchiaceae
Trematodon ambiguus (Hedw.) Hornsch.ON0.39 ± 0.003384Raphanus sativus0.51 ± 0.055*
Climaciaceae
Climacium dendroides (Hedw.) F. Weber and D.MohrON1.00 ± 0.041983Glycine max1.48 ± 0.029*
Dicranaceae
Dichodontium pellucidum (Hedw.) Schimp.MB0.34 ± 0.005329Raphanus sativus0.42 ± 0.017
Dicranoweisia cirrata (Hedw.) Lindb.BC0.25 ± 0.001243Raphanus sativus0.57 ± 0.016
Dicranum condensatum Hedw.ON0.81 ± 0.026795Raphanus sativus0.87 ± 0.072*
Dicranum flagellare Hedw.ON0.57 ± 0.018557Glycine max0.50 ± 0.015*
Dicranum fuscescens TurnerON0.65 ± 0.017639Glycine max0.57 ± 0.087*
Dicranum fuscescens TurnerBC0.74 ± 0.014728Raphanus sativus0.44 ± 0.010
Dicranum groenlandicum Brid.MB0.60 ± 0.013585Raphanus sativusN/A
Dicranum montanum Hedw.ON0.52 ± 0.010507Raphanus sativus0.52 ± 0.029*
Dicranum polysetum Sw.ON0.78 ± 0.027758Raphanus sativus1.11 ± 0.030*
Dicranum scoparium Hedw.ON0.38 ± 0.010375Solanum lycopersicum0.98 ± 0.048*
Dicranum scoparium Hedw.BC0.72 ± 0.013709Raphanus sativus1.22 ± 0.014
Dicranum spurium Hedw.MB0.35 ± 0.004338Raphanus sativus0.59 ± 0.029
Ditrichaceae
Ceratodon purpureus (Hedw.) Brid.ON0.47 ± 0.004456Raphanus sativus0.51 ± 0.060*
Ditrichum lineare (Sw.) Lindb.MB0.35 ± 0.003343Raphanus sativus0.32 ± 0.026
Fissidentaceae
Fissidens taxifolius Hedw.ON0.32 ± 0.001§313Raphanus sativus0.40 ± 0.039*
Hedwigiaceae
Hedwigia ciliata (Hedw.) P.Beauv.ON0.30 ± 0.003§291Raphanus sativus0.34 ± 0.030*
Hylocomiaceae
Hylocomium splendens (Hedw.) Schimp.ON0.48 ± 0.003471Raphanus sativus0.53 ± 0.165*
Pleurozium schreberi (Willd. Ex Brid.) Mitt.ON0.83 ± 0.039809Raphanus sativus0.35 ± 0.079*
Pleurozium schreberi (Willd. Ex Brid.) Mitt.MB0.43 ± 0.008418Raphanus sativus0.74 ± 0.028
Rhytidiadelphus triquetrus (Hedw.) Warnst.ON0.57 ± 0.020555Glycine max0.52 ± 0.036*
Hypnaceae
Callicladium haldanianum (Grev.) H.A. CrumON0.83 ± 0.023816Raphanus sativus0.69 ± 0.187*
Calliergonella lindbergii (Mitt.) HedenäsON0.40 ± 0.010389Raphanus sativus0.78 ± 0.236*
Hypnum curvifolium Hedw.ON0.59 ± 0.004580Glycine max1.30 ± 0.107*
Hypnum pallescens (Hedw.) P.Beauv.ON0.38 ± 0.011376Raphanus sativus0.96 ± 0.078*
Hypnum recurvatum (Lindb. and Arnell) Kindb.ON0.37 ± 0.007365Raphanus sativus0.34 ± 0.104*
Ptilium crista-castrensis (Hedw.) De Not.ON0.40 ± 0.010388Raphanus sativus0.27 ± 0.016*
Pylaisia polyantha (Hedw.) Schimp.ON0.41 ± 0.008399Raphanus sativus0.37 ± 0.054*
Lembophyllaceae
Isothecium cristatum (Hampe) H.Rob.BC0.44 ± 0.006427Raphanus sativus0.36 ± 0.021
Isothecium myosuroides Brid.BC0.53 ± 0.011518Raphanus sativusN/A
Leskeaceae
Claopodium crispifolium (Hook.) Renauld and CardotBC0.40 ± 0.000393Raphanus sativus0.81 ± 0.080
Haplocladium microphyllum (Hedw.) Broth.ON0.44 ± 0.011432Raphanus sativus0.41 ± 0.086*
Leucodontaceae
Antitrichia curtipendula (Timm ex Hedw.) Brid.BC0.52 ± 0.002507Solanum lycopersicum0.73 ± 0.017
Dendroalsia abietina (Hook.) E. Britton ex Broth.BC0.37 ± 0.004363Raphanus sativus0.67 ± 0.139
Mniaceae
Leucolepis acanthoneura (Schwägr.) Lindb.BC1.18 ± 0.0101155Solanum lycopersicum0.93 ± 0.062
Plagiomnium drummondii (Bruch and Schimp.) T.J. Kop.ON0.63 ± 0.004612Glycine max1.37 ± 0.054*
Plagiomnium medium (Bruch and Schimp.) T.J. Kop.ON0.97 ± 0.012949Glycine max1.21 ± 0.152*
Neckeraceae
Metaneckera menziesii (Drumm.) SteereBC0.44 ± 0.004427Raphanus sativus1.13 ± 0.129
Neckera douglasii Hook.BC0.51 ± 0.005498Raphanus sativus0.73 ± 0.074
Orthotrichaceae
Orthotrichum speciosum NeesON0.35 ± 0.009343Raphanus sativus0.30 ± 0.071*
Plagiotheciaceae
Plagiothecium denticulatum (Hedw.) Schimp.ON0.55 ± 0.014540Raphanus sativus1.05 ± 0.160*
Plagiothecium laetum Schimp.ON0.55 ± 0.000536Glycine max1.71 ± 0.062*
Polytrichaceae
Polytrichastrum formosum (Hedw.) G.L. Sm.BC0.67 ± 0.008655Raphanus sativus0.51 ± 0.065
Polytrichum commune Hedw.ON1.08 ± 0.0011056Zea mays0.33 ± 0.055*
Polytrichum juniperinum Hedw.ON0.46 ± 0.019455Raphanus sativus0.60 ± 0.060*
Sphagnaceae
Sphagnum recurvum P. Beauv.ON0.56 ± 0.012549Raphanus sativus0.00 ± 0.000*
Thuidiaceae
Cyrto-hypnum minutulum (Hedw.) W.Raphanus Buck & H.A. CrumON0.44 ± 0.002§435Raphanus sativus0.41 ± 0.025*
Thuidium delicatulum (Hedw.) Schimp.ON0.43 ± 0.000418Raphanus sativus0.91 ± 0.119*
TaxonCollection locality1C-value ± s.e.m. (pg)1C-value (Mbp)StandardEI ± s.e.m.
Amblystegiaceae
Campylium chrysophyllum (Brid.) LangeON1.00 ± 0.022982Solanum lycopersicum0.64 ± 0.057
Sanionia uncinata (Hedw.) LoeskeMB0.37 ± 0.007358Raphanus sativus1.53 ± 0.023
Aulacomniaceae
Aulacomnium androgynum (Hedw.) Schwägr.ON0.34 ± 0.007336Raphanus sativus0.64 ± 0.076*
Brachytheciaceae
Brachythecium acuminatum (Hedw.) AustinON1.02 ± 0.022999Glycine max0.54 ± 0.045*
Brachythecium salebrosum (Hoffm. ex F.Weber and D.Mohr) Schimp.BC0.55 ± 0.004534Glycine max1.01 ± 0.037
Brachythecium salebrosum (Hoffm. ex F.Weber and D.Mohr) Schimp.ON0.97 ± 0.057952Glycine max0.14 ± 0.018*
Brachythecium velutinum (Hedw.) Schimp.ON0.46 ± 0.004§449Raphanus sativus0.51 ± 0.071*
Cirriphyllum piliferum (Hedw.) GroutMB1.04 ± 0.0091021Glycine max0.63 ± 0.056
Eurhynchium pulchellum (Hedw.) Jenn.ON0.52 ± 0.024507Raphanus sativus0.27 ± 0.044*
Homalothecium aeneum (Mitt.) E. Lawton BC0.26 ± 0.006257Glycine max1.63 ± 0.114
Pohlia wahlenbergii (F. Weber and D. Mohr) A.L. AndrewsON0.49 ± 0.006481Raphanus sativus1.13 ± 0.125*
Bruchiaceae
Trematodon ambiguus (Hedw.) Hornsch.ON0.39 ± 0.003384Raphanus sativus0.51 ± 0.055*
Climaciaceae
Climacium dendroides (Hedw.) F. Weber and D.MohrON1.00 ± 0.041983Glycine max1.48 ± 0.029*
Dicranaceae
Dichodontium pellucidum (Hedw.) Schimp.MB0.34 ± 0.005329Raphanus sativus0.42 ± 0.017
Dicranoweisia cirrata (Hedw.) Lindb.BC0.25 ± 0.001243Raphanus sativus0.57 ± 0.016
Dicranum condensatum Hedw.ON0.81 ± 0.026795Raphanus sativus0.87 ± 0.072*
Dicranum flagellare Hedw.ON0.57 ± 0.018557Glycine max0.50 ± 0.015*
Dicranum fuscescens TurnerON0.65 ± 0.017639Glycine max0.57 ± 0.087*
Dicranum fuscescens TurnerBC0.74 ± 0.014728Raphanus sativus0.44 ± 0.010
Dicranum groenlandicum Brid.MB0.60 ± 0.013585Raphanus sativusN/A
Dicranum montanum Hedw.ON0.52 ± 0.010507Raphanus sativus0.52 ± 0.029*
Dicranum polysetum Sw.ON0.78 ± 0.027758Raphanus sativus1.11 ± 0.030*
Dicranum scoparium Hedw.ON0.38 ± 0.010375Solanum lycopersicum0.98 ± 0.048*
Dicranum scoparium Hedw.BC0.72 ± 0.013709Raphanus sativus1.22 ± 0.014
Dicranum spurium Hedw.MB0.35 ± 0.004338Raphanus sativus0.59 ± 0.029
Ditrichaceae
Ceratodon purpureus (Hedw.) Brid.ON0.47 ± 0.004456Raphanus sativus0.51 ± 0.060*
Ditrichum lineare (Sw.) Lindb.MB0.35 ± 0.003343Raphanus sativus0.32 ± 0.026
Fissidentaceae
Fissidens taxifolius Hedw.ON0.32 ± 0.001§313Raphanus sativus0.40 ± 0.039*
Hedwigiaceae
Hedwigia ciliata (Hedw.) P.Beauv.ON0.30 ± 0.003§291Raphanus sativus0.34 ± 0.030*
Hylocomiaceae
Hylocomium splendens (Hedw.) Schimp.ON0.48 ± 0.003471Raphanus sativus0.53 ± 0.165*
Pleurozium schreberi (Willd. Ex Brid.) Mitt.ON0.83 ± 0.039809Raphanus sativus0.35 ± 0.079*
Pleurozium schreberi (Willd. Ex Brid.) Mitt.MB0.43 ± 0.008418Raphanus sativus0.74 ± 0.028
Rhytidiadelphus triquetrus (Hedw.) Warnst.ON0.57 ± 0.020555Glycine max0.52 ± 0.036*
Hypnaceae
Callicladium haldanianum (Grev.) H.A. CrumON0.83 ± 0.023816Raphanus sativus0.69 ± 0.187*
Calliergonella lindbergii (Mitt.) HedenäsON0.40 ± 0.010389Raphanus sativus0.78 ± 0.236*
Hypnum curvifolium Hedw.ON0.59 ± 0.004580Glycine max1.30 ± 0.107*
Hypnum pallescens (Hedw.) P.Beauv.ON0.38 ± 0.011376Raphanus sativus0.96 ± 0.078*
Hypnum recurvatum (Lindb. and Arnell) Kindb.ON0.37 ± 0.007365Raphanus sativus0.34 ± 0.104*
Ptilium crista-castrensis (Hedw.) De Not.ON0.40 ± 0.010388Raphanus sativus0.27 ± 0.016*
Pylaisia polyantha (Hedw.) Schimp.ON0.41 ± 0.008399Raphanus sativus0.37 ± 0.054*
Lembophyllaceae
Isothecium cristatum (Hampe) H.Rob.BC0.44 ± 0.006427Raphanus sativus0.36 ± 0.021
Isothecium myosuroides Brid.BC0.53 ± 0.011518Raphanus sativusN/A
Leskeaceae
Claopodium crispifolium (Hook.) Renauld and CardotBC0.40 ± 0.000393Raphanus sativus0.81 ± 0.080
Haplocladium microphyllum (Hedw.) Broth.ON0.44 ± 0.011432Raphanus sativus0.41 ± 0.086*
Leucodontaceae
Antitrichia curtipendula (Timm ex Hedw.) Brid.BC0.52 ± 0.002507Solanum lycopersicum0.73 ± 0.017
Dendroalsia abietina (Hook.) E. Britton ex Broth.BC0.37 ± 0.004363Raphanus sativus0.67 ± 0.139
Mniaceae
Leucolepis acanthoneura (Schwägr.) Lindb.BC1.18 ± 0.0101155Solanum lycopersicum0.93 ± 0.062
Plagiomnium drummondii (Bruch and Schimp.) T.J. Kop.ON0.63 ± 0.004612Glycine max1.37 ± 0.054*
Plagiomnium medium (Bruch and Schimp.) T.J. Kop.ON0.97 ± 0.012949Glycine max1.21 ± 0.152*
Neckeraceae
Metaneckera menziesii (Drumm.) SteereBC0.44 ± 0.004427Raphanus sativus1.13 ± 0.129
Neckera douglasii Hook.BC0.51 ± 0.005498Raphanus sativus0.73 ± 0.074
Orthotrichaceae
Orthotrichum speciosum NeesON0.35 ± 0.009343Raphanus sativus0.30 ± 0.071*
Plagiotheciaceae
Plagiothecium denticulatum (Hedw.) Schimp.ON0.55 ± 0.014540Raphanus sativus1.05 ± 0.160*
Plagiothecium laetum Schimp.ON0.55 ± 0.000536Glycine max1.71 ± 0.062*
Polytrichaceae
Polytrichastrum formosum (Hedw.) G.L. Sm.BC0.67 ± 0.008655Raphanus sativus0.51 ± 0.065
Polytrichum commune Hedw.ON1.08 ± 0.0011056Zea mays0.33 ± 0.055*
Polytrichum juniperinum Hedw.ON0.46 ± 0.019455Raphanus sativus0.60 ± 0.060*
Sphagnaceae
Sphagnum recurvum P. Beauv.ON0.56 ± 0.012549Raphanus sativus0.00 ± 0.000*
Thuidiaceae
Cyrto-hypnum minutulum (Hedw.) W.Raphanus Buck & H.A. CrumON0.44 ± 0.002§435Raphanus sativus0.41 ± 0.025*
Thuidium delicatulum (Hedw.) Schimp.ON0.43 ± 0.000418Raphanus sativus0.91 ± 0.119*

§Value published in Bainard et al. (2010).

*Value published in Bainard and Newmaster (2010).

Table 1.

DNA content estimates for moss species collected at various locations in Canada (BC, British Columbia; MB, Manitoba; ON, Ontario). Taxa are classified according to the Taxonomic Name Resolution Service (http://tnrs.iplantcollaborative.org) and are arranged alphabetically by family. Genome size is reported as average 1C-value ± standard error of the mean in picograms (pg) as well as average Mbp (1 pg = 0.978 × 109 bp; Doležel et al., 2003). Degree of endopolyploidy is reported as the endoreduplication index (EI) ± s.e.m.

TaxonCollection locality1C-value ± s.e.m. (pg)1C-value (Mbp)StandardEI ± s.e.m.
Amblystegiaceae
Campylium chrysophyllum (Brid.) LangeON1.00 ± 0.022982Solanum lycopersicum0.64 ± 0.057
Sanionia uncinata (Hedw.) LoeskeMB0.37 ± 0.007358Raphanus sativus1.53 ± 0.023
Aulacomniaceae
Aulacomnium androgynum (Hedw.) Schwägr.ON0.34 ± 0.007336Raphanus sativus0.64 ± 0.076*
Brachytheciaceae
Brachythecium acuminatum (Hedw.) AustinON1.02 ± 0.022999Glycine max0.54 ± 0.045*
Brachythecium salebrosum (Hoffm. ex F.Weber and D.Mohr) Schimp.BC0.55 ± 0.004534Glycine max1.01 ± 0.037
Brachythecium salebrosum (Hoffm. ex F.Weber and D.Mohr) Schimp.ON0.97 ± 0.057952Glycine max0.14 ± 0.018*
Brachythecium velutinum (Hedw.) Schimp.ON0.46 ± 0.004§449Raphanus sativus0.51 ± 0.071*
Cirriphyllum piliferum (Hedw.) GroutMB1.04 ± 0.0091021Glycine max0.63 ± 0.056
Eurhynchium pulchellum (Hedw.) Jenn.ON0.52 ± 0.024507Raphanus sativus0.27 ± 0.044*
Homalothecium aeneum (Mitt.) E. Lawton BC0.26 ± 0.006257Glycine max1.63 ± 0.114
Pohlia wahlenbergii (F. Weber and D. Mohr) A.L. AndrewsON0.49 ± 0.006481Raphanus sativus1.13 ± 0.125*
Bruchiaceae
Trematodon ambiguus (Hedw.) Hornsch.ON0.39 ± 0.003384Raphanus sativus0.51 ± 0.055*
Climaciaceae
Climacium dendroides (Hedw.) F. Weber and D.MohrON1.00 ± 0.041983Glycine max1.48 ± 0.029*
Dicranaceae
Dichodontium pellucidum (Hedw.) Schimp.MB0.34 ± 0.005329Raphanus sativus0.42 ± 0.017
Dicranoweisia cirrata (Hedw.) Lindb.BC0.25 ± 0.001243Raphanus sativus0.57 ± 0.016
Dicranum condensatum Hedw.ON0.81 ± 0.026795Raphanus sativus0.87 ± 0.072*
Dicranum flagellare Hedw.ON0.57 ± 0.018557Glycine max0.50 ± 0.015*
Dicranum fuscescens TurnerON0.65 ± 0.017639Glycine max0.57 ± 0.087*
Dicranum fuscescens TurnerBC0.74 ± 0.014728Raphanus sativus0.44 ± 0.010
Dicranum groenlandicum Brid.MB0.60 ± 0.013585Raphanus sativusN/A
Dicranum montanum Hedw.ON0.52 ± 0.010507Raphanus sativus0.52 ± 0.029*
Dicranum polysetum Sw.ON0.78 ± 0.027758Raphanus sativus1.11 ± 0.030*
Dicranum scoparium Hedw.ON0.38 ± 0.010375Solanum lycopersicum0.98 ± 0.048*
Dicranum scoparium Hedw.BC0.72 ± 0.013709Raphanus sativus1.22 ± 0.014
Dicranum spurium Hedw.MB0.35 ± 0.004338Raphanus sativus0.59 ± 0.029
Ditrichaceae
Ceratodon purpureus (Hedw.) Brid.ON0.47 ± 0.004456Raphanus sativus0.51 ± 0.060*
Ditrichum lineare (Sw.) Lindb.MB0.35 ± 0.003343Raphanus sativus0.32 ± 0.026
Fissidentaceae
Fissidens taxifolius Hedw.ON0.32 ± 0.001§313Raphanus sativus0.40 ± 0.039*
Hedwigiaceae
Hedwigia ciliata (Hedw.) P.Beauv.ON0.30 ± 0.003§291Raphanus sativus0.34 ± 0.030*
Hylocomiaceae
Hylocomium splendens (Hedw.) Schimp.ON0.48 ± 0.003471Raphanus sativus0.53 ± 0.165*
Pleurozium schreberi (Willd. Ex Brid.) Mitt.ON0.83 ± 0.039809Raphanus sativus0.35 ± 0.079*
Pleurozium schreberi (Willd. Ex Brid.) Mitt.MB0.43 ± 0.008418Raphanus sativus0.74 ± 0.028
Rhytidiadelphus triquetrus (Hedw.) Warnst.ON0.57 ± 0.020555Glycine max0.52 ± 0.036*
Hypnaceae
Callicladium haldanianum (Grev.) H.A. CrumON0.83 ± 0.023816Raphanus sativus0.69 ± 0.187*
Calliergonella lindbergii (Mitt.) HedenäsON0.40 ± 0.010389Raphanus sativus0.78 ± 0.236*
Hypnum curvifolium Hedw.ON0.59 ± 0.004580Glycine max1.30 ± 0.107*
Hypnum pallescens (Hedw.) P.Beauv.ON0.38 ± 0.011376Raphanus sativus0.96 ± 0.078*
Hypnum recurvatum (Lindb. and Arnell) Kindb.ON0.37 ± 0.007365Raphanus sativus0.34 ± 0.104*
Ptilium crista-castrensis (Hedw.) De Not.ON0.40 ± 0.010388Raphanus sativus0.27 ± 0.016*
Pylaisia polyantha (Hedw.) Schimp.ON0.41 ± 0.008399Raphanus sativus0.37 ± 0.054*
Lembophyllaceae
Isothecium cristatum (Hampe) H.Rob.BC0.44 ± 0.006427Raphanus sativus0.36 ± 0.021
Isothecium myosuroides Brid.BC0.53 ± 0.011518Raphanus sativusN/A
Leskeaceae
Claopodium crispifolium (Hook.) Renauld and CardotBC0.40 ± 0.000393Raphanus sativus0.81 ± 0.080
Haplocladium microphyllum (Hedw.) Broth.ON0.44 ± 0.011432Raphanus sativus0.41 ± 0.086*
Leucodontaceae
Antitrichia curtipendula (Timm ex Hedw.) Brid.BC0.52 ± 0.002507Solanum lycopersicum0.73 ± 0.017
Dendroalsia abietina (Hook.) E. Britton ex Broth.BC0.37 ± 0.004363Raphanus sativus0.67 ± 0.139
Mniaceae
Leucolepis acanthoneura (Schwägr.) Lindb.BC1.18 ± 0.0101155Solanum lycopersicum0.93 ± 0.062
Plagiomnium drummondii (Bruch and Schimp.) T.J. Kop.ON0.63 ± 0.004612Glycine max1.37 ± 0.054*
Plagiomnium medium (Bruch and Schimp.) T.J. Kop.ON0.97 ± 0.012949Glycine max1.21 ± 0.152*
Neckeraceae
Metaneckera menziesii (Drumm.) SteereBC0.44 ± 0.004427Raphanus sativus1.13 ± 0.129
Neckera douglasii Hook.BC0.51 ± 0.005498Raphanus sativus0.73 ± 0.074
Orthotrichaceae
Orthotrichum speciosum NeesON0.35 ± 0.009343Raphanus sativus0.30 ± 0.071*
Plagiotheciaceae
Plagiothecium denticulatum (Hedw.) Schimp.ON0.55 ± 0.014540Raphanus sativus1.05 ± 0.160*
Plagiothecium laetum Schimp.ON0.55 ± 0.000536Glycine max1.71 ± 0.062*
Polytrichaceae
Polytrichastrum formosum (Hedw.) G.L. Sm.BC0.67 ± 0.008655Raphanus sativus0.51 ± 0.065
Polytrichum commune Hedw.ON1.08 ± 0.0011056Zea mays0.33 ± 0.055*
Polytrichum juniperinum Hedw.ON0.46 ± 0.019455Raphanus sativus0.60 ± 0.060*
Sphagnaceae
Sphagnum recurvum P. Beauv.ON0.56 ± 0.012549Raphanus sativus0.00 ± 0.000*
Thuidiaceae
Cyrto-hypnum minutulum (Hedw.) W.Raphanus Buck & H.A. CrumON0.44 ± 0.002§435Raphanus sativus0.41 ± 0.025*
Thuidium delicatulum (Hedw.) Schimp.ON0.43 ± 0.000418Raphanus sativus0.91 ± 0.119*
TaxonCollection locality1C-value ± s.e.m. (pg)1C-value (Mbp)StandardEI ± s.e.m.
Amblystegiaceae
Campylium chrysophyllum (Brid.) LangeON1.00 ± 0.022982Solanum lycopersicum0.64 ± 0.057
Sanionia uncinata (Hedw.) LoeskeMB0.37 ± 0.007358Raphanus sativus1.53 ± 0.023
Aulacomniaceae
Aulacomnium androgynum (Hedw.) Schwägr.ON0.34 ± 0.007336Raphanus sativus0.64 ± 0.076*
Brachytheciaceae
Brachythecium acuminatum (Hedw.) AustinON1.02 ± 0.022999Glycine max0.54 ± 0.045*
Brachythecium salebrosum (Hoffm. ex F.Weber and D.Mohr) Schimp.BC0.55 ± 0.004534Glycine max1.01 ± 0.037
Brachythecium salebrosum (Hoffm. ex F.Weber and D.Mohr) Schimp.ON0.97 ± 0.057952Glycine max0.14 ± 0.018*
Brachythecium velutinum (Hedw.) Schimp.ON0.46 ± 0.004§449Raphanus sativus0.51 ± 0.071*
Cirriphyllum piliferum (Hedw.) GroutMB1.04 ± 0.0091021Glycine max0.63 ± 0.056
Eurhynchium pulchellum (Hedw.) Jenn.ON0.52 ± 0.024507Raphanus sativus0.27 ± 0.044*
Homalothecium aeneum (Mitt.) E. Lawton BC0.26 ± 0.006257Glycine max1.63 ± 0.114
Pohlia wahlenbergii (F. Weber and D. Mohr) A.L. AndrewsON0.49 ± 0.006481Raphanus sativus1.13 ± 0.125*
Bruchiaceae
Trematodon ambiguus (Hedw.) Hornsch.ON0.39 ± 0.003384Raphanus sativus0.51 ± 0.055*
Climaciaceae
Climacium dendroides (Hedw.) F. Weber and D.MohrON1.00 ± 0.041983Glycine max1.48 ± 0.029*
Dicranaceae
Dichodontium pellucidum (Hedw.) Schimp.MB0.34 ± 0.005329Raphanus sativus0.42 ± 0.017
Dicranoweisia cirrata (Hedw.) Lindb.BC0.25 ± 0.001243Raphanus sativus0.57 ± 0.016
Dicranum condensatum Hedw.ON0.81 ± 0.026795Raphanus sativus0.87 ± 0.072*
Dicranum flagellare Hedw.ON0.57 ± 0.018557Glycine max0.50 ± 0.015*
Dicranum fuscescens TurnerON0.65 ± 0.017639Glycine max0.57 ± 0.087*
Dicranum fuscescens TurnerBC0.74 ± 0.014728Raphanus sativus0.44 ± 0.010
Dicranum groenlandicum Brid.MB0.60 ± 0.013585Raphanus sativusN/A
Dicranum montanum Hedw.ON0.52 ± 0.010507Raphanus sativus0.52 ± 0.029*
Dicranum polysetum Sw.ON0.78 ± 0.027758Raphanus sativus1.11 ± 0.030*
Dicranum scoparium Hedw.ON0.38 ± 0.010375Solanum lycopersicum0.98 ± 0.048*
Dicranum scoparium Hedw.BC0.72 ± 0.013709Raphanus sativus1.22 ± 0.014
Dicranum spurium Hedw.MB0.35 ± 0.004338Raphanus sativus0.59 ± 0.029
Ditrichaceae
Ceratodon purpureus (Hedw.) Brid.ON0.47 ± 0.004456Raphanus sativus0.51 ± 0.060*
Ditrichum lineare (Sw.) Lindb.MB0.35 ± 0.003343Raphanus sativus0.32 ± 0.026
Fissidentaceae
Fissidens taxifolius Hedw.ON0.32 ± 0.001§313Raphanus sativus0.40 ± 0.039*
Hedwigiaceae
Hedwigia ciliata (Hedw.) P.Beauv.ON0.30 ± 0.003§291Raphanus sativus0.34 ± 0.030*
Hylocomiaceae
Hylocomium splendens (Hedw.) Schimp.ON0.48 ± 0.003471Raphanus sativus0.53 ± 0.165*
Pleurozium schreberi (Willd. Ex Brid.) Mitt.ON0.83 ± 0.039809Raphanus sativus0.35 ± 0.079*
Pleurozium schreberi (Willd. Ex Brid.) Mitt.MB0.43 ± 0.008418Raphanus sativus0.74 ± 0.028
Rhytidiadelphus triquetrus (Hedw.) Warnst.ON0.57 ± 0.020555Glycine max0.52 ± 0.036*
Hypnaceae
Callicladium haldanianum (Grev.) H.A. CrumON0.83 ± 0.023816Raphanus sativus0.69 ± 0.187*
Calliergonella lindbergii (Mitt.) HedenäsON0.40 ± 0.010389Raphanus sativus0.78 ± 0.236*
Hypnum curvifolium Hedw.ON0.59 ± 0.004580Glycine max1.30 ± 0.107*
Hypnum pallescens (Hedw.) P.Beauv.ON0.38 ± 0.011376Raphanus sativus0.96 ± 0.078*
Hypnum recurvatum (Lindb. and Arnell) Kindb.ON0.37 ± 0.007365Raphanus sativus0.34 ± 0.104*
Ptilium crista-castrensis (Hedw.) De Not.ON0.40 ± 0.010388Raphanus sativus0.27 ± 0.016*
Pylaisia polyantha (Hedw.) Schimp.ON0.41 ± 0.008399Raphanus sativus0.37 ± 0.054*
Lembophyllaceae
Isothecium cristatum (Hampe) H.Rob.BC0.44 ± 0.006427Raphanus sativus0.36 ± 0.021
Isothecium myosuroides Brid.BC0.53 ± 0.011518Raphanus sativusN/A
Leskeaceae
Claopodium crispifolium (Hook.) Renauld and CardotBC0.40 ± 0.000393Raphanus sativus0.81 ± 0.080
Haplocladium microphyllum (Hedw.) Broth.ON0.44 ± 0.011432Raphanus sativus0.41 ± 0.086*
Leucodontaceae
Antitrichia curtipendula (Timm ex Hedw.) Brid.BC0.52 ± 0.002507Solanum lycopersicum0.73 ± 0.017
Dendroalsia abietina (Hook.) E. Britton ex Broth.BC0.37 ± 0.004363Raphanus sativus0.67 ± 0.139
Mniaceae
Leucolepis acanthoneura (Schwägr.) Lindb.BC1.18 ± 0.0101155Solanum lycopersicum0.93 ± 0.062
Plagiomnium drummondii (Bruch and Schimp.) T.J. Kop.ON0.63 ± 0.004612Glycine max1.37 ± 0.054*
Plagiomnium medium (Bruch and Schimp.) T.J. Kop.ON0.97 ± 0.012949Glycine max1.21 ± 0.152*
Neckeraceae
Metaneckera menziesii (Drumm.) SteereBC0.44 ± 0.004427Raphanus sativus1.13 ± 0.129
Neckera douglasii Hook.BC0.51 ± 0.005498Raphanus sativus0.73 ± 0.074
Orthotrichaceae
Orthotrichum speciosum NeesON0.35 ± 0.009343Raphanus sativus0.30 ± 0.071*
Plagiotheciaceae
Plagiothecium denticulatum (Hedw.) Schimp.ON0.55 ± 0.014540Raphanus sativus1.05 ± 0.160*
Plagiothecium laetum Schimp.ON0.55 ± 0.000536Glycine max1.71 ± 0.062*
Polytrichaceae
Polytrichastrum formosum (Hedw.) G.L. Sm.BC0.67 ± 0.008655Raphanus sativus0.51 ± 0.065
Polytrichum commune Hedw.ON1.08 ± 0.0011056Zea mays0.33 ± 0.055*
Polytrichum juniperinum Hedw.ON0.46 ± 0.019455Raphanus sativus0.60 ± 0.060*
Sphagnaceae
Sphagnum recurvum P. Beauv.ON0.56 ± 0.012549Raphanus sativus0.00 ± 0.000*
Thuidiaceae
Cyrto-hypnum minutulum (Hedw.) W.Raphanus Buck & H.A. CrumON0.44 ± 0.002§435Raphanus sativus0.41 ± 0.025*
Thuidium delicatulum (Hedw.) Schimp.ON0.43 ± 0.000418Raphanus sativus0.91 ± 0.119*

§Value published in Bainard et al. (2010).

*Value published in Bainard and Newmaster (2010).

Flow cytometric analyses

To estimate genome size, methods followed Galbraith et al. (1983) as modified by Bainard et al. (2010). Seeds for standards with known DNA content were acquired from the Laboratory of Molecular Cytogenetics and Cytometry, Olomouc, Czech Republic, and the standards were grown in the University of Guelph Phytotron. The standards used in this study included: Raphanus sativus L. ‘Saxa’, 2C value = 1.11 pg (Doležel et al., 1998), Solanum lycopersicum L. ‘Stupicke polni tyckove rane’, 2C value = 1.96 pg (Doležel et al., 1992), Glycine max Merr. ‘Polanka’, 2C value = 2.50 pg (Doležel et al., 1994) and Zea mays L. ‘CE-777’, 2C value = 5.43 pg (Lysák and Doležel, 1998). Approximately 10 mg of air-dried moss gametophyte tissue (1C) was co-chopped with fresh leaf tissue (2C) from an appropriate plant standard (the fluorescence intensity of the standard G1 nuclei was within a 4-fold range of the sample G1 nuclei). Tissues were chopped in 1.2 mL of cold LB01 lysis buffer (Doležel et al., 1989), in the presence of 150 μg mL−1 propidium iodide (PI, Sigma) and 50 μg mL−1 RNase A (Sigma). The higher than average concentration of 150 μg mL−1 PI was used according to Bainard et al. (2010), where this concentration was found to be saturating (i.e. at lower concentrations the genome size was underestimated). The resulting homogenate of leaf tissues and staining solution was filtered through a 30-μm mesh (CellTrics, Sysmex) and incubated on ice for 20–40 min. For each sample, over 1000 nuclei were obtained, but in a few cases where tissue amounts were minimal fewer than 1000 nuclei were obtained per flow accession. Three independent replicates of the same moss specimen were analysed on separate days and the estimates were averaged. Where the same moss taxon was collected from distinct localities, separate estimates were obtained. To estimate genome size, the 1C nuclei of the moss (in G1 phase of the cell cycle) were compared with the 2C nuclei (G1) of the standard. Genome size was calculated by determining the ratio between the mean fluorescence intensity of the moss 1C peak and the standard 2C peak, and multiplying by the known DNA content of the standard.

To determine the degree of endopolyploidy for each moss sample, preparation methods followed those given above for genome size. (Although it is recognized that endopolyploidy can vary between different plant organs and tissues, because of the small size of mosses it is very difficult to acquire enough tissue from only leaf material, so samples included a mix of stem and leaf tissue.) If the moss nuclei could be easily counted in each endopolyploid peak from samples that were co-chopped with a standard, those replicates were used; however, in most cases an additional three replicates were prepared of the moss tissue alone, and run on separate days. On average, over 4000 nuclei were analysed over all peaks, and the number of nuclei in each ploidy level was determined. There is a small risk of misinterpreting the 2C peak as the 1C peak if there are very few nuclei in the 1C peak [as occurred in cultured samples of Physcomitrella patens (Reski et al., 1994; Schween et al., 2003)], therefore high nuclei counts were desired and all flow histograms were carefully examined. The endoreduplication index (EI), or cycle value, reports the average number of endoreduplication cycles undergone by the nuclei measured, and is calculated as:

where n is the number of nuclei in each ploidy level (Barow and Jovtchev, 2007). As moss gametophyte (1C) tissue was analysed, one endoreduplication cycle results in nuclei at the 2C level. EI values <0.1 were not considered endopolyploid (Barow and Meister, 2003; Jovtchev et al., 2006). This threshold can account for the small number of nuclei at higher ploidies that are not actually endopolyploid, but rather are due to nuclei in the G2 phase of the cell cycle or to doublet formation (nuclei stuck together).

Flow cytometric analyses were carried out on a Partec CyFlow SL (Partec, Münster, Germany) equipped with a blue solid-state laser tuned at 20 mW and operating at 488 nm. The flow cytometer was calibrated using 3-µm calibration beads (Partec, Münster, Germany) before each use. For each sample, the following parameters were observed: fluorescence intensity at 590 ± 25 nm (‘FL2’, measured on a linear scale to calculate genome size), fluorescence intensity at 630 nm (‘FL3’, measured on a log scale to calculate degree of endopolyploidy), as well as forward scatter and side scatter. In order to calculate EI and genome size from the same sample, both fluorescence parameters were measured as genome size must be measured on a linear scale, while EI could only be observed on a log scale. As PI has an emission wavelength of 617 nm (Doležel et al., 2007), both FL2 and FL3 parameters accurately report the relative fluorescence. Histograms were analysed using FloMax Software (version 2.52; Partec). The fluorescence parameters were observed alone and in combined scattergrams including: fluorescence versus side scatter and fluorescence versus forward scatter. Polygon gates were drawn on these scattergrams to separate the nuclei of interest from debris particles.

Phylogenetic analyses

Species names were standardized and the families identified for all taxa with genome size estimates analysed in this study, including both newly generated data (Table 1) and previously published values (Supplementary Data Table S2) using the online taxonomic name resolution service (Boyle et al., 2013; The Taxonomic Name Resolution Service, accessed 22 Jan 2018). Sequence data were downloaded from the NCBI database (NCBI Resource Coordinators, 2016) using SUMAC 2.22 (Freyman, 2015), which enables a bulk download of data from all species in a family. The minimum number of required sequences per cluster was set to 500 and all other settings were as default. Using these criteria, six clusters corresponding to the gene regions nad5, rbcL, trnS-rps4-trnT-trnL-trnF, trnL-trnF, 18S-ITS1-5.8S-ITS2-26S and ITS2-26S were identified. Due to the large amount of overlap between the trnS-trnF and trnL-trnF clusters, only the latter cluster was retained, with the former removed from subsequent analyses. The 18S-ITS1-5.8S-ITS2-26S and ITS2-26S clusters were combined with sequences added to the 18S-ITS1-5.8S-ITS2-26S cluster for any species missing data for this gene region from the ITS2-26S cluster. All sequences with tenuous species identifications indicated by ‘cf.’ were removed from subsequent analyses.

Sequences were clustered using the UCLUST algorithm (Edgar, 2010) in SUMAC and each of the four gene regions (nad5; rbcL; trnL-trnF; 18S-ITS1-5.8S-ITS2-26S) were independently aligned using ClustalW 1.82 (Larkin et al., 2007), then trimmed and concatenated in Geneious 9.1.8 (Kearse et al., 2012). Data partitions and models were chosen using the corrected Akaike information criterion (AICc) and the search scheme greedy in PartitionFinder2 2.1.1 (Guindon et al., 2010; Lanfear et al., 2017). Analyses were performed using RAxML 8.2.10 (Stamatakis, 2014). Alignments, model selection and analyses were carried out via the CIPRES Science Gateway (Miller et al., 2010). The resulting maximum likelihood tree was rescaled in units of time using treePL (Smith and O’Meara, 2012), which implements the penalized likelihood dating method for large phylogenies (Sanderson, 2002). The rate-smoothing parameter was determined using the randomcv option, testing five values between 0.1 and 1000 separated by one order of magnitude using cross-validation and the χ2 test Additionally, the thorough option was used to iterate until convergence, and branch lengths were scaled with the root age set to 1. Trees were rooted with the genus Sphagnum as the outgroup. Alignments and tree files were uploaded to TreeBASE (submission ID 25488).

All analyses were carried out using R version 3.4.2 (R Core Team, 2017). When multiple genome size estimates were available for a given species from the new data or published data, the smallest (most conservative) estimate was used. Genome size and EI were independently mapped onto the pruned phylogenies using the ContMap function with default settings from the phytools package (Revell, 2012). Both datasets showed skewed distributions and thus were log10-transformed prior to analysis. Pagel’s λ (Pagel, 1999) was used to test for phylogenetic signal, since this analysis was the least affected by variation in species number in comparison with other indices (Münkemüller et al., 2012). Pagel’s λ was used to test for phylogenetic signal assuming Brownian motion by optimizing the value of λ using maximum likelihood with no constraints and comparing that with the likelihood of a model where λ was constrained to zero (no phylogenetic signal) using the phylosig function from the phytools package. In addition, a phylogenetically correct linear model (Felsenstein, 1985) was used to test for a relationship between genome size and degree of endopolyploidy in mosses. This analysis only used species with a 1C-value estimate and EI determined from the same tissue sample (reported in this study or Bainard and Newmaster, 2010). Phylogenetically independent contrasts were calculated for the 1C-value estimates and EI values independently using the pic function from the ape package (Paradis et al., 2004) and then a regression through the origin using the lm function was performed on these adjusted values.

RESULTS

DNA content in mosses

Genome size estimates were acquired for 60 moss samples, representing 56 species from 20 families (Table 1). Estimates for 33 species have not previously been reported in the literature, including representatives from two additional families, Bruchiaceae and Orthotrichaceae. Across the 60 estimates of genome size, 1C-values ranged from 0.25 pg (Dicranoweisia cirrata) to 1.18 pg (Leucolepis acanthoneura) (Table 1). Quality of the flow cytometry histograms was suitable, as the coefficients of variation ranged from 2.51 to 7.94 % (mean = 4.81 %) in the moss peak and from 2.27 to 7.77 % (mean = 3.45 %) in the standard peak. While lower coefficients of variation are often recommended (e.g. less than 3 % or 5 %) it is recognized that this can be difficult when dealing with very small nuclei that approach the resolution capacity of the flow cytometer (Voglmayr, 2007).

Four moss taxa were collected from two different locations in this study, and in all cases the genome sizes were different (Table 1). All samples listed in Table 1 were personally identified by the authors to decrease the likelihood of misidentification. In three of the species (Brachythecium salebrosum, Dicranum scoparium and Pleurozium schreberi) the samples differ by almost an exact doubling, which could be attributed to variation in ploidy. In addition, the two Dicranum fuscescens samples differ by ~13 % and this variation within a single morphologically identifiable species could be attributed to convergent evolution that is obscuring a cryptic species.

Additionally, 20 moss species estimated in this study (represented by 23 accessions) also have a 1C-value estimated by Voglmayr (2000) (Table 2). As Voglmayr (2000) estimated genome size using both Feulgen staining and PI flow cytometry, we only compared values that had been obtained using PI. When comparing variation in estimates between different populations of the same species in his study, Voglmayr (2000) suggested that a ratio lower than 1.15 (maximum/minimum) was indicative of low, if any, variation in C value. Differences between estimates up to 10 % have also been considered within the margin of error in previous genome size studies (Bennett and Smith, 1976; Bennett and Leitch, 2005). When comparing our estimates with those published in Voglmayr (2000), ten accessions have a ratiomax/min lower than 1.15 (Table 2), suggesting the estimates are equivalent. Five accessions had disparate genome size estimates that were close to double or triple those of each other, which might suggest polyploidization (Table 2). In the remaining comparisons, estimates from the present study were all higher than in Voglmayr (2000).

Table 2.

Comparison of estimates from the current study and Voglmayr (2000). Ratiomax/min measures the ratio of the higher value divided by the lower value. Bold values indicate ratiomax/min values lower than 1.15. All 1C-values from both studies were estimated using PI flow cytometry

Species1C-value (pg), this study1C-value (pg), Voglmayr (2000)Ratiomax/min
Aulacomnium androgynum0.340.261.32
Brachythecium salebrosum (BC)0.550.901.65
Brachythecium salebrosum (ON)0.970.901.08
Calliergonella lindbergii0.400.301.33
Campylium chrysophyllum1.000.362.79
Ceratodon purpureus0.470.391.20
Cirriphyllum piliferum1.040.432.43
Climacium dendroides1.000.462.18
Dicranum polysetum0.780.701.11
Dicranum scoparium (BC)0.720.731.01
Dicranum scoparium (ON)0.380.731.90
Fissidens taxifolius0.320.331.03
Hylocomium splendens0.480.391.23
Isothecium myosuroides0.530.451.18
Plagiothecium laetum0.550.411.34
Pleurozium schreberi (MB)0.430.761.78
Pleurozium schreberi (ON)0.830.761.09
Polytrichum commune1.080.47*2.30
Polytrichum juniperinum0.460.421.10
Ptilium crista-castrensis0.400.391.02
Pylaisia polyantha0.410.401.02
Rhytidiadelphus triquetrus0.570.521.09
Thuidium delicatulum0.430.391.11
Species1C-value (pg), this study1C-value (pg), Voglmayr (2000)Ratiomax/min
Aulacomnium androgynum0.340.261.32
Brachythecium salebrosum (BC)0.550.901.65
Brachythecium salebrosum (ON)0.970.901.08
Calliergonella lindbergii0.400.301.33
Campylium chrysophyllum1.000.362.79
Ceratodon purpureus0.470.391.20
Cirriphyllum piliferum1.040.432.43
Climacium dendroides1.000.462.18
Dicranum polysetum0.780.701.11
Dicranum scoparium (BC)0.720.731.01
Dicranum scoparium (ON)0.380.731.90
Fissidens taxifolius0.320.331.03
Hylocomium splendens0.480.391.23
Isothecium myosuroides0.530.451.18
Plagiothecium laetum0.550.411.34
Pleurozium schreberi (MB)0.430.761.78
Pleurozium schreberi (ON)0.830.761.09
Polytrichum commune1.080.47*2.30
Polytrichum juniperinum0.460.421.10
Ptilium crista-castrensis0.400.391.02
Pylaisia polyantha0.410.401.02
Rhytidiadelphus triquetrus0.570.521.09
Thuidium delicatulum0.430.391.11

*Renzaglia et al. (1995) also estimated genome size in P. commune with a 1C-value of 0.46 pg.

BC, British Columbia; MB, Manitoba; ON, Ontario.

Table 2.

Comparison of estimates from the current study and Voglmayr (2000). Ratiomax/min measures the ratio of the higher value divided by the lower value. Bold values indicate ratiomax/min values lower than 1.15. All 1C-values from both studies were estimated using PI flow cytometry

Species1C-value (pg), this study1C-value (pg), Voglmayr (2000)Ratiomax/min
Aulacomnium androgynum0.340.261.32
Brachythecium salebrosum (BC)0.550.901.65
Brachythecium salebrosum (ON)0.970.901.08
Calliergonella lindbergii0.400.301.33
Campylium chrysophyllum1.000.362.79
Ceratodon purpureus0.470.391.20
Cirriphyllum piliferum1.040.432.43
Climacium dendroides1.000.462.18
Dicranum polysetum0.780.701.11
Dicranum scoparium (BC)0.720.731.01
Dicranum scoparium (ON)0.380.731.90
Fissidens taxifolius0.320.331.03
Hylocomium splendens0.480.391.23
Isothecium myosuroides0.530.451.18
Plagiothecium laetum0.550.411.34
Pleurozium schreberi (MB)0.430.761.78
Pleurozium schreberi (ON)0.830.761.09
Polytrichum commune1.080.47*2.30
Polytrichum juniperinum0.460.421.10
Ptilium crista-castrensis0.400.391.02
Pylaisia polyantha0.410.401.02
Rhytidiadelphus triquetrus0.570.521.09
Thuidium delicatulum0.430.391.11
Species1C-value (pg), this study1C-value (pg), Voglmayr (2000)Ratiomax/min
Aulacomnium androgynum0.340.261.32
Brachythecium salebrosum (BC)0.550.901.65
Brachythecium salebrosum (ON)0.970.901.08
Calliergonella lindbergii0.400.301.33
Campylium chrysophyllum1.000.362.79
Ceratodon purpureus0.470.391.20
Cirriphyllum piliferum1.040.432.43
Climacium dendroides1.000.462.18
Dicranum polysetum0.780.701.11
Dicranum scoparium (BC)0.720.731.01
Dicranum scoparium (ON)0.380.731.90
Fissidens taxifolius0.320.331.03
Hylocomium splendens0.480.391.23
Isothecium myosuroides0.530.451.18
Plagiothecium laetum0.550.411.34
Pleurozium schreberi (MB)0.430.761.78
Pleurozium schreberi (ON)0.830.761.09
Polytrichum commune1.080.47*2.30
Polytrichum juniperinum0.460.421.10
Ptilium crista-castrensis0.400.391.02
Pylaisia polyantha0.410.401.02
Rhytidiadelphus triquetrus0.570.521.09
Thuidium delicatulum0.430.391.11

*Renzaglia et al. (1995) also estimated genome size in P. commune with a 1C-value of 0.46 pg.

BC, British Columbia; MB, Manitoba; ON, Ontario.

The degree of endopolyploidy was determined for an additional 20 moss samples not included in Bainard and Newmaster (2010) (Table 1). We were unable to determine an EI for two samples due to tissue shortages. All new samples had an EI well over 0.1, which is further evidence that endopolyploidy is prevalent across mosses, with the exception of Sphagnaceae. Over the 57 species that had endopolyploid nuclei, the average EI was 0.71 ± 0.39 (standard deviation); all samples had 2C and 4C nuclei present, and as high as 16C nuclei in some cases (see also Bainard and Newmaster, 2010).

Phylogenetic analyses

The combined matrix was 5790 bp long and contained 2214 taxa from 35 families, which represent 15 of the 31 taxonomic orders of mosses (Supplementary Data Table S3). Details for individual gene regions, including number of base pairs in the alignments, number of base pairs analysed, percent missing data, number of variable sites and number of parsimony-informative characters, are listed in Supplementary Data Table S4. Four partitions with the following models for each gene region were identified using PartitionFinder2 (nad5 = GTR+G; rbcL, trnL-trnF and 18S-ITS1-5.8S-ITS2-26S = GTR+I+G) and then subsequently analysed in RAxML using 1000 bootstrap replicates. Model parameters were allowed to vary freely between these partitions, but RAxML on the CIPRES portal only accommodates a single model and thus the most complex rate model (GTR+I+G), which was identified for three out of four loci, was used for each partition.

For the 2214 taxa dataset, the most likely tree (log-likelihood = −334771.733244) from a single run was determined (TreeBASE, submission ID 25488). This large tree was assembled in order to recover relationships consistent with other large-scale molecular phylogenies of mosses (Cox et al., 2010; Stech et al., 2013; Johnson et al., 2016). The tree was pruned to remove all species not present in the two continuous character datasets. The pruned tree included 173 of the species present in the genome size dataset (84 % of the species; Fig. 1) and 48 of the species in the EI dataset (89 % of the species; Figs 2 and 3), which accounts for species with data missing from the analysed matrix. Average 1C-values ranged from 0.17 to 2.05 across 173 species and the EI from 0 to 1.71 across 48 moss species. For species with multiple 1C-values from two independent analyses (Table 1, Supplementary Data Table S2), the smallest value was used as a conservative estimate of genome size. Species with more than one 1C-value that was approximately double the smallest value are indicated on the phylogeny with an asterisk as a potential within-species polyploidization event (Fig. 2).

Pruned phylogram of 173 species with the average 1C-values for each species plotted and the moss orders indicated with vertical bars. For species with multiple 1C-values, the smallest value was used as a conservative estimate of genome size.
Fig. 1.

Pruned phylogram of 173 species with the average 1C-values for each species plotted and the moss orders indicated with vertical bars. For species with multiple 1C-values, the smallest value was used as a conservative estimate of genome size.

Continuous character state mapping of the average 1C-values, ranging from 0.17 pg (red) to 2.05 pg (blue), onto a pruned ultrametric tree that includes 173 taxa using the ContMap function with default settings from the phytools package in R. For species with multiple 1C-values, the smallest value was used as a conservative estimate of genome size. Species with more than one 1C-value that was approximately double the smallest value are indicated on the phylogeny with a blue asterisk as a potential within-species polyploidization event.
Fig. 2.

Continuous character state mapping of the average 1C-values, ranging from 0.17 pg (red) to 2.05 pg (blue), onto a pruned ultrametric tree that includes 173 taxa using the ContMap function with default settings from the phytools package in R. For species with multiple 1C-values, the smallest value was used as a conservative estimate of genome size. Species with more than one 1C-value that was approximately double the smallest value are indicated on the phylogeny with a blue asterisk as a potential within-species polyploidization event.

Continuous character state mapping of the endoreduplication index (EI) ranging from 0 (red) to 1.71 (blue) on a pruned ultrametric tree that includes 48 taxa using the ContMap function with default settings from the phytools package in R (Revell, 2012; R Core Team, 2017).
Fig. 3.

Continuous character state mapping of the endoreduplication index (EI) ranging from 0 (red) to 1.71 (blue) on a pruned ultrametric tree that includes 48 taxa using the ContMap function with default settings from the phytools package in R (Revell, 2012; R Core Team, 2017).

The ancestral character state mapping indicates multiple evolutionary transitions from a very small ancestral genome size to slightly larger genome sizes in some derived lineages (Figs 1 and 2). There are at least four independent transitions to slightly larger genome sizes within the Sphagnales, with potentially one reversal to a smaller genome size in Sphagnum magellanicum. There is one transition in the Polytrichales and a gradual increase to slightly larger genome sizes in the Dicranales (Fig. 2). Members of the Bryales have the largest moss genome sizes, which appears to represent a single transition. This lineage also appears to contain two reversals to smaller genome sizes in Plagiomnium + Pohlia, and Rosulabryum (Fig. 2). On the whole, the Hypnales contain relatively small genomes with the exception of two transitions to slightly larger genome sizes in Brachythecium and Callicladium. The only member sampled from the Hookeriales, Hookeria lucens, has a genome size that is nearly double that of members of the closely related Hypnales. Overall, this analysis reconstructs ten independent increases in genome size across the moss phylogeny and the potential for three reversals (Fig. 2), which calls into question the idea that genome size evolution is unidirectional and does not support the genetic obesity hypothesis (Bennetzen and Kellogg, 1997) for mosses.

Comparative phylogenetic analyses were calculated independently for genome size and EI across the pruned trees. We optimized the value of Pagel’s λ using maximum likelihood with no constraints and compared that with the likelihood of a model where λ was constrained to zero (no phylogenetic signal). Based on likelihood ratio tests, significant phylogenetic signal was detected for genome size (λ = 0.56, logL = 119.92, logL0 = 95.17, P = 1.98e−12), whereas significant phylogenetic signal was not detected for the EI (λ = 6.62e−5, logL = 4.75, logL0 = 4.75, P = 1) across the pruned phylogenies.

The most likely tree for the full dataset was then pruned to include only the taxa for which 1C-values and EI values were available. This resulted in a tree that included 48 moss species. Using the phylogenetically corrected values, which take into account the distance between species, genome size and EI were found to be negatively correlated; however, this relationship was not statistically significant (F1,46 = 1.39, r= −0.31, adjusted r2 = 0.008, P = 0.245).

Overall the vast majority of the mosses sampled have detectable levels of endoreduplication with the exception of the single member of the genus Sphagnum included in this study (Fig. 3). Members of the genera Ditrichum, Orthotrichum, Hedwigia, Hypnum and Ptilidium have lower levels of endoreduplication relative to the ancestral condition, while Plagiomnium, Sanionia and Plagiothecium have higher levels (Fig. 3).

DISCUSSION

This study analysed the most comprehensive dataset of 1C-values and endopolyploidy data assembled to date from a broad phylogenetic sample of moss species. These data do not support the genetic obesity hypothesis (Bennetzen and Kellogg, 1997) for mosses, which postulates that genome size evolution is unidirectional, resulting in species with larger genomes occupying derived positions within the phylogeny. We determined that there is phylogenetic signal for genome size across mosses, which is the tendency of closely related species to resemble each other more than a random set of species from the same tree (Harvey and Pagel, 1991); however, no phylogenetic signal was detected for endopolyploidy. We also did not find a significant correlation between endopolyploidy and genome size across mosses (Nagl, 1978; De Rocher et al., 1990; Barow and Meister, 2003; Bainard et al., 2012), using phylogenetic comparative methods that account for the non-independence of data collected across species (Felsenstein, 1985).

Variation in genome size

Relative to other land plant lineages (Bennett and Leitch, 2012), the diversity of genome size estimates we observed across mosses is significantly smaller (Figs 1 and 2, Table 1, Supplementary Data Table S2), which is in line with previous findings (Reski et al., 1994; Renzaglia et al., 1995; Lamparter et al., 1998; Temsch et al., 1998; Zouhair and Lecocq, 1998; Voglmayr, 2000; Schween et al., 2003; Melosik et al., 2005; Bainard et al., 2010). Thus far, no moss genomes have been found that are larger than 2004 Mbp (Mnium marginatum; Voglmayr, 2000), and in the present study only three species had genomes over 1000 Mbp (Cirriphyllum piliferum, Leucolepis acanthoneura and Polytrichum commune; Table 1). This is similar to hornworts, where all genome size estimates to date are under 500 Mbp (Bainard and Villarreal, 2013) but is in contrast to the liverworts which have many representatives with small genomes, but also several species with 1C-values over 1000 Mbp and one species over 20 000 Mbp (Phyllothallia fuegiana; Bainard et al., 2013). Despite the sister relationship between the moss and liverwort lineages (Puttick et al., 2018; Renzaglia et al., 2018), it appears that the larger genome condition has arisen independently within the liverwort clade and is not a feature shared with mosses. Within mosses, some orders and families demonstrate slightly larger genome sizes compared with others (Fig. 1). For example, the Brachytheciaceae and Mniaceae, which are both in the Bryales, contain a number of species with relatively larger genome sizes, including the species with the largest moss genome size, Mnium marginatum. The Bryales appear to have a considerable number of polyploid occurrences within the order based on chromosome sizes (Fritsch, 1991), which may contribute to the larger genome sizes. The single member of the Hookeriales included in this study also has a slightly larger genome (Hookeria lucens, 1.61 pg; Figs 1 and 2), however, additional samples are needed to confirm this observation throughout the order.

Though the majority of genome size estimates from the same species were equivalent, we also found evidence of intraspecific variation in 1C-values, both within this study and in comparison with previous estimates (Tables 1 and 2). Species that include 1C-values that are approximately double each other may be due to polyploidy (noted with an asterisk in Fig. 2), which is common in mosses, and is thought to occur in as many as 14.3 % of moss species (Såstad, 2005). Once a polyploidization event has occurred (potentially through unreduced spore production or hybridization), a population of diploid gametophytes can be maintained via fragmentation or other forms of asexual reproduction. Aneuploidy, which is a change in chromosome number by less than a complete chromosome set, may also explain intraspecific variation in 1C-values and is suggested to play a major role in bryophyte evolution (Newton, 1984). However, the wide variation in chromosome counts for a single species of mosses (Fritsch, 1991) means that chromosome numbers must be determined from the same sample as the genome size estimates, which could not be determined post hoc for the genome sizes compiled from the literature in this study. It is notable that in two of the mosses analysed here that show possible ploidy variation, Campylium chrysophyllum and Polytrichum commune (Fig. 2), Fritsch (1991) also reports chromosome counts in some accessions that are double that of the rest.

Other variations in the genome size estimates between the present study and Voglmayr (2000) are possibly due to differences in flow cytometry methodology. Specifically, the use of higher PI concentration (150 versus 60 μg mL−1) has been shown to result in higher DNA content estimates (Bainard et al., 2010). All of the estimates that were determined to be different between the present study and Voglmayr (2000), as based on the criterion of a ratiomax/min >1.15, were found to be higher here than those in Voglmayr (2000), excluding differences attributable to a potential variation in ploidy. Voglmayr (2000) also used Baranyi’s buffer, which has a chemical composition different from the LB01 buffer and was found to produce slightly higher 1C-value estimates than LB01 (Bainard et al., 2010).

Across plants, genome size is strongly correlated with the proportion of transposable elements in the genome (Ågren and Wright, 2015). Genomic research on the model moss Physcomitrella patens found that, similar to many other plants, transposable elements make up a considerable portion of the P. patens genome, with ~50 % of the genome consisting of LTR retrotransposons (Rensing et al., 2008). In P. patens, greater accumulation of repetitive DNA may be limited by extremely efficient homologous recombination (Reski, 1998; Schween et al., 2003). Across mosses, high amounts of asexual reproduction might also play a role in the maintenance of a small genome, as transposable elements are unlikely to be maintained (Dolgin and Charlesworth, 2006)

Variation in endopolyploidy

The new estimates determined in this study continue to support the high prevalence of endoreduplication in mosses (Fig. 3, Table 1), except for Sphagnum. Despite the lack of endopolyploidy detected for Sphagnum, this process may play a role in the development of the large hyaline cells that enable these mosses to hold up to 10–25 times their dry weight in water (Andrus, 1986). Transmission electron micrographs of developing hyaline cells show large nuclei compared with nuclei in the surrounding chlorophyllose cells (Kremer and Drinnan, 2004). Detecting endopolyploidy in these cells is impossible at maturity due to disintegration of nuclei and cell death. While our samples for this study were taken from the actively growing apical regions of the Sphagnum gametophytes, the samples may have lacked immature hyaline cells with intact nuclei. Sampling of additional taxa with a focus on large amounts of young, meristematic tissues may increase the likelihood of endopolyploidy detection, if it is present at all in Sphagnum. The apparent lack of endoreduplication in hornworts, liverworts, ferns and gymnosperms suggests that this trait arose independently in mosses and again in specific angiosperm lineages. Additional work is needed to more fully understand the distribution of endopolyploidy across land plants.

Surveys of endopolyploidy across angiosperms found that genome size was negatively correlated with degree of endopolyploidy in broad surveys across taxonomic groups (e.g. Bainard et al., 2012) and in specific families: Brassicaceae, Solanaceae and Urticaceae (Nagl, 1978; Barow and Meister, 2003). Our study includes multiple members from some moss families (i.e. Brachytheciaceae, Dicranaceae, Hypnaceae and Mniaceae); however, our focus on sampling across the breadth of the moss phylogeny did not allow similar tests within families. Despite the lack of correlation between genome size and endopolyploidy across the moss phylogeny, all mosses sampled have small genomes and all were found to be endopolyploid with the exception of Sphagnum. Increased sampling within targeted sets of moss families will enable us to explore this relationship on a similar level in future studies.

Biological significance of DNA content variation in mosses

The amount of DNA in a genome, known as genome size or C value, varies greatly across living organisms and is known to correlate with a number of phenotypic traits, most notably cell size (e.g. Cavalier-Smith, 1978; Gregory, 2001), which in turn has been suggested to impact a variety of other morphological and physiological factors (the nucleotypic theory; Bennett, 1971; ,Bennett, 1972). For example, in angiosperms genome size has been linked with seed size (Beaulieu et al., 2007), stomata size and density (Beaulieu et al., 2008; Hodgson et al., 2010) and primary productivity (Simonin and Roddy, 2018). Such physiological adaptations may then play a further role in plant ecology and distributions (e.g. Knight and Ackerly, 2002; Knight et al., 2005).

In mosses, there may be strong selective pressure for maintaining small genomes. Renzaglia et al. (1995) discovered a strong correlation between sperm cell length and C value in hornworts, liverworts and mosses, providing a possible explanation for the constrained genome sizes. The selective pressures acting on sperm size are expected to be high, as reproductive success relies heavily on sperm locomotion (Renzaglia et al., 1995). Another physiological aspect that might be under selective pressure in mosses is desiccation tolerance. In mosses, cell size appears to be a limiting factor for desiccation tolerance (Proctor et al., 1998), which could then link back to minimum DNA content. Baniaga et al. (2016) also suggested that small genomes may play a role in desiccation tolerance in the Selaginellales and in Genlisea tuberosa.

Biologically, endopolyploidy plays a role in the formation of specialized cells and tissues (Nagl, 1978; Maluszynska et al., 2013), and in mosses occurs in food-conducting cells, mucilagenous hairs and rhizoids (Leitch and Dodsworth, 2017). The fact that these specialized tissues have endopolyploid nuclei suggests a potential functional significance for endoreduplication, including an increase in gene copy number that may lead to increases in gene expression and the ability to produce a range of cell sizes. The highly ubiquitous nature of endopolyploid nuclei in mosses, which is absent in many other early-diverging plant lineages, provides an impetus to study this group in more detail. Targeted approaches with high levels of sampling within particular lineages, such as the Bryales and Hookeriales, will enable us to test explicit hypotheses about the evolution of relatively larger genome sizes in these lineages. Many lineages also showed evidence of polyploidization, and pairing genome size data with chromosome data from the same populations will strengthen our understanding of these patterns. Further exploration of the nucleotypic theory in mosses, specifically focusing on sperm size and desiccation tolerance, may yield unique insights into the evolution of these traits.

SUPPLEMENTARY INFORMATION

Supplementary data are available online at https://dbpia.nl.go.kr/aob and consist of the following. Table S1: voucher specimens of all collected materials deposited in the Biodiversity Institute of Ontario Herbarium. Table S2: genome size data analysed from the literature. Table S3: SUMAC-generated list of the 2214 moss species from 35 families, including GenBank numbers for the four gene regions. Table S4: data set details for individual gene regions and the full data set of 2214 species.

FUNDING

This work was supported by The Natural Sciences and Engineering Research Council of Canada (NSERC) to J.D.B. and to S.G.N, and the Canadian Foundation for Innovation to S.G.N.

ACKNOWLEDGEMENTS

We thank the following people for contributing to specimen collection: A. Garrett, M. Kuzmina, J. Maloles and N. Webster. We value the expert assistance of N. R. Patel with uploading our data to TreeBASE. We greatly appreciate comments from P. Kron and anonymous reviewers on earlier versions of this manuscript.

LITERATURE CITED

Ågren
JA
,
Wright
SI
.
2015
.
Selfish genetic elements and plant genome size evolution
.
Trends in Plant Science
20
:
195
196
.

Andrus
RE
.
1986
.
Some aspects of Sphagnum ecology
.
Canadian Journal of Botany
64
:
416
426
.

Bainard
JD
,
Newmaster
SG
.
2010
.
Endopolyploidy in bryophytes: widespread in mosses and absent in liverworts
.
Journal of Botany
2010
: 316356.

Bainard
JD
,
Villarreal
JC
.
2013
.
Genome size increases in recently diverged hornwort clades
.
Genome
56
:
431
435
.

Bainard
JD
,
Fazekas
AJF
,
Newmaster
SG
.
2010
.
Methodology significantly affects genome size estimates: quantitative evidence using bryophytes
.
Cytometry Part A
77A
:
725
732
.

Bainard
J
,
Henry
T
,
Bainard
L
,
Newmaster
S
.
2011a
.
DNA content variation in monilophytes and lycophytes: large genomes that are not endopolyploid
.
Chromosome Research
19
:
763
775
.

Bainard
JD
,
Husband
BC
,
Baldwin
SJ
, et al.
2011b
.
The effects of rapid desiccation on estimates of plant genome size
.
Chromosome Research
19
:
825
842
.

Bainard
JD
,
Bainard
LD
,
Henry
TA
,
Fazekas
AJ
,
Newmaster
SG
.
2012
.
A multivariate analysis of variation in genome size and endoreduplication in angiosperms reveals strong phylogenetic signal and association with phenotypic traits
.
New Phytologist
196
:
1240
1250
.

Bainard
JD
,
Forrest
LL
,
Goffinet
B
,
Newmaster
SG
.
2013
.
Nuclear DNA content variation and evolution in liverworts
.
Molecular Phylogenetics and Evolution
68
:
619
627
.

Baniaga
AE
,
Arrigo
N
,
Barker
MS
.
2016
.
The small nuclear genomes of Selaginella are associated with a low rate of genome size evolution
.
Genome Biology and Evolution
8
:
1516
1525
.

Barlow
PW
.
1978
.
Endopolyploidy: towards an understanding of its biological significance
.
Acta Biotheoretica
27
:
1
18
.

Barow
M
,
Jovtchev
G
.
2007
.
Endopolyploidy in plants and its analysis by flow cytometry.
In:
Doležel
J
,
Greilhuber
J
,
Suda
J
, eds.
Flow cytometry with plant cells
.
Weinheim
:
Wiley
,
349
372
.

Barow
M
,
Meister
A
.
2003
.
Endopolyploidy in seed plants is differently correlated to systematics, organ, life strategy and genome size
.
Plant Cell and Environment
26
:
571
584
.

Beaulieu
JM
,
Moles
AT
,
Leitch
IJ
,
Bennett
MD
,
Dickie
JB
,
Knight
CA
.
2007
.
Correlated evolution of genome size and seed mass
.
New Phytologist
173
:
422
437
.

Beaulieu
JM
,
Leitch
IJ
,
Patel
S
,
Pendharkar
A
,
Knight
CA
.
2008
.
Genome size is a strong predictor of cell size and stomatal density in angiosperms
.
New Phytologist
179
:
975
986
.

Bennett
MD
.
1971
.
The duration of meiosis
.
Proceedings of the Royal Society of London B
178
:
277
299
.

Bennett
MD
.
1972
.
Nuclear DNA content and minimum generation time in herbaceous plants
.
Proceedings of the Royal Society of London B
181
:
109
135
.

Bennett
MD
,
Leitch
IJ
.
2005
.
Plant genome size research: a field in focus
.
Annals of Botany
95
:
1
6
.

Bennett
MD
,
Leitch
IJ
.
2012
.
Plant DNA C-values database.
http://data.kew.org/cvalues/
(1 September 2018
).

Bennett
MD
,
Smith
JB
.
1976
.
Nuclear DNA amounts in angiosperms
.
Philosophical Transactions of the Royal Society B
274
:
227
274
.

Bennetzen
JL
,
Kellogg
EA
.
1997
.
Do plants have a one-way ticket to genomic obesity?
Plant Cell
9
:
1509
1514
.

Boyle
B
,
Hopkins
N
,
Lu
Z
, et al.
2013
.
The taxonomic name resolution service: an online tool for automated standardization of plant names
.
BMC Bioinformatics
14
:
16
.

Burleigh
JG
,
Barbazuk
WB
,
Davis
JM
,
Morse
AM
,
Soltis
PS
.
2012
.
Exploring diversification and genome size evolution in extant gymnosperms through phylogenetic synthesis
.
Journal of Botany
2012
: 292857.

Cavalier-Smith
T
.
1978
.
Nuclear volume control by nucleoskeletal DNA, selection for cell volume and cell growth rate, and the solution of the DNA C-value paradox
.
Journal of Cell Science
34
:
247
278
.

Clark
J
,
Hidalgo
O
,
Pellicer
J
, et al.
2016
.
Genome evolution of ferns: evidence for relative stasis of genome size across the fern phylogeny
.
New Phytologist
210
:
1072
1082
.

Cox
CJ
,
Goffinet
B
,
Wickett
NJ
,
Boles
SB
,
Shaw
AJ
.
2010
.
Moss diversity: a molecular phylogenetic analysis of genera
.
Phytotaxa
9
:
175
195
.

Crum
HA
,
Anderson
LE
.
1981
.
Mosses of eastern North America, Vols 1 and 2
.
New York
:
Columbia University Press
.

Doležel
J
,
Binarová
P
,
Lucretti
S
.
1989
.
Analysis of nuclear DNA content in plant cells by flow cytometry
.
Biologia Plantarum
31
:
113
120
.

Doležel
J
,
Sgorbati
S
,
Lucretti
S
.
1992
.
Comparison of three DNA fluorochromes for flow-cytometric estimation of nuclear DNA content in plants
.
Physiolgia Plantarum
85
:
625
631
.

Doležel
J
,
Doleželová
M
,
Novák
FJ
.
1994
.
Flow cytometric estimation of nuclear DNA amount in diploid bananas (Musa acuminata and M. balbisiana)
.
Biologia Plantarum
36
:
351
357
.

Doležel
J
,
Greilhuber
J
,
Lucretti
S
, et al.
1998
.
Plant genome size estimation by flow cytometry: inter-laboratory comparison
.
Annals of Botany
82
:
17
26
.

Doležel
J
,
Bartoš
J
,
Voglmayr
H
,
Greilhuber
J
.
2003
.
Nuclear DNA content of trout and human
.
Cytometry Part A
51A
:
127
128
.

Doležel
J
,
Greilhuber
J
,
Suda
J
.
2007
.
Estimation of nuclear DNA content in plants using flow cytometry
.
Nature Protocols
2
:
2233
2244
.

Dolgin
ES
,
Charlesworth
B
.
2006
.
The fate of transposable elements in asexual populations
.
Genetics
174
:
817
827
.

Edgar
RC
.
2010
.
Search and clustering orders of magnitude faster than blast
.
Bioinformatics
26
:
2460
2461
.

Felsenstein
J
.
1985
.
Phylogenies and the comparative method
.
American Naturalist
125
:
1
15
.

Fleischmann
A
,
Michael
TP
,
Rivadavia
F
, et al.
2014
.
Evolution of genome size and chromosome number in the carnivorous plant genus Genlisea (Lentibulariaceae), with a new estimate of the minimum genome size in angiosperms
.
Annals of Botany
113
:
1651
1663
.

Freyman
WA
.
2015
.
SUMAC: constructing phylogenetic supermatrices and assessing partially decisive taxon coverage
.
Evolutionary Bioinformatics
11
:
263
266
.

Fritsch
R
.
1991
.
Index to bryophyte chromosome counts
.
Berlin
:
J. Cramer
.

Galbraith
DW
,
Harkins
KR
,
Maddox
JM
, et al.
1983
.
Rapid flow cytometric analysis of the cell cycle in intact plant tissues
.
Science
220
:
1049
1051
.

Gregory
TR
.
2001
.
Coincidence, coevolution, or causation? DNA content, cell size, and the C-value enigma
.
Biological Reviews
76
:
65
101
.

Greilhuber
J
,
Såstad
SM
,
Flatberg
KI
.
2003
.
Ploidy determination in Sphagnum samples from Svalbard, Arctic Norway, by DNA image cytometry
.
Journal of Bryology
25
:
235
239
.

Greilhuber
J
,
Dolezel
J
,
Lysak
M
,
Bennett
MD
.
2005
.
The origin, evolution and proposed stabilization of the terms ‘genome size’and ‘C-value’ to describe nuclear DNA contents
.
Annals of Botany
95
:
255
260
.

Grotkopp
E
,
Rejmanek
M
,
Sanderson
MJ
,
Rost
TL
.
2004
.
Evolution of genome size in pines (Pinus) and its life-history correlates: supertree analysis
.
Evolution
58
:
1705
1729

Guindon
S
,
Dufayard
JF
,
Lefort
V
,
Anisimova
M
,
Hordijk
W
,
Gascuel
O
.
2010
.
New algorithms and methods to estimate maximum-likelihood phylogenies: assessing the performance of PhyML 3.0
.
Systematic Biology
59
:
307
321
.

Hanson
L
,
Leitch
IJ
.
2002
.
DNA amounts for five pteridophyte species fill phylogenetic gaps in C-value data
.
Botanical Journal of the Linnean Society
140
:
169
173
.

Harvey
PH
,
Pagel
MD
.
1991
.
The comparative method in evolutionary biology
.
Oxford
:
Oxford University Press
.

Hidalgo
O
,
Pellicer
J
,
Christenhusz
MJM
,
Schneider
H
,
Leitch
IJ
.
2017
.
Genomic gigantism in the whisk-fern family (Psilotaceae): Tmesipteris obliqua challenges record holder Paris japonica
.
Botanical Journal of the Linnean Society
183
:
509
514
.

Hodgson
JG
,
Sharafi
M
,
Jalili
A
, et al.
2010
.
Stomatal vs. genome size in angiosperms: the somatic tail wagging the genomic dog?
Annals of Botany
105
:
573
584
.

Johnson
MG
,
Malley
C
,
Goffinet
B
,
Shaw
AJ
,
Wickett
NJ
.
2016
.
A phylotranscriptomic analysis of gene family expansion and evolution in the largest order of pleurocarpous mosses (Hypnales, Bryophyta)
.
Molecular Phylogenetics and Evolution
98
:
29
40
.

Jovtchev
G
,
Schubert
V
,
Meister
A
,
Schubert
I
.
2006
.
Nuclear DNA content and nuclear and cell volume are positively correlated in angiosperms
.
Cytogenetic and Genome Research
114
:
77
82
.

Karlin
EF
,
Temsch
EM
,
Bizuru
E
, et al.
2014
.
Invisible in plain sight: recurrent double allopolyploidy in the African Sphagnum × planifolium (Sphagnaceae)
.
The Bryologist
117
:
187
201
.

Kearse
M
,
Moir
R
,
Wilson
A
, et al.
2012
.
Geneious Basic: an integrated and extendable desktop software platform for the organization and analysis of sequence data
.
Bioinformatics
28
:
1647
1649
.

Knight
CA
,
Ackerly
DD
.
2002
.
Variation in nuclear DNA content across environmental gradients: a quantile regression analysis
.
Ecology Letters
5
:
66
76
.

Knight
CA
,
Molinari
NA
,
Petrov
DA
.
2005
.
The large genome constraint hypothesis: evolution, ecology and phenotype
.
Annals of Botany
95
:
177
190
.

Kremer
CL
,
Drinnan
AN
.
2004
.
Secondary walls in hyaline cells of Sphagnum
.
Australian Journal of Botany
52
:
243
256
.

Lamparter
T
,
Brücker
G
,
Esch
H
,
Hughes
J
,
Meister
A
,
Hartmann
E
.
1998
.
Somatic hybridisation with aphototrophic mutants of the moss Ceratodon purpureus: genome size, phytochrome photo-reversibility, tip-cell phototropism and chlorophyll regulation
.
Journal of Plant Physiology
153
:
394
400
.

Lanfear
R
,
Frandsen
PB
,
Wright
AM
,
Senfeld
T
,
Calcott
B
.
2017
.
PartitionFinder 2: new methods for selecting partitioned models of evolution for molecular and morphological phylogenetic analyses
.
Molecular Biology and Evolution
34
:
772
773
.

Larkin
MA
,
Blackshields
G
,
Brown
NP
, et al.
2007
.
Clustal W and Clustal X version 2.0
.
Bioinformatics
23
:
2947
2948
.

Lawton
E
.
1971
.
Moss flora of the Pacific Northwest
.
Japan
:
The Hattori Botanical Laboratory
.

Leitch
IJ
,
Dodsworth
S
.
2017
.
Endopolyploidy in plants
.
eLS
30
:
1
10
.

Leitch
IJ
,
Leitch
AR
.
2013
.
Genome size diversity and evolution in land plants.
In:
Leitch
IJ
,
Greilhuber
J
,
Doležel
J
,
Wendel
JF
, eds.
Plant genome diversity, Volume 2. Physical structure, behaviour and evolution of plant genomes.
Vienna
:
Springer
,
307
322
.

Leitch
IJ
,
Chase
MW
,
Bennett
MD
.
1998
.
Phylogenetic analysis of DNA C-values provides evidence for a small ancestral genome size in flowering plants
.
Annals of Botany
82
:
85
94
.

Leitch
IJ
,
Soltis
DE
,
Soltis
PS
,
Bennett
MD
.
2005
.
Evolution of DNA amounts across land plants (Embryophyta)
.
Annals of Botany
95
:
207
217
.

Lysák
MA
,
Doležel
J
.
1998
.
Estimation of nuclear DNA content in Sesleria (Poaceae)
.
Caryologia
52
:
123
132
.

Magill
RE
.
2010
.
Moss diversity: new look at old numbers
.
Phytotaxa
9
:
167
174
.

Maluszynska
J
,
Kolano
B
,
Sas-Nowosielska
H
.
2013
.
Endopolyploidy in plants.
In:
Leitch
IJ
,
Greilhuber
J
,
Doležel
J
,
Wendel
JF
, eds.
Plant genome diversity, Volume 2. Physical structure, behaviour and evolution of plant genomes.
Vienna
:
Springer
,
99
119
.

Melosik
I
,
Ordzykoski
II
,
Sliwinska
E
.
2005
.
Delimitation of taxa of Sphagnum subsecundum s.l. (Musci, Sphagnaceae) based on multienzyme phenotype and cytological characters
.
Nova Hedwigia
80
:
397
412
.

Miller
MA
,
Pfeiffer
W
,
Schwartz
T
.
2010
.
Creating the CIPRES Science Gateway for inference of large phylogenetic trees
.
Proceedings, Gateway Computing Environments Workshop (GCE)
1
8
.

Morris
JL
,
Puttick
MN
,
Clark
JW
, et al.
2018
.
The timescale of early land plant evolution
.
Proceedings of the National Academy of Sciences of the USA
115
:
E2274
E2283
.

Münkemüller
T
,
Lavergne
S
,
Bzeznik
B
, et al.
2012
.
How to measure and test phylogenetic signal
.
Methods in Ecology and Evolution
3
:
743
756
.

Nagl
W
.
1978
.
Endopolyploidy and polyteny in differentiation and evolution
.
Amsterdam
:
North-Holland
.

NCBI Resource Coordinators
.
2016
.
Database resources of the National Center for Biotechnology Information
.
Nucleic Acids Research
44
(
Database issue
):
D7
D19
.

Newton
ME
.
1984
.
The cytogenetics of bryophytes.
In:
Dyer
AF
,
Duckett
JG
, eds.
The experimental biology of bryophytes
.
London
:
Academic Press
,
65
96
.

Obermayer
R
,
Leitch
IJ
,
Hanson
L
,
Bennett
MD
.
2002
.
Nuclear DNA C-values in 30 species double the familial representation in Pteridophytes
.
Annals of Botany
90
:
209
217
.

Ohri
D
,
Khoshoo
TN
.
1986
.
Genome size in gymnosperms
.
Plant Systematics and Evolution
153
:
119
132
.

Pagel
M
.
1999
.
Inferring the historical patterns of biological evolution
.
Nature
401
:
877
884
.

Paradis
E
,
Claude
J
,
Strimmer
K
.
2004
.
APE: Analyses of Phylogenetics and Evolution in R language
.
Bioinformatics
20
:
289
290
.

Pellicer
J
,
Fay
MF
,
Leitch
IJ
.
2010
.
The largest eukaryotic genome of them all?
Botanical Journal of the Linnean Society
164
:
10
15

Proctor
MCF
,
Nagy
Z
,
Csintalan
Z
,
Takacs
Z
.
1998
.
Water-content components in bryophytes: analysis of pressure-volume relationships
.
Journal of Experimental Botany
49
:
1845
1954
.

Puttick
MN
,
Morris
JL
,
William
TA.
et al.
2018
.
The interrelationships of land plants and the nature of the ancestral embryophyte
.
Current Biology
28
:
733
745
.

R Core Team
.
2017
.
R: a language and environment for statistical computing
.
Vienna, Austria
:
R Foundation for Statistical Computing
. https://www.R-project.org/ (
6 December 2017)
.

Rensing
SA
,
Lang
D
,
Zimmer
AD
, et al.
2008
.
The Physcomitrella genome reveals evolutionary insights into the conquest of land by plants
.
Science
319
:
64
69
.

Renzaglia
KS
,
Garbary
DJ
.
2001
.
Motile gametes of land plants: diversity, development, and evolution
.
Critical Reviews in Plant Sciences
20
:
107
213
.

Renzaglia
KS
,
Rasch
EM
,
Pike
LM
.
1995
.
Estimates of nuclear DNA content in bryophyte sperm cells: phylogenetic considerations
.
American Journal of Botany
82
:
18
25
.

Renzaglia
KS
,
Villarreal
JC
,
Garbary
DJ
.
2018
.
Morphology supports the setaphyte hypothesis: mosses plus liverworts form a natural group
.
Bryophyte Diversity and Evolution
40
:
11
17
.

Revell
LJ
.
2012
.
phytools: an R package for phylogenetic comparative biology (and other things)
.
Methods in Ecology and Evolution
3
:
217
223
.

Reski
R
.
1998
.
Development, genetics and molecular biology of mosses
.
Botanica Acta
111
:
1
15
.

Reski
R
,
Faust
M
,
Wang
X
, et al.
1994
.
Genome analysis of the moss Physcomitrella patens (Hedw.) B.S.G
.
Molecular and General Genetics
244
:
352
359
.

De Rocher
EJ
,
Harkins
KR
,
Galbraith
DW
,
Bohnert
HJ
.
1990
.
Developmentally regulated systemic endopolyploidy in succulents with small genomes
.
Science
250
:
99
101
.

Sanderson
MJ
.
2002
.
Estimating absolute rates of molecular evolution and divergence times: a penalized likelihood approach
.
Molecular Biology and Evolution
19
:
101
109
.

Såstad
SM
.
2005
.
Patterns and mechanisms of polyploid speciation in bryophytes.
In:
Bakker
FT
,
Chatrou
LW
,
Gravendeel
B
,
Pelser
PB
, eds.
Plant species-level systematics
.
Ruggell
:
ARG Gantner
.

Schween
G
,
Gorr
G
,
Hohe
A
,
Reski
R
.
2003
.
Unique tissue-specific cell cycle in Physcomitrella
.
Plant Biology
5
:
50
58
.

Simonin
KA
,
Roddy
AB
.
2018
.
Genome downsizing, physiological novelty, and the global dominance of flowering plants
.
PLoS Biology
16
:
e2003706
.

Smith
SA
,
O’Meara
BC
.
2012
.
treePL: divergence time estimation using penalized likelihood for large phylogenies
.
Bioinformatics
28
:
2689
2690
.

Söderström
L
,
Hagborg
A
,
von Konrat
M
, et al.
2016
.
World checklist of hornworts and liverworts
.
PhytoKeys
59
:
1
828
.

Soltis
D
,
Soltis
P
,
Endress
P
, et al.
2018
.
Phylogeny and evolution of the angiosperms: revised and updated edition
.
Chicago
:
University of Chicago Press
.

de Sousa
F
,
Foster
PG
,
Donoghue
PC
,
Schneider
H
,
Cox
CJ
.
2019
.
Nuclear protein phylogenies support the monophyly of the three bryophyte groups (Bryophyta Schimp.)
.
New Phytologist
222
:
565
575
.

Stamatakis
A
.
2014
.
RAxML Version 8: a tool for phylogenetic analysis and post-analysis of large phylogenies
.
Bioinformatics
30
:
1312
1313
.

Stech
M
,
McDaniel
SF
,
Hernández-Maqueda
R
, et al.
2013
.
Phylogeny of haplolepideous mosses – challenges and perspectives
.
Journal of Bryology
34
:
173
186
.

Temsch
EM
,
Greilhuber
J
,
Krisai
R
.
1998
.
Genome size in Sphagnum (peat moss)
.
Botanica Acta
111
:
325
330
.

Temsch
EM
,
Greilhuber
J
,
Krisai
R
.
2010
.
Genome size in liverworts
.
Preslia
82
:
63
80
.

The Taxonomic Name Resolution Service
.
iPlant collaborative. Version 4.0.
http://tnrs.iplantcollaborative.org (
22 January 2018
).

De Veylder
L
,
Larkin
JC
,
Schnittger
A
.
2011
.
Molecular control and function of endoreplication in development and physiology
.
Trends in Plant Science
16
:
624
634
.

Voglmayr
H
,
2000
.
Nuclear DNA amounts in mosses (Musci)
.
Annals of Botany
85
:
531
546
.

Voglmayr
H
,
2007
.
DNA flow cytometry in non-vascular plants.
In:
Doležel
J
,
Greilhuber
J
,
Suda
J
, eds.
Flow cytometry with plant cells
.
Weinheim
:
Wiley
,
267
286
.

Zouhair
R
,
Lecocq
M
.
1998
.
Organisation nucleaire et teneur en ADN de plusieurs especes de cryptogames
.
Revue de Cytologie et Biologie Végétale, Le Botaniste
21
:
15
32
.

This article is published and distributed under the terms of the Oxford University Press, Standard Journals Publication Model (https://dbpia.nl.go.kr/journals/pages/open_access/funder_policies/chorus/standard_publication_model)

Supplementary data