Biodiversity Data Journal : Data Paper (Biosciences)
Data Paper (Biosciences)
Report of two distinct ribotypes in ITS sequences of Phalaris arundinacea (Poaceae) in western Canada and Alaska
expand article infoDiana M. Percy, Quentin C. B. Cronk‡,§
‡ Department of Botany, University of British Columbia, Vancouver, Canada
§ Beaty Biodiversity Museum, University of British Columbia, Vancouver, Canada
Open Access



Phalaris arundinacea L. (reed canary grass) is a widely occurring grass throughout the Northern Hemisphere. In North America, it is thought to consist of introduced agricultural forms from Europe as well as native populations.

New information

During a survey of Phalaris arundinacea in western Canada, we discovered two distinct ribotypes in the sequences of the internal transcribed spacer (ITS) of the nuclear ribosomal DNA: one full length (ITS-long) and one with a seven base pair deletion (ITS-short). In addition, ITS-long plants have fixed heterozygosity indicating possible polyploidy. Phylogenetic analysis reveals that ITS-short is a unique ribotype that characterises an intraspecific clade. We designed an efficient PCR-based assay that allows sizing of a 238/245 base pair fragment in a capillary sequencer. This approach provides a novel marker that could be useful in future surveys of Phalaris arundinacea.


internal transcribed spacer, invasive plant, Phalaris, reed canary grass


Phalaris arundinacea L., commonly called reed canary grass (RCG), is a Eurasian and North American perennial grass, with many uses in agriculture (Jakubowski et al. 2011) and biomass energy (Lewandowski et al. 2003). In North America, native populations are considered under threat from invasion and replacement by vigorous introduced genotypes of P. arundinacea that have now become a significant invader of wetland and riparian habitats in North America (Lavergne and Molofsky 2004) with considerable ecological impacts (Spyreas et al. 2010). The distribution of Phalaris arundinacea in North America, based on databased herbarium specimens, is shown in Fig. 1.

Figure 1.  

Map of North American Phalaris arundinacea herbarium specimens from the Global Biodiversity Information Facility (GBIF; accessed October 2021). Red = 1822-1940; blue = 1941-2018. The dotted line marks the boundary of the western cordilleras.

Molecular methods have often been used to distinguish populations of RCG, including isozymes (Gifford et al. 2002), AFLP (Casler et al. 2009), SSR (Jakubowski et al. 2013, Jakubowski et al. 2014, Kettenring et al. 2019), ISSR (Anderson et al. 2016), DartSeq (Noyszewski et al. 2019, Noyszewski et al. 2021) and ITS sequencing (Graper et al. 2021). However, there is still much uncertainty and, in some cases, disagreement, regarding the extent of distribution and location of present day native versus introduced RCG populations in North America (Jakubowski et al. 2013). The aim of this note is to detail an easily scored novel genetic marker that may be of use in future surveys of RCG.

Sampling methods


Sources of material - herbarium and field

A total of 86 samples of Phalaris arundinacea were obtained from herbarium material and additional targeted sampling carried out for this study (Tables 1, 2, Suppl. materials 1, 3). Herbarium samples, from modern to 130 years old and in relatively good condition, were selected for sampling from the University of British Columbia Herbarium (UBC) and the Herbarium of the Bell Museum, University of Minnesota (MIN). Further dried leaf samples (used in a previous study; Kettenring et al. (2019)) were kindly provided by Professor Karen Mock of Utah State University. In addition, extensive field sampling was carried out in Elk Island National Park, Alberta, where park authorities were concerned about the ecologically harmful spread of, as well as appropriate control methods for, Phalaris arundinacea. Further recent samples were sourced from Greater Vancouver. Voucher specimens are deposited in UBC. As outgroups for the phylogenetic analyses, we used eight individuals obtained from herbarium samples of P. aquatica Guss., P. canariensis L., P. caroliniana Walter, P. coerulescens Desf. and P. paradoxa L. (Suppl. material 2).

Table 1.

Herbarium specimens identified as ITS-short: determined by sequencing or sizing assay to have a 7 bp deletion in ITS2. An asterisk indicates one individual identified as ITS-short in assay data, but putative hybrid in sequence data; and [] indicates the only sequence found on GenBank with the ITS-short genotype. Region abbreviations: AB Alberta, AK Alaska, BC British Columbia, NWT Northwest Territories.

Accession no.









Chilcotin, Madden Lake


not recorded




Chilcotin, Meldrum Creek






near Shamrock, ca. 30 miles northwest of Prince George


in post-glacial bed of the Stuart River




Beaver Lake, Wilson Creek Road, nr. Slocan Lake


swampy lake edge




S. of Ft Smith


scattered in clumps along dried-up slough




Kootenay District, Flathead, Procter Lake


in 2 ft (60 cm) of water at lake edge




Kootenay District, Sage Creek Lodge.


wet edge of slough




Flathead valley, Marl Lake


wet edge of lake




Kootenay, Nakusp, Wilson Lake.


in peat bog




5 mi (7.5 km) southeast of Fort Simpson,


rare in moist black ground in Carex meadow




Yoho National Park, Hoodoo Creek Campground area


somewhat calcareous swampy lakeshore

V119175 [KF753778]



Cook Inlet lowlands, Otter Creek at Loop Road


herbaceous border of ponded creek




Just east of Fort Saskatchewan


creek bottom

Table 2.

Herbarium specimens identified as ITS-long: determined by sequencing or sizing assay to lack the 7 bp deletion in ITS2. Region abbreviations: BC British Columbia, MB Manitoba, MN Minnesota, NC North Carolina, WA Washington, YT Yukon Territory.

Accession no.









Alaska Highway km 1016


apparently seeded along highway




Sage Creek, Flathead


grassy meadow




Salmon Arm


not recorded




Thompson-Nicola Regional District, Tranquille


wet meadow




Greater Vancouver, Delta, Westham Island


tidal shore (var. picta)




Avery County, Elk River at Heaton






Osoyoos, Haynes Point Provincial Park


meadow beside wetland




Pencil Lake, Riding Mountain National Park


road allowance, jet ski trail






sewage treatment facility




Vancouver Island, Duncan, Somenos Marsh


thick grassy marsh margin




Vancouver Island, Cumberland


roadside with introduced grasses




Palouse River, Pullman


shallow pools of drying streambed




St Anthony Park, Ramsey


see Noyszewski et al. (2021)






see Noyszewski et al. (2021)

Step description: 

DNA extraction, PCR and sequencing

Dried leaf material was ground to a slurry in liquid nitrogen and the DNA extracted using a modified CTAB method (Doyle and Doyle 1987). Full length PCR (ITS1-5.8S-ITS2) was performed using primers ITS-A (forward) (Blattner 1999) and ITS4 (reverse) (White et al. 1990) and PCR conditions 94°C/4 min, followed by 30 cycles of 94°C/30 sec, 50°C/1 min, 72°C/1 min and final extension of 72°C/10min. In cases of highly degraded DNA from older herbarium specimens, ITS1 and ITS2 were amplified separately using primers ITS3P (forward) (Möller and Cronk 1997) and the reverse complement ITS2P (reverse). Bidirectional Sanger sequencing was performed by Eurofins (Kentucky, USA) and sequences were checked using Sequencher version 4.8 (Gene Codes).

Sequence alignment and phylogenetic analysis

Sequences of 60 individuals were aligned manually using Sequencher and Se-Al (Rambaut 2002). Subunit boundaries follow those determined for Oryza (Takaiwa et al. 1985, Yokota et al. 1989) as follows: 18S/ITS1 CATTG/TCGTG; ITS1/5.8S AAATC/CACAC; 5.8S/ITS2 CACGC/CAAAA; ITS2/26S GGACC/GCGAC (an example of a full Oryza sequence for location is GenBank accession MF029734). Eight putative hybrids (between the different ribotypes) were excluded from the phylogenetic analysis due to sequence superposition. We included one sample from GenBank (KF753778) as the only previously databased sequence with the ITS-short genotype. Phylogenetic analysis was performed using three approaches: a Neighbour-joining (NJ) analysis with uncorrected (p) distances and 1000 bootstrap replicates, a Maximum Parsimony (MP) analysis with heuristic search (random addition of taxa and TBR branch swapping), both methods being performed in PAUP* (Swofford 2003); and a Maximum Likelihood (ML) analysis using RAxML (v. 8.2.4) with GTRCAT, 1000 rapid bootstraps and Gamma optimisation of tree space run on the CIPRES Science Gateway (Miller et al. 2010, Stamatakis 2014). The MP analysis also included a gap code matrix (for nine gaps: three in P. arundinacea and six in outgroup taxa). Sequences are deposited in GenBank under accession numbers: OQ740187-OQ740255.

Structural analysis of ITS2

Structural analyses were performed using the ITS2 database (Ankenbrand et al. 2015). We used the Phalaris arundinacea ITS2 structure of GenBank accessions FJ821785 (MFE -66.8 kcal/mol) in the ITS2 database for homology modelling (Wolf et al. 2005) of our common variant (ITS-long) as it had a near identical sequence. As homology modelling of the rare variant (ITS-short) fails on FJ821785, alternative templates for homology modelling were investigated. Plausible configurations for ITS2-short were obtained using Arctagrostis latifolia (EU792351) and Phalaris canariensis (FJ377670) as templates.

Capillary sizing assay

A primer was designed using the NCBI Primer-BLAST tool (Ye et al. 2012) ITS2AindelR: 5’-GCAGCCATATCTTCGGC-3’ for use in conjunction with ITS primer ITS3P to allow an accurate sizing assay on an ABI 3730 automated DNA Sequencer (Applied Biosystems). The primer was combined with a M13 tail (5'-TGTAAAACGACGGCCAGT-3') on the forward primer to facilitate fluorescent dye labelling and a further PIG tail (5’-GTTTCTT-3’) on the reverse primer to promote terminal adenylation. We used a hot start touchdown PCR protocol with 95°C/3 min, followed by 10 cycles of 94°C/30 sec, 65°C/30 sec (-1°C per cycle, R 3°C/sec), 72°C/45 sec, followed by a further 30 cycles of 94°C/30 sec, 55°C/30 sec, 72°C/45 sec and a final extension at 72°C/4 min. PCR products were loaded into the capillary machine at 1:30 dilution and traces read using the programme Geneious 8.1.9 (Biomatters Ltd.). The PCR assay was designed to give products of 238 or 245 bp depending on the presence of the 7 bp deletion.

A sequencing survey and phylogenetic analysis reveals intraspecific divergence in ITS including a 7 bp deletion

Initial results of an ITS sequencing survey of Phalaris arundinacea from western Canada revealed two distinctive sequences. One is full length with fixed heterozygosity characteristic of polyploids; the other is shorter, with a 7 bp deletion in ITS2 and with no fixed heterozygous base positions. The differences are summarised in Table 3. The tree topologies recovered from the different phylogenetic approaches were nearly identical. The matrix length was 603 bp (612 characters with gap coding) and the MP search recovered two trees with length 117 (CI: 0.93, RI: 0.98); we present the strict consensus topology in Fig. 2 showing majority rule consensus values as well as NJ and ML bootstrap support values. The best ML model fit for the data (AIC) was GTR+G (-lnL 1611.45). Use of outgroups showed that the full length sequence (which we call ITS-long) was likely the ancestral one and the deletion (ITS-short) is a putatively-derived character so far known only from plants in north-western North America (Fig. 3). When compared with all available world-wide sequences from GenBank (including Asia, Europe, North and South America), only one sequence was found to have the ITS-short genotype (KF753778) from Cook Inlet, Alaska; all other GenBank samples are the ITS-long genotype and ITS-long sequences found in North America are highly similar or identical to European genotypes. Tables 1, 2 show to which clade (ITS-long/-short) historical herbarium specimens can be assigned.

Table 3.

Molecular characteristics of the 7 bp deletion clade (ITS-short) in comparison to the full length variant (ITS-long). Length variation in Phalaris arundinacea is caused by one 7 bp deletion and a 1 bp homopolymer indel, giving a combined length difference of 6 bp. The aligned sequence length for 52 Phalaris arundinacea individuals using the ITS1-5.8S-ITS2 subunit boundaries following Takaiwa et al. (1985) and Yokota et al. (1989) is 600 bp and, including six outgroup taxa (eight individuals), it is 603 bp. Ambiguity codes (Y, R, S) are given for heterozygotes. Sites homozygous, but polymorphic between different individuals, are given as C/T etc. Individuals that were interpreted as putative hybrids are given in Suppl. material 1.





No. of individuals




Total sequence length, ITS1-5.8S-ITS2 (bp)

599 (no variation)

593 (no variation)


ITS1 length




5.8S length




ITS2 length




Fixed heterozygosity in ITS1-long (aligned position)

Y(30), Y(181), Y(193), S(208)

C(30), C(181), C(193), C(208)

T/C(30), C(181), T/C(193), C(208)

Fixed heterozygosity in 5.8S-long (aligned position)

Y(345), Y(359)

C(345), C(359)

C(345), C/T(359)

Fixed heterozygosity in ITS2-long (aligned position)

Y(421), R(489), Y(587)

C(421), A/R(489), C(587)

C/T(421), G(489), C(587)

Fixed SNPs between groups in ITS1 (aligned position)

A(7), C(60), C(195)

C(7), T(60), Y/T(195)

C(7), C/T(60), C(195)

Fixed SNPs between groups in ITS2 (aligned position)

T(413), C(493), T(528)

C(413), T/Y(493),C/Y(528)

T(413), C(493), T(528)

SSR in ITS2 (aligned position)




Figure 2.  

Phylogeny of 53 individuals of Phalaris arundinacea and five outgroup taxa, based on ITS variation. Included are 60 individuals sampled for this study as well as the only GenBank sample of P. arundinacea found with the ITS-short sequence [KF753778]. Asterisks indicate samples obtained from herbarium material. The tree is a strict consensus from the MP analysis with Majority Rule consensus values above nodes and NJ/ML bootstrap support values below nodes. Two clades can be seen: the deletion clade (ITS-short) and the full length ITS clade (ITS-long). Sample details are given in Tables 1, 2 and Suppl. materials 1, 2, 3.

Figure 3.  

Map of western Canada showing the locations of 51 genotyped samples of Phalaris arundinacea. Dotted line indicates the Province of British Columbia. Red dots show the locations of the “short” ribotypes (n = 13); blue “long” (n = 32) and orange putative hybrids (n = 6). Only three placeholder specimens are given for Elk Island National Park (arrowed; see additional map Suppl. material 4). Sample details are given in Tables 1, 2 and Suppl. materials 1, 2, 3.

The 7 bp deletion alters the secondary structure of helix I of ITS2. The predicted secondary structure of the common variant (ITS2-long) of Phalaris arundinacea ITS2 is the usual eukaryotic four helix model (Fig. 4). Homology modelling of the structure of the ITS2-short sequence against this structure fails, as helix I, which has the 7 bp deletion, is not a suitable model. However, homology modelling with a related grass of similar ITS2 sequence suggests a plausible model for helix I despite the deletion (Fig. 4).

Figure 4.  

Secondary structure consequences of the deletion in ITS2. A) Predicted secondary structure of Phalaris arundinacea ITS2, based on the common variant (ITS2-long). B) Detail of helix I; DEL = the bases (GGGATGC) deleted in the ITS2-short variant; HR – C5 = 5 cytosine homopolymer repeat; asterisk T – position of the T/C single nucleotide polymorphism (aligned position 413). C) Possible alternative structure of helix I in the ITS2-short variant, based on homology modelling using Arctagrostis latifolia as the template; the cytosine homopolymer repeat is now C6 (6 cytosines); the arrow shows the position of the deleted sequence.

A PCR-based capillary sizing assay allows rapid detection of the 7 bp deletion clade

In order to genotype individuals without sequencing, we developed a primer that amplifies a 238 vs. 245 bp amplicon (short enough to size accurately to a single base pair on a capillary machine). ITS-long gave a clear peak at 245 bp and a complete absence of a peak at 238 bp. Despite using a design to promote terminal adenylation (see Methods), if there is a large amount of starting DNA, this peak was split, showing a peak or shoulder at 244 bp. However, in all cases, the fully adenylated peak was unambiguous and as strong or stronger than the unadenylated peak. ITS-short samples gave a strong, unambiguous peak at 238 bp. Product without terminal adenylation sometimes showed as a shoulder, but never a separate peak. ITS-short samples sometimes showed a small peak at 245 bp, but the 238 peak was, in all cases, much stronger. A total of 68 individuals were sized with this method, providing clade (ITS-long/-short/hybrid) affiliation for an additional 34 individuals. Putative hybrids (10 individuals) were identified either by both sequencing and sizing assay (seven individuals), sequence data only (one individual) and two specimens identified as ITS-short in the length assay, but were determined as a putative hybrid with sequence data (Suppl. material 1).

A survey of Elk Island National Park, Alberta, reveals presence of both ITS ribotypes

Using the molecular tools detailed above, we were able to conduct extensive sampling of Elk Island National Park (EINP), Alberta. Phalaris arundinacea is extremely abundant at EINP and the material in the Park tends to be strongly spreading-rhizomatous and invasive. EINP is bisected into a northern and southern portion by the east-west highway 16. These portions have different management histories, with the northern portion experiencing much greater public access and road development. We refer to these portions as north EINP and south EINP. In all sampled localities of north EINP, ITS-long was the only genotype detected (except a few possible hybrids at Tawayik Lake). In south EINP the situation is very different. Of the 12 individuals genotyped from south EINP, five were ITS-short (DPQC10A and DPQC11A-D).

Geographic coverage


North-western North America

Taxonomic coverage


Phalaris arundinacea, P. aquatica, P. canariensis, P. caroliniana, P. coerulescens and P. paradoxa.

Usage licence

Usage licence: 
Creative Commons Public Domain Waiver (CC-Zero)

Data resources

Data package title: 
Specimen details for all 94 samples genotyped (86 Phalaris arundinacea and eight outgroup taxa sampled).
Number of data sets: 
Data set name: 
Specimen details for all 94 samples genotyped (86 Phalaris arundinacea and eight outgroup taxa sampled).

Suppl. material 3 contains specimen details for all 94 samples genotyped (86 Phalaris arundinacea and eight outgroup taxa sampled).

Column label Column description
occurrenceID Specimen Code identifier for the Occurrence.
basisOfRecord Specimen type as the specific nature of the data record.
eventDate Date of specimen collection.
eventRemarks Note of incomplete date information.
decimalLatitude The geographic latitude (in decimal degrees, using the spatial reference system given in geodeticDatum) of the geographic centre of a Location.
decimalLongitude The geographic longitude (in decimal degrees, using the spatial reference system given in geodeticDatum) of the geographic centre of a Location.
geodeticDatum The ellipsoid, geodetic datum or spatial reference system (SRS) upon which the geographic coordinates given in decimalLatitude and decimalLongitude are based.
eventRemarks Ribotype of ITS sequence.
country The name of the country or major administrative unit in which the Location occurs.
locality The specific description of the place.
verbatimLocality The original textual description of the place.
scientificName The full scientific name, with authorship.
identificationQualifier Qualifier on current identification.
taxonRank The taxonomic rank of the most specific name in the scientificName.
institutionCode The name (or acronym) in use by the Herbarium institution having custody of the object(s) or information referred to in the record.
collectionCode The name, acronym, coden or initialism identifying the collection or dataset from which the record was derived.

Additional information

Implications of two highly divergent intraspecific ribotypes

The making of a ribosome is a complex process: it involves multiple steps and over 200 biogenesis factors (Sáez-Vásquez and Delseny 2019). In this process, ITS2 plays an important role. The excision of ITS2 from the pre-ribosomal RNA is essential to generate mature 25/26S and 5.8S and the secondary structure of ITS2 is important for this process (Schultz et al. 2005). Embryophytes have four helices (numbered I-IV) arising from a central ring. These helices require complementary base pairing to form (and be stable). They are, therefore, generally quite conserved in sequence, with mutations only surviving if they preserve the pairing energetics of the helix (Zhang et al. 2020). For this reason, it is surprising to see an intraspecific seven base-pair deletion in helix I. In addition, this helix carries an SNP and an extra cytosine in a cytosine repeat sequence. There is an energetically plausible alternative structure for this helix, but it still represents a marked change in helix pairing structure. Furthermore, there are seven SNPs in helix III (although these do not markedly impact helix structure). Given this, it is evident that there are two distinctive ITS2 ribotypes in north-western Canada, being distinguished by two indel events, one with a major impact on helix nucleotide pairing and five SNPs.

The ITS-long sequence was highly similar or identical to sequences of known European genotypes obtained from GenBank. In contrast, the ITS-short individuals are often from non-agricultural and remote localities, (e.g. Yoho NP and Cook Inlet Lowlands of Alaska and North West Territory) or from older herbarium specimens (e.g. a 1945 specimen from Fort Saskatchewan, AB). These ITS-short genotypes are almost uniformly from riparian and lacustrine habitats and never grassland. This genotype is currently unknown outside north-western North America. Of historical and previously studied samples, the late 19th century samples (1891), obtained from mid-western North America, Minnesota and proposed as native genotypes in that region by Noyszewski et al. (2021), had the ITS-long genotype in our study; a 1935 specimen from Pullman, Washington, proposed to be an early European introduction by Kettenring et al. (2019), also had the ITS-long genotype; and a modern (2010) specimen from remote northern BC (Kitimat), interpreted as native by Jakubowski et al. (2014), but of mixed heritage by Kettenring et al. (2019), also had ITS-long in our study. In summary therefore, across North America, the ITS-long genotype may be present in both native and introduced RCG, whereas the ITS-short genotype appears to be a localised variant in the Pacific northwest.

The existence of distinctive North American genotype(s) (e.g. Noyszewski et al. (2021)) suggests that RCG was widespread in North America prior to the massive seeding of introduced agronomic genotypes in forage and revegetation seed mixes (Merigliano and Lesica 1998). However, there is still much uncertainty and, in some cases, disagreement, regarding the extent of distribution and location of present-day native RCG populations in North America (Jakubowski et al. 2013). One potential use of our relatively easily scored genetic marker would be to establish representation and association of the different ribotypes in native populations. Preliminary observations of the growth forms of our sampled RCG suggests that specimens with the ITS-short ribotype tended to be smaller, less strongly rhizomatous and were not noted to be invasive. However, there is no morphologically reliable method of distinguishing native from invasive RCG (Kettenring et al. 2019). The main indicators are vigour of growth and rhizomatous spread, but the usefulness of these indicators is uncertain and subject to environmental variation. Presently, molecular markers will likely remain the primary means of making broad surveys of RCG, to determine the geographical and ecological patterns of native persistence and to identify cryptic invasions of RCG across North America and the potential signature of intraspecific hybrids.


We thank Karin Kettenring, Karen Mock, Jim Walton (Utah State University) and Adam Pidwerberski (Prince Albert National Park, SK) for material of RCG; Frank Lomer for material of Phalaris canariensis; Timothy Whitfeld (Collections Manager) and staff of the University of Minnesota Herbarium, Bell Museum (MlN) for loan of specimens; Spencer Goyette and Linda Jennings (UBC Herbarium) for assistance; Hanna Schoenberg and Pinette Robinson for assistance with work at Elk Island National Park (contract no: 085-5P426); Edward Sun (UBC) for assistance in the laboratory; and Neil Anderson (University of Minnesota) for advice. We are grateful for a permit (no: 21-362) to collect at Miquelon Lake issued by Alberta Environment and Sustainable Resource Development. Lastly, we are grateful for reviews by Jeffrey Saarela, Neil Anderson and one annonymous reviewer that helped improve the manuscript.

Author contributions

QCBC planned the research; DMP conducted the lab work; both authors collected and analysed the data and both authors wrote the manuscript.


Supplementary materials

Suppl. material 1: Ten putative hybrids between ITS-long and ITS-short clades. 
Authors:  Diana M. Percy, Quentin C. B. Cronk
Data type:  occurrences
Brief description: 

Ten putative hybrids between ITS-long and ITS-short clades. Seven based on both sequence and assay data, one based on sequence data only (marked ^) and two samples which appeared hybrid in sequence data, but ITS-short in sizing assay data (marked with *). Region abbreviations: AB Alberta, BC British Columbia.

Suppl. material 2: Herbarium specimens used as outgroups. 
Authors:  Diana M. Percy, Quentin C. B. Cronk
Data type:  occurrences
Brief description: 

Herbarium specimens used as outgroups.

Suppl. material 3: Specimen details for all 94 samples genotyped. 
Authors:  Diana M. Percy, Quentin C. B. Cronk
Data type:  occurrences
Brief description: 

Specimen details for all 94 samples genotyped (86 Phalaris arundinacea and eight outgroup taxa sampled).

Suppl. material 4: Map of Elk Island National Park with the locations of 38 genotyped samples marked. 
Authors:  Diana M. Percy, Quentin C. B. Cronk
Data type:  occurrences
Brief description: 

Map of Elk Island National Park with the locations of 38 genotyped samples marked. Red crosses show the locations of the “short” ribotypes (n = 4); blue crosses “long” (n = 29), and orange circles putative hybrids (n = 5).

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