- Research article
- Open Access
Population genomics of an exceptional hybridogenetic system of Pelophylax water frogs
BMC Evolutionary Biology volume 19, Article number: 164 (2019)
Hybridogenesis can represent the first stage towards hybrid speciation where the hybrid taxon eventually weans off its parental species. In hybridogenetic water frogs, the hybrid Pelophylax kl. esculentus (genomes RL) usually eliminates one genome from its germline and relies on its parental species P. lessonae (genomes LL) or P. ridibundus (genomes RR) to perpetuate in so-called L-E and R-E systems. But not exclusively: some all-hybrid populations (E-E system) bypass the need for their parental species and fulfill their sexual cycle via triploid hybrid frogs. Genetic surveys are essential to understand the great diversity of these hybridogenetic dynamics and their evolution. Here we conducted such study using RAD-sequencing on Pelophylax from southern Switzerland (Ticino), a geographically-isolated region featuring different assemblages of parental P. lessonae and hybrid P. kl. esculentus.
We found two types of hybridogenetic systems in Ticino: an L-E system in northern populations and a presumably all-hybrid E-E system in the closely-related southern populations, where P. lessonae was not detected. In the latter, we did not find evidence for triploid individuals from the population genomic data, but identified a few P. ridibundus (RR) as offspring from interhybrid crosses (LR × LR).
Assuming P. lessonae is truly absent from southern Ticino, the putative maintenance of all-hybrid populations without triploid individuals would require an unusual lability of genome elimination, namely that P. kl. esculentus from both sexes are capable of producing gametes with either L or R genomes. This could be achieved by the co-existence of L- and R- eliminating lineages or by “hybrid amphigamy”, i. e. males and females producing sperm and eggs among which both genomes are represented. These hypotheses imply that polyploidy is not the exclusive evolutionary pathway for hybrids to become reproductively independent, and challenge the classical view that hybridogenetic taxa are necessarily sexual parasites.
Hybridization can promote adaptive divergence and speciation [1,2,3,4], but interspecific hybrids must first overcome the meiotic disorders associated with gametogenesis of diverged, non-coadapted genomes. The best-studied evolutionary strategies to bypass this barrier include clonal reproduction by parthenogenesis, gynogenesis/hybridogenesis  or allopolyploidy, by the production of unreduced diploid gametes [6, 7]. If they are accompanied by reproductive isolation with the parental taxa, these mechanisms can represent the first stages towards hybrid speciation [8, 9]. Nevertheless, hybrid taxa may still arise without clonality and polyploidization , and their contribution to biodiversity is presumed to be marginal . Characterizing the processes responsible for the maintenance of hybrid taxa is thus a fundamental step towards understanding how they can lead to speciation.
Hybridogenesis and polyploidization are well-known attributes of Pelophylax water frogs . The edible frog P. kl. esculentus is the hybrid between the pool frog P. lessonae (genomes LL) and the marsh frog P. ridibundus (genomes RR). It is often found in diploid form (LR) co-existing with one or both of the other parental species. In the lessonae-esculentus system (L-E), common in Western Europe, LR hybrids exclude their L genome and produce clonal R gametes. Inter-hybrid crosses yield unviable RR offspring because the R hemiclone irreversibly accumulated deleterious mutations through Müller’s ratchet [12,13,14]. Pelophylax. kl. esculentus must then backcross with LL P. lessonae to perpetuate, and is therefore considered a sexual parasite. In Eastern Europe, the system is essentially the reverse (ridibundus-esculentus, R-E): LR P. kl. esculentus hybrids predominantly produce L gametes and rely on RR P. ridibundus to reproduce.
Interestingly, P. kl. esculentus can also be widely found by itself in so-called all-hybrid populations (E-E system), where the life cycle is fulfilled by the production of polyploids. Female hybrids can produce bivalent LR eggs that develop into triploid LLR and RRL frogs upon fertilization by haploid L or R hemiclonal sperm, respectively [15,16,17]. These triploids may also produce unreduced gametes (e. g. LL sperm from LLR males, ). As the diploid genomes (LL or RR) are able to recombine in triploids, the all-hybrid population as a whole becomes a sexually functional unit . Yet it is worth noting the strong mutation load of such system, which induces RR and LL zygotes that do not reach sexual maturity . Hence the respective proportions of each gamete (LR, LL, R, L) produced by each sex of each hybrid type (LR, LLR, LRR) is key to the persistence of all-hybrid P. kl. esculentus populations at an evolutionary stable but sensitive equilibrium .
Comparative population genetics of P. kl. esculentus can shed light on the origin, composition and evolutionary dynamics of all-hybrid populations [20, 21]. Because of the high diversity of breeding systems, clonal genomes, sex-determination and genetic variation in this frog complex [21, 22], comparative analyses of closely-related groups of populations are of prime interest, since their biogeographic history should not be a confounding factor. In addition, many European populations have been largely compromised by multiple invasions of Pelophylax alien species, resulting in genetic pollution and/or disruption of their hybridogenetic complexes [23,24,25,26].
The present study focusses on Pelophylax populations from southern Switzerland, namely the canton of Ticino. This area is mostly inhabited by P. lessonae and P. kl. esculentus in its northern parts (L-E system) but P. lessonae frogs are missing from most of the southern parts, which may consist only of E-E systems [12, 27]. This set of populations could therefore provide a standardized framework in which to examine the composition and dynamics of L-E derived all-hybrid Pelophylax populations – P. ridibundus is naturally absent from the Apennine Peninsula, . The Ticino area also has the advantage of being free of alien Pelophylax taxa .
South-alpine populations are also attractive from a phylogenetic perspective. Our recent phylogeography of water frogs from the Apennine Peninsula revealed a cryptic nuclear lineage basal to the two known pool frog taxa (P. lessonae and P. bergeri), and restricted to the Alpine catchments valleys of the Po plain (named “Pelophylax. n. t. 2”, ). Mostly based on the intronic sequence marker Serum Albumin intron 1 (SAI-1), but lacking mitochondrial divergence, the origin of this lineage is pending additional analyses.
In order to characterize the genetic nature and hybridogenetic mechanisms of the subalpine Pelophylax populations, we conducted a population genomic and morphometric survey of nine sites inhabited by P. lessonae and P. kl. esculentus in southern Switzerland. The objectives were (1) to assess the genetic composition of putative L-E and E-E populations, (2) to understand whether E-E populations are maintained through triploid individuals or other mechanisms, and (3) to infer the nature and origin of the P. n. t. 2 lineage previously proposed .
Population genomics of Pelophylax in Ticino
In northern Ticino, we sampled both P. lessonae and P. kl. esculentus, occurring in syntopy at most sites (Fig. 1, Table 1). In southern Ticino, we only found P. kl. esculentus from the three extant water frog populations known, expect a few hundred meters from site STA, where we captured 5 females of the P. ridibundus morphotype (Fig. 1, Additional file 2: Table S1).
Genetic analyses corroborated our field observations. Based on 2521 SNPs, Bayesian clustering with STRUCTURE (k = 2) recovered the two main gene pools corresponding to P. lessonae (northern Ticino, Joux Valley, northern Italy) and P. ridibundus (STA). Hybrids P. kl. esculentus were accordingly assigned with half probabilities (Fig. 1). Analyses with increasing k separated P. lessonae from the north-alpine Joux Valley (k = 3) and distinguished the L genomes of southern Ticino hybrids (k = 4). The most likely k was k = 2 according to the Δk statistic (Δk = 3689.9) and k = 3 according to the L(k) statistic (L(k) = − 108,408.6). In south Ticino, one P. kl. esculentus (AGR08) featured the northern Ticino L genome, while all others had the southern Ticino L, or a mix of both (Fig. 1). The first axis of the PCA depicted a similar signal, highlighting the genetic structure within P. lessonae and between P. kl. esculentus from north and south Ticino (Fig. 2). Genetic diversity was accordingly higher for the hybrid P. kl. esculentus (Ho = 0.18–0.21) compared to the parental P. lessonae (Ho = 0.06–0.07) (Table 1, Additional file 1: Figure S1). The five P. ridibundus specimens featured very low heterozygosity (Ho = 0.02) (Table 1, Additional file 1: Figure S1).
All frogs from Ticino possessed P. lessonae mtDNA (Fig. 3). A single cyt-b haplotype (LES25s) was sequenced in all populations but a few additional ones were private from northern (LES22s, LES24s and LES28s) and southern Ticino (LES16s, LES30s). The P. ridibundus females from STA featured two different P. lessonae haplotypes (LES25s and LES30s).
Phylogenomics of Pelophylax in Ticino
Phylogenetic reconstruction of RAD sequences (13.1 kb) recovered the six species included in the analysis (Fig. 4). Parental Pelophylax frogs from northern Ticino all belong to a fully supported monophyletic P. lessonae clade, sister of P. bergeri, with little intraspecific structure. The five frogs from southern Ticino identified as P. ridibundus were accordingly grouped with our P. ridibundus reference samples.
Identification of triploids
We could not find evidence of triploid hybrid frogs in Ticino. No tri-allelic genotypes were found at the three diagnostic L/R microsatellite loci: Res16, Rica1b5 and Rica2a34, see Methods). For locus Res16, allele 127 was fixed in the R genome, while five different alleles segregate on the L genome, including allele 127 and a null allele (Additional file 2: Table S1). For locus Rica2a34, allele 106 and a null allele could be isolated from the R genome, while 16 other variants segregate on the L genome (Additional file 2: Table S1). Because of this strong variation, both in terms of polymorphism and amplification success, it was not appropriate to quantify the peak height ratio (PHR) between the two alleles of hybrid frogs for Res16 and Rica2a34. For locus Rica1b5, allele 137 was R-specific in all populations, while alleles 122, 123, 127 and 145 were L-specific (Additional file 2: Table S1). Fortunately, the majority of P. kl. esculentus frogs were represented by the nearly-identical genotypic profiles 122/137 (n = 31) and 123/137 (n = 20), which allowed for comparison of their PHR. Computed as log(H137 /H122–123) (see Methods), the PHR averaged − 0.22 (− 0.29 – − 0.09) in northern Ticino (putative L-E system) and − 0.19 (− 0.31 – − 0.03) in southern Ticino (putative E-E system, Fig. 5), which fall within the range obtained by Christiansen  for diploid LR frogs of an analogous genotype at this marker (120/136; PHR = − 0.23 – 0.00). In contrast, Christiansen  reported PHR averaging − 0.39 (− 0.54 – − 0.29) for LLR triploids and 0.17 (0.09–0.25) for LRR triploids at this genotype (illustrated in Fig. 5 for comparison).
RAD markers also supported diploidy for all hybrid frogs. Among the 2521 SNP genotypes, we identified 376 RAD tags with fixed differences between P. lessonae and P. ridibundus. For these L/R diagnostic loci, relative allele coverage (highest allele coverage/lowest allele coverage) tended towards 1 for all loci (mean = 1.1×, range: 1.01× − 1.3×). This average value (1.1×) was also obtained separately for northern (putative L-E system) and southern Ticino (putative E-E system) (Fig. 5). No frogs showed relative coverage ratios anywhere near 2×, as expected for LLR or LRR triploids.
A MANOVA analysis on Ticino frogs combining five morphometric variables (see Methods) suggested a significant effect of taxa (F = 54.1, P < 0.001) and population (F = 2.6, P < 0.001), but not of sex (F = 1.9, P = 0.10). PCAs on different sets of individuals (both sexes pooled) clearly differentiated the five P. ridibundus of site STA (Fig. 6, top), as well as between P. lessonae and P. kl. esculentus (Fig. 6, middle). The difference between northern and southern P. kl. esculentus was not obvious (Fig. 6, bottom), but remained significant even when including sex and population in the MANOVA (F = 4.7, P = 0.002).
Two contrasting hybridogenetic systems in Ticino
Several hybridogenetic systems are known from the Pelophylax model, where the hybrid P. kl. esculentus co-exists with either P. lessonae (L-E system), P. ridibundus (R-E system), sometimes with both (L-R-E system) and sometimes with neither (E-E system), in which case the sexual cycle relies on triploid individuals (see Background). In Ticino, we characterized two putatively different hybridogenetic systems in otherwise closely-related populations.
In northern Ticino, the hybrid P. kl. esculentus was found together with P. lessonae at sites BIA, CAM, GUD, PIA and LOS. At GOL (a river bank) only hybrids were captured but these frogs most likely breed elsewhere, perhaps at the nearby site LOS, where P. lessonae occurs in large numbers. Hence, all these populations fit the expectations of an L-E system, where P. kl. esculentus exclusively produces R gametes and backcrosses P. lessonae to perpetuate (Fig. 7a).
In southern Ticino however, we did not find P. lessonae at any site, despite equivalent search efforts. All populations were exclusively composed of P. kl. esculentus of both sexes, except for five females at site STA that we unexpectedly identified as P. ridibundus (Table 1). Several clues indicate that these P. ridibundus were not parental frogs, but rather the offspring of P. kl. esculentus × P. kl. esculentus hybrid crosses. First, P. ridibundus is not naturally present in Ticino and northern Italy; the closest naturally-connected populations are in Croatia . Second, all five possessed local P. lessonae mitotypes, while parental P. ridibundus normally conserve their maternal lineages throughout hybridogenesis, because of mating preferences: in mixed populations, the large P. ridibundus females are preferentially chosen by the males of the other smaller species, rarely the other way around (e.g. ). Third, the nuclear diversity of these females was extremely low (Ho = 0.02), as expected for hemiclonal RR individuals. Fourth, these frogs were much smaller (SVL = 45–65 mm) than regular P. ridibundus (up to 170 mm, ). While they could be subadults, all our other observations at the same time of the year in Ticino involved sexually mature frogs, and their small size could rather reflect the mutation load and low fitness expressed by diploid clonal RR genotypes. Although rarely fit, non-hybrid frogs are supposed to arise every year in all-hybrid populations [15, 31]. Hence, southern Ticino could be inhabited by all-hybrid E-E- systems that sometimes produce non-hybrid individuals.
Surprisingly however, we did not find evidence for mixed ploidy. First, L/R-diagnostic SNP alleles received even sequence coverage in all hybrids, as expected for LR diploids, where the L and R alleles should be present in equal quantities. While no confirmed triploid frogs could be included here as controls, the same approach efficiently disentangles diploids from asymmetric polyploids in other hybridogenetic systems (G Lavanchy, pers. com.). Second, no individual was tri-allelic at our diagnostic microsatellites. For the latter, the strong diversity of L alleles should have allowed to detect LLR individuals if these were present. Third, the allelic profiles of our hybrid frogs were far from the range of allele quantity difference reported for LRR frogs at the microsatellite locus RICA1b5 . Hence, the data at hand suggests that the putatively all-hybrid P. kl. esculentus populations of southern Ticino are maintained without triploids, unlike in other parts of Europe. This assumption necessitates confirmation by direct evidence from experimental crosses to trace allele inheritance, and from cytogenetics.
Alternatively, P. lessonae could be cryptically present in southern Ticino, in which case populations would be composed of unnoticed L-E systems. In a bioacoustic survey over 2001–2002, Mattei-Roesli & Maddalena  mostly reported P. kl. esculentus in this area, but suspected the presence of P. lessonae at a few sites. A few years before, Vorburger  identified two P. lessonae among tens of P. kl. esculentus captured nearby STA (locality Seseglio, now extinct). These observations could represent a recent shift in the composition of these populations (as seen elsewhere ), but they could also be the scarce LL offspring from hybrid crosses (rather than parental P. lessonae). Occasional dispersal from northern to southern Ticino is also possible, as illustrated by one “northern” frog caught at site AGR (Fig. 2). Therefore, formally rejecting the hypothetical presence of breeding P. lessonae in southern Ticino will require additional monitoring efforts throughout an entire breeding season.
On the causes and consequences of a putative diploid all-hybrid system
How could a diploid all-hybrid E-E hybridogenetic system perpetuate? To our knowledge, such situation has never been reported. Importantly, because sex is supposedly determined by an XY system , and because primary hybridization events preferentially involve P. lessonae males (LxLy) with P. ridibundus females (RxRx), the L hemiclone of P. kl. esculentus hybrids can carry either an X or a Y, while the R is strictly X-linked, i. e. hybrid males are LyRx and hybrids females are LxRx . Therefore, both sexes must provide L and R gametes so sons and daughters can be generated (Fig. 7b). As a consequence, RxRx females (like the ones we found in STA, see also ) and LxLy males should also be produced. However, it is worth noting that Vorburger  failed to obtain any viable metamorphs from a few inter-hybrid crosses from the extinct Seseglio site. This suggests an important hybridogenetic load and if they exist, that hybrid frogs producing both L and R gametes might be rather infrequent. In counterpart, the occasional LL and RR individuals would provide opportunities for recombination to purge deleterious mutations from hemiclones.
The pre-requisites of this putative diploid E-E system are difficult to reconcile given our current knowledge of Pelophylax gametogenesis. In R-E populations, P. kl. esculentus males can produce sperm of either hemiclones , or sometimes both simultaneously by hybrid amphispermy [35, 36]. We are not aware of reciprocal dynamics in female hybridogens, which either transmit their R hemiclone (in L-E systems), or both the R and L within diploid eggs (in regular E-E- systems with mixed ploidy) . Alternated L or R genome exclusion between hybrid females, or between the germ cells of the same female – what could be referred to as “hybrid amphigamy” – is yet to be documented. Nevertheless, gametogenesis and notably oogenesis might be more labile than previously assumed in diploid P. kl. esculentus , including the mechanism and timing of genome exclusion .
How could such a system arise? Lability in genome elimination could stem from a mixed origin of these frogs, involving secondary contact between L- and R-eliminating lineages. The amphispermic hybrid reported by Ragghianti et al.  was a cross between P. lessonae from a L-E system and P. ridibundus from a R-E system. Water frogs most likely colonized the south-alpine region from a Central European refugia, where a great diversity of hybridogenetic systems (including L-E and R-E populations) and clonal lineages co-exist .
The effective maintenance of a diploid P. kl. esculentus system, although pending further investigations to confirm the total absence of P. lessonae and of triploids, contributes to the ongoing debate of the evolutionary fate of hybridogenetic hybrids. First, since both genomes would be transmitted, this system challenges the usual view that hybridogenetic hybrids are sexual parasites . Second, it suggests that polyploidization is not required to become reproductively independent, as a preliminary stage of hybrid speciation. Triploidy is often seen as a springboard towards tetraploidy, from which hybrid species are easier to evolve . The diploid hybridogens from Ticino would emphasize an alternative pathway, although whether they are truly self-sustainable (if they reproduce by “hybrid amphigamy”) or rely on interdependent L- and R-eliminating lineages, remains an open question. In a later step, these populations could eventually evolve reproductive isolation from P. lessonae and P. ridibundus by allopatric divergence, leading to homoploid hybrid speciation. Such outcome yet appears unlikely given the frequent reshuffling of amphibian distributions throughout the Quaternary. For the time being, water frogs from Ticino represent some of the last genuine Pelophylax assemblages in Western Europe and offer a promising framework to study these fascinating aspects of hybridogenesis.
No evidence for a south-alpine endemic water frog lineage
In contrast to our previous investigations based on the SAI-1 intronic marker , we did not recover a south-alpine lineage endemic to Ticino and northern Italy using genome-wide RAD data. Instead, all pool frogs belonged to a monophyletic, well-supported P. lessonae clade (Fig. 4) and all possessed P. lessonae mitotypes (Fig. 3). SAI-1 thus features strong ancestral polymorphism and does not always seem representative of the evolutionary history of species, perhaps because it contains a retro-transposon . Hence, we recommend that phylogenetic and phylogeographic inferences relying on this marker to be treated with caution (e.g. [29, 41, 42]).
In particular, we previously hypothesized that the hemiclone of Italian hybrid frogs P. kl. hispanicus is related to an undescribed extinct lineage of Anatolian origin, based on SAI-1 variation (“P. n. t. 1”, clearly differing from the north-Italian hemiclones; ). Alternatively, this "lineage" could thus simply represent intraspecific SAI-1 alleles of P. ridibundus, or of a related Middle Eastern taxon. Yet, despite several molecular surveys focusing on this region [41, 42], such alleles have still never been reported from extant populations. Similarly, the Cyprus endemic P. cypriensis, which was described from mtDNA and nuclear SAI-1 divergence , deserves a re-evaluation. Pelophylax phylogeography and systematics are in clear need for more comprehensive molecular analyses, as offered by genome-wide loci.
Through a comprehensive genomic survey, we rejected the hypothesis of an endemic south-alpine lineage of Pelophylax water frogs, and emphasized two types of hybridogenetic systems from southern Switzerland: a rather classic P. lessonae – P. kl. esculentus (L-E) system in northern populations and a putatively all-hybrid P. kl. esculentus (E-E) system in the south, where frogs unexpectedly showed no sign of triploidy. Nevertheless, we cannot formally exclude the cryptic presence of P. lessonae in the latter, and call for future monitoring efforts in southern Ticino and nearby Italy. If confirmed, these all-hybrid diploids could persist by labile genome elimination, i. e. frogs produce eggs and sperm carrying L or R genomes indiscriminately, which would challenge the classic views that hybridogenetic hybrids are sexual parasites and that they require transient polyploid steps to reach sexual independence.
In July 2017 and 2018, nine localities were surveyed by day and night under good meteorological conditions for Pelophylax activity (sunny days, temperatures between 20 °C and 30 °C), covering the entire distribution of these frogs in the canton of Ticino (southern Switzerland) (Table 1). A total of 115 individuals were captured and identified based on the shape of their metatarsal tubercle . Buccal cells were sampled using non-invasive cotton swabs and adults (n = 111) were measured for the following variables, relevant for comparative morphometry in Pelophylax: snout-vent length (SVL), tibia length (LTi), total hind leg length (LTo), length (LMT) and height (HMT) of the metatarsal tubercle. Animals were sampled and measured directly in the field, and then immediately released at their place of capture.
DNA was extracted using the Qiagen BioSprint Robotic workstation. In complement, we included 18 DNA samples collected in the study area during Spring 2014, as well as 25 samples from other Pelophylax populations/species available from our previous studies [24, 29], used as references to identify the taxa inhabiting Ticino. The latter consisted of six P. lessonae from the Joux Valley (north-western Switzerland), four P. lessonae/P. kl. esculentus from northern Italy, nine P. bergeri from Italy and Corsica, two P. ridibundus from eastern Europe, two P. kurtmuelleri from Albania, one P. cretensis from Crete, and one P. c.f. bedriagae from Turkey. Full details are provided in Additional file 2: Table S1.
For mtDNA-based barcoding, a portion of cytochrome-b (cyt-b) was sequenced and aligned (511 bp) in 91 samples from Ticino, using custom Ranid-specific primers CytB-F2 (5′-TTAGTAATAGCCACAGCTTTTGTAGGC-3′) and CytB-R2 (5′-AGGGAACGAAGTTTGGAGGTGTGG-3′). Amplification were carried out in 25 μL reaction volumes, including 1 μL of each primers (10 μM), 7.5 μL of Qiagen Multiplex Primer Mix (MPMM, a premix including hot-start polymerase, dNTP and buffer), 12.5 μL of milli-Q water and 3 μL of template DNA. The PCR ran as follow: 95 °C for 15′, 35 cycles of 94 °C for 30″, 53 °C for 45″ and 72 °C for 1′, followed by 10′ at 72 °C. Longer cyt-b haplotypes published for 18 additional samples from this region  were included in the downstream analyses.
We prepared a double digest RAD (ddRAD) multiplexed library following the protocol by Brelsford et al. , which performs nicely for population genomics in anuran amphibians (e. g. ), including Pelophylax . The library contained the 133 frogs from Ticino plus the 25 reference samples, and was sequenced on two Illumina lanes (single read 125). Raw sequences were quality-checked (FastQC v0.10.1) and processed with Stacks v1.48  to demultiplex, stack and catalog homologous loci in all samples using the default -m -n, and -M values. We then called SNPs to conduct population genomic analyses on Ticino and the closely-related frogs from Joux and northern Italy. We flagged 17 Ticino samples featuring high rates of missing data with a custom python script (available at: https://github.com/DanJeffries/RADweek/blob/master/code/Summary_plotter.py), and subsequently outputted a genotype matrix for 126 samples, considering SNPs present in 80% of individuals of each population (2521 SNPs). We also produced a sequence alignment (13,098 bp from 111 RAD tags) for 45 non-hybrid individuals from different Pelophylax taxa, to be used in the phylogeny (list in Additional file 2: Table S1).
Genetic detection of triploid hybrids
We followed two separate approaches to identify the ploidy of hybrids P. kl. esculentus. First, we genotyped microsatellite loci known to co-amplify and have specific L and R alleles: RICA1b5, Res16 and RICA2a34 (reviewed in ). Triploids may be tri-allelic, or, in the absence of polymorphism on the duplicated genome, one allele should be amplified in double quantity compared to the other. Because the amplification performance of microsatellites is also affected by allele size and potential nucleotide mismatch on the priming sequence, the height of the absorbance peaks must be interpreted with caution and independently for different genotypes. Christiansen  calibrated such approach for several northeastern European genotypes and showed that their peak height ratio (PHR) were not overlapping between LLR, LR and LRR hybrids, and could thus be used as an identification tool.
We amplified the three loci in 113 water frogs from Ticino by 10 μL multiplexed PCRs containing 3 μL of MPMM, 2.2 μL of milli-Q water, 3 μL of template DNA, as well as primers (10 μM) for RICA1b5 (0.1 μL each), Res16 (0.3 μL each) and RICA2a34 (0.5 μL) each. PCRs were conducted as follow: 95 °C for 15′, 35 cycles of 94 °C for 30″, 53 °C for 45″ and 72 °C for 1′, followed by 30′ at 60 °C. Amplicons were diluted 4× and run on an ABI Prism 3100 genetic analyzer. Importantly, PCR conditions and dilution were optimized to ensure the readability of absorbance peaks. Peaks were scored and their height measured with GeneMapper 4.0 (Applied Biosystems). When comparable (see Results), we calculated the PHR as log(HR/HL), where HR is the height of the R-specific allele, and HL is the height of the L-specific allele, following Christiansen .
Our second approach aimed at comparing the coverage (sequence depth) between RAD tags with fixed L-R differences. In LR diploids, the two alleles should have approximately been sequenced at the same depth, and so their relative coverage should on average tend towards one. In LLR and LRR triploids however, one allele should have been sequenced twice compared to the other and so their relative coverage should on average tend towards two. To compute L-R coverage differences, we first flagged SNPs that were fixed between the R and the L genome, i. e. with allele frequency differences of 1.0 between the frogs identified as P. lessonae (LL) and P. ridibundus (RR) in our study area (see Results). For each of these SNPs, we then calculated the ratio of the highest allele coverage by the lowest, for every P. kl. esculentus hybrid frog identified in the study area.
Population genetic analyses
We explored the genetic structure of the water frog populations from Ticino, Joux and northern Italy based on our matrix of 2521 SNPs (n = 126 individuals). First, we used the Bayesian clustering algorithm of STRUCTURE  with the admixture model and performed three replicate runs from k = 1 to 6, each with 100,000 iterations after a burnin period of 10,000. Because the divergence between the L and R genomes (~ 16Mya, G. Mazepa unpublished data) pre-date any intraspecific differentiation, we expected two major gene pools and thus k = 2 as the most informative solution, which we verified with STRUCTURE Harvester . Second, we conducted a Principal Component Analyses (PCA) on individual genotypes with the R packages adegenet and ade4. We also computed average heterozygosity for each population with n ≥ 5, separately for P. lessonae, P. kl. esculentus and P. ridibundus.
In addition, we visualize mitochondrial sequence variation of our ~ 500 bp cyt-b fragment in Ticino by an haplotype network (TCS, ).
We conducted a Bayesian phylogenetic reconstruction of RAD sequences of non-hybrid frogs from Ticino, complemented by reference individuals from six different species (n = 45, 13.1 kb; Additional file 2: Table S1). This analysis was performed in BEAST (BEAST 2.4.8, ). We used a lognormal relaxed molecular clock calibrated to the divergence of the Cretan endemic P. cretensis at the end of the Messinian Salinity Crisis at 5.33 ± 1.0 Mya , and the midpoint root between pool frogs (here represented by P. lessonae and P. bergeri) and marsh frogs (here represented by P. ridibundus, P. cf. bedriagae, P. cretensis and P. kurtmuelleri) at 16 ± 3.0 Mya My (G. Mazepa, unpublished data), using normally distributed priors and a birth-death tree model. We applied a GTR + G substitution model (BEAST package bModelTest; ) and ran the chain for 100 million iterations, sampling one tree every 50,000. We verified stationarity and effective sample sizes of parameters with Tracer 1.5, and built maximum-clade credibility trees with the BEAST module TreeAnnotator, discarding the first 20% of sampled trees as burnin.
The morphology of Ticino frogs was assessed using the field-measured variables LTi, LTo, LMT and HMT corrected by individual size (SVL), as well as the ratio LMT/HMT, which reflects the shape of the metatarsal tubercle (an important anatomical feature to compare Pelophylax taxa and their hybrids, ). Combining these five variables, the general morphology was first compared between species, sex and population by a MANOVA. Because there were no significant differences between sexes (see Results), we then conducted several PCA analyses (ade4 package in R) with males and females pooled together.
Availability of data and materials
Microsatellite genotypes, cyt-b haplotypes and morphometric measurements are provided in Additional file 2: Table S1. cyt-b haplotype sequences are available on GenBank (MF094328-MF094354). Raw sequence reads from the RAD libraries are available on the NCBI SRA archive under bioproject PRJNA549908.
- cyt-b :
double digest restriction site associated DNA
- E-E system:
metatarsal tubercle height
- L-E system:
metatarsal tubercle length
total hind leg length
multivariate analysis of variance
- n. t.:
principal component analysis
polymerase chain reaction
peak height ratio
restriction site associated DNA
restriction site associated DNA-sequencing
- R-E system:
Serum-Albumin intron 1
single nucleotide polymorphism
Seehausen O. Hybridization and adaptive radiation. Trends Ecol Evol. 2004;19:198–207.
Mallet J. Hybrid speciation. Nature. 2007;446:279–83.
Mallet J. Hybridization, ecological races and the nature of species: empirical evidence for the ease of speciation. Philos Trans Royal Soc B. 2008;363:2971–86.
Soltis P, Soltis D. The role of hybridization in plant speciation. Annu Rev Plant Biol. 2009;60:561–88.
Dawley RM. An introduction to unisexual vertebrates. In: Dawley RM, Bogart JP, editors. Evolution and Ecology of Unisexual Vertebrates. Albany, New York: New York State Museum; 1989. p. 1–18.
Arnold ML. Natural hybridization and evolution. New York: Oxford University Press; 1997.
Stöck M, Lamatsch DK, Steinlein C, Epplen J, Grosse W-R, Hock R, et al. A bisexually reproducing all-triploid vertebrate. Nature Genet. 2002;30:325–8.
Rieseberg LH, Willis JH. Plant speciation. Science. 2007;317:910–4.
Abbot R, Albach D, Ansell S, Arntzen JW, Baird SJE, et al. Hybridization and speciation. J Evol Biol. 2013;26:229–46.
Choleva L, Janko K. Rise and persistence of animal polyploidy: evolutionary constraints and potential. Cytogenet Genome Res. 2013;140:151–70.
Graf J-D, Polls PM. Evolutionary genetics of the Rana esculenta complex. In: Dawley R, Bogart JP, editors. Evolution and ecology of unisexual vertebrates. Albany, New York: New York State Museum; 1989. p. 289–301.
Vorburger C. Fixation of deleterious mutations in clonal lineages: evidence from hybridogenetic frogs. Evolution. 2001;55:2319–32.
Guex GD, Hotz H, Semlitsch RD. Deleterious alleles and differential viability in progeny of natural hemiclonal frogs. Evolution. 2002;56:1036–44.
Bove P, Milazzo P, Barbuti R. The role of deleterious mutations in the stability of hybridogenetic water frog complexes. BMC Evol Biol. 2015;14:107.
Christiansen DG, Fog K, Pedersen BV, Boomsma JJ. Reproduction and hybrid load in all-hybrid populations of Rana esculenta water frogs in Denmark. Evolution. 2005;59:1348–61.
Arioli M. Reproductive patterns and population genetics in pure hybridogenetic water frog populations of Rana esculenta. PhD thesis. University of Zurich, Ecology department; 2007:154. http://www.dissertationen.uzh.ch.
Pruvost NBM, Hoffmann A, Reyer H-U. Gamete production patterns, ploidy, and population genetics reveal evolutionary significant units in hybrid water frogs (Pelophylax esculentus). Ecol Evol. 2013;3:2933–46.
Christiansen DG, Reyer HU. From clonal to sexual hybrids: genetic recombination via triploids in all-hybrid populations of water frogs. Evolution. 2009;63:1754–68.
Christiansen DF. Gamete types, sex determination and stable equilibria of all-hybrid populations of diploid and triploid edible frogs (Pelophylax esculentus). BMC Evol Biol. 2009;9:135.
Mikulicek P, Kautman M, Demovic B, Janko K. When a clonal genome finds its way back to a sexual species: evidence from ongoing but rare introgression in the hybridogenetic water frog complex. J Evol Biol. 2014;27:628–42.
Hoffman A, Plötner J, Pruvost NBM, Christiansen DG, Röthlisberger S, Choleva L, et al. Genetic diversity and distribution patterns of diploid and polyploid hybrid water frog populations (Pelophylax esculentus complex) across Europe. Mol Ecol. 2015;24:4371–91.
Berger L, Uzzell T, Hotz H. Sex determination and sex ratios in western Palearctic water frogs: XX and XY female hybrids in the Pannonian Basin? Proc Acad Nat Sci Phila. 1988;140:220–39.
Holsbeek G, Jooris R. Potential impact of genome exclusion by alien species in the hybridogenetic water frogs (Pelophylax esculentus complex). Biol Invasions. 2015;12:1–13.
Dufresnes C, Di Santo L, Leuenberger J, Schuerch J, Mazepa G, Grandjean N, et al. Cryptic invasion of Italian pool frogs (Pelophylax bergeri) across Western Europe unraveled by multilocus phylogeography. Biol Invasions. 2017a;19:1407–20.
Dufresnes C, Denoël M, Di Santo L, Dubey S. Multiple uprising invasions of Pelophylax water frog, potentially inducing a new hybridogenetic complex. Sci Rep. 2017b;7:6506.
Dufresnes C, Leuenberger J, Amrhein V, Bühler C, Thiébaud J, Bohnenstengel T, Dubey S. Invasion genetics of marsh frogs (Pelophylax ridibundus sensu lato) in Switzerland. Biol J Linn Soc. 2018a;123:402–10.
Mattei-Roesli M, Maddalena T. La situazione delle Rane verdi (Rana esculenta L., 1758 e Rana lessonae Camerano, 1882) nel Cantone Ticino (Svizzera). Bollettino della Società ticinese di Scienze naturali. 2006;94:61–7.
Dufresnes C. Amphibians of Europe, North Africa and the Middle East. London: Bloomsbury; 2019.
Dubey S, Dufresnes C. An extinct vertebrate preserved by its living hybridogenetic descendant. Sci Rep. 2017;5:12768.
Christiansen DG. A microsatellite-based method for genotyping diploid and triploid water frogs of the Rana esculenta hybrid complex. Mol Ecol Notes. 2005;5:190–3.
Vorburger C. Non-hybrid offspring from matings between hemiclonal waterfrogs suggest occasional recombination between clonal genomes. Ecol Lett. 2001b;4:628–36.
Hotz H, Berger L, Uzzell T, Tunner HG, Beerli P, Guex G-D. Sex determination, sex linkage, and two kinds of unisexuality among XX and XY genotypes in western Palearctic water frogs. In: Catzeflis FM, Gautier M, editors. Evolution 93, vol. 181. Montpellier: Fourth Congress of the European Society for Evolutionary Biology; 1993.
Schempp W, Schmid M. Chromosome banding in Amphibia. VI. BrdU-replication patterns in Anura and demonstration of XX-XY sex chromosomes in Rana Esculenta. Chromosoma. 1981;83:697–710.
Dedukh D, Litvinchuk S, Rosanov J, Shabanov D, Krasikova A. Mutual maintenance of di- and triploid Pelophylax esculentus hybrids in R-E systems: results from artificial crossings experiments. BMC Evol. Biol. 2017;17:220.
Vinogradov AE, Borkin LJ, Günther R, Rosanov JM. Two germ cell lineages with genomes of different species in one and the same animal. Hereditas. 1991;114:245–51.
Ragghianti M, Bucci S, Marracci S, Casola C, Mancino G, Hotz H, et al. Gametogenesis of hybrids between two population systems of hemiclonally reproducing water frogs. Genet Res. 2007;89:39–45.
Doležálková M, Sember A, Marec F, Ráb P, Plötner J, Choleva L. Is premeiotic genome elimination an exclusive mechanism for hemiclonal reproduction in hybrid males of the genus Pelophylax? BMC Genet. 2016;17:100.
Lehtonen J, Schmidt DJ, Heubel K, Kokko H. Evolutionary and ecological implications of sexual parasitism. Trends Ecol Evol. 2013;28:297–306.
Cunha C, Doadrio I, Coelho MM. Speciation towards tetraploidization after intermediate processes of non-sexual reproduction. Phil. Trans. R. Soc. Lond. B biol. Sci. 2008;363:2921–9.
Plötner J, Köhler F, Uzzell T, Beerli P, Schreiber R, Guex GD, Hotz H. Evolution of serum albumin intron-1 is shaped by a 5′ truncated non-long terminal repeat retrotransposon in western Palearctic water frogs (Neobatrachia). Mol Phylogenet Evol. 2009;53:784–91.
Plötner J, Uzzell T, Beerli P, Akın C, Bilgin CC, Haefeli C, et al. Genetic divergence and evolution of reproductive isolation in eastern Mediterranean water frogs. In: Glaubrecht M, Schneider H, editors. Evolution in action. Case studies in adaptive radiation and the origin of biodiversity. Special volume from the SPP 1127 “Radiations – Genesis of Biological Diversity” of the DFG. Berlin: Heidelberg: Springer; 2010. p. 372–403.
Plötner J, Baier F, Akin C, Mazepa G, Schreiber R, Beerli P, et al. Genetic data reveal that water frogs of Cyprus (genus Pelophylax) are an endemic species of Messinian origin. Zoosystematics Evol. 2012;88:261–83.
Brelsford A, Dufresnes C, Perrin N. High-density sex-specific linkage maps of a European tree frog (Hyla arborea) identify the sex chromosome without information on offspring sex. Heredity. 2016a;116:177–81.
Dufresnes C, Mazepa G, Rodrigues N, Brelsford A, Litvinchuk SN, Sermier R, et al. Genomic evidence for cryptic speciation in tree frogs from the Apennine Peninsula, with description of Hyla perrini sp. nov. Front. Ecol. Evol. 2018b;6:144.
Jeffries DL, Lavanchy G, Sermier R, Sredl MJ, Borzée A, Barrow LN, et al. A rapid rate of sex-chromosome turnover and non-random transitions in true frogs. Nat Commun. 2018;9:4088.
Catchen J, Hohenlohe P, Bassham S, Amores A, Cresko W. Stacks: an analysis tool set for population genomics. Mol Ecol. 2013;22:3124–40.
Leuenberger J, Gander A, Schmidt BR, Perrin N. Are invasive marsh frogs (Pelophylax ridibundus) replacing the native P. lessonae / P. esculentus hybridogenetic complex in Western Europe? Genetic evidence from a field study. Conserv. Genet. 2014;15:869–78.
Pritchard JK, Stephens M, Donnelly P. Inference of population structure using multilocus genotype data. Genetics. 2000;155:945–59.
Earl DA, vonHoldt BM. STRUCTURE HARVESTER: a website and program for visualizing STRUCTURE output and implementing the Evanno method. Conserv. Genet. Resour. 2012;4:359–361.
Clement M, Posada D, Crandall KA. TCS: a computer program to estimate gene genealogies. Mol Ecol Notes. 2000;9:1657–9.
Bouckaert R, Heled K, Khünert D, Vaughan T, Wu CH, Xie D, et al. BEAST 2: a software platform for Bayesian evolutionary analysis. PLoS Comput Biol. 2014;10:e1003537.
Beerli P, Hotz H, Uzzell T. Geologically dated sea barriers calibrate a protein clock for Aegean water frogs. Evolution. 1996;50:1676–87.
Bouckaert RR, Drummond AJ. bModelTest: Bayesian phylogenetic site model averaging and model comparison. BMC Evol Biol. 2017;17:42.
We thank G. Mazepa for sharing samples used in the phylogeny and G. Lavanchy for his useful feedback on a previous version of this manuscript. We are also grateful to the karch (B. Schmidt) for support, as well as the LBC (L. Fumagalli) for lab access.
This study was funded by the Federal Office for the Environment (FOEN/OFEV/BAFU; Francis Cordillot), the Museo cantonale di storia natural of Lugano and the Fondation des Bolle di Magadino. The funding bodies were not involved in the design of the study, collection, analysis, interpretation of data, and the writing of the manuscript.
Frogs were captured following collecting permits issued by the relevant Institutional Animal Care and Use Committee, namely the Ufficio della natura e del paesaggio.
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About this article
- Hybrid speciation
- Hybrid amphigamy
- Hybrid amphispermy
- Pelophylax kl. esculentus
- P. lessonae
- Sex chromosomes
- Water frogs