- Research article
- Open Access
Conservation implications of asymmetric introgression and reproductive barriers in a rare primrose species
BMC Plant Biology volume 19, Article number: 286 (2019)
Primula is a large genus of flowering herbs well known for their heterostyly. Currently few natural hybrids are known and reproductive barriers in this genus in the wild have received little attention. However, there is instance of hybridization between rare and widely-spread species, and conservation implications of such situation is poorly understood. In the present study, we investigated hybridization patterns and reproductive barriers between a wide spread species, Primula poissonii and a rare species P. anisodora, of which only three populations are currently known.
Pollinator-mediated reproductive isolation was strong between parental species but not significant between hybrids and parental species. Hand pollination experiments showed significant reduction of both fruit- and seed-set for heterospecific pollination as compared with conspecific pollination for both parental species. Furthermore, hybrids had higher fruit- and seed-set when pollinated with P. anisodora pollen as opposed to P. poissonii pollen. Microsatellites identified backcrosses to P. anisodora in two of the three populations of P. anisodora, and additionally more individuals of P. anisodora showed introgression from P. poissonii than vice versa.
These results provide evidence for potential genetic swamping of the P. anisodora populations, which could pose a serious threat for this locally endemic species.
Natural hybridization is of significance in the study of several aspects of evolution, including the origins of new ecotypes or species, the origin and transfer of genetic adaptations, and the reinforcement or breakdown of reproductive barriers [1,2,3]. However, natural hybridization can also be a serious threat to rare plant species because of pollen and/or ovule discounting in the process of hybridization, if hybrids are sterile and/or have low viability. Furthermore, there can be a risk of genetic swamping by which partially fertile and viable hybrids are replacing pure parental genotypes [4, 5].
It is generally believed that habitat disturbance can be a driving force for hybridization [6,7,8], as it can alter patterns of contact between reproductively compatible species, favoring successful establishment of hybrids due to, for example, the creation of suitable intermediate habitats. Human mediated hybridization is expected to increase worldwide and therefore potential threats to rare species are becoming more serious than ever before. In developed countries (e.g. US, Canada) conservation issues arising from hybridization have been well explored and even addressed by national conservation regulations [4, 7, 9, 10]. In contrast, there seems to be little research effort in developing countries to address the matter, which impacts negatively on the awareness of policymakers with regards to the involved threats posed by anthropogenic change of the environment.
Though hybridization in plants has been frequently reported, most cases involve wide spread species with limited numbers of hybrid zones occurring in their sympatric distribution areas [7, 11,12,13]. In such scenarios, there is little risk to either species, as geographical isolation is still strong enough to maintain populations of both species with minimal to no introgression. If, however, one of the hybridizing species has a narrow distribution, all of its populations might be exposed to geneflow from the other species.
Primula is a large plant genus (> 500 species) that is well known for its heterostyly. Interspecific hybridization and reproductive isolation have been studied for over a century in two European species; however other species of the genus have received barely any attention in this regard . In the present study we investigated patterns of hybridization and reproductive barriers between the wide spread species Primula poissonii and the rare species P. anisodora, for which only three populations are currently known. Both of the species are heterostylous. Our aims were to (1) clarify the genetic structure of a hybrid swarm between these two species, and (2) investigate how reproductive barriers contribute to the pattern of hybridization; and then (3) assess the role of hybridization for the conservation of P. anisodora in order to develop meaningful conservation management strategies.
Pollinator mediated reproductive isolation (RI)
For the pollinator observations in the natural setting, focusing on pure parental species, we observed a total of 804 visits by insects to flowers of P. poissonii: 347 visits by bumblebees (43%), 224 by bees (Anthophora sp., 28%), 217 by butterflies (27%) and 16 by hoverflies (2%). For P. anisodora plants, 435 visits were recorded: 336 by bumblebees (77%), 96 by bees (Anthophora sp., 22%) and only three visits by butterflies (0.3%). Although bumblebees are the dominant pollinator for both parental species, they make up a significantly higher proportion of overall visits for P. anisodora (77% vs 43%, χ2 = 131.2; p < 0.001). Furthermore, butterflies were important pollinators for P. poissonii, but seemed to only accidentally end up on a P. anisodora flower.
A total of 124 pollination bouts were observed in Plot 1, including 31 cross-specific and 93 con-specific bouts. A total of 276 transitions were observed, including 71 heterospecific transitions. Thus the overall ethological RI in Plot 1 between parental species = 1–31/124 * 71/276 = 0.940. For Plot 2, a total of 144 bouts were observed, including 39 cross-specific and 105 con-specific bouts. A total of 443 transitions were observed, including 88 bouts with heterospecific transitions. The overall ethological RI in Plot 2 between parental species = 1–39/144 * 88/443 = 0.946.
In Plot 3, 114 bouts (39 solely within species/hybrids) were observed, and a total of 561 transitions were observed from one plant to another. Of these transitions, 404, accounting for 72% of the total, were within taxa. The remaining 157 transitions, accounting for 18% of the total, occurred between species (Fig. 1; Additional file 3: Table S3). The group of pollinators for which most visitations, and hence transitions, was observed were bees (Anthophora sp.), but for P. poissonii butterflies (Aporia bieti) were much more frequent visitors (Fig. 1). For butterflies no heterospecific transition was observed between the two species, but transitions between P. poissonii and hybrids did occur (Fig. 1); only bees and bumblebees realized heterospecific transitions, but also very few in comparison to conspecific transitions. However, transitions between either species and hybrids occurred much more frequently (Fig. 2), with no bias towards any of the parental species (hybrids x P. anisodora vs. hybrids x P. poissonii: 66 vs. 63; χ2 = 0.09; p = 0.7). So we were able to reject the hypothesis that directions of hybridization and/or backcrossing was determined by the flight behavior of the pollinators.
Hand pollination experiments
Between parental species
Results from fruit- and seed-set showed nearly exactly the same pattern: when a certain type of cross resulted more often in fruit set, that type of cross also resulted, on average, in higher seed numbers per fruit (Fig. 3a, b). Furthermore, both species produced comparable numbers of seed as there was no significant effect of the factor ‘Mother Species’ on fruit-set or seed-set (Table 1). As expected intra-morph (pin-pin, thrum-thrum) cross pollinations produced significantly lower number of fruits and seeds than inter-morph (pin-thrum, thrum-pin) cross pollinations (Fig. 3a, b; ‘Cross Type’ in Table 1). Thrum flowers seemed to be more selective, as they produced many fewer fruits/seeds from inter-specific pollen. Overall P. anisodora was the more successful pollen-parent, and this was most pronounced in intra-morph pollinations (Fig. 3a, b ‘Pollen Source’, ‘Pollen Source x Cross Type’, ‘Pollen Source x Mother Species’ and ‘Pollen Source x Flower Type’ in Table 1).
The three-way ANOVA analysis for intra-specific crosses (8 treatments) suggested that inter-morph pollination can produce significantly higher numbers of fruits (F = 159.8, p < 0.001), seed numbers per fruits (F = 168.4, p < 0.001) and seed numbers per flower (F = 115.4, p < 0.001) than those produced from intra-morph pollination treatments (‘Cross type’ in Additional file 2: Table S2).
Between parental species and hybrids
In total, 7 of the 16 cross-pollination treatments between hybrids and parental species did not produce any fruits. Especially, P. poissonii pollen failed to produce any seed on hybrid mothers (Fig. 3a, b, ‘hybrids’), accounting for six of the failed pollination treatments (Additional file 1: Table S1). This resulted in significantly lower fruit-set and seed numbers following pollinations between hybrids and P. poissonii (16/143 = 11.2%) compared to hybrids and P. anisodora (37/168 = 22.0%), (fruit-set: χ2 = 5.67; p = 0.02); seed numbers (hybrids x P. poissonii 6.25 vs. hybrids x P. anisodora 10.75; Mann-Whitney U = 14, p = 0.048, Additional file 1: Table S1).
Population genetic analysis
We genotyped 168 accessions for all 6 nuclear microsatellite loci screened across three allopatric populations and the hybrid zone: only two accessions failed to amplify at all loci (Ab17 for P39450–2 and AX9 for P28273). There was a single instance of evidence for linkage disequilibrium among the pairs of loci (P39450–2/P47381) in the hybrids in the Baishuitai population. There was one locus (P33802) displaying deviation from Hardy–Weinberg equilibrium (HWE) in the Xiaoyanjing population. As no consistent patterns of deviations from HWE or linkage equilibrium were detected across sites, downstream analyses were based on genotypic data at all microsatellite loci [14, 15].
Population genetic analysis showed that the putative hybrids had the highest numbers of effective alleles (2.136), and the highest observed (0.573), expected (0.511) and unbiased expected heterozygosity (0.518) (Additional file 4: Table S4). Pairwise FST values between parental species and putative hybrids among populations were highest between P. poissonii at Shangri-La and P. anisodora in Langdu (0.614) and lowest of P. anisodora between Baishuitai and Langdu populations (0.045). Within the hybrid zone in Baishuitai, the highest pairwise FST value was (0.472) between parental species whereas hybrids and P. anisodora has lowest FST value (0.119), and intermediate FST value (0.177) between hybrids and P. poissonii (Additional file 5: Table S5).
Parent and hybrid assignment
The value of ΔK was clearly highest for K = 2, and therefore we carried out all further analyses assuming two clusters (Additional file 7: Figure S2). Following ten independent Structure runs with K = 2, individuals of the Shangri-La population that had been identified morphologically as P. poissonii were assigned to one cluster with high probability, whereas those identified by us as P. anisodora had been assigned to the second cluster with similarly high probability (Fig. 4a). However, in the Xiaoyanjing population three accessions show certain amounts of mixed ancestry (P. anisodora cluster proportion < 90%), suggesting the occurrence of hybridization in the past. Within the Baishuitai hybrid zone, 13 accessions of P. anisodora and three accessions of P. poissonii show the same pattern, with the main cluster ancestry being < 90% indicative of introgression.
The proportion of backcrossed individuals of P. anisodorais higher than the proportion of backcrossed individuals of P. poissoniiin the hybrid zone (13:3; χ2 = 5.67, df = 1, p = 0.018). Overall, two of the three investigated P. anisodora populations show signs of present or past introgression from P. poissonii (Fig. 4a).
The output from NewHybrids is in agreement with the clustering in Structure: the same 13 individuals of P. anisodora and three individuals of P. poissonii have posterior probabilities of less than 90% that they are not of hybrid origin (Fig. 4b). Hence, significantly more P. anisodora individuals show traces of introgression than P. poissonii (χ2 = 6.71, df = 1, p = 0.01). Of the 39 putative hybrids, two were identified as pure P. anisodora with posterior probabilities > 90%, whereas 30 as backcrosses to P. anisodora with posterior probabilities > 60%. The remaining hybrids, with any posterior probabilities< 60%, were all classified as later generation hybrids (Fig. 4b). Noticeably, no individuals in the hybrid zone were identified as F1 (in all cases the posterior probability for this class was under 30%).
Of the 150 individuals simulated from the Baishuitai data, 134 individuals were assigned to the correct class with > 90% probability, thus 89.4% assignment success was identified according to our SSRs. Of the F1s and simulated parental species, 100% were correctly assigned.
Pre- and post- zygotic reproductive barriers to hybrid formation
In the sympatric hybrid zone in Baishuitai, the flowering periods of P. poissonii and P. anisodora overlapped completely. However, despite this no F1 s were detected with nearly 100% distinguishing power from hybrid simulations for this category.Part of this lack can likely be explained by the relatively high constancy of the pollinators (Fig. 2, conspecific vs. heterospecifc), combined with the observation that P. poissonii is largely pollinated by butterflies (Fig. 1), which generally do not visit P. anisodora at all. That this initial stage of hybridization can be expected to be rare is also visible from the overall ethological reproductive isolation indexes at the pollination stage in both P. poissonii- and P. anisodora-dominated parts of the population (Plot 1 and Plot 2), which were both above 0.94. Furthermore, certain intrinsic compatibilities between the species seem to exist, as conspecific pollinations produced significantly more fruit and seed than heterospecifc ones (Fig. 3; pin/thrum, thrum/pin), although considerable amounts of seed were produced, especially for pairings where intra-species-morph incompatibilities exist (Fig. 3, pin/pin).
Different isolating barriers act in hierarchical order, and thus early barriers can contribute more to total isolation than late barriers [16, 17], suggesting a key role for pollinator-mediated reproductive isolation between parental species, as evidenced by the high ethological reproductive isolation. We assume that the different flower colors (deep-red vs. magenta) are differently attractive for the two major pollinator groups (bees/bumblebees vs. butterflies), but additionally the flower orientation in P. anisodora (drooping) makes it very difficult for butterflies to access them. This results in bees and bumblebees preferring P. anisodora, but occasionally visiting P. poissonii, while butterflies are restricted to P. poissonii. However, as no mechanical barrier exists, transition rates of bees/bumblebees could be locally altered by context-dependent selection, as exemplified by hybridization patterns between Rhinanthus minor and R. angustifolius . Although the initial formation of F1s is rare, as soon as some hybrids exist, further hybridization seems to be facilitated by partial breakdown of pollinator discrimination, as pollinators showed many more transitions between hybrids and parental species than between parental species (Fig. 2, heterospecifc vs. hybrid).
Highly asymmetric introgression
The genetic data provided evidence for significant introgression into P. anisodora, while only few P. poissonii individuals showed such signs (Fig. 4a, b). Asymmetry in backcrossing is not uncommon in nature, assuming asymmetric strength of reproductive barriers in both pre- and post-zygotic stages - it can even be expected [4, 19,20,21,22]. With regards to pre-zygotic isolation, no significant difference between transition rates from hybrids to P. anisodora (66) and hybrids to P. poissonii (63) was apparent in the observed pollinators, and hence is unlikely to have an effect on the direction of backcrossing. On the other hand, intrinsic compatibilities seemed to favor backcrossing to P. anisodora, ashybrid mothers were only successfully fertilized by P. anisodora pollen. It should be noted that as no F1s were detected in the hybrid zone, most hybrids that were included in the pollinator observations and hand pollination experiments were probable backcrosses to P. anisodoraand potentially other types of later generation hybrids, but likely with reduced P. poissonii heritage. This might have led to comparably lower RI between hybrids in our study and P. anisodora plants, than would have been detected if F1s had been involved, but does not entirely explain why hybrids did not produce fruit from P. poissonii pollen, as P. anisodora plants could be fertilized.
Additionally, one factor contributing to the asymmetry could be the differences in abundance of the two species: many more flowering plants of P. poissonii than P. anisodora were present in the population in Baishuitai, reaching a ratio of nearly 4:1 in the sympatric area (in 2017). Assuming that some F1s have been formed, and that pollinators distinguish well between species but worse between hybrids and either of the species, abundance differences in the parental species would lead to a skew just by sampling bias. E.g. for a ratio of 4:1 (P. poissonii to P. anisodora), and including 4% hybrids or: 76.8% P. poissonii, 19.2% P. anisodora, 4% hybrids, assuming pollen will originate from the species and hybrids with equal likelihood, hybrid pollen (as compared to conspecific pollen) being deposited on P. poissonii and P. anisodora flowers would be 4 / (4 + 76.8) = 4.95%, and 4 / (4 + 19.2) = 17.2%, respectively. Furthermore, for hybrids, only pollen from P. anisodora would lead to fertilization, reinforcing the bias.
Conservation management of P. anisodora to prevent genetic swamping
As P. anisodora has only three currently known wild populations, and it is known to hybridize with a widely distributed species, conservation may be necessary to prevent genetic swamping. According to our results, the population of P. anisodora in Baishuitai was severely affected by introgression of P. poissonii markers, indicating that a threat of genetic swamping might exist. In a second population in Xiaoyanjing, in which no other Primula species were found, only four individuals out of 20 showed possible introgression of P. poissonii. The last sampled population of P. anisodora, in Langdu, had no evidence of any past introgression, and we suggest that urgent conservation action should be taken to protect this population.
Guidelines have been recently proposed outlining action when hybridization involves endangered species [9, 10]. The first thing necessary to clarify is whether the hybridization occurred naturally or was induced anthropogenically . We consider that the hybridization between P. poissonii and P. anisodora was probably induced by human activity, because a new road going through the hybrid zone was constructed in the 2000s, and close by, hotels have been built to attract tourists. With greater human population pressure, grazing by livestock becomes a more serious threat. For instance, during the periods of the field experiment, it was common to see cows eating the leaves and flowers of P. anisodora. Furthermore, all putative hybrids were growing together with parental species and we did not observe any hybrids occupying new habitats, indicating potential competition for the remaining habitat. In contrast, the “pure” P. anisodora population in Langdu showed no evidence of human activity and is situated in a remote area far from any villages. The remaining population of P. anisodora in Xiaoyanjing, while far from any villages, is very close to an asphalt road, and hence might be under threat.
Furthermore, the present study suggests that hybrids interfere with pollinator-mediated RI, and can lead to an acceleration of the invasion of the genepool of P. anisodora, which can be especially dangerous in situations where P. poissonii is more frequent. While the first step towards hybridization (F1s) seems to be a difficult one, later backcrossing seems to occur with more ease.
Therefore, based on our main findings, we recommend the following conservation action plan for P. anisodora. (i) Given the road going through the hybrid zone in Baishuitai, two protective plots should be set separately. The first plot will be above the road and very close to the local village. This plot should be protected because the largest number of P. anisodora individuals can be found here. The second plot, below the road, would include some P. anisodora, some hybrids and many individuals of P. poissonii. It would be preferable to conduct these actions with the help and support of the local people, rather than enforcing protection by strict regulation. (ii) Over the course of several years populations should be screened for hybrids, at best during the flowering season, and all plants resembling morphological hybrids in both plots should be removed. Thus a sympatric area without flowering hybrids would be recovered. We would expect that much stronger reproductive isolation will be maintained between P. poissonii and P. anisodora in such a setting. (iii) A detailed field investigation should be carried out in Xiaoyanjing to verify whether or not any other P. poissonii populations occur on the same mountain. Both species grow along streams, and seed can be easily dispersed by water. Hence if a P. poissonii population exists even some distance away from the P. anisodora population, a sympatric area can form if a stream is shared. If no P. poissonii is found, no conservation action needs to be undertaken here, as we would expect that after successive generations of backcrosses between those P. anisodora plants with P. poissonii genetic material and P. anisodora, all individuals here will eventually become almost pure P. anisodora. (iv) Given that the population of P. anisodora in Langdu is most strongly differentiated from the other two populations (FST for Langdu & Xiaoyanjing = 0.433; FST for Langdu & Baishuitai = 0.347; FST for Baishuitai & Xiaoyanjing = 0.045), this population could be used to reinforce genetic diversity in the other populations. To this end, seed should be collected, and plants propagated before introduction to the other two populations.
We investigated hybridization and reproductive barriers between a wide spread (P. poissonii) and a rare promise species (P. anisodora). Microsatellites analysis for the hybridizing species clarified the occurrence of backcrosses to P. anisodora in two of the three populations of P. anisodora, and more individuals of P. anisodora showed introgression from P. poissonii than vice versa in the sympatric area. Pollinator observations revealed that pollinator-mediated reproductive isolation was found to be still strong between parental species but not significant between hybrids and parental species. Hand pollination treatments showed intrinsic incompatibilities between parental species and moreover, hybrids had higher fruit- and seed-set when pollinated with P. anisodora pollen as opposed to P. poissonii pollen, indicating that asymmetric hybrid incompatibility might also play roles for the genetic structure of the hybrid zone. Overall evidence of potential genetic swamping of the P. anisodora populations was detected in the present study, and detailed conservation managements to reduce the risk by genetic swamping to P. anisodora were advised.
Plant species, study site and sampling
The two study species P. poissonii and P. anisodora are perennial herbs, growing on alpine meadows at altitudes between 2500 and 3700 m . While P. poissonii is relatively widespread, occurring in the eastern Himalayas (Tibet, Yunnan and Sichuan), P. anisodora is only known from three populations in Yunnan province (China): two populations (Langduand Baishuitai) in Shangri-La county and one population (Xiaoyanjing) in Nujiang county (Additional file 6: Figure S1). We only know of one area where both species grow in sympatry and seem to form hybrids (Baishuitai). This hybrid zone spans an area of about 15 km2 in Baishuitai, Shangri-La, NW Yunnan (27.6°N, 100.04°W, 3100 m). The population is situated in wet alpine meadow, with a stream running through it. In 2017, individual counts for P. anisodora and P. poissonii were 517 and 2349 flowering plants, respectively.
Parental species and hybrids can be easily distinguished by flower color and floral orientation: P. anisodora has dark-red, drooping flowers; P. poissonii has magenta-colored flowers that are oriented perpendicular to the stem; putative hybrids have intermediate color and floral orientation (Fig. 5a, b, c).
During the flowering period in 2014, a total of 168 individuals were sampled: 108 from the hybrid zone (P. anisodora: 36 individuals; P. poissonii: 33 individuals; putative hybrids: 39 individuals); 20 each from the two allopatric P. anisodora populations - Xiaoyanjing (26.58°N, 99.44°W), Langdu (27.95°N, 99.7°W); and 20 P. poissonii from an allopatric reference population near Shangri-La county (28.2°N, 100.04°W). Leaves were collected and preserved in silica gel in individually numbered containers. We stated here that all samples collected and used in this study as well as pollination experiments performed below in the field do not need any permission. We declare plant materials used in the current research complied with government regulations.
Reproductive barriers in the hybrid zone
The flowering times of the two species overlap completely, starting early in July, and ending in mid August. Therefore we predicted that pollinator-mediated isolation and intrinsic incompatibilities could play a role for isolating parental species and hybrids, and might also determine hybridization patterns in the sympatric area.
Pollinator-mediated reproductive isolation
Pollinator observations were carried out in two types of setting: (1) natural setting - from 6 July to 10 July in 2015 pollinators were observed in natural either P. poissonii- or P. anisodora-dominated parts of the population, to assess their pollinator assemblages; and (2) artificially controlled plot setting - three plots were established within the hybrid zone to evaluate reproductive barriers between parental species. The first of these plots (Plot 1) was set up in a P. poissonii-dominated part of the population and comprised both parental species (10 plants each) in an alternating setup (Fig. 5d); Plot 2 had an identical layout to plot 1, but was placed in a P. anisodora-dominated part of the population (Fig. 5f); Plot 3 was placed inside the hybrid zone, and comprised both parents and hybrids (Fig. 5e). Individual plants in the grid setups were placed approximately 50 cm apart, and species / hybrid identity was assigned according to morphological characters. From 6 July to 12 July in 2015, both Plot 1 and Plot 2 were observed for 7 days; each observation day lasting from 09:00 to 17:00. However, if weather conditions were unfavorable (rain) for pollinators, field observations were stopped during those hours. Plot 3 was observed on five sunny days from 7 to 11 July, 2015. We recorded a flower approach by a pollinator as a visit only if the pollinator had foraged or interacted with the flower by touching the reproductive structures of the plant. All types of flower visitors were photo recorded, identified, and preserved in the insect collections of Kunming Institute of Botany, CAS.
Following Natalis and Wesselingh , we calculated overall ethological reproductive isolation (RI) in P. poissonii- as well as P. anisodora-dominated parts of the population as: 1 - (No. cross-species foraging bouts / total number of foraging bouts) × (heterospecific transitions / all transitions). Herein one bout means the visitation of an insect to the plot, from approaching the plot up to its departure, irrespective of how many plants within the plot were visited, whereas transition refers to the type (conspecific vs heterospecifc) and number of visitations within one bout.
Hand pollination experiments
Pollination experiments were carried out in 2015 and 2016. The main focus between the years was different: in 2015 cross-compatibility between the species was tested, and in 2016 fertility between hybrids and parental species was investigated. Although it would have been desirable to carry out both of the experiments in either year, this was not possible, as the number of flowering plants of P. anisodora would not allow appropriate sample sizes for both experiments in the same year.
Cross-compatibility of the parental species
In July 2015, cross-pollination experiments were carried out for 16 possible combinations between the flower-morph types and species. Because both species are heterostylous, four intra specific pollination treatments are possible (♀-♂): P-P; P-T; T-P; T-T. These same four treatments also apply to inter-specific cross-pollination, and hence 16 treatments are necessary to cover all possible combinations.
For each treatment a minimum of 30 plants were selected as mothers. Up to three flowers per plant were selected while in bud, and the rest removed mechanically; afterwards the plant was labeled and bagged with a nylon net. When the flowers had just opened, flowers of the respective pollen parent were collected, and recipient flowers were pollinated manually by brushing the anthers against the stigma. After application of pollen the nylon net-bag was replaced and left for a further 3 days. In September 2015, fruits were harvested, and seed numbers per fruit were counted. Several plants were damaged by grazing before they could be harvested, resulting in 15 to 35 flowers per treatment that could be assessed and which are given as sample size ( Additional file 1: Table S1).
Fertility between hybrids and parental species
In July 2016, we focused on barriers to backcrossing between hybrids and parental species. To this end we performed cross-pollinations between hybrids and the parental species. As before, the different plant morph types were treated separately, resulting in 16 treatment combinations (Additional file 1: Table S1). The experiment was carried out as in 2015, but for some treatments grazing damage was higher, resulting in assessable sample sizes between 12 and 33 pollinated flowers. Fruits were again harvested in September, 2016.
To detect differences of visitation percentages between parental species, a χ2 test was employed. For assessing the effect of factors below on fruit- and seed-set for the pollination treatment data we employed ANOVAs as implemented in SPSS 15.0 for Windows (Chicago, IL, USA).
For the 2015 data we included four factors: Mother Species (anisodora, poissonii); Flower Type of mother plant (pin, thrum); Pollen Source (anisodora, poissonii); and Cross Type (intra-morph, inter-morph). Additionally a three-way ANOVA analysis for intra-specific pollination treatments was done including the factors Mother Species, Flower Type and Pollen Source. In order to improve ANOVA assumptions of normality and homogeneity, fruit sets were arcsine square-root transformed whereas seed numbers per fruit and seed numbers per flower were both log (x + 1) transformed.
For the 2016 data 7 treatments did not produce any fruits. We first compared differences in fruit sets and seed numbers between cross-pollinations of P. poissonii x hybrids and P. anisodora x hybrids using a χ2 test (fruit sets for pollination treatments of P. poissonii x hybrids and P. anisodora x hybrids were calculated as the total number of fruits divided by the total number of flowers within each treatment) and a Mann-Whitney nonparametric test (mean seed numbers per treatment as replicates, thus both P. poissonii x hybrids and P. anisodora x hybrids cross-pollinations comprising 8 replicates).
DNA extraction and microsatellite genotyping
We extracted genomic DNA from the dried leaf tissue using a modified cetyl trimethyl ammonium (CTAB) protocol. Quantification of DNA was carried out with a SmartSpecTM Plus Spectrophotometer (Bio-Rad). To select candidate diagnostic microsatellites to identify parental species and hybrids, 219 SSR primers were designed based on sequences previously obtained on a MiSeq Benchtop Sequencer (Illumina, Inc., San Diego, CA, USA) for the close relative P. chungensis . Detailed protocols for PCR amplification and condition regarding these primers followed Zhou et al. . PCR products were directly analyzed on a 3730xl Sequence Analyzer (Applied Biosystems, Foster City, CA, USA), using a LIZ GeneScan-500 size standard. Resulting chromatograms were visualized and converted to diploid genotypes using automated allele-calling implemented in GENEMARKER v.4.0 (SoftGenetics LLC, State College, PA, USA). All automated genotyping was re-checked manually. All genotypes for each locus and individual were entered into an Excel file following the format of GenALEx 6.5 .
Population genetic analysis
All basic summary statistics for the microsatellite data, and an AMOVA were calculated using GenALEx 6.5. Deviation from Hardy–Weinberg equilibrium (HWE) for each locus, and linkage disequilibrium (LD) for all loci pairs, were assessed with the web version of GENEPOP, v4.0.10 . For the HW test the heterozygote deficiency option was used. For the LD test the following Markov Chain parameters were set: 5000 dememorization runs; 1000 batches each with 5000 iterations.
Parent and hybrid assignment
To estimate parental ancestry proportions for each hybrid, microsatellite data was analyzed using the program STRUCTURE version 2.3.1 . We adopted the admixture model with correlated allele frequencies . No prior knowledge of the species was included in the analyzed data set. To determine the optimal number of groups (K), we ran STRUCTURE with K varying from 1 to 10, with five runs for each K value, and following Evanno et al. (2005) used ΔK to choose the most likely number of clusters. MCMC runs were then performed using a burn-in of 10,000 followed by 10,000 iterations.
Hybrid class assessment based on the microsatellite data was carried out with the program NewHybrids , using the following settings: burn-in of 10,000 followed by 100,000 MCMC iterations with the Uniform priorsmode. For the classification of individuals into each of the three groups, a relatively strict posterior probability of 0.9 was used, and only individuals reaching such a probability were taken as being classified; others were considered not properly classified by the program.
Hybrid swarm simulation
As the analyses were based on six loci only, we assessed their discriminatory power in NewHybrids by simulating several classes of hybrids based on parental individuals that had membership to either cluster in STRUCTURE close to 1 (‘pure’ parents). We simulated 5 hybrid categories (two parental species, F1and the first backcross to each parent) from 23 each of pure P. anisodora and P. poissonii (both > 90% probability in both structure and NewHybrids) using HYBRIDLAB version 1.0 . For each category, 30 individuals were generated, hence a total of 150 individuals (30 of each parent, 30 F1s and 30 BC to each parent) were simulated for the hybrid swarm in Baishuitai, and these were subsequently analyzed in NewHybrids.
Availability of data and materials
The data sets supporting the results of the present study are included within this article (and its additional files).
Analysis of Variance
Simple sequence repeat
Arnold ML. Natural hybridization and evolution. New York: Oxford University Press; 1997.
Soltis PS, Soltis DE. The role of hybridization in plant speciation. Annu Rev Plant Biol. 2009;60:561–88.
Abbott R, Albach D, Ansell S, Arntzen JW, Baird SJE, Bierne N, et al. Hybridization and speciation. J Evol Biol. 2013;26:229–46.
Balao F, Casimiro-Soriguer R, García-Castaño JL, Terrab A, Talavera S. Big thistle eats the little thistle: does unidirectional introgressive hybridization endanger the conservation of Onopordum hinojense? New Phytol. 2015;206:448–58.
Todesco M, Pascual MA, Owens GL, Ostevik KL, Moyers BT, Hübner S, et al. Hybridization and extinction. Evol Appl. 2016;9:892–908.
Anderson E. Hybridization of the habitat. Evolution. 1948;2:1–9.
Levin DA, Francisco-Ortega J, Jansen RK. Hybridization and the extinction of rare plant species. Conserv Biol. 1996;10:10–6.
Rieseberg LH, Carney SE. Plant hybridization. New Phytol. 1998;140:599–624.
Bohling JH, Dellinger J, McVey JM, Cobb DT, Moorman CE, Waits LP. Describing a developing hybrid zone between red wolves and coyotes in eastern North Carolina, USA. Evol Appl. 2016;9:791–804.
Wayne RK, Shaffer HB. Hybridization and endangered species protection in the molecular era. Mol Ecol. 2016;25:2680–9.
Rieseberg LH, Zona S, Aberbom L, Martin TD. Hybridization in the island endemic, Catalina mahogany. Conserv Biol. 1989;3:52–8.
Rhymer JM, Simberloff D. Extinction by hybridization and introgression. Annu Rev Ecol Syst. 1996;27:83–109. https://doi.org/10.1146/annurev.ecolsys.27.1.83.
Ma Y, Xie W, Tian X, Sun W, Wu Z, Milne R. Unidirectional hybridization and reproductive barriers between two heterostylous primrose species in north-West Yunnan, China. Ann Bot. 2014;113:763–75.
Milián-García Y, Ramos-Targarona R, Pérez-Fleitas E, Sosa-Rodríguez G, Guerra-Manchena L, Alonso-Tabet M, et al. Genetic evidence of hybridization between the critically endangered Cuban crocodile and the American crocodile: implications for population history and in situ/ex situ conservation. Heredity. 2015;114:272–80.
Riesgo A, Pérez-Portela R, Pita L, Blasco G, Erwin PM, López-Legentil S. Population structure and connectivity in the Mediterranean sponge Ircinia fasciculata are affected by mass mortalities and hybridization. Heredity. 2016;117:427–39.
Dell’Olivo A, Hoballah ME, Gübitz T, Kuhlemeier C. Isolation barriers between Petunia axillaris and Petunia integrifolia (solanaceae). Evolution. 2011;65:1979–91.
Ma YP, Xie WJ, Sun WB, Marczewski T. Strong reproductive isolation despite occasional hybridization between a widely distributed and a narrow endemic Rhododendron species. Sci Rep. 2016;6:19146.
Natalis LC, Wesselingh RA. Parental frequencies and spatial configuration shape bumblebee behavior and floral isolation in hybridizing Rhinanthus. Evolution. 2013;67:1692–705.
Lepais O, Petit RJ, Guichoux E, Lavabre JE, Alberto F, Kremer A, et al. Species relative abundance and direction of introgression in oaks. Mol Ecol. 2009;18:2228–42.
Arnold ML, Tang S, Knapp SJ, Martin NH. Asymmetric introgressive hybridization among Louisiana Iris species. Genes. 2010;1:9–22.
Beatty GE, Philipp M, Provan J. Unidirectional hybridization at a species’ range boundary: implications for habitat tracking. Divers Distrib. 2010;16:1–9.
Ma Y, Milne RI, Zhang C, Yang J. Unusual patterns of hybridization involving a narrow endemic Rhododendron species (Ericaceae) in Yunnan, China. Am J Bot. 2010;97:1749–57.
Chi-ming H, Kelso S. Flora of China. Beijing: Science Press, and St. Louis: Missouri Botanical Garden Press; 1996.
Zhou W, Li H, Wu Z, Barrett SCH, Li D, Wang H. Characterization of 24 microsatellite markers in Primula chungensis (Primulaceae), a distylous homostylous species, using MiSeq sequencing. Plant Divers. 2016;38:89–91.
Peakall R, Smouse PE. GenALEx 6.5: genetic analysis in excel. Population genetic software for teaching and research-an update. Bioinformatics. 2012;28:2537–9.
Raymond M, Rousset F. GENEPOP (version 1.2): population genetics software for exact tests and ecumenicism. J Hered. 1995;86:248–9.
Hubisz MJ, Falush D, Stephens M, Pritchard JK. Inferring weak population structure with the assistance of sample group information. Mol Ecol Resour. 2009;9:1322–32.
Anderson EC, Thompson EA. A model-based method for identifying species hybrids using multilocus genetic data. Genetics. 2002;160:1217–29.
Nielsen EE, Bach LA, Kotlicki P. HYBRIDLAB (version 1.0): a program for generating simulated hybrids from population samples. Mol Ecol Notes. 2006;6:971–3.
We thank Dr. Richard Milne for constructive comments and Mr. Xiaoling Tian for pollinator observation.
This work was supported by a program in international cooperation (2016IA021), Youth Innovation Promotion Association, Chinese Academy of Sciences (2018428) and the Biodiversity Survey and Assessment Project of the Ministry of Ecology and Environment, China (2019HJ2096001006). Moreover, the funders had no role in the design of the study and collection, analysis and interpretation of data, decision to publish, or the preparation of the manuscript.
Ethics approval and consent to participate
Consent for publication
The authors declare that they have no competing interests.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Table S1. Fruit set and seed numbers per fruits from 16 pollination treatmentswithin and between parental species in 2015 and between hybrids and parental species in 2016, with n referring to sample size and na to not available when no seeds were found in fruit. (DOCX 24 kb)
Table S2. The three-way ANOVA analysis for intra-specific crosses (8 treatments) in 2015.Significant results are highlighted in boldface. (DOCX 14 kb)
Table S3. Numbers of transitions of different pollinators in plot 3. For these 9 types of transitions, the first plant is the currently visited species and the second plant is the species that the pollinator’s next approaching to. PA, P. anisodora; PP, P. poissonii and PH, putative hybrids. (DOCX 14 kb)
Table S4. Sample number (N), mean allele number per locus (Na), number of effective alleles (Ne), information index (I), observed heterozygosity (Ho), expected(He) and unbiased expected (uHe) heterozygosity of microsatellite loci in each population of P. anisodora, P. poissonii and hybrids. (DOCX 14 kb)
Table S5. Pairwise Fst values between parental species and putative hybrids among populations. (DOCX 14 kb)
Figure S1. Basic information on all known populations of P. poissonii and P. anisodora as well as our sampling and experimental locations; with 1 = Langdu population, 2 = Shangeri-La, 3 = Baishuitai, 4 = Xiaoyanjing. The distribution maps are plotted based on the species distribution data at the county level supplied by the Chinese Virtual Herbarium (http://www.cvh.ac.cn/). (DOCX 189 kb)
Figure S2. ΔK values for the Structure analysis. (DOCX 34 kb)
About this article
Cite this article
Ma, Y., Marczewski, T., Xue, D. et al. Conservation implications of asymmetric introgression and reproductive barriers in a rare primrose species. BMC Plant Biol 19, 286 (2019) doi:10.1186/s12870-019-1881-0
- Asymmetric introgression
- Conservation implication
- Genetic swamping
- Reproductive isolation