Printer Friendly

The genetic structure of wild Orobanche cumana Wallr. (Orobanchaceae) populations in Eastern Bulgaria reflects introgressions from weedy populations.

1. Background

Broomrapes (Orobanche spp. and Phelipanche spp.) are a group of around 170 holoparasitic plant species mainly distributed in the northern hemisphere. They do not have photosynthetic activity and entirely depend on a host plant for nutrition [1]. Even though most of the Orobanche spp. only parasitize wild plants, some of them have become noxious weeds on a variable range of cultivated hosts [2]. This is the case of Orobanche cumana Wallr. (sunflower broomrape), which is nowadays one of the most limiting factors for sunflower (Helianthus annuus L.) production in Europe and Asia [3].

Orobanche cumana is naturally distributed from central Asia to south-eastern Europe, where it parasitizes wild Asteraceae species, mainly Artemisia spp. [4]. Even though it has been considered by some authors as an intraspecific taxon of Orobanche cernua L. [5], its treatment as a separate species is nowadays widely accepted [2, 6, 7]. The Black Sea coast in eastern Bulgaria is one of the main natural distribution areas for O. cumana, where this species is mainly found parasitizing Artemisia maritima L. [8].

Though domesticated in eastern North America and widely used as a staple food in the pre-Columbian period [9], the transformation of sunflower into one of the major world oil crops started in Russia in the second half of the nineteenth century [10]. Plants of O. cumana parasitizing sunflower were observed for the first time in Russia in the 1890s [11]. In Bulgaria, O. cumana parasitization on sunflower was first detected in 1935 [12]. Currently, O. cumana is present in the main sunflower-producing countries around the world, particularly in Central and Eastern Europe, Spain, Turkey, Israel, Russia, Ukraine, Iran, Kazakhstan, and China [2]. Moreover, the parasite has spread to new areas in recent years [13,14]. Broomrape seed transport has been suggested as one of the main factors in the dispersion of the infestation [15]. Broomrape seeds are extremely small (dust-like seeds), and individual plants can produce an impressive number that remain viable in the soil for up to 20 years, which are easily dispersed by water, wind, animals, humans, machinery, or though attachment to sunflower seeds [15,16].

Unlike most weedy Orobanche spp., which have a broad range of host crops, weedy O. cumana only parasitizes sunflower [2]. The high host specificity of O. cumana is probably associated with the mode of inheritance of genetic resistance in sunflower. Whereas in most host crops genetic resistance to Orobanche spp. is horizontal, that is, polygenic and nonrace specific, resistance to O. cumana in sunflower is primarily vertical, that is, monogenic, dominant, and race specific [16]. The development of sunflower resistant cultivars has been paralleled by the appearance of O. cumana populations that overcame sunflower genetic resistance, a recurrent process that has continued until today [11]. Several physiological races of O. cumana have been reported. Vranceanu et al. [17] identified races A through E using five sunflower differential lines carrying the dominant resistance genes Or1 through Or5, respectively. More virulent races named as F, G, and H were later detected in the main sunflower cultivation areas of the Old World [3]. In Bulgaria, races D and E were predominant till few years ago [18], but a more virulent race G has become increasingly important in recent years [19].

There are few studies on genetic interactions between wild and weedy forms of parasitic plant species. Knowledge about such interactions is important because wild vegetation may play a role as reservoir of genetic diversity for overcoming genetic resistance mechanisms in the host crops [20, 21]. But on the other hand, evolution of virulence in weedy populations may also have an impact on the distribution of the species in the wild [22]. Botanga et al. [23] used seeds of eight populations of the parasitic weed Striga asiatica (L.) Kuntz collected on wild hosts to conduct infestation experiments on susceptible maize and sorghum cultivars. None of the populations parasitized on sorghum, whereas five out of the eight populations failed to parasitize on maize. The authors concluded the occurrence of local adaptation of the parasite to a host species as well as a high degree of host specialization. Similarly, Botanga and Timko [24, 25] reported the stratification by host preference of Striga gesnerioides (Willd.) Vatke genotypes parasitizing cowpea [Vigna unguiculata (L.) Walp.] and the wild legume Indigofera hirsuta L. Conversely, Olivier et al. [26], using isozyme loci, showed little genetic differentiation based on host specificity among Striga hermonthica (Del.) Benth. populations parasitizing sorghum, pearl millet, maize, and wild grasses. Similarly, Vaz Patto et al. [20] found low genetic differentiation between populations of Orobanche foetida Poir. collected on a wild host and a population growing on cultivated vetch (Vicia sativa L.) using AFLP analyses.

Studies on genetic diversity within and between O. cumana populations are scarce and focused on weedy populations collected on sunflower. Gagne et al. [27] studied genetic diversity in eight populations from several countries using RAPD markers. They identified large interpopulation and low intrapopulation genetic variation, concluding the existence of two main gene pools, one comprising populations from Eastern Europe and another one including populations from Southern Spain. Pineda-Martos et al. [28] identified two main gene pools for O. cumana in Spain, comprising populations from the Guadalquivir Valley (Southern Spain) and Cuenca Province (Central Spain), respectively. Both groups were genetically distant, but both intra- and interpopulation genetic variation were in general extremely low within each gene pool due probably to a founder effect. However, a reduced number of populations exhibited larger genetic diversity, which was attributed to the presence of individuals from both gene pools and the occurrence of crosses between them. Even though O. cumana is considered to be primarily a self-pollinated species [29], the occurrence of a certain rate of cross pollination has been experimentally demonstrated [30].

There is no information on the population structure of O. cumana populations parasitizing wild species and their genetic relationship with weedy populations in areas where they coexist. There is also no information on their virulence on sunflower. The objective of this research was to investigate the genetic diversity, population structure, and ability to parasitize sunflower of O. cumana populations growing on wild plants in the Black Sea coast of Bulgaria, as well as their relationship with weedy populations parasitizing sunflower.

2. Materials and Methods

2.1. Orobanche cumana Populations. Two field expeditions were conducted in July 2006 and June 2012 along the Black Sea coast of Bulgaria, where the distribution of O. cumana in the wild has been largely documented [8, 31-33], to collect fresh tissue and mature seeds of O. cumana populations parasitizing wild Asteraceae species. Six populations were located in both expeditions, one of them in both years (Table 1, Figure 1). Samples from the latter population were managed separately in the study to evaluate potential changes between both collection dates. Voucher specimens of the populations are housed in the herbarium of the University of Cordoba, Spain (herbarium code COA). Duplicated specimens can also be found at the herbarium SOA (Agricultural University of Plovdiv, Bulgaria). Populations CUMBUL-1 (COA-45783 and COA-45784), CUMBUL-2 (COA-45789), CUMBUL-3 (COA-45790), CUMBUL-4 (cOA-45785) CUMBUL-6 (COA-53262 and COA-54519), and CUMBUL-7 (COA-54510) were collected on A. maritima L. (Table 1). Figure 2 shows details of population CUMBUL-1. Population CUMBUL-5 was found parasitizing Anthemis arvensis L., Chamaemelum nobile (L.) All., and another species of the Asteraceae that could not be identified, though in the latter case only two plants were presen and they were not collected. Plants collected on A. arvensis (CUMBUL-5_1; COA-45791) and C. nobile (CUMBUL-5_2; COA-45792) were analyzed separately to evaluate potential differences associated with the host plant. The populations were located at a distance of less than 3 km from agricultural fields. Fresh tissue (young stalks) from 6 to 30 individual plants (Table 1), depending on population size, was collected in situ for each population and kept under drying conditions in ziplock bags with silica gel for subsequent freezing at -80[degrees]C. Fresh tissue of three O. cumana populations parasitizing sunflower crops in two different areas of Bulgaria (Table 1) was collected in the 2012 expedition. Additionally, fresh tissue was also collected in situ from three populations parasitizing sunflower in two different areas of Spain in which contrasting gene pools have been identified [28], to be used as a control (Table 1).

Mature seeds were collected in bulk from 5 to 30 mature plants of populations CUMBUL-1, CUMBUL-2, CUMBUL-4, and CUMBUL-5_1. No mature plants were available at the time of the collection expeditions for the other populations, including the O. cumana populations parasitizing sunflower in Bulgaria. Alternatively, seeds from three populations of O. cumana collected in sunflower fields in Bulgaria (OC-9, OC11, and OC-13) were used for virulence studies. Populations OC-9 and OC-13 were kindly provided by Professor Rossitza Batchvarova, AgroBioInstitute, Sofia, Bulgaria. Population OC-11 was collected by one of the authors (K. Stoyanov). Spanish race F population OC-88 was also used as a control for virulence studies.

2.2. DNA Extraction and SSR Analysis. Frozen tissue was lyophilized and ground to a fine powder. DNA was extracted from individual O. cumana plants using a modified version of the protocol described in Perez-Vich et al. [34]. Microsatellite analyses were carried out as described in Pineda-Martos et al. [28], using the same set of fifteen high-quality, polymorphic SSR primer pairs (Table S1 in Supplementary Material available online at http://dx.doi.org/10.1155/2014/150432). Amplification products were resolved by electrophoresis on 3% Metaphor agarose (BMA, Rockland, ME, USA gels in 1x TBE buffer at 100 V constant voltage, with SaveView Nucleic Acid Stain (NBS Biologicals Ltd., Huntingdon, UK) incorporated in the gels and visualized under UV light. A 100 bp DNA ladder (Solis BioDyne, Tartu, Estonia) was used as a standard molecular weight marker to get an approximate size of DNA fragments. Bands were scored manually with the aid of QuantityOne 1-D Analysis Software (Bio-Rad Laboratories Inc., Hercules, CA, USA) at least twice independently for each population.

2.3. Molecular Data Analysis

2.3.1. Genetic Diversity Analysis. For each SSR locus, the number of alleles (Na), observed and expected heterozygosity (Ho and He), and [F.sub.ST] were calculated using GenAlEx ver. 6.5 [35]. Additionally, each locus was tested for departure from Hardy-Weinberg equilibrium (HWE) and linkage disequilibrium within each of the populations with Arlequin ver. 3.5.1.3 [36]. To characterize the genetic diversity of O. cumana populations collected on wild hosts and the control populations collected on sunflower, the percentage of polymorphic loci (P), the average observed number of alleles (Na), the number of different alleles with a frequency [greater than or equal to] 5% (Na [greater than or equal to] 5%), the number of effective alleles (Ne), the number of private alleles unique to a single population (Npa), the observed and expected heterozygosity (Ho and He), the Shannon's diversity index (I), and the fixation index ([F.sub.is]) were calculated for all loci at each population. All calculations were carried out using GenAlEx ver. 6.5. Fis was used to estimate the selfing rate (S) from S = 2[F.sub.is]/(1 + [F.sub.is]) [37]. As additional measures of intrapopulation diversity, the mean number of pairwise differences between individuals within each population, estimated as the mean number of differences between all pairs of SSR haplotypes in each population, and the genotypic richness (R), defined as (G- 1)/(N - 1), where G is the number of MLGs (the observed number of multilocus genotypes) and N is the number of samples per population, were determined using Arlequin ver. 3.5.1.3, and GenClone 2.0 [38], respectively.

2.3.2. Genetic Differentiation Analysis. To evaluate genetic differentiation between populations, initial frequency-based analysis was carried out by calculating pairwise genetic distances between populations using the genetic distance coefficient [G.sub.ST] as implemented in GenAlEx ver. 6.5 using 1000 random permutations to assess significance. Pairwise distance matrices were also calculated using GenAlEx ver. 6.5 with other frequency-based estimators of population structure for codominant data such as Nei's [G.sub.ST], Nei's standardized [G.sub.ST], Hedrick's standardized GST, Hedrick's further standardized [G.sub.ST] for small number of populations, and Jost's estimate of differentiation, following calculations detailed in [39]. The pairwise relationship between the genetic distance matrices was tested through a Mantel's test with 999 permutations. Since the different statistical measures were highly correlated (r > 0.94, P = 0.001 for all comparisons, excepting those including the Jost's estimate of differentiation in which r > 0.90, P = 0.001), only the resultsbased on the genetic distance coefficient GST with the corrections of Nei and Chesser [40] and Nei [41] are presented. To assess genetic relationships among populations, the matrix of [G.sub.ST] pairwise distances was used as input for a principal coordinates analysis (PCoA) using GenAlEx ver. 6.5. PCoA has the main advantage of not requiring strong assumptions about the underlying genetic model [42].

To identify genetically homogeneous groups (gene pools), Bayesian model-based clustering algorithms implemented in the software package STRUCTURE ver. 2.3.4 [43] were applied. Cluster grouping in STRUCTURE is based on iterative analysis using K number of groups previously defined by the user, with individuals in the sample being assigned probabilistically to one or several groups. The admixture model and the allele frequencies correlated model were used [44]. No prior information was used to define the clusters. For each value of K (from 1 to 14), 10 independent runs were made that were used to estimate the probability of the data Pr(X | K). For each run, 1,000,000 Monte Carlo Markov chain (MCMC) iterations were carried out after a burn-in period of 200,000 steps. To detect the number of genetically homogeneous groups (K) that best fits the data, the STRUCTURE HARVESTER website [45], which implements the Evanno method [46], was used. The 10 runs from the most probable number of K groups were averaged applying the FullSearch algorithm provided in the CLUMPP ver. 1.1.2b software [47] and the output was entered into Distruct ver. 1.1 for display [48]. To explore the genetic structure further, the STRUCTURE analyses were also carried out only with the 11 Bulgarian populations, as described above. We also used the program InStruct [49] for analyzing population structure, since this program is an extension of STRUCTURE that does not assume Hardy-Weinberg equilibrium and can incorporate selfing in the model. In addition, it can estimate the level of selfing in each population. Five independent chains were run for each K. Each chain was run for 1,000,000 iteration steps, with a burn-in of 500,000, and a thinning of 10. Graphical representations of population assignments from InStruct were produced from the program Distruct ver. 1.1 [48].

Finally, an analysis of molecular variance (AMOVA) [50] within populations, among populations, and among population groups (based on a priori grouping variables such as wild or cultivated host or based on the gene pools determined with clustering methods) was carried out to determine the distribution of variation at different hierarchical levels. The variance components were tested statistically by nonparametric randomization tests using 1000 permutations. Fixation indices (F-statistics) were also estimated by AMOVA. All calculations were carried out with Arlequin ver. 3.5.1.3.

2.4. Parasitization Ability and Virulence on Sunflower. Mature seeds were collected for wild O. cumana populations CUMBUL-1, CUMBUL-2, CUMBUL-4, and CUMBUL-5.1. However, the amount of available seed was very low, which restricted the number of sunflower genotypes for virulence studies as well as the number of plants per genotype. Accordingly, their parasitization ability and virulence on sunflower was evaluated in two separated experiments. The first experiment was aimed at determining whether the populations had the ability to parasitize sunflower genotypes with no genetic resistance to weedy O. cumana physiological races. Two confectionery sunflower landraces, B117 and B206, with no known resistance to any O. cumana race were used. Both landraces were collected by L. Velasco in isolated vegetable patches in Valdepenas (Jaen Province, Spain) and Quintana de la Serena (Badajoz Province, Spain), respectively. Orobanche cumana population OC-88 [with known virulence (race F)] was used as a positive control. In a second experiment, the virulence of the populations was tested on a set of sunflower lines with varying levels of genetic resistance to O. cumana physiological races. Jdanovski 8281 (J8281) is a line incorporating resistance gene Or2 that confers resistance to O. cumana race B [17]. AC03-1589 is a line incorporating resistance gene Or3 that confers resistance to O. cumana race C, kindly provided by Dr. Maria Pacureanu, National Agricultural Research and Development Institute, Fundulea, Romania. S1358 is a line incorporating resistance gene Or4 that confers resistance to O. cumana race D [17]. P-1380 is a line containing the resistance gene Or5, which determines resistance to O. cumana race E [17]. P96 is a line with recessive resistance to O. cumana race F [34]. B117 with no known resistance to any O. cumana race was used as positive control. Populations OC-9, OC-11, OC-13, and OC-88 were used as controls. Because the amount of seed of populations CUMBUL-1, CUMBUL-4, and CUMBUL-5_1 was not enough for evaluating them on all sunflower lines of the second experiment, it was decided not to test them on line S1358.

Seeds of O. cumana populations were used to inoculate small pots 7 x 7 x 8 cm filled with a mixture of sand and peat (1: 1 by vol). Twenty-five mg of O. cumana seeds per pot was used. The soil mixture containing O. cumana seeds was carefully mixed to obtain a homogeneously infested substrate. Seeds of sunflower cultivars were germinated on moistened filter paper in Petri dishes and two-day-old seedlings were planted in the pots inoculated with O. cumana seeds. Eight pots (replications) per combination of sunflower cultivar and O. cumana population were used. The plants were maintained in a growth chamber for 21 days at 25[degrees]C/20[degrees]C (day/night) with a 16 h photoperiod for incubation. After this time, the plants were transplanted to pots containing 3 L of an uninfested sand-silt-peat (2: 1: 1 by vol) soil mixture and maintained under open air conditions. The plants were watered as needed and were not fertilized. The number of O. cumana shoots per sunflower plant was counted at sunflower maturity. Differences between mean numbers of O. cumana shoots per plant for each O. cumana population and sunflower cultivar were analyzed through one way ANOVA and Tukey's range test using IBM SPSS Statistics version 19.

3. Results

3.1. Genetic Diversity and Population Structure. All SSR markers were polymorphic (Table S1). The total number of alleles scored was 38, ranging from 2 to 4 for each SSR locus. Allelic diversity was generally low for all fifteen SSR loci when considering the whole set of 260 individual O. cumana plants (Table S1). All the loci exhibited an important heterozygote deficiency (Table S1). A significant deviation (P < 0.05) from Hardy-Weinberg equilibrium was found for almost all loci when all samples were considered. Linkage disequilibrium was significant (P < 0.05) in 238 out of 430 paired loci comparisons when considering all the samples. It has been established that linkage disequilibrium is predicted to approach zero for an ideal population, in the absence offorces such as genetic drift, population mixing, mutation, natural selection, or inbreeding [51]. High linkage disequilibrium observed suggested the existence of some genetic structure, apart from other factors determining the organization of genetic variation in the studied populations, as it will be further discussed below.

Genetic diversity within each population, measured by the mean number of observed and effective alleles, the expected heterozygosity, and Shannon's diversity indexes, was in general low, and only one population (CUMBUL-4) contained a substantial number of private alleles (Table 2). As expected from previous studies, Spanish populations were characterized by extremely low level of intrapopulation genetic diversity due probably to a founder effect [28], with no polymorphic loci being detected in two out of the three populations (Table 2). In contrast, populations from Bulgaria exhibited higher diversity values, with the exception of population CUMBUL-3, which showed no polymorphic loci. However, it is important to note that this was the smallest population, in which only six individual plants could be collected. Amongst the other Bulgarian populations, the highest genetic diversity corresponded to the populations collected on wild hosts CUMBUL-2, CUMBUL-5_2, and CUMBUL-7, which showed He, I and pairwise difference (between individuals) values over 0.25, 0.4, and 3.5, respectively (Table 2). The lowest genetic diversity corresponded to populations CUMBUL-8 and CUMBUL-9, collected on sunflower, which showed He, I and pairwise difference (between individuals) values below 0.05, 0.1, and 0.5 respectively (Table 2). The other six populations, excluding CUMBUL-3, showed intermediate diversity values, ranging from 0.10 to 0.23 for He, from 0.18 to 0.35 for I, and from 1.8 to 3.1 for pairwise differences between individuals. The fixation index (Fis) and selfing rate (S) values were high for the populations studied (Table 2).

For measuring differentiation between populations, pairwise Gst values were computed (Table S2). No significant or very low ([G.sub.ST] [less than or equal to] 0.01) differentiation was found for populations CUMBUL-8 and CUMBUL-9, collected on sunflower at close locations, CUMBUL-2 and CUMBUL-7, collected on A. maritima at near sites the same year, and CUMBUL-5_1 and CUMBUL-5_2, collected at the same location but on different wild hosts. Populations CUMBUL-1 and CUMBUL-7, which were collected at the same site but with a six-year difference, showed slightly higher [G.sub.ST] values (0.107). The highest differentiation values (Gst > 0.8) were found between the following three groups of populations: (i) IASCum-2, IASCum-3, and IASCum-4 collected on sunflower in Spain, (ii) CUMBUL-8 and CUMBUL-9 collected on sunflower in Bulgaria, and (iii) CUMBUL-3 and CUMBUL-4 collected on wild A. maritima in Bulgaria (Table S2). In principal coordinate analyses, the first three axes explained 39.4%, 26.6%, and 178%, respectively of the variation, producing five differentiated groups of populations: (i) IASCum-2 and IASCum-3, (ii) IASCum-4, (iii) CUMBUL-8 and CUMBUL-9, (iv) CUMBUL-3 and CUMBUL-4, and (v) the remaining seven populations, six of them collected on wild hosts in Bulgaria and one of them collected on sunflower in Bulgaria (Figure 3).

Bayesian-based analysis of the structure of the whole set of populations including those from Spain and Bulgaria with STRUCTURE revealed a close relationship among populations whatever their geographical origin, with an optimal K value of 2 (Figures S1 and S2). Secondary peaks were observed at K = 4 and 7 (Figure S1), and the standard deviation of Pr(X | K) began to increase substantially at K values higher than these (Figure S1). Visualization of the cluster membership for K = 2 to K = 7 showed a general trend towards classification of populations IASCum-2, IASCum-3, IASCum-4, CUMBUL-3, CUMBUL-4, CUMBUL-8, and CUMBUL-9 within uniform pools, while the rest of the populations were included within mixed pools (Figure S2), assignments that recurred at all monitored levels of K (Figure S2).

A more detailed analysis of population structure including only Bulgarian populations was carried out. STRUCTURE analyses indicated the existence of two (K = 2; Figure S3) major genetic groups, mainly represented by populations CUMBUL-3 and CUMBUL-4 on one hand (Gene Pool 1), and CUMBUL-8 and CUMBUL-9 on the other hand (Gene Pool 2) (Table 3; Figure 4(a)). The remaining seven populations were categorized in-between these two groups, although the average proportion of membership was shifted towards Gene Pool 1 for populations CUMBUL2 and CUMBUL-10, whereas populations CUMBUL-5_1, CUMBUL-5_2, and CUMBUL-6 were clearly shifted towards Gene Pool 2 (Table 3; Figure 1). When the membership value of each individual for each population was analyzed in detail, it was shown that an important number of individuals from populations CUMBUL-5_1, CUMBUL-5_2, and CUMBUL-6 [19 individuals out of 28 (67.9%), 10 out of 20 (50%), and 15 out of 23 (65.2%), resp.] showed a high (> 0.90) membership value for Gene Pool 2 (Figure 4(b)). Classifications of individuals at K = 2 by the algorithms of STRUCTURE and Instruct were very similar qualitatively (Figure 4(a)). Within-cluster selfing rates estimated from Instruct analyses were very high (on average, 0.947 for Gene Pool 1 and 0.951 for Gene Pool 2).

Different AMOVA analyses were carried out within the O. cumana populations collected in Bulgaria. First, AMOVA analyses were conducted on populations collected on wild hosts. When no population structure was considered, 53.6% of the genetic variance was attributable to differences among populations, while the remaining 46.4% was due to differences within populations (Table 4). When populations were structured according to clustering results, differences among groups accounted for 50.4% of the total variance, while differences among populations of each group only accounted for 17.6% (Table 4). When populations collected on sunflower were added to the model, no significant structuring according to the ecological status of the populations was detected (Table 4). Structured analysis based on clustering groups produced similar results to the analysis of populations collected on wild hosts alone; that is, variation among groups accounted for 42.0% of total variation, while variation among populations at each group accounted for 25.1% (Table 4).

3.2. Parasitization Ability and Virulence on Sunflower. A first experiment demonstrated that O. cumana populations CUMBUL-1, CUMBUL-2, CUMBUL-4, and CUMBUL-5.1, collected on wild hosts, had the ability to parasitize sunflower lines B117 and B206, with no resistance genes, though some differences between populations were observed (Table 5). On B117, populations CUMBUL-1 and CUMBUL-5_1 produced similar number of shoots per sunflower plant to the control population OC-88, while CUMBUL-2 produced around four times more shoots per plant and CUMBUL-4 produced about half of shoots per plant than the control. On B206, both CUMBUL-1 and CUMBUL-2 yielded more shoots per plant than the control, while CUMBUL-4 produced less shoots per plant than the control (Table 5). In a second experiment the virulence of the populations collected on wild hosts, together with Bulgarian populations collected on sunflower, was evaluated on sunflower lines with varying degrees of genetic resistance. On sunflower line J8281, resistant to O. cumana race B, the number of shoots per sunflower plant did not differ significantly between Bulgarian O. cumana populations collected on wild hosts and those collected on sunflower (Table 6). The results were similar on sunflower line AC031589, resistant to race C, except for a significantly higher number of shoots in population CUMBUL-5_1. Similarly, the only wild population evaluated on line S1358 resistant to race D (CUMBUL-2) did not differ from the Bulgarian populations collected on sunflower. When the populations were tested on sunflower line P-1380, resistant to race E, only population CUMBUL-5_1 produced a few number of shoots per plant, whereas neither the other populations collected on wild species nor the Bulgarian populations collected on sunflower did possess the ability to parasitize P-1380. None of the populations parasitized on race-F resistant line P96 (Table 6).

4. Discussion

The genetic structure of O. cumana populations analyzed in this study was not determined by the fact that the populations were collected on wild or cultivated hosts. This was an unexpected result, since, within a number of largely self-pollinated parasitic plant species, host specificity has been found as a mechanism of accelerating isolation and subsequently genetic divergence among populations, for example, in Orobanche minor Sm. [52-54], Striga asiatica [23], and S. gesnerioides [24,25]. Conversely, Vaz Patto et al. [20] studied the genetic structure of five Moroccan O.foetida populations, four of them parasitizing wild plants (Scorpiurus muricatus L. and Ornithopus sativus Brot.) and another one parasitizing cultivated vetch. The authors found that the vetch-parasitizing population was closer to the three populations parasitizing S. muricatus, while the population collected on O. sativus was the most genetically divergent. This suggested that parasitization of wild or cultivated hosts was not among the main factors determining genetic differences between these populations. Since host specificity in Orobanche spp. is mainly determined by induction of seed germination by specific chemical stimulants exuded by the host root [55], host-induced selection is expected to have an impact on verysmall portions of the genome, probably even at a single locus by modifying the binding site of the stimulant receptor [56]. Such limited genetic modifications, despite having a huge phenotypic impact, might not be detected with overall genome scans such as the one carried out in this research, while the rest of the genome is predominantly shaped by other evolutionary sources, namely, recombination and migration [29].

Nevertheless, an important observation in this study was that the genetic structure of wild O. cumana populations reflected introgressions from weedy populations parasitizing sunflower. This was shown not only by the analysis of population structure, but also by similar levels of virulence on sunflower of weedy and wild O. cumana populations. To the best of our knowledge, this is the first study on molecular diversity and virulence on sunflower of O. cumana populations parasitizing wild hosts. Previous studies focusing exclusively on weedy populations have shown the existence of several gene pools in this species, with low genetic diversity within each gene pool [27, 28, 57-59]. Gagne et al. [27] identified two gene pools, one of them comprising populations from eastern Europe (Romania, Bulgaria, and Turkey) and another one including populations from southern Spain. Studies on Spanish populations identified two well-separated gene pools, one of them in the south (Guadalquivir Valley) and another one in the central area (Cuenca Province) [28, 58, 59]. The study of Spanish populations [28] revealed that, although intrapopulation genetic diversity was in general extremely low, some populations showed larger diversity, which was hypothesized to be produced by genetic recombination between individuals from both gene pools. In the present research, two contrasting gene pools were identified in Bulgaria, one of them best represented by weedy populations from the central area (CUMBUL-8 and CuMBuL-9), and another one represented by wild populations from the eastern coast (CUMBUL-3 and CUMBUL-4), which showed in all cases low intrapopulation diversity. The fact that some wild populations had higher genetic diversity values and contained individuals that exhibited membership values very close to a weedy gene pool (> 0.90) suggested the existence of genetic flow between both gene pools, which could be attributed to cross fertilization and/or seed movement. It is important to note that in the Black Sea coast of Bulgaria weedy and wild O. cumana populations coexist at short distances. The existence of cross fertilization within this species has been demonstrated in controlled experiments at a local scale [30] as well as in the molecular evaluation of field-collected weedy populations, where heterozygous individuals for unique alleles of different gene pools have been identified [28]. In relation to gene flow through seed dispersal, Orobanche seeds are easily dispersed by water, wind, and animals. Individual broomrape plants produce an impressive number of seeds from 50,000 to 500,000 [1] that maintain their viability in the soil for up to 20 years [11]. These seeds are of near-microscopic size, from 250 to 380 [micro]m long and from 150 to 240 [micro]m wide, with a weight from 1.0 to 2.5 pg and are considered as "dust-seeds" [11,15,60,61]. These factors are regarded as adaptations for being an obligate parasite, in order to be dispersed through vegetation so as to be as close as possible to the host plant and increasing the probability of finding an appropriate host [61]. Additionally, at a landscape scale, Orobanche cumana seed dispersion is highly influenced by human-derived agricultural and cultivation practices, as well as crop-seed trade and the use of contaminated sunflower seed stocks [15,29], which might overpass spatial distances or barriers to gene flow common in natural ecosystems.

Wild and cultivated host plants represent different habitats for parasitic plants, especially when cultivated plants carry qualitative resistance genes, as is the case of the sunflower-O. cumana system [16]. The use of cultivars expressing vertical resistance mechanisms has contributed to a rapid development of O. cumana physiological races in most cultivation areas on the Old World, including Bulgaria [3, 19], which may explain why weedy populations of O. cumana generally show low genetic diversity, since new physiological races most likely evolve from single mutations events [62]. This is in general agreement with reports on plant pathogenhost interactions [22, 63, 64]. For parasitic plant-host interactions, higher intrapopulation variability was reported in a Striga gesnerioides population parasitizing the wild legume Indigofera hirsuta L. when compared to populations growing on cultivated cowpea [25]. Another study identified genetic diversity differences for a population of S. hermonthica grown on rice accessions of varying resistance to Striga, with the lowest diversity corresponding to a highly resistant rice accession [65]. This was not exactly the case of the present study, since we found genetic diversity values in wild populations similar or even lower than those reported in weedy O. cumana recombinant populations [28]. This could be explained on the basis of the existence of introgression from weedy populations into wild O. cumana populations. Studies in nonparasitic plant species, for example, in rice, have shown that introgression from cultivated species can considerably shape genetic diversity of wild populations [66, 67].

The study of O. cumana populations in their natural habitat provided new data about its breeding system. A clear heterozygote deficiency similar to that observed in populations parasitizing sunflower, deviation of genotypic frequencies at most loci from Hardy-Weinberg equilibrium, high inbreeding and selfing rate values, and the relatively low levels of genetic variation within populations coupled with substantial differences among populations, supported that wild populations of this species show a high degree of self-pollination, as reported previously for O. cumana populations parasitizing sunflower [27], and for other predominantly self-pollinating broomrape species such as Phelipanche ramosa (L.) Pomel [68].

Orobanche spp. differ for host specificity. Within this genus, O. cumana is one of species with the narrowest range of host plants. In the wild, it mainly parasitizes Artemisia spp. [4], whereas sunflower is the only crop in which O. cumana occurs as a parasitic weed [2]. Orobanche cumana belongs to the native flora of Bulgaria, where it parasitizes wild species of the Asteraceae, mainly A. maritima [8]. Conversely, the genus Helianthus is from North American origin [69]. The first report of O. cumana parasitization on sunflower dates back to the 1890s in Russia [11] and to 1935 in Bulgaria [12]. It is unknown whether O. cumana possesses natural ability to parasitize sunflower or this ability arose in particular genotypes following mutation [70]. The possibility that O. cumana possesses natural ability to parasitize sunflower cannot be discarded, since molecules of the same nature to those involved in O. cumana stimulation of germination by sunflower root exudates occur commonly in plant organs of Asteraceae species [55]. The results of the present research did not shed light on this aspect, since both the population structure analysis as well as the virulence study indicated that the wild populations used in the study contain introgressions from weedy populations. The existence of genetic flow between O. cumana populations parasitizing sunflower and those parasitizing wild species opens up an interesting field of research on how increasing virulence in weedy populations observed in recent years in Bulgaria [19] may influence the parasitization ability of O. cumana on wild species and on how genetic variability of wild populations may favour the ability of weedy populations to overcome sunflower resistance mechanisms.

http://dx.doi.org/10.1155/2014/150432

Conflict of Interests

The authors declare that there is no conflict of interests regarding the publication of this paper.

Acknowledgments

The research was partially funded by Fundacion Ramon Areces, Madrid. R. Pineda-Martos was the recipient of a PhD fellowship from the Spanish National Research Council (CSIC) (JAEPre_08_00370).

References

[1] M. Gevezova, T. Dekalska, K. Stoyanov et al., "Recent advances in broomrapes research," Journal of BioScience & Biotechnology, vol. 1, no. 2, pp. 91-105, 2012.

[2] C. Parker, "The parasitic weeds of the Orobanchaceae," in Parasitic Orobanchaceae-Parasitic Mechanisms and Control Strategies, D. M. Joel, J. Gressel, and L. J. Musselman, Eds., pp. 313-344, Springer, Heidelberg, Germany, 2013.

[3] J. M. Fernandez-Martinez, L. Velasco, and B. Perez-Vich, "Progress in research on breeding for resistance to broomrape," in

Proceedings of the 18th International Sunflower Conference, 2012, http://www.asagir.org.ar/asagir2008/buscar_congreso.asp.

[4] I. V Novopokrovsky and N. N. Tzvelev, "Orobanchaceae Lindl," in Flora SSSR, V L. Komarov, Ed., no. 23, pp. 19-117, Botaniceskij Institut Akademija Nauk SSSR, Leningrad, Russia, 1958.

[5] G. Beck-Mannagetta, "Orobanchaceae," in Das Pflanzenreich, A. Engler, Ed., vol. 4, pp. 1-348, von Wilhelm Engelmann, Leipzig, Germany, 1930.

[6] A. J. Pujadas-Salva and L. Velasco, "Comparative studies on Orobanche cernua L. and O. cumana Wallr. (Orobanchaceae) in the Iberian Peninsula," Botanical Journal of the Linnean Society, vol. 134, no. 4, pp. 513-527, 2000.

[7] B. Roman, C. Alfaro, A. M. Torres et al., "Genetic relationships among Orobanche species as revealed by RAPD analysis," Annals of Botany, vol. 91, no. 6, pp. 637-642, 2003.

[8] D. Delipavlov, "Orobanchaceae," in Flora Reipublicae Bulgaricae, S. I. Kozuharov and B. A. Kuzmanov, Eds., vol. 10, pp. 291-325, Marin Drinov Academic Publishing House, Sofia, Bulgaria, 1995.

[9] B. K. Blackman, M. Scascitelli, N. C. Kane et al., "Sunflower domestication alleles support single domestication center in eastern North America," Proceedings of the National Academy of Sciences of the United States of America, vol. 108, no. 34, pp. 14360-14365, 2011.

[10] E. D. Putt, "Sunflower early history," in Sunflower Production and Technology, A. A. Schneiter, Ed., Agronomy Monograph no. 35, pp. 1-21, ASA-CSSA-SSSA, Madison, Wis, USA, 1997.

[11] D. Skoric, "The genetics of sunflower," in Sunflower Genetics and Breeding, D. Skoric and Z. Sakac, Eds., pp. 1-163, Serbian Academy of Sciences and Arts, Novi Sad, Serbia, 2012.

[12] V. Encheva and P. Shindrova, "Broomrape (Orobanche cumana Wallr.)--a hindrance to sunflower production in Bulgaria," in Proceedings of the 3rd International Workshop on Orobanche and Related Striga Research, pp. 619-622, Royal Tropical Institute, Amsterdam, The Netherlands, 1994.

[13] P. Jouffret and V. Lecomte, "Orobanche sur tournesol. Un parasite en extension," Lettre d'Informations Regionales CETIOM, Zone Sud, 2010, http://www.cetiom.fr/fileadmin/ cetiom/regions/Sud/PDF/2010/oleomail/OleoMail_TO_Prophylaxie_O_cumana_sud_07092010.pdf.

[14] M. Amri, Z. Abbes, S. B. Youssef, M. Bouhadida, H. B. Salah, and M. Kharrat, "Detection of the parasitic plant, Orobanche cumana on sunflower (Helianthus annuus L.) in Tunisia," African Journal of Biotechnology, vol. 11, no. 18, pp. 4163-4167, 2012.

[15] M. Castejon, F. Romero-Munoz, and L. Garcla-Torres, "Orobanche cernua seed dispersal through sunflower achenes," Helia, vol. 14, pp. 51-54, 1991.

[16] B. Perez-Vich, L. Velasco, P. J. Rich, and G. Ejeta, "Marker-assisted and physiology-based breeding for resistance to Orobanchaceae," in Parasitic Orobanchaceae--Parasitic Mechanisms and Control Strategies, D. M. Joel, J. Gressel, and L. J. Musselman, Eds., pp. 369-391, Springer, Heidelberg, Germany, 2013.

[17] A. V Vranceanu, V A. Tudor, F. M. Stoenescu, and N. Pirvu, "Virulence groups of Orobanche cumana Wallr. differential hosts and resistance sources and genes in sunflower," in Proceedings of the 9th International Sunflower Conference, pp. 74-80, International Sunflower Association, Paris, France, 1980.

[18] P. Shindrova, "Broomrape (Orobanche cumana Wallr.) in Bulgaria--distribution and race composition," Helia, vol. 29, no. 44, pp. 111-120, 2006.

[19] P. Shindrova and E. Penchev, "Race composition and distribution of broomrape (Orobanche cumana Wallr.) in Bulgaria during 2007-2011," Helia, vol. 35, no. 57, pp. 87-94, 2012.

[20] M. C. Vaz Patto, R. Diaz-Ruiz, Z. Satovic, B. Roman, A. J. Pujadas-Salva, and D. Rubiales, "Genetic diversity of Moroccan populations of Orobanche foetida: evolving from parasitising wild hosts to crop plants," Weed Research, vol. 48, no. 2, pp. 179-186, 2008.

[21] J. R. Qasem, "Parasitic flowering plants on cultivated plants in Jordan--the present status and management," Pakistan Journal of Weed Science, vol. 16, no. 2, pp. 227-239, 2010.

[22] J. J. Burdon and P. H. Thrall, "Pathogen evolution across the agro-ecological interface: implications for disease management," Evolutionary Applications, vol. 1, no. 1, pp. 57-65, 2008.

[23] C. J. Botanga, J. G. Kling, D. K. Berner, and M. P. Timko, "Genetic variability of Striga asiatica (L.) Kuntz based on AFLP analysis and host-parasite interaction," Euphytica, vol. 128, no. 3, pp. 375-388, 2002.

[24] C. J. Botanga and M. P. Timko, "Genetic structure and analysis of host and nonhost interactions of Striga gesnerioides (Witchweed) from Central Florida," Phytopathology, vol. 95, no. 10, pp. 1166-1173, 2005.

[25] C. J. Botanga and M. P. Timko, "Phenetic relationships among different races of Striga gesnerioides (Willd.) Vatke from West Africa," Genome, vol. 49, no. 11, pp. 1351-1365, 2006.

[26] A. Olivier, J. C. Glaszmann, C. Lanaud, and G. D. Leroux, "Population structure, genetic diversity and host specificity of the parasitic weed Striga hermonthica (Scrophulariaceae) in Sahel," Plant Systematics and Evolution, vol. 209, no. 1-2, pp. 33-45, 1998.

[27] G. Gagne, P. Roeckel-Drevet, B. Grezes-Besset et al., "Study of the variability and evolution of Orobanche cumana populations infesting sunflower in different European countries," Theoretical and Applied Genetics, vol. 96, no. 8, pp. 1216-1222, 1998.

[28] R. Pineda-Martos, L. Velasco, J. Fernandez-Escobar, J. M. Fernandez-Martinez, and B. Perez-Vich, "Genetic diversity of Orobanche cumana populations from Spain assessed using SSR markers," Weed Research, vol. 53, no. 4, pp. 279-289, 2013.

[29] Z. Satovic, D. M. Joel, D. Rubiales, J. I. Cubero, and B. Romn, "Population genetics in weedy species of Orobanche," Australasian Plant Pathology, vol. 38, no. 3, pp. 228-234, 2009.

[30] M. I. Rodrlguez-Ojeda, J. M. Fernandez-Martinez, L. Velasco, and B. Perez-Vich, "Extent of cross-fertilization in Orobanche cumana Wallr," Biologia Plantarum, vol. 57, no. 3, pp. 559-562, 2013.

[31] B. Achtarov, "Beitrag zur Kenntnis der Flora Bulgariens, nebst kritischen Bemerkungen," Bulletin of the Bulgarian Botanical Society, vol. 9, pp. 57-73, 1943.

[32] N. Stojanov and B. Stefanov, Flora Bulgarica, University Press, Sofia, Bulgaria, 1948.

[33] K. Stoyanov, "The trophic plasticity of genus Orobanche L. (Orobanchaceae) in Bulgaria," Agricultural Sciences, vol. 4, no. 12, pp. 67-72, 2013.

[34] B. Perez-Vich, B. Akhtouch, S. J. Knapp et al., "Quantitative trait loci for broomrape (Orobanche cumana Wallr.) resistance in sunflower," Theoretical and Applied Genetics, vol. 109, no. 1, pp. 92-102, 2004.

[35] R. Peakall and P. E. Smouse, "GenALEx 6.5: genetic analysis in Excel. Population genetic software for teaching and researchan update," Bioinformatics, vol. 28, no. 19, Article ID bts460, pp. 2537-2539, 2012.

[36] L. Excoffier and H. E. L. Lischer, "Arlequin suite ver 3.5: a new series of programs to perform population genetics analyses under Linux and Windows," Molecular Ecology Resources, vol. 10, no. 3, pp. 564-567, 2010.

[37] T. de Meeus, K. D. McCoy, F. Prugnolle et al., "Population genetics and molecular epidemiology or how to "debusquer la bete"" Infection, Genetics and Evolution, vol. 7, no. 2, pp. 308-332, 2007.

[38] S. Arnaud-Haond and K. Belkhir, "GENCLONE: a computer program to analyse genotypic data, test for clonality and describe spatial clonal organization," Molecular Ecology Notes, vol. 7, no. 1, pp. 15-17, 2007

[39] P G. Meirmans and P W. Hedrick, "Assessing population structure: [F.sub.ST] and related measures," Molecular Ecology Resources, vol. 11, no. 1, pp. 5-18, 2011.

[40] M. Nei and R. K. Chesser, "Estimation of fixation indices and gene diversities," Annals of Human Genetics, vol. 47, no. 3, pp. 253-259, 1983.

[41] M. Nei, Molecular Evolutionary Genetics, Columbia University Press, New York, NY, USA, 1987.

[42] T. Jombart, D. Pontier, and A.-B. Dufour, "Genetic markers in the playground of multivariate analysis," Heredity, vol. 102, no. 4, pp. 330-341, 2009.

[43] J. K. Pritchard, M. Stephens, and P Donnelly, "Inference of population structure using multilocus genotype data," Genetics, vol. 155, no. 2, pp. 945-959, 2000.

[44] D. Falush, M. Stephens, and J. K. Pritchard, "Inference of population structure using multilocus genotype data: linked loci and correlated allele frequencies," Genetics, vol. 164, no. 4, pp. 1567-1587, 2003.

[45] D. A. Earl and B. M. von Holdt, "STRUCTURE HARVESTER: a website and program for visualizing STRUCTURE output and implementing the Evanno method," Conservation Genetics Resources, vol. 4, no. 2, pp. 359-361, 2012.

[46] G. Evanno, S. Regnaut, and J. Goudet, "Detecting the number of clusters of individuals using the software STRUCTURE: a simulation study," Molecular Ecology, vol. 14, no. 8, pp. 2611-2620, 2005.

[47] M. Jakobsson andN. A. Rosenberg, "CLUMPP: a cluster matching and permutation program for dealing with label switching and multimodality in analysis of population structure," Bioinformatics, vol. 23, no. 14, pp. 1801-1806, 2007

[48] N. A. Rosenberg, "DISTRUCT: a program for the graphical display of population structure," Molecular Ecology Notes, vol. 4, no. 1, pp. 137-138, 2004.

[49] H. Gao, S. Williamson, and C. D. Bustamante, "A markov chain monte carlo approach for joint inference of population structure and inbreeding rates from multilocus genotype data," Genetics, vol. 176, no. 3, pp. 1635-1651, 2007.

[50] L. Excoffier, P E. Smouse, and J. M. Quattro, "Analysis of molecular variance inferred from metric distances among DNA haplotypes: application to human mitochondrial DNA restriction data," Genetics, vol. 131, no. 2, pp. 479-491, 1992.

[51] T. Ohta, "Linkage disequilibrium due to random genetic drift in finite subdivided populations," Proceedings of the National Academy of Sciences of the United States of America, vol. 79, no. 6, pp. 1940-1944, 1982.

[52] C. J. Thorogood, F. J. Rumsey, S. A. Harris, and S. J. Hiscock, "Host-driven divergence in the parasitic plant Orobanche minor Sm. (Orobanchaceae)," Molecular Ecology, vol. 17, no. 19, pp. 4289-4303, 2008.

[53] C. J. Thorogood, F. J. Rumsey, S. A. Harris, and S. J. Hiscock, "Gene flow between alien and native races of the holoparasitic angiosperm Orobanche minor (Orobanchaceae)," Plant Systematics and Evolution, vol. 282, no. 1-2, pp. 31-42, 2009.

[54] C. J. Thorogood, F. J. Rumsey, and S. J. Hiscock, "Host-specific races in the holoparasitic angiosperm Orobanche minor: implications for speciation in parasitic plants," Annals of Botany, vol. 103, no. 7, pp. 1005-1014, 2009.

[55] K. Yoneyama, C. Ruyter-Spira, and H. Bouwmeester, "Induction of germination," in Parasitic Orobanchaceae--Parasitic Mechanisms and Control Strategies, D. M. Joel, J. Gressel, and L. J. Musselman, Eds., pp. 167-194, Springer, Heidelberg, Germany, 2013.

[56] D. M. Joel, S. K. Chaudhuri, D. Plakhine, H. Ziadna, and J. C. Steffens, "Dehydrocostus lactone is exuded from sunflower roots and stimulates germination of the root parasite Orobanche cumana" Phytochemistry, vol. 72, no. 7, pp. 624-634, 2011.

[57] M. Castejon, M. J. Suso, F. Romero-Munoz, and L. GarciaTorres, " Isoenzymatic study of broomrape (Orobanche cernua) populations infesting sunflower (Helianthus annuus)" in Proceedings of the 5th International Symposium on Parasitic Weeds, pp. 313-319, International Maize and Wheat Improvement Center (CIMMYT), Nairobi, Kenya, 1991.

[58] R. Pineda-Martos, R. Batchvarova, J. M. Fernandez-Martinez, L. Velasco, and B. Peorez-Vich, "Genetic diversity of Orobanche cumana populations from Spain and Eastern Europe," in Proceedings of the 10th World Congress of Parasitic Plants, D. Rubiales, J. Westwood, and A. Uludag, Eds., p. 145, IPPS, International Parasitic Plant Society, Kusadasi, Turkey, 2009.

[59] L. Molinero-Ruiz, A. B. Garcia-Carneros, M. Collado-Romero, S. Raranciuc, J. Dominguez, and J. M. Melero-Vara, "Pathogenic and molecular diversity in highly virulent populations of the parasitic weed Orobanche cumana (sunflower broomrape) from Europe," Weed Research, vol. 54, no. 1, pp. 87-96, 2014.

[60] D. M. Joel, "Identification of Orobanche seeds," in Proceedings of the 4th International Symposium on Parasitic Flowering Plants, H. C. Weber and W. L. Forstreuter, Eds., pp. 437-444, Philipps-Universitat, Marburg, Germany, 1987

[61] L. Plaza, I. Fernandez, R. Juan, J. Pastor, and A. Pujadas, "Micromorphological studies on seeds of Orobanche species from the Iberian Peninsula and the Balearic Islands, and their systematic significance," Annals of Botany, vol. 94, no. 1, pp. 167-178, 2004.

[62] M. I. Rodriguez-Ojeda, R. Pineda-Martos, L. C. Alonso et al., "A dominant avirulence gene in Orobanche cumana triggers Or5 resistance in sunflower," Weed Research, vol. 53, no. 5, pp. 322-327, 2013.

[63] F. Guerin, P. Gladieux, and B. L. Cam, "Origin and colonization history of newly virulent strains of the phytopathogenic fungus Venturia inaequalis" Fungal Genetics and Biology, vol. 44, no. 4, pp. 284-292, 2007.

[64] C. Xhaard, B. Fabre, A. Andrieux et al., "The genetic structure of the plant pathogenic fungus Melampsora larici-populina on its wild host is extensively impacted by host domestication," Molecular Ecology, vol. 20, no. 13, pp. 2739-2755, 2011.

[65] K. Huang, R. Whitlock, M. C. Press, and J. D. Scholes, "Variation for host range within and among populations of the parasitic plant Striga hermonthica" Heredity, vol. 108, no. 2, pp. 96-104, 2012.

[66] Z. P. Song, X. Xu, B. Wang, J. K. Chen, and B.-. Lu, "Genetic diversity in the northernmost Oryza rufipogon populations estimated by SSR markers," Theoretical and Applied Genetics, vol. 107, no. 8, pp. 1492-1499, 2003.

[67] H.-W. Cai, X.-K. Wang, and H. Morishima, "Comparison of population genetic structures of common wild rice (Oryza rufipogon Griff.), as revealed by analyses of quantitative traits, allozymes, and RFLPs," Heredity, vol. 92, no. 5, pp. 409-417, 2004.

[68] M. C. Vaz Patto, M. FernAndez-Aparicio, Z. Satovic, and D. Rubiales, "Extent and pattern of genetic differentiation within and between European populations of Phelipanche ramosa revealed by amplified fragment length polymorphism analysis," Weed Research, vol. 49, no. 1, pp. 48-55, 2009.

[69] C. B. Heiser, D. M. Smith, S. B. Clevenger, and W. C. Martin Jr., "The North American sunflowers (Helianthus)," Memoirs of the Torrey Botanical Club, vol. 22, pp. 1-218, 1969.

[70] A. Honiges, A. Ardelean, X. Xi, K. Yoneyam, and K. Wegmann, "Towards understanding Orobanche host-specificity," Romanian Agricultural Research, vol. 29, pp. 313-322, 2012.

Rocio Pineda-Martos, (1) Antonio J. Pujadas-Salva, (2) Jose M. Fernandez-Martinez, (1) Kiril Stoyanov, (3) Leonardo Velasco, (1) and Begona Perez-Vich (1)

(1) Institute for Sustainable Agriculture (IAS-CSIC), Finca Alameda del Obispo, Avenida Memndez-Pidal s/n, 14004 Cordoba, Spain

(2) Department of Agricultural and Forestry Sciences and Resources, University of Cordoba, Campus de Rabanales, Edificio Celestino Mutis, Carretera de Madrid Km 396,14071 Cordoba, Spain

(3) Department of Botany, Agricultural University of Plovdiv, 12 Mendeleev, 4000 Plovdiv, Bulgaria

Correspondence should be addressed to Leonardo Velasco; lvelasco@ias.csic.es

Received 10 February 2014; Revised 17 June 2014; Accepted 1 July 2014; Published 20 July 2014

Academic Editor: Antonio Amorim

TABLE 1: Host species, collecting site, characteristics,
and number of individuals analyzed for the studied
Orobanche cumana populations.

Population   Host          Collecting site           Region
             species

0. cumana populations collected on wild hosts

CUMBUL-1     Artemisia     Bulgaria, Burgas,         South-Eastern
               maritima      Atanasovsko Lake          Bulgaria
CUMBUL-2     Artemisia     Bulgaria, Burgas,         South-Eastern
               maritima      Pomorie-Aheloj            Bulgaria
CUMBUL-3     Artemisia     Bulgaria, Kranevo         North-Eastern
               maritima                                Bulgaria
CUMBUL-4     Artemisia     Bulgaria, Balchik         North-Eastern
               maritima                                Bulgaria
CUMBUL-5.1   Anthemis      Bulgaria, Kavarna,        North-Eastern
               arvensis      Gorun-Tyulenovo           Bulgaria
CUMBUL-5.2   Chamaemelum   Bulgaria, Kavarna,        North-Eastern
               nobile        Gorun-Tyulenovo           Bulgaria
CUMBUL-6     Artemisia     Bulgaria, Burgas, Poda    South-Eastern
               maritima      Protected Area            Bulgaria
CUMBUL-7     Artemisia     Bulgaria, Burgas,         South-Eastern
               maritima      Atanasovsko Lake          Bulgaria

0. cumana populations collected on sunflower

CUMBUL-8     Helianthus    Bulgaria, Sadovo          Central Bulgaria
               annuus
CUMBUL-9     Helianthus    Bulgaria, Plodiv          Central Bulgaria
               annuus
CUMBUL-10    Helianthus    Bulgaria, Balgarevo       North-Eastern
               annuus                                  Bulgaria
IASCum-2     Helianthus    Spain, Sevilla, Ecija     Southern Spain
               annuus
IASCum-3     Helianthus    Spain, Sevilla, Osuna     Southern Spain
               annuus
IASCum-4     Helianthus    Spain, Cuenca, Montalbo   Central Spain
               annuus

Population   Latitude, Longitude,              Year   n
             Altitude

0. cumana populations collected on wild hosts

CUMBUL-1     42[degrees]33'02.7"N;             2006   16
               27[degrees]29'24"E; 14 m
CUMBUL-2     42[degrees]37'02.8"N;             2006   30
               27[degrees]37'31.l"E; 17 m
CUMBUL-3     43[degrees]20'05.6"N;             2006   6
               28[degrees]3'41.9"E; 112 m
CUMBUL-4     43[degrees]24'36.9"N;             2006   29
               28[degrees]9'23.5"E; 21 m
CUMBUL-5.1   43[degrees]29'12.6"N;             2006   28
               28[degrees]31'13.3"E; 44 m
CUMBUL-5.2   43[degrees]29'12.6"N;             2006   20
               28[degrees]31'13.3"E; 44 m
CUMBUL-6     42[degrees]26'35.91"N;            2012   23
               27[degrees]27'58.64"E; 7 m
CUMBUL-7     42[degrees]33'05.88"N;            2012   14
               27[degrees]29'22.91"E; 8 m

0. cumana populations collected on sunflower

CUMBUL-8     42[degrees]07,13.49"N;            2012   20
               24[degrees]54'53.40"E; 156 m
CUMBUL-9     42[degrees]03'35.43"N;            2012   20
               24[degrees]49'26.28"E; 189 m
CUMBUL-10    43[degrees]24'58.14"N;            2012   18
               28[degrees]26'43.83"E; 81 m
IASCum-2     37[degrees]34'24"N;               2008   12
               5[degrees]8'45"W; 181 m
IASCum-3     37[degrees]15'19"N;               2008   12
               5[degrees]3'49"W; 304 m
IASCum-4     39[degrees]51'03"N;               2008   12
               02[degrees]39'54"W; 838 m

n, final studied sample size [including a number of plants excluded
from the analysis because of lack of amplification, belonging to
each of the populations CUMBUL-1 (four plants excluded), CUMBUL-4
(one plant), CUMBUL-5J (two plants), CUMBUL-5_2 (two plants),
CUMBUL-6 (three plants), and CUMBUL-10 (two plants)].

TABLE 2: Genetic diversity parameters of Orobanche cumana
populations from Bulgaria collected on wild hosts and on
sunflower (prefix CUMBUL-) and from Spain collected on
sunflower (prefix IASCum-).

Population      P      Na ([+ or -] SE)   Na [greater than
                                          or equal to] 5%
                                          ([+ or -] SE)

O. cumana populations collected on wild hosts

CUMBUL-1        66.7   1.733 (0.15)       1.667 (0.13)
CUMBUL-2        86.9   2.000 (0.14)       1.933 (0.15)
CUMBUL-3        0.0    1.000 (0.00)       1.000 (0.00)
CUMBUL-4        53.3   1.600 (0.16)       1.333 (0.13)
CUMBUL-5.1      80.0   2.000 (0.17)       1.867 (0.16)
CUMBUL-5_2      80.0   1.933 (0.15)       1.933 (0.15)
CUMBUL-6        73.3   1.800 (0.14)       1.667 (0.16)
CUMBUL-7        73.3   1.800 (0.14)       1.800 (0.14)
Mean            64.2   1.733 (0.06)       1.650 (0.12)

O. cumana populations collected on sunflower

CUMBUL-8        40.0   1.400 (0.13)       1.133 (0.09)
CUMBUL-9        13.3   1.133 (0.09)       1.133 (0.09)
CUMBUL-10       46.7   1.467 (0.13)       1.467 (0.13)
Mean-Bulgaria   33.3   1.333 (0.10)       1.244 (0.11)
IASCum-2        0.0    1.000 (0.00)       1.000 (0.00)
IASCum-3        0.0    1.000 (0.00)       1.000 (0.00)
IASCum-4        6.7    1.067 (0.07)       1.067 (0.07)
Mean-Spain      2.2    1.022 (0.02)       1.022 (0.02)

Population      Ne ([+ or -] SE)   Npa ([+ or -] SE)

O. cumana populations collected on wild hosts

CUMBUL-1        1.391 (0.10)       0.000 (0.00)
CUMBUL-2        1.521 (0.10)       0.000 (0.00)
CUMBUL-3        1.000 (0.00)       0.000 (0.00)
CUMBUL-4        1.145 (0.05)       0.067 (0.07)
CUMBUL-5.1      1.250 (0.07)       0.000 (0.00)
CUMBUL-5_2      1.418 (0.10)       0.000 (0.00)
CUMBUL-6        1.294 (0.10)       0.000 (0.00)
CUMBUL-7        1.467 (0.12)       0.000 (0.00)
Mean            1.311 (0.03)       0.008 (0.01)

O. cumana populations collected on sunflower

CUMBUL-8        1.039 (0.02)       0.000 (0.00)
CUMBUL-9        1.014 (0.01)       0.000 (0.00)
CUMBUL-10       1.175 (0.06)       0.000 (0.00)
Mean-Bulgaria   1.076 (0.05)       0.000 (0.00)
IASCum-2        1.000 (0.00)       0.000 (0.00)
IASCum-3        1.000 (0.00)       0.000 (0.00)
IASCum-4        1.026 (0.03)       0.000 (0.00)
Mean-Spain      1.009 (0.01)       0.000 (0.00)

Population      Ho ([+ or -] SE)   He ([+ or -] SE)

O. cumana populations collected on wild hosts

CUMBUL-1        0.004 (0.01)       0.229 (0.05)
CUMBUL-2        0.000 (0.00)       0.297 (0.05)
CUMBUL-3        0.000 (0.00)       0.000 (0.00)
CUMBUL-4        0.000 (0.00)       0.105 (0.03)
CUMBUL-5.1      0.032 (0.01)       0.171 (0.04)
CUMBUL-5_2      0.014 (0.01)       0.248 (0.05)
CUMBUL-6        0.003 (0.01)       0.181 (0.05)
CUMBUL-7        0.010 (0.01)       0.258 (0.05)
Mean            0.008 (0.002)      0.186 (0.02)

O. cumana populations collected on sunflower

CUMBUL-8        0.021 (0.01)       0.034 (0.01)
CUMBUL-9        0.000 (0.00)       0.013 (0.01)
CUMBUL-10       0.015 (0.01)       0.123 (0.04)
Mean-Bulgaria   0.012 (0.01)       0.057 (0.03)
IASCum-2        0.000 (0.00)       0.000 (0.00)
IASCum-3        0.000 (0.00)       0.000 (0.00)
IASCum-4        0.000 (0.00)       0.019 (0.02)
Mean-Spain      0.000 (0.00)       0.006 (0.01)

Population      I ([+ or -] SE)    Pairwise
                                  differences

O. cumana populations collected on wild hosts

CUMBUL-1        0.349 (0.08)      3.111 (1.66)
CUMBUL-2        0.458 (0.07)      4.393 (2.20)
CUMBUL-3        0.000 (0.00)      0.000 (0.00)
CUMBUL-4        0.184 (0.06)      1.595 (0.96)
CUMBUL-5.1      0.306 (0.06)      2.449 (1.34)
CUMBUL-5_2      0.400 (0.07)      3.597 (1.86)
CUMBUL-6        0.300 (0.07)      2.629 (1.43)
CUMBUL-7        0.398 (0.08)      3.947 (2.04)
Mean            0.299 (0.03)      2.715 (0.05)

O. cumana populations collected on sunflower

CUMBUL-8        0.071 (0.03)      0.446 (0.41)
CUMBUL-9        0.026 (0.02)      0.195 (0.25)
CUMBUL-10       0.201 (0.06)      1.825 (1.07)
Mean-Bulgaria   0.099 (0.05)      0.822 (0.51)
IASCum-2        0.000 (0.00)      0.000 (0.00)
IASCum-3        0.000 (0.00)      0.000 (0.00)
IASCum-4        0.030 (0.03)      0.290 (0.32)
Mean-Spain      0.010 (0.01)      0.097 (0.10)

Population      Genotypic       [F.sub.is]      S
                richness      ([+ or -] SE)

                 G     R

O. cumana populations collected on wild hosts

CUMBUL-1         7    0.40    0.984 (0.01)    0.992
CUMBUL-2         8    0.24    1.000 (0.00)    1.000
CUMBUL-3         1    0.00         --           --
CUMBUL-4         6    0.18    1.000 (0.00)    1.000
CUMBUL-5.1      11    0.37    0.776 (0.04)    0.874
CUMBUL-5_2       7    0.32    0.920 (0.04)    0.958
CUMBUL-6        10    0.41    0.968 (0.03)    0.984
CUMBUL-7         7    0.46    0.975 (0.01)    0.987
Mean            7.1   0.30       0.946        0.971

O. cumana populations collected on sunflower

CUMBUL-8         3    0.11    0.194 (0.10)    0.325
CUMBUL-9         2    0.05    1.000 (0.00)    1.000
CUMBUL-10        8    0.41    0.915 (0.04)    0.956
Mean-Bulgaria   4.3   0.19       0.703        0.760
IASCum-2         1    0.00         --           --
IASCum-3         1    0.00         --           --
IASCum-4         2    0.09    1.000 (0.02)    1.000
Mean-Spain      0.7   0.03

P: percentage of polymorphic loci, Na: average observed allele
number, Na > 5%: number of different alleles with a frequency
[greater than or equal to] 5%, Ne: number of effective alleles,
Npa: number of private alleles unique to a single population,
Ho: observed heterozygosity, He: expected heterozygosity,
I: Shannons diversity index, Pairwise differences: mean number
of pairwise differences between individuals within each
population ([+ or -] SD), G: number of distinct multilocus
genotypes (MLGs), R: genotypic richness; [F.sub.is]: fixation
index, and S: selling rate.

TABLE 3: Proportion of membership
of each Bulgarian Orobanche cumana
population in inferred STRUCTURE
groups for K = 2. Populations
collected on wild hosts are
highlighted in bold.

Population    Genetic   Genetic
              group 1   group 2

CUMBUL-1#      0.491     0.509
CUMBUL-2#      0.677     0.323
CUMBUL-3#      0.984     0.016
CUMBUL-4#      0.969     0.031
CUMBUL-5.1#    0.138     0.862
CUMBUL-5.2#    0.239     0.76
CUMBUL-6#      0.104     0.896
CUMBUL-7#      0.541     0.459
CUMBUL-8       0.023     0.977
CUMBUL-9       0.022     0.978
CUMBUL-10      0.647     0.352

Note: Populations collected on
wild hosts are indicated with #.

TABLE 4: Analysis of molecular variance (AMOVA) of Orobanche
cumana populations from Bulgaria.

Hierarchical structure and source    df      AMOVA statistics
of variation

                                           Sum of     Variance
                                           squares   components

Bulgarian populations collected on wild hosts
(8 populations; 166 individuals)

Not structured
    Among populations                 7    491.05       1.69
    Within populations/group         324   473.19       1.46
Structured based on gene pools (b)
    Among groups                      1    294.36       2.29
    Among populations/group           6    196.69       0.80
    Within populations/group         324   473.19       1.46

Total of Bulgarian populations (wild and cultivated host)
(11 populations; 224 individuals)

Not structured
    Among populations                10    713.97       1.74
    Within populations/group         437   517.64       1.18
Structured based on ecological
  status (c)
    Among groups                      1     93.81       0.14
    Among populations/group           9    620.16       1.68
    Within populations/group         437   517.64       1.18
Structured based on gene pools (d)
    Among groups                      2    423.05       1.51
    Among populations/group           8    290.91       0.90
    Within populations/group         437   517.64       1.18

Hierarchical structure and source    % Variance     F-statistics
of variation                                             (a)

Bulgarian populations collected on wild hosts
(8 populations; 166 individuals)

Not structured
    Among populations                  53.64      [F.sub.ST] = 0.54
    Within populations/group           46.36
Structured based on gene pools (b)
    Among groups                       50.37      [F.sub.CT] = 0.50
    Among populations/group            17.56      [F.sub.SC] = 0.35
    Within populations/group           32.07      [F.sub.ST] = 0.68

Total of Bulgarian populations (wild and cultivated host)
(11 populations; 224 individuals)

Not structured
    Among populations                  59.54      [F.sub.ST] = 0.60
    Within populations/group           40.46
Structured based on ecological
  status (c)
    Among groups                        4.55      [F.sub.CT] = 0.05
    Among populations/group            56.05      [F.sub.SC] = 0.59
    Within populations/group           39.40      [F.sub.ST] = 0.61
Structured based on gene pools (d)
    Among groups                       42.01      [F.sub.CT] = 0.42
    Among populations/group            25.05      [F.sub.SC] = 0.43
    Within populations/group           32.94      [F.sub.ST] = 0.67

Hierarchical structure and source    P value
of variation

Bulgarian populations collected on wild hosts
(8 populations; 166 individuals)

Not structured
    Among populations                <0.001
    Within populations/group
Structured based on gene pools (b)
    Among groups                      0.032
    Among populations/group          <0.001
    Within populations/group         <0.001

Total of Bulgarian populations (wild and cultivated host)
(11 populations; 224 individuals)

Not structured
    Among populations                <0.001
    Within populations/group
Structured based on ecological
  status (c)
    Among groups                      0.234
    Among populations/group          <0.001
    Within populations/group         <0.001
Structured based on gene pools (d)
    Among groups                      0.002
    Among populations/group          <0.001
    Within populations/group         <0.001

(a) F-statistics represents differentiation among groups
([F.sub.CT]), among populations within groups ([F.sub.SC]),
and among populations within the whole population ([F.sub.ST]).

(b) The gene pools defined with clustering analyses comprised
(i) populations CUMBUL-3 and -4 and (ii) populations CUMBUL-1,
-2, -5_1, -5_2, -6, and -7

(c) The structured groups based on the ecological status were
(i) wild hosts (populations CUMBUL-1, -2, -3, -4, -5_1, -5_2,
-6, and -7) and (ii) cultivated host (sunflower) (populations
CUMBUL-8, -9, -10).

(d) The gene pools defined with clustering analyses were
(i) populations CUMBUL-3, -4, (ii) populations CUMBUL-8 and -9,
and (iii) populations CUMBUL-1, -2, -5.1, -5.2, -6, -7, and -10.

TABLE 5: Number of emerged Orobanche cumana shoots per
sunflower plant (mean [+ or -] standard deviation) in the
evaluation of O. cumana populations CUMBUL-1, CUMBUL-2, and
CUMBUL-4, collected in Bulgaria on Artemisia maritima,
CUMBUL-5_1, collected in Bulgaria on Anthemis arvensis, and
control population OC-88, collected in Spain on cultivated
sunflower, on two sunflower lines (B117 and B206) with no
genetic resistance to O. cumana, conducted in pots in 2007 (a).

                    B117 (b)                 B206 (a)

CUMBUL-1     14.5 [+ or -] 9.9 (b)    35.3 [+ or -] 13.1 (c)
CUMBUL-2     39.5 [+ or -] 7.7 (c)    36.3 [+ or -] 11.3 (c)
CUMBUL-4      5.2 [+ or -] 4.7 (a)     1.7 [+ or -] 1.0 (a)
CUMBUL-5_1   11.5 [+ or -] 8.9 (ab)   14.3 [+ or -] 4.5 (b)
OC-88        10.3 [+ or -] 6.0 (ab)   18.5 [+ or -] 7.2 (b)

(a) Eight pots per each combination of sunflower cultivar and
O. cumana population.

(b) Means with different letters for each sunflower cultivar
differ significantly (P < 0.05).

TABLE 6: Number of emerged Orobanche cumana shoots per sunflower
plant (mean [+ or -] standard deviation) in the evaluation of
O. cumana populations CUMBUL-1, CUMBUL-2, and CUMBUL-4, collected
in Bulgaria on Artemisia maritima, CUMBUL-5_1, collected in
Bulgaria on Anthemis arvensis, OC-9, OC-11, and OC-13, collected
in Bulgaria on cultivated sunflower, and OC-88, collected in Spain
on cultivated sunflower, on six sunflower lines with different
levels of genetic resistance, conducted in pots in 2008 (a). The
O. cumana race to which each sunflower line is expected to be
resistant (if any) is given in parenthesis.

                    B117 (b)                 J8281 (B)

CUMBUL-1     17.7 [+ or -] 6.3 (bc)    2.6 [+ or -] 2.4 (ab)
CUMBUL-2      20.6 [+ or -] 3.2 (c)    1.3 [+ or -] 1.7 (ab)
CUMBUL-4     10.9 [+ or -] 7.1 (ab)    0.1 [+ or -] 0.4 (a)
CUMBUL-5.1   12.6 [+ or -] 6.7 (ab)    2.0 [+ or -] 1.1 (ab)
OC-9         13.8 [+ or -] 7.4 (abc)   3.0 [+ or -] 2.5 (ab)
OC-11         8.6 [+ or -] 5.3 (a)     2.5 [+ or -] 2.1 (ab)
OC-13        14.3 [+ or -] 7.9 (abc)   4.1 [+ or -] 1.9 (b)
OC-88         9.9 [+ or -] 6.9 (a)     16.6 [+ or -] 6.5 (c)

                AC03-1589 (C)            S1358 (D)

CUMBUL-1     1.1 [+ or -] 1.2 (a)          NE (c)
CUMBUL-2     0.5 [+ or -] 1.1 (a)   2.0 [+ or -] 1.4 (a)
CUMBUL-4     0.6 [+ or -] 0.7 (a)            NE
CUMBUL-5.1   5.1 [+ or -] 2.6 (b)            NE
OC-9         0.5 [+ or -] 0.8 (a)   0.8 [+ or -] 1.0 (a)
OC-11        0.2 [+ or -] 0.4 (a)   0.7 [+ or -] 0.8 (a)
OC-13        1.1 [+ or -] 1.1 (a)   1.2 [+ or -] 0.8 (a)
OC-88        1.6 [+ or -] 1.3 (a)   1.2 [+ or -] 1.2 (a)

                  P-1380 (E)        P96 (F)

CUMBUL-1            0 (a)              0
CUMBUL-2            0 (a)              0
CUMBUL-4            0 (a)              0
CUMBUL-5.1   0.4 [+ or -] 0.7 (a)      0
OC-9                0 (a)              0
OC-11               0 (a)              0
OC-13               0 (a)              0
OC-88        6.9 [+ or -] 4.3 (b)      0

(a) Eight pots per each combination of sunflower cultivar and
O. cumana population.

(b) Means with different letters for each sunflower cultivar
differ significantly (P < 0.05).

(c) NE = not evaluated.
COPYRIGHT 2014 Hindawi Limited
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2014 Gale, Cengage Learning. All rights reserved.

Article Details
Printer friendly Cite/link Email Feedback
Title Annotation:Research Article
Author:Pineda-Martos, Rocio; Pujadas-Salva, Antonio J.; Fernandez-Martinez, Jose M.; Stoyanov, Kiril; Velas
Publication:The Scientific World Journal
Article Type:Report
Geographic Code:4EXBU
Date:Jan 1, 2014
Words:11003
Previous Article:Identification and evaluation of strain B37 of Bacillus subtilis antagonistic to sapstain fungi on poplar wood.
Next Article:Approximate solution of Urysohn integral equations using the Adomian decomposition method.
Topics:

Terms of use | Privacy policy | Copyright © 2019 Farlex, Inc. | Feedback | For webmasters