Genetic diversity in populations of Isatis glauca Aucher ex Boiss. ssp. from Central Anatolia in Turkey, as revealed by AFLP analysis
© Özbek et al.; licensee Springer. 2013
Received: 5 August 2013
Accepted: 14 October 2013
Published: 4 November 2013
Isatidae L. is a complex and systematically difficult genus in Brassicaceae. The genus displays great morphological polymorphism, which makes the classification of species and subspecies difficult as it is observed in Isatis glauca Aucher ex Boiss. The aim of this study is characterization of the genetic diversity in subspecies of Isatis glauca Aucher ex Boiss. distributed widely in Central Anatolia, in Turkey by using Amplified Fragment Length Polymorphism (AFLP) technique.
Eight different Eco RI-Mse I primer combinations produced 805 AFLP loci, 793 (98.5%) of which were polymorphic in 67 accessions representing nine different populations. The data obtained by AFLP was computed with using GDA (Genetic Data Analysis) and STRUCTURE (version 2.3.3) software programs for population genetics. The mean proportion of the polymorphic locus (P), the mean number of alleles (A), the number of unique alleles (U) and the mean value of gene diversity (He) were 0.59, 1.59, 20, and 0.23 respectively. The coancestry coefficient (ϴ) was 0.24. The optimal number of K was identified as seven. The principal component analysis (PCA) explained 85.61% of the total genetic variation.
Isatis glauca ssp. populations showed a high level of genetic diversity, and the AFLP analysis revealed that high polymorphism and differentiated subspecies could be used conveniently for population genetic studies. The principal coordinate analysis (PCoA) based on the dissimilarity matrix, the dendrogram drawn with UPGMA method and STRUCTURE cluster analysis distinguished the accessions successfully. The accessions formed distinctive population structures for populations AA, AB, E, K, and S. Populations AG1 and AG2 seemed to have similar genetic content, in addition, in both populations several hybrid individuals were observed. The accessions did not formed distinctive population structures for both populations AI and ANP. Consequently, Ankara province might be the area, where species Isatis glauca Aucher ex Boiss. originated.
Taxonomic and cytological investigations on the Isatis L., species grown in the Eastern and South Eastern Anatolia and across the Eastern Mediterranean region were made by Mısırdalı (1985) (Figure 1, the region on the left side of red diagonal line on the map of Turkey). Mısırdalı (1985) displayed that there were 31 species, 14 subspecies, and 2 varieties in Isatis collections from East & Southeast Anatolia, and the Eastern Mediterranean - regions in Turkey. Yıldırımlı and Doğan (1986) investigated palynological polymorphism in 790 pollen grains collected from Isatis glauca ssp. glauca flowers in Sivas province of Turkey. They observed that 505 (62.92%) of those pollen grains were tricolpate (normal), 129 (16.33%) were syncolpate, 87 (11.01%) were stefanocolpate and 69 (8.73%) were dicolpate. Gilbert et al. (2002) screened genetic diversity in Isatis ssp. (Isatis tinctoria L., dyer’s woad) by using AFLP. Al-Shehbaz et al. (2006) discussed the evaluation of characters and their utilisation in infrafamilial classifications, delimitations of genera, the collection of molecular data and major subdivisions of the family, problematic taxa and future challenges in the Brassicaceae (Cruciferae). Kızıl (2006) reported morphological and agronomical characteristics of some wild and cultivated Isatis species. Moazzeni and Zarre (2006) studied the presence of Isatis tinctoria in Iran by using its morphological characters. Moazzeni et al. (2007) examined the systematic application of seed-coat surfaces of 23 species (41 populations) in four genera of tribe Isatidae using scanning electron microscopy (SEM). Spataro et al. (2007) displayed genetic variation and population structure in a Eurasian collection of Isatis tinctoria L. by using AFLP and SAMPL molecular markers. Spataro and Negri (2008) analysed phenotypic and genetic diversity of a Eurasian collection of Isatis tinctoria as well as its adaptability according to a wide range of altitudes. Tu et al. (2008) assessed intertribal somatic hybrids between Brassica rapa and Raphanus sativus with dye and medicinal plant Isatis indigotica. Du et al. (2009) presented the production and cytogenetic characterisation of intertribal somatic hybrids between Brassica napus and Isatis indigotica, and backcrosses. Tu et al. (2009) showed the chromosome elimination, addition, and introgression in intertribal partial hybrids between Brassica rapa and Isatis indigotica. Moazzeni et al. (2010) analysed the phylogeny of 28 Iranian taxa of Isatidae by using ITS sequence of ribosomal DNA and morphological characters. Rocha et al. (2011) detected genetic diversity in woad (Isatis tinctoria L.) by using ISSR markers. All these studies reveal that although there are many reports on morphological and genetic variation in the Brassicaceae family, very few studies are found on morphological or genetic variation in Isatis glauca Aucher ex Boiss.
The aim of this study was to analyse genetic diversity and population structure using molecular marker techniques among the I. glauca, subspecies populations from Central Anatolia in Turkey. AFLP method was used to estimate genetic diversity (He), population structure and genetic differentiation between populations using coancestry coefficient ϴP (= FST). In addition, the study also aimed to find the effects of climate (temperature T, humidity HU, and rainfall R), and geography (altitudes AL, latitudes LA and longitudes LN) on the genetic diversity of nine I. glauca populations.
Materials and Methods
Fluorescent based AFLP analysis
Genomic DNA was extracted from 1 to 1.5 month old leaves of individual plants from each of 67 accession using CTAB method, as described by Kidwell and Osborn (1992). AFLP analysis was carried out as described by Vos et al. (1995), with minor modifications. The primers, adaptors, and altogether, eight primer combinations used in this study are given in Additional file 2: Table S2 and Additional file 3: Table S3 respectively.
The aliquots of the restriction-ligation master-mix (a-RLMM) were prepared in a 2 mL Eppendorf tube without enzymes and the T4 DNA ligase buffer 10x. In a- restriction-ligation master-mix (RLMM) for one sample, the following were added; 0.617 μL H2O, 1.1 μL NaCl (0.5 M), 0.55 μL BSA 10× (1 g/L), 1 μL Mse I adaptor (50 pmol/μL = 50 μM) and 1 μL Eco R I adaptor (5 pmol/L = 5 μM). The RLMM was prepared by using 1.1 μL aliquots T4 DNA ligase buffer 10x, 4.267 μL a-RLMM, 0.05 μL Mse I (20 U/μL) enzyme, 0.05 μL Eco R I (100 U/μL) enzyme, and 0.033 μL T4 DNA ligase enzyme (30 weissU/μL). 96 well PCR microtiter plates were used for 67 samples. For each sample a 5.5 μL RLMM aliquot was dispensed into the wells and the 5.5 μL of the diluted sample genomic DNA (50 ng) was added. PCR microtiter plates were short spinned in a centrifuge (Sigma 1–14) and left for incubation (Techne TC-412) at 37°C for 6 hours.
Preselective PCR amplification
Before the preselective PCR amplification, the 5-μL restriction-ligation products were diluted by adding 95 μL TE (1X). For the preselective PCR amplification, the primers, were complementary to the sequences of the Eco R I and Mse 1 adaptors, that contained one selective nucleotide. Preselective PCR, reaction consisted of 2 μL (10X) PCR buffer, 1.6 μL (2 mM) MgCl2, 1.2 μL (2.5 mM) dNTPs, 1 μL (5 pmol) Eco R I primer, 1 μL (5 pmol) Mse I primer, 0.2 μL (1 μ/μL) Taq DNA polymerase, 9 μL ddH2O, and 4 μL diluted restriction-ligation products. The diluted restriction-ligation products were kept at −20°C until used. Preselective amplification for 20 cycles was carried out through PCR. Initial extended denaturation was carried out at 94°C for 2 min, followed by denaturation at 94°C for 30 sec, annealing at 56°C for 30 sec, extension at 72°C for 2 min, and the final extension at 60°C for 30 min.
Selective PCR amplification
Selective PCR amplification was carried out using 10 μL preselective PCR amplification products diluted in 190 μL TE (1X). The diluted preselective PCR amplification products were kept at −20°C until used. The selective PCR amplification was done with Eco R I and Mse I primers, which contained three selective nucleotides. For the fluorescent-based fragment analysis, the Eco R I selective primers of 39, 36, 39, and 36 were labelled with FAM-1, FAM-2, FAM-3, and FAM-4 respectively, while the Eco R I selective primers 33, 36, 33, and 36 were labelled with VIC-1, VIC-2, VIC-3, and VIC-4 fluorescent dye. Mse I primers were used with the unlabelled ones. The selective PCR amplification used in this study is given in Additional file 4: Table S4.
Capillary electrophoresis of selective amplification products were performed by using ABI 3130 × l (Applied Biosytems Inc., Foster City, CA). For capillary electrophoresis; 1 μL selective PCR amplification products were denatured using 0.2 μL LIZ-500 size standard at 95°C for 5 min followed by heat shock applied by chilling on ice at 0°C for 5 min. Then, permanently denatured single stranded DNA was loaded on ABI 3130 X l. After capillary electrophoresis, AFLP fragments were scored into a binary data matrix as 1 (present) or 0 (absent) using Gene Mapper 4.0 software package (Applied Biosystems).
For investigation of population structures of nine I. glauca ssp. populations, we used the software program STRUCTURE (Pritchard et al. 2000). STRUCTURE provides a model-based Bayesian approach to explain population structure by using our entire AFLP markers data set to identify K clusters to which the program then assigns each individual. We used 67 individuals to infer the optimal value of K (ie., the number of clusters) by evaluating K = 1–9. For parameter set, in our model, we selected with admixture as ancestry model and the allele frequencies were assumed to be correlated, since it is more reasonable to assume common ancestry of such closely related populations. The length of burn-in Markov Chain Monte Carlo (MCMC) replications was set to 10000 and data were collected over 100000 MCMC replications in run, based on previous literature suggesting that this level is sufficient (Evanno et al. 2005). We determined the optimal value of K using the second order statistics (∆K) developed by Evanno et al. (2005) and the ad hoc procedure described by Pritchard et al. (2000).
Principal component analysis (PCA)
PCA was calculated by using the following genetic indices, and the sample sizes: P, A and He, and N respectively, as well as geographical (AL, LA, and LN) and climatic (RA, T, and HU) data (Additional file 5: Table S5) as variables according to the Pearson’s (one-tailed) correlation matrix using XLSTAT (version 2013, Addinsoft™) a software package for Windows.
Since AFLPs are dominant markers, data were scored as binary data. Polymorphic bands, exhibiting presence or absence of bands, were scored as alternative alleles. The data thus obtained were considered as haploid and analysed by GDA.
Gene diversity () (Nei He1973), estimating within-population diversity, was computed as the expected heterozygosity based on allele frequencies for each locus and for all loci, polymorphic and non-polymorphic ones.
Genetic differentiation between populations is often estimated with the Nei’s coefficient GST (Nei 1973) for dominantly inherited DNA markers. This coefficient may tell us how genetic variation is partitioned within- and between-populations; a high GST value indicates that plants within a population are relatively similar, but populations are considerably different. When there are two alleles (1 and 0), this GST is identical to Wright’s (1951) FST (Nei 1973). Thus, F statistics was used to estimate the extent of differentiation, between groups (populations and sub-populations) (Hartl and Clark 1997). The coancestry coefficient ϴ (= FST) was measured for every locus and for all loci in each population.
Multiple regression analysis (MR) (SPSS version 11 for Windows) was conducted with AFLP diversity and allele diversity in nine populations. MR employed the genetic variables (P, A and He) as dependent and the environmental variables (AL, LA, LN, RA, T, and HU) as independent.
Reproducibility of AFLP profiles
The reproducibility of scoring of the AFLP profiles was checked by analysing the genotyping error rate in repeated runs of the same extracts from eight plants. In the beginning of the study, 12 different primer combinations were scanned for eight samples (accessions) and the eight polymorphic primer sets selected and applied for all of the 67 accessions. The data were obtained using selected eight primer combinations in both pre-scanning and applied through all accessions including those eight accessions were compared to evaluate the reproducibility of AFLP markers. The percent of reproducibility was calculated for each primer combination. Average percent of reproducibility was calculated as 90.62% that ranged 86.38% (E36XM35) to 97.78% (E36XM34) among the primer combinations.
AFLP fragment analysis
In AFLP analysis, eight Eco R I and Mse I primer combinations generated 805 fragments. The primer combination E36xM34 produced the highest number (194) of fragments, while the primer combination E36xM33 produced the least number (32) of fragments (data not shown). The primer combination E36xM34 displayed the highest number (510) of fragments in population AA in total of eight individuals, while the primer combination E39xM41 displayed the least number (81) of fragments in population AI in total of six individuals. Average number of fragments per population was calculated according to total present fragment numbers produced by eight primer combinations in all individuals of each population and ranged 252.17 (in population AI) to 314.75 (in population AA).
The number of sample size ( N ), the proportion of polymorphic locus ( P ), number of alleles ( A ), the genetic diversity value ( He ) and unique allele ( U ) numbers per population, and coancestry coefficient ( ϴ ) for studied nine Turkish Isatis glauca subspecies populations
The mean value of the coancestry coefficient ϴ (= FST) or genetic differentiation between the populations is 0.24 (95% confidence interval) (Table 1). The highest genetic distance (GD = 0.24) was observed between population AA and population S, while the lowest genetic distance (GD = 0.04) was observed between AG1 and AG2 (Data not shown).
In AFLP analysis of nine I. glauca ssp. populations, 19 unique alleles were observed (Additional file 6: Table S6). About the unique alleles, two existed in population AA, 1 in each of populations AG1 and E, 3 in population AG2 and 12 in population S. The frequencies of unique alleles range 0.13 (in populations AG1, AG2 and S) to 1.00 (population S).
Accessions formed distinctive population structures for populations AA, AB, E, K, and S. Populations AG1 and AG2 seemed to have similar genetic content, in addition in both populations several hybrid individuals were observed. Populations AI and ANP did not display distinctive population structures. In these populations, all individuals, except one individual in population AI, were seemed to be hybrids. In general, all populations have hybrid individuals.
The hybrid individuals detected in this study is an indication of gene flow between populations. Particularly, extensive gene flow was observed between AG1, AG2, AI, and ANP. It is noteworthy that there is a population (light green colour) found in hybrid individuals, although there is no such a distinctive population among the populations analysed in this study. This might be because of there is no any sample from this population among the analysed populations or that might be extinct in the evolutionary history of subspecies populations. Therefore, some individuals are still carrying on the genetic material on their genetic background.
Cluster analysis (UPGMA)
In the dendrogram, there are two main groups (Figure 4). All the populations except, population S clustered together in the first main group, while population S (I. glauca ssp. sivasica) clustered in the second main group. In the first main group, population AA (I. glauca ssp. galatica) separated clearly from rest of the populations in the first subgroup. In the second subgroup populations clustered into further subgroups. The populations AG1 (I. glauca ssp. glauca) and AG2 (I. glauca ssp. galatica), populations AB (I. glauca ssp. glauca) and ANP (Isatis glauca ssp. galatica), and population AI (I. glauca ssp. glauca) clustered together in the second subgroup. In third subgroup, population K (Isatis glauca ssp. galatica) and E (Isatis glauca ssp. galatica) clustered together.
Principal components analysis (PCA)
Total variance explained by principal component analysis (PCA) was performed by using data of sample size N , genetic indices ( P , A , and He ), climatic ( T , RA , and HU ), and geographical ( AL , LA , and LN ) as variables according to Pearson’s correlation (one-tailed) matrix with Eigen values, percentage of variance and cumulative percentage of variance
Cumulative variance (%)
Principal coordinates analysis (PCoA)
The three coordinates, which obtained according to the PCoA, explained 29.23% of total variation. The first axis (Eigen vector) displayed 11.96% of the variance, while the second axis (Eigen vector) and the third axis (Eigen vector) showed 9.41% and 7.85% of the variance respectively (data not shown). The codes of 67 accessions are plotted according to the first and the second axis that corresponded to different regions, from where nine I. glauca subspecies populations collected (Figure 3). The accessions from populations AA, E, K and S seperated clearly, the accessions from populations AB, AG1, AG2, AI and ANP were clustered in the same region.
Multiple regression analysis
Displaying the effects of eco-geographical factors on genetic indices by multiple regression analysis (Abbreviations: Dependent variable DV, independent variable IV, coefficient of multiple regression R 2 , proportion of polymorphic locus P , the mean number of allele A , the mean value of genetic diversity He , temperature T , rainfall RA , humidity HU , altitude AL , latitude LA and longitude LN )
T, RA, HU, AL, LA, and LN
T, RA, HU, AL, LA, and LN
T, RA, HU, AL, LA, and LN
The AFLP technique is a reliable method, which combines the reliability of RFLPs and the power of PCR in a single method (Krumm et al. 2008) to produce highly polymorphic markers, which are used to analyse genetic diversity in plants. Garcia et al. (2004) reported that AFLP seemed to be the most appropriate molecular essay for fingerprinting and analysing genetic relationships among tropical maize inbred lines with high accuracy. It generates fingerprints of DNA from any origin or complexity (Vos et al. 1995) and produces high number of polymorphic loci. By this way, it overcomes the loss of information because of its dominance (Gerber et al. 2000) was the main reason for giving preference to AFLP method. Taking into account, the results of this study, the AFLP molecular markers could be used effectively to distinguish I. glauca subspecies in agreement with Gilbert et al. (2002) and Spataro et al. (2007).
When we compared the results of this study having 793 polymorphic loci, and 98.5% polymorphism, using 8 AFLP primer combinations on 67 accessions, with previous studies (Gilbert et al. 2002;Spataro et al. 2007), it was observed that this study reported a greater polymorphism among nine Turkish Isatis glauca subspecies populations. The genetic data analysis provides important information regarding genetic structure of the populations. This methodology also helps in screening the populations for genetic diversity within and among populations. The populations E and K displayed the higher values of genetic diversity. Population S, being a remote population to the rest of the populations, showed the least genetic diversity. The geographic distance may prevent gene transfer via pollination or other types of transfers. In addition, ecogeographical conditions in Sivas, where the population S collected are harder compared to other locations, from which the other populations collected. In addition observation of high number of unique alleles in population S displayed that ecogeograhical conditions might have effecs on the adaptation of different genotypes and causing the genetic differentiation in the population S.
AFLP fragment analysis indicated that the primer combinations E39XM40, E36XM34 and E36XM33 amplified more present fragments compared to other primer combinations. However, amplification of fragments by primer combinations varied according to populations. In general the lowest amplified present fragments were observed in population AI that had the lowest polymorphic locus and also lower genetic diversity. According to STRUCTURE analysis results, all individuals, except one are hybrid plants in population AI. This might cause the decrease in amplified fragments. During the hybridisation process, the members of the population AI might have lost some fragments. The population AI most probably inhabited in the area in the recent past according to previous field observations (personel communication with Şinasi Yıldırımlı 2013). According to fragment analysis, the highest number of present fragments were observed in population AA from Ankara/Ayaş. STRUCTURE analysis results indicated that accessions formed a distinctive and stable population structure for population AA. Although, high number of fragments were amplified, low level of genetic diversity was observed. There might be low or no gene flow with other populations due to geographic distance or some other reasons. Therefore, observed homozygosity might be higher than the other populations analysed in this study. We also considered that anthropogenic stresses might have important role on the level of genetic diversity observed in population AA. There is a paper factory in the area and also the plants generally grow on the highway road sides. These factors might cause to reduce genetic diversity in the population. On the other hand amplification of higher number of present fragments might refer that accesions from the population AA that still contain genetic upload of the original population of ssp. galatica in the area.
In outcrossing populations, a higher genetic variation is observed within than among populations or subpopulations (Hamrick and Godt 1990). The finding of this study showed that the gene diversity within-populations (0.76) were much larger compared to the gene diversity (0.24) between-populations is in agreement with Hamrick and Godt (1990) and Spataro et al. (2007). Although to date there is no report of detailed research about the breeding system of I. glauca as in the case of I. tinctoria (Spataro et al. 2007), these results might indicate that I. glauca is an outcrossing species.
The presence and frequency of unique alleles reveal useful and important information about the differentiation in genetic structure of a population. The new alleles in a population exist because of mutations and if they have ability to adapt to their environment, they have a chance to be fitted in the population gene pool. In this study, the population S had a large number (12) of unique alleles, which had frequencies higher than 0.05. The population S is geographically distant from the rest of the populations analysed in this study. Therefore, existed unique alleles in populations will drive genetic differentiation between populations as it was observed between population S and the other populations in this study.
Unique alleles have potential as favourable genes for tolerance to severe conditions, especially at higher altitudes (Mondini et al. 2010). The number and frequency of unique alleles have important features, which may be used for improvement of cultivated forms. Isatis L. is economically important plant especially for natural dyestuff beside its medicinal uses. The unique alleles found in I. glauca ssp. populations as molecular markers might be an indication of desirable traits, which can be used in the future breeding programs of Isatis L. plant species.
In the Brassicaceae, hybridization, introgression and hybrid speciation are reported as significant evolutionary forces (Marhold and Lihová 2006). Interspecific gene flow and hybridization promote evolution and species diversity of some genera, e.g. hybrids in Rorippa, as reported by Bleeker and Hurka (2001); Bleeker (2003); Schranz et al. (2005); C. x insueta Urbanska and C. schulzii, (Urbanska et al. 1997) (cited in Marhold & Lihova, 2006) and causes genetic variation (Marhold and Lihová 2006). In breeding programs, landraces or wild relatives have desirable traits such as resistance to cold, drought etc., have been used for improvement of cultivated plants (Du et al. 2009). By this way, transfer of favourable genes/gene complexes from wild allies to cultivated plant gene pools could be possible. However, in most species, incompatibility barriers between wild forms and cultivated forms usually resulted with observation of low fertility in F1 generations that constraint the possible transfer of desirable traits (Inomata, 1993;Rieseberg et al. 1995;Shivanna, 1996;Choudhary and Joshi 2001: cited in Du et al. 2009). Therefore, intertribal somatic hybrids between Brassica napus and I. indigotica (Du et al. 2009), between Brassica rapa and Raphanus sativus with dye and medicinal plant I. indigotica (Tu et al. 2008), and between Brassica rapa and I. indigotica (Tu et al. 2008) assessed to overcome genetic barriers by previous researchers. If intertribal hybridization is possible under control of breeders, the possibility to see natural hybrids among Isatis L. species or subspecies in the nature should be the expected case.
Isatis L. species from the Brassicaceae, displays morphological polymorphism and these morphological differences are often masked, even in fruits, which display the most valuable diagnostic features (Davis 1965;Hedge 1968;Jafri 1973: cited in Moazzeni et al. 2007). These variations indicate that hybridization is playing a significant role in the evolution of the genus Isatis L. (Moazzeni et al. 2007). The outcrossing mating system, associated with the perennial habit and vegetative reproduction is a significant factor for hybridization, constitution, and emplacement of the polyploids (Ančev 2006). Consequently, the great morphological (Görgülü et al. 2013) and genetic variation observed in subspecies of I. glauca in this study might be related to hybridization process. This was confirmed with the STRUCTURE analysis results, which showed that in all populations hybrid individuals were observed. Particularly, hybridisation was observed extensively in populations AG1, AG2, AI, and ANP.
According to UPGMA, PCoA and STRUCTURE analysis results, the population S was clustered as a distant population to the rest of the populations. Also, the genetic distances between population S and rest of the populations were quite high (Data not shown). This might show that formation of I. glauca ssp. sivasica is genetically differentiated obviously more than the rest of the subspecies populations analysed in this study. If the unique AFLP fragments detected in only one subspecies, were extracted, cloned, and sequenced to prepare specific primers, which might be used for simple diagnostics PCR assay of large-scale samples to identify species/subspecies or landraces (Gilbert et al. 2002).
According to the results of this study and previous studies (Yıldırımlı 1988;Görgülü et al. 2013), we suggested that Ankara/Ayaş (population AA) was the germplasm centre of I. glauca ssp. galatica. Some genotypes from Ankara/Ayaş (pop AA) migrated through Ankara/Polatlı (population ANP) and Eskişehir (population E) (Figure 2). On the other hand, some genotypes from Ankara/Ayaş (pop AA) migrated through Ankara/Gölbaşı1 (AG1), Ankara/Gölbaşı2 (AG2) and Ankara/Incek (AI) and Konya (population K). We also considered that Ankara/Beytepe was the germplasm centre of I. glauca ssp. glauca (Yıldırımlı 1988). The genotypes migrated from population AB through the area, where the populations AG1, AG2, AI, and ANP were collected. By this way ssp. galatica and ssp. glauca populations are overlaped in that area causing to a hybrid zone formation for I. glauca subspecies.
The populations from Eskişehir (E) and Konya (K) have distinctive population structures now and they can be recognised as the varieties of I. glauca ssp. galatica. The gene flow rates between the population ANP and the populations AG1, AG2, and AI seemed to be considerably high. Therefore, in populations AI and ANP all individuals except, one in pop AI, were hybrids.
The mutations and recombinations generates variation, which underpin genetic diversity in a population. However, selection, genetic drift and gene flow may play an important role in the genetic diversity of particularly in small size populations. The selection might be natural or artificial as it was observed in cultivated crop plant species (Suneson 1960;Frankel 1977;Nevo et al. 1984;Brown 1988;Hamrick et al. 1992: cited in Rao and Hodgkin 2002). Despite the mutations and recombinations raise the genetic diversity as evolutionary frorces in a population, the amount of molecular variation observed in this study can not be attributed to only these forces. PCA and multiple regression analysis represented the effects of environmental components. According to PCA, the environmental factors accept LA and AL, mainly contributed to the second and third components. The sum of those components is 48.55%. In addition, multiple regression analysis displayed that when all environmental factors combined they had great effect on the genetic data (P, A and He). These results displayed that natural selection might play important role in genetic diversity of I. glauca ssp. populations.
During the field studies, it was noticed that population sizes of the I. glauca subspecies were quite small (data not shown). Plants usually grow on the highway road sides, which negatively effect the population size because, the construction of new highways or extending road widths, remove some plant genotypes from those places or they have to move inner sides or different niches (personal communications with Şinasi Yıldırımlı 2013). Anthropogenic stressess may result in genotypes, which have desirable traits such as drought tolerance, climatic changes, etc. to be disappeared and may cause to the genetic drift or bottleneck effect in the germplasms of I. glauca subspecies populations.
Isatis L. was economically an important plant during the Roman times in both Europe and Asia (Guarino et al. 2000). Recently, an increased interest into natural dye products in textile industry raised attention to Isatis L. as an economically important plant once again. The leaves of Isatis subspecies synthesise indoxyl-forming substances, which are indican (Schunk 1855) and isatan B Beijerinck (1900), when they are exposed to the air, reflect the blue compound, indigo (Epstein et al. 1967;Gilbert et al. 2002), which is used in dying. In ancient times I. tinctoria L. (woad) was used for large scale indigo production in Europe. However, according to some recent phytochemical studies (Gilbert et al. 2002;Kızıl 2006;Akar 2006) I. glauca can also be used for indigo production. Although it was not used for large scale production, recent studies indicated that it had great potential for the production of indigo. I. glauca ssp. iconia, I. glauca ssp. galatica and I. glauca ssp. sivasica are endemic plant species of Turkey. I. glauca ssp. glauc a is native to Lebanon, Syria, Iran, and Transcaucasia (Tübives 2013;Yıldırımlı1988). When breeding programs for I. glauca are planned in future, the populations, which have high genetic diversity has more potential for breeding programs. Therefore, the genotypes, from those populations might produce high quality and amount of indigo, and have resistance to environmental stresses factors, such as fungi, bacteria, climatic, and drought, etc. should be selected for cultivation, and the promotion of large scale indigo production.
Evaluating germplasm of genetic resources is an important issue for effective conservation of plant genetic resources. Loveless and Hamrick (1984) reported that the genetic variation in plant populations is structured in space and time. What the extent of genetic diversity and its distribution in a species, it is shaped in which way are the requirements prior to determine what to conserve, and where and how to conserve it (Rao and Hodgkin 2002). Most of the molecular markers are used to determine genetic diversity and construction of genetic distances and physical map. Correlation between expression of a useful trait and a linked molecular marker could be used to construct a genetic linkage map by placing many monogenic and polygenic traits within specific regions of the plant genome (Mondini et al. 2010). Breeders may plan appropriate breeding programs for the marker assisted selection of those quality genes and introgression of these genes to develop standard varieties, which can then be used for large scale production (Gilbert et al. 2002).
Compared to traditional taxonomy, which is based on morphological characters, molecular tools are used to explain taxonomy, brings in new insights into the phylogeny and taxonomy of many plant groups (Rao and Hodgkin 2002). This is the first study, in which molecular techniques were used to determine the genetic diversity and genetic differentiation among subspecies populations of I. glauca from Turkey.
The results of this study showed that AFLP molecular markers could be used effectively to distinguish I. glauca subspecies.
According to molecular data, the UPGMA, PCoA and STRUCTURE analysis, results showed that the accessions from the population S was clustered as a remote population to the rest of the populations. Populations AA, AB, E, K and S had distinctive population structures.
It is suggested that the population AA is the origin of subspecies I. glauca ssp. galatica germplasm center, while the population AB was the origin of subspecies I. glauca ssp. glauca. germplasm center.
The populations from Eskişehir (E) and Konya (K) were recognised as the varieties of I. glauca ssp. galatica.
Ankara province might be the area, where species Isatis glauca Aucher ex Boiss. originated.
The genetic information obtained in the present study will assist to acquire more information about the population genetic structure, the basis for speciation or subspecies formation in Isatis glauca species and its taxonomy. Consequently, the subspecies and their varieties will be allocated taxonomically in appropriate way.
EG is doing her PH.D at Hacettepe University in Ankara, Turkey.
ÖÖ is an assistant professor at Hitit University, Faculty of Art and Science, Department of Biology, Çorum, Turkey.
ŞY is a professor at Hacettepe University, Faculty of Science, and Department of Biology in Ankara, Turkey.
This is a part of Masters Thesis of Elcin Görgülü and supported by a grant, which was provided by the Scientific Research Projects Department (BAP) of Hitit University with the project number FEF03.11.001. The authors are also grateful to Prof. Dr. Hakan Özkan for facilitating AFLP analyses, in his lab at the Department of Field Crops, Faculty of Agriculture, Cukurova University, Adana, Turkey. We would like to thank to assistant professor Muhammet Şakiroğlu at Kafkas University, Kars, in Turkey for his contributions about the evaluating the STRUCTURE analysis results.
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