Research & Reviews: Research Journal of Biology
MenuISSN: 2322-0066
ISSN: 2322-0066
Department of Biology, Faculty of Arts and Science, Erzincan University, Erzincan, Turkey
Received date: 09/10/2015 Accepted date: 29/01/2016 Published date: 08/02/2016
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Uechtritzia armena Freyn (Asteraceae) which is an endemic species for Turkey grows in the provinces of Gumushane, Erzurum and Artvin. In this study, its distribution, ecological features and threats are discussed. Its local future is treated. The distribution of the species is related to P. sylvestris var. hamata. It grows in the northern aspect in P. sylvestris var. hamata forest. The results of the soil analysis showed that the soil type of the species is loamy with clay. The pH of the soil varies between 6-7.52. The percentage of organic matter in the soil is between 2.9 to 4.24. In addition, genetic diversity among populations was determined by RAPD. 16 primer generated a total of 127 bands, with a mean of 7.94 bands per primer. RAPD analyses showed various band sizes, which ranged from 250 to 3000 bp. Mean polymorphic locus ratios were determined as 92.13% considering four populations. The percentage of polymorphic bands for this species was 96.21%. The Nei’s gene diversity (H) ranged from 0.166 to 0.183, Shannon’s Information Index (I) differed from 0.258 to 0.299, while Nei’s gene diversity (H) varied from 0.166 to 0.183. Genetic distances between populations ranged from 0.981 to 0.201. Cluster analysis showed correlation between genetic and geographic distance.
Ecological properties, Endemic plant, Population genetics, RAPD, Uechtritzia armena
Uechtritzia Freyn (Asteraceae) is represented by three species in the world: U. armena Freyn, U. kokonica (Rgl. and Schmalh.) Pobed, U. lacei (Watt) C.Jeffrey. U. kokonica is located in Central Asia and Afghanistan [1] while U. lacei is observed in N.W India and S. Jammu and Kashmir [2]. Uechtritzia is allied to the genus Gerbera L. which is grows in S. Africa. It appears to differ from Gerbera principally by its paleaceus receptacle [3].
Turkey has a very rich flora with about 11.000 taxa. About 3.700 of 11.000 taxa are endemic for Turkey [4]. There are many reasons why Turkey is so rich with flora. The soil types, variability in topography climatic conditions, geological diversity and geological history of the country and its location between the two continents can be can be considered as the main reasons of this plant diversity in Turkey [5]. A large number of endemic species has limited distribution like U. armena. It was first collected on Mount Spikor (Gümüshane-recorded as Erzincan in Turkish Flora) in 1892 by Sintenis. It was known from type specimen and evaluated as Endangered (EN) based on IUCN criteria [6]. This species were recorded from provinces of Erzurum, Artvin and Van for the past 15 years [7-9].
The species with narrow distribution like U. armena is more sensitive to extinction due to low genetic variation. Before planning conservation activities on such species, critical information related to distribution, biological relationships, threats, reproductive mechanisms, ecological properties, genetic diversity and habitat characteristics is required [10]. Although genus Uechtritzia was taxonomically revised [11], no information on above mentioned conservation planning has been detected.
Molecular markers are widely used to characterize genetic structures of plant populations. These contain polymerase chain reaction (PCR) based markers like RAPD, ISSR, SSR, AFLP. RAPD and ISSR analyses have been used to describe population structures and genetic polymorphism especially in rare and endangered species such as. Caldesia grandis [12], Buxus sinica [13], Magnolia officinalis [14]. The aim of the present study is to determine the level of genetic diversity and genetic variation and differentiation within and among populations based on RAPD markers and to collect ecological data, type of reproduction and habitat characteristics. The results will show the degree of threat of U. armena and help to develop effective conservation strategies for this endangered species.
Macro-Morphological Data: 15 plant samples were randomly collected from each population. Then, the samples were prepared as herbarium materials by using standard herbarium techniques. The fruit samples were also collected from each population. Skap and capitula length, and size of leaves were measured in centimeter (cm). In order to monitor the adaptation to external side of their natural zone, the living material was planted in the pot.
Soil analyses: The soil analyses were conducted in the Soil Laboratory of Erzincan Horticultural Research Institute. The saturation % and constitution, salt %, pH, lime %, organic matter %, phosphorus (P), and potassium (K) kg/ha in the soil samples were determined according to the methods described by Tüzüner [15] (total salt quantity), Hindistan and Inceoglu [16] (determination of soil reaction (pH)), Çaglar [17] (lime (CaCO3) determination), Ülgen and Atesalp [18] (phosphorus (P2O5) determination), Doll and Lucas [19] (potassium (K2O) determination), Ülgen and Atesalp [18] ( determination of organic matter), and Tuzuner [15] (classification of the soils).
Plant Materials and DNA extraction: The plant samples were collected from distribution areas in Gumushane (Sipikor: symbolized as "S" in table and map), Artvin (Mutlugun: symbolized as "M", and Demirkent: as "M") and Erzurum (Ormanagzi: symbolized as "O"). Leaf samples of 15 randomly selected individuals per population were collected. Each leaves were stored in zip-lock plastic bags with silica gel. The leaf tissue was then stored at ambient temperature until DNA extraction. Total DNA was extracted from 100 mg leaf tissue using the Qiagen DNA extraction Kit (Qiagen, Hilden, Germany) according to manufacturer’s instructions. The quantity of DNA was determined at 1% agarose gels and concentration was determined by UV spectrometer.
RAPD analysis: First, thirty-five randomly obtained RAPD primers were tested in DNA bulks. Sixteen primers were proved to be clear and reproducible. PCR amplification reactions were carried out in thirty μl final volume of reaction mixture containing 10x Buffer 3.0 μl, dNTPs (10 mM) 1.2 μl, magnesium chloride (25 mM) 1.2 μl, primer (5 μM) 2.0 μl, Taq polymerase (5 units) 0.4 μl, water 19.2 μl sample DNA 3.0 μl (100 ng/ μl). The thermal cycler (Eppendorf Company) was programmed to 2 min at 95°C; 2 cycles of 30 sec at 95°C, 1 minute at 37°C, 2 minutes at 72°C; 2 cycles of 30 sec at 95°C, 1 minute at 35°C, 2 minutes at 72°C; 41 cycles of 30 sec at 94°C, 1 minute at 35°C, 2 minutes at 72°C; followed by a final 5 minute extension at 72°C then brought down to 4°C .
Electrophoresis: The PCR products (27 μl) were mixed with 6x gel loading buffer (3 μl) and loaded onto an agarose (1.5% w/v) gel electrophoresis in 0.5XTBE (Tris-Borate- EDTA) buffer at 70 V for 150 min. The gel was stained in ethidium bromide solution (2 μl Etbr/100ml 1xTBE buffer) for 40 min and visualized under UV in Bio Doc Image Analysis System with Uvisoft analysis package (Cambridge, UK).
Data analysis: All clearly detectable RAPD product bands were scored as either present (1) or absent (0), and a matrix of RAPDs data were assembled. Only reproducible and well-defined bands were scored. The matrix was then used for the following analyses: the percentage of polymorphic band (PPB), observed number of alleles (na), effective number of alleles (ne), Shannon’s information index (I) [20] and Nei’s gene diversity (H) [21]. These measures were obtained at both species level and population level using the software package POPGENE [22]. To examine the genetic relationship among populations, a dendrogram was also constructed based on Ne’'s genetic distance (D) using an unweiged paired group method of cluster analysis employing arithmetic averages (UPGMA) of NTSYS-pc version 2.02c [23].
Uechtritzia armena Freyn: Perennial. Rhizome brown, covered with brown scaly leaves. Scape 1, 40-72 cm long, whitetomentose, pubescent near capitulum. All leaves basal, 2-7; lamina, 7-18 x 6-14 cm, green and subglabrouse above, densely white-tomentose beneath, entire, acute to obtuse at apex, cordate at base; Petiole 6-20 cm long, weakly winged, floccose white tomentose. Capitula 1, 2.5-3 (to 4 cm when dried) cm broad; phyllaries oblong-lanceolate, acuminate at apex, purpish, whitetomentose. Flowers carmine. Marginals female, bilabiate; lower lobes with 3 apical teeth; upper lobes bifid, clavate; staminal tube short, 1-1,4 mm; style clearly exserted, bifid, papillate. Inner flowers hermaphrodite, lips ± in size; staminal tube clearly exserted; filaments attached in middle of tube, longer than anthers; style bifid, ± exserted. Achens 5-7 mm long, villose, immature; pappus, 11-15 mm long (Figures 1 and 2).
Figure 1: Uechtriztia armena in nature.
Figure 2: Rhizomes of Uechtriztia armena.
Ecological Properties: U. armena grows on top boundary of the Pinus sylvestris L. var. hamata forest on Mount Sipikor (Gümüshane). The other populations are found at the aperture of P. sylvestris L. var. hamata forest in Artvin and Erzurum. The number of individuals in each populations except those on Sipikor are over 2000. It is approximately 200 on Sipikor. Leaf, skap and leaf size are the least among Sipikor (S) population. Sipikor population is also found at the highest altitude (Table 1).
Table 1: The findings of some properties of the populations.
Considering the results of soil analysis, saturation value, electrical conductivity (Ec), organic matter (%), lime (CaCO3) (%), salt concentration (%) phosphorus (kg/ha), potassium concentration (kg/ha) and texture are indicated in (Table 2).
Table 2: Soil analysis for each population.
Genetic diversity and differentiation: In this study, 16 RAPD primers were selected and used to determine genetic diversity and population structure between and among four populations of U.armena. RAPD primer combinations produced 127 visible bands out of 250 to 3000 bp across 60 individuals (Table 3). The highest number of 12 bands was produced by OPW 6 and the least of 4 marker levels was produced by OPY 19. Banding patterns of D population genotypes using the primer OPA-01 are illustrated in (Figure 3).
Table 3: List of the selected primers and the degree of polymorphism obtained among the four populations.
Figure 3: Ampliication products generated from 15 individuals of D populations of Uechtritzia armena using primer OPA-01. M = molecular marker.
The average numbers of bands and polymorphic bands per primer were 7.93 and 7.31 respectively. The percentage of polymorphic bands (PPB) per population varied from 53.85% to 69.23% with an average of 63.74%. The percentage of polymorphic bands for this species was 96.21%. The percentage of polymorphic loci, the average genetic diversity within populations of the four U. armena populations showed the following order S, O, M, D.
The Nei’s gene diversity (H) ranged from 0.166 to 0.183, with an average of 0.171 and 0.192 at the population and species level respectively. Shannon’s index (I) varied from 0.258 to 0.299 with an average of 0.275 and 0.333 at the population and species level respectively. U. armena, the highest and lowest levels of diversity occurred in populations D (PPB: 69.23%; H: 0.183; I 0.299) and S (PPB: 53.85%; H 0.166; I 0.258), respectively as shown in (Table 4). The coefficient of genetic differentiation among populations (Gst) was 0.321 with an observed effective gene flow between populations of (Nm) was 0.72. The overall genetic diversity of U. armena, based on RAPD analysis, is relatively high (PPB: 93.21%; I: 0.345; He: 0.265) at the species level, while it is relatively low (PPB: 63.74%; I: 0.275; He: 0.171) at the population level.
Table 4: Genetic variability within Uechtriztia armena populations detected by RAPD markers.
Cluster analysis: In order to represent the relationship among populations, cluster analysis (UPGMA) was used to generate a dendrogram based on Nei’s genetic distance among the four populations studied. The dendrogram realized from the RAPD markers grouped four populations into two major clusters. Cluster 1 formed S population. Cluster 2 was divided into 2 subclusters: D and M populations formed sub-clusters. O populations formed other sub-clusters. The distance matrix showed that the highest genetic distance (0.981) was between S and O populations and D and M populations were found to be the most distinct with the lowest genetic distance (0.201) (Figure 4).
Figure 4: UPGMA clustering for 4 U. armena populations based on RAPD markers.
The species was first collected on Mount Sipikor in 1892 by Sintenis. It was indicated that the achens were immature in Sipikor population [3]. In this study, the same condition was detected for all populations. The individuals in the each population are dispersed in groups. Considering the distribution of populations in Turkey (Figure 5), the critical question is if the species reproduces as vegetative and how its distribution can best be explained. Except the population in Van, the distribution of the species is related to P. sylvestris var. hamata. Distribution of P. sylvestris was limited in the lastglacial period [24,25]. Anatolia was a refuge for P. sylvestris and some conifers during the last glacial maximum (LMG) (Figure 6). After the last glacial period, the distribution of P. sylvestris has been changed. It moved back to north and higher altitude following colder climate [26]. During this movement, Pinus forests were fragmented. This fragmentation was accelerated by human destruction. According to Atalay [27], the most important factors of Pinus forests destruction in Anatolia are related to human-beings. It is estimated that U. armena was distributed in wider areas and its distribution was limited with habitat fragmentation after the last glacial period and during civilization in Anatolia.
Figure 5: Distribution of Pinus sylvestris and Uechtritzia armena in Turkey.
Figure 6: Distribution of Boreal forests including Pinus sylvestris during the Last Glacial Maximum in Anatolia and its surroundings.
The genus Uechtritzia is allied to the S. African Gerbera [3]. In addition, the species of the Uechtritzia extends up toKashmir (U. kokonica grows in Central Asia and Afghanistan; U. lacei is in N.W India and S. Jammu and Kashmir). The species of the genus are represented by isolated populations like U. armena. Probably, they were growing in larger geographical range in the past. The distribution scenario from past to present related to U. armena tells that the species is a paleoendemic.
Effective population size should consist of at least 4000-5000 members for sufficient genetic diversity in small populations. Loss of genetic variability and related problems of inbreeding and genetic drift are common in small populations [10]. Around 200 individuals were counted in Sipikor population. Moreover, the population is found on roadsides. It is estimated that the species may become locally extinct in the near future. The number of the species is quite high among Artvin and Erzurum populations. The members are very common in all of the gaps among the P. sylvestris in forests in Artvin and Erzurum. The total number cannot be determined due to a high number of individuals. The populations in Erzurum and Artvin are not under any threat yet. In other words, the future of the species is evaluated as good at the global level but U. armena may loss its natural habitats because of unexpected forestry activities in the future.
The results of the soil analysis showed that the soil type of the species is loamy with clay. It is slightly alkaline in Demirkent population while slightly asidic among Ormanagzi and Mutlugün populations. It is neutral in Sipikor population. While organic matter is in medium amount in Mutlugün population, it is higher in the rest of the populations. It is saltless for all populations. Whilst phosphorous is low in Sipikor population, it is medium in the others. Finally, potassium content is medium in Ormanagzi population butit is low in the others.
In terms of morphological characters, scap and petiole in Sipikor population are in average shorter than the others (Table 1). Two factors may be effective in this regard. First the soil is neutral and phosphorous content is low in Sipikor population. Second the population is distributed in more open areas and the light is sufficient in Sipikor population. The rest of the populations are surrounded by P. sylvestris which partially blocks sunlight.
Without any research of genetic variation in other Uechtritzia species, in comparison with other Asteraceae species, such as Saussurea chabyoungsanica (P: 90.5%; H: 0.352; I: 0.445 at the species level), (P: 45.6%; H: 0.173; I: 0.207) at the population level [28] and O. longilobus (PPB: 95.16%, H: 0.349, I: 0.517) at the species level, (P: 68.55%; H :0.271; I: 0.395) at the population level, O. taihangensis (PPB: 94.58%; H: 0.332; I: 0.504) at the species level, (P:71.50%; H: 0.208; I: 0.310) at the population level [29], U. armena was found to process high genetic diversity at the species level but lower genetic diversity at the population level.
Many studies demonstrate that endemic and endangered species tend to have a low level of genetic diversity [30]. The population and species average genetic diversity obtained in the present study was similar to that referred to other endangered and endemic species as Sinojackia dolichocarpa (PPB: 72.99%; H: 0.225; I: 0.3453), (PPB:36.32%; H:0.127; I; 0.189) [31], Taihangia rupestris (PPB: 80.43%; H: 0.248; I: 0.378), (PPB: 47.01%; H: 0.186; I: 0.272) [32], L. Sinense [33] at the population level and species level, respectively. Saruma henryi Oliv is an endangered perennial herb endemic to middle China, and the genetic diversity is quite low at the population level (in average, PPB = 22.8%, H= 0.083, I= 0.123) [34].
The level of genetic diversity, considering all U. armena populations, was similar to that obtained in studies conducted with the same molecular markers on L.sinense (PPB= 43.86, H= 0.169, I= 0.249) [33], C. amonea (PPB= 37.2, H= 0.120) [35].
In rare plants, demographic history, breeding system, geographic distribution range, somatic mutations, habitat fragmentation can significantly affect genetic diversity and it’s partitioning within and among populations. Selfing species tend to have lower genetic diversity and heterozygosis within populations, as well as higher genetic differentiation among populations than mixed or outcrossing ones [36-38]. The loss in genetic diversity that is, extinction risk is resulted from reduction in population size of a species [39].
In conclusion, the present study showed that a great genetic diversity occurred among the U. armena populations due to their geographic and morphological differentiation. Morphology and RAPD markers are powerful tools for evaluating the genetic diversity and relationships in different U. armena populations.
This study was supported by Erzincan University Scientific Research Coordination Units (Project number: BAP 120105).