Genetic diversity and population structure analysis of the endangered endemic and economically important plant, Red Sanders, distributed in the Eastern Ghats. 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India Mohana Kumara P, Prabuddha H R, Divakara B N, M V Sneha, A H Madhushree, and 2 more This is a preprint; it has not been peer reviewed by a journal. https://doi.org/ 10.21203/rs.3.rs-7357158/v1 This work is licensed under a CC BY 4.0 License Status: Under Review Version 1 posted 14 You are reading this latest preprint version Abstract Pterocarpus santalinus , or Red Sanders, is an Indian native tree species that is under threat of decline in natural populations due to illicit felling in Eastern Ghats. In the present study, we assessed the genetic variation and population structure across 22 natural populations 16 highly polymorphic SSR markers in 361 individuals. The average number of alleles (Na) was 7.79, with an expected heterozygosity (He) of 0.65, which is lower than that of other woody plants. Interestingly, the Tirupati base-Sadashiva Kona population presented the greatest genetic diversity (He = 0.87), whereas the Chitaleti Pati base Camp population presented the least genetic diversity (He = 0.44). The analysis revealed that extensive genetic variation among populations (72%) contrasted with that within populations (28%). The Tirupati circle (He = 0.93) and Chittor divisions (He = 0.91) presented high genetic diversity. The FST values revealed considerable genetic differentiation among the populations, with a value of 0.31 and poor gene flow (Nm = 0.82). Cluster analysis of 361 samples from 22 populations revealed three main genetic groups. Populations located at lower latitudes presented greater genetic diversity than those located at higher latitudes did, and geographical and genetic distances were positively correlated. The population as a whole presented moderate level of genetic diversity, with clear variation between the populations at lower and higher latitudes and positive geographical and genetic correlations. These results indicate the importance of conserving P. santalinus . Pterocarpus santalinus Red Sader Eastern Ghats Genetic diversity Microsatellite Population structure Figures Figure 1 Figure 2 Figure 3 Figure 4 Figure 5 Figure 6 Figure 7 1. Introduction Pterocarpus santalinus , commonly known as Red Sanders, is a forest tree species that is found exclusively in the Eastern Ghats of Andhra Pradesh, India. It is an endangered species with a naturally limited distribution range. P. santalinus , a member of the Fabaceae family, is a slow-growing tree species that relies on cross-pollination and insects for reproduction [ 54 ]. In natural forests, it typically takes between 50 and 60 years for a pole-sized tree (measuring 30 cm girth at breast height or 173 cm from the ground) to achieve a harvestable girth of 70 cm. This species has been prized for centuries for its dyeing properties, traditional medicinal uses, and use as a source of timber. The heartwood of the tree boasts a reddish-brown hue, a distinctive wavy grain, and exceptional durability. Presently, P. santalinus heart wood is highly valued on the global market [ 2 , 53 , 67 ]. The legal trade of seized wood is currently limited to occasional sales through the Forest Departments of Andhra Pradesh (APFD), Tamil Nadu, and Karnataka (NDF, 2019). This includes a range of products, such as wood chips, extracts, timber, and wood carvings. According to a report by the APFD, the auction of 8179.85 MT of seized wood from 2005–2018-19 generated revenue of Rs.1688.24 crores. However, there is still a balance of 6285.909 MT of wood waiting for auctions in the APFD alone [ 26 ]. This species is highly vulnerable because of the overharvesting of mature trees from the wild due to the continued high demand for timber [ 2 ]. In 1988, the species was listed as endangered and categorized under the A2cd criterion [ 28 , 3 ], which explains habitat loss and population size reduction in the natural distributions of Eastern Ghats, India. The species is listed in Appendix II of the Convention for International Trade in Endangered Species of Wild Fauna and Flora (CITES) in 1995 because of its declining population and restricted distribution. Recently, a drastic decline (7.8–3.9%) in the number of harvestable trees (GBH > 70 cm) has been observed within the last six years [ 3 , 25 ]. One reason for the decline of this species is the hot and dry conditions of its natural habitat, which put its pollination ecology at risk. The tree blooms during the dry season. Its yellow flowers attract honey bees, especially Apis dorsata , which are the primary pollinators. The other two species, A. indica and A. florea , visit only in the early morning. This tree mainly prevents the growth of fruits from self-pollinated flowers, and only 6% of flowers grow into fruits due to various factors [ 55 ]. Genetic diversity plays a crucial role in biodiversity, influencing how well a species can adapt to environmental challenges and changes [ 22 , 40 ]. By measuring the genetic diversity within a species, we gain valuable insights into its evolution and the variations in its genetic makeup [ 4 , 44 ]. Genetic variation among and within populations of various plant species has been studied extensively molecular markers over the last three decades. In recent years, advanced molecular tools and next-generation sequencing (NGS) technologies have helped us discover robust molecular markers and use these markers to elucidate genetic variation in tree species [ 15 ]. Among the molecular markers available, microsatellites or simple sequence repeats (SSRs) are often preferred because they are highly mutated, generate multiple allelic forms and mutations per locus per generation, and are codominant [ 18 , 69 ]. The combination of both characteristics allows them to be used as a sensitive tool for assessing genetic diversity among species, determining population structure, reconstructing phylogenetics, genetic mapping, evolutionary analyses, and molecular breeding [ 59 ]. In practice, SSRs are popular, simple to implement, and reproducible in most research environments because they require minimal resources (i.e., technical skills, laboratory equipment, and consumables) [ 46 ]. Despite being a highly economically valuable tree species, very few studies have been reported on P. santalinus via the use of DNA molecular markers. However, recent advancements in next-generation sequencing (NGS) have made it possible to sequence transcriptomes and whole genomes de novo [ 1 , 63 ]. Previous genetic diversity studies have used molecular markers such as RAPD and ISSRs, which are dominant, nonlocus-specific, and have poor reproducibility. Moreover, past studies have used small sample sizes that do not represent the entire range of species distributions. However, this study emphasized covering the entire species distribution range of red sanders in close association with field officers of the Andhra Pradesh Forest Department. This study analyzed the genetic variation and population structure of P. santalinus across 22 populations using 16 SSR markers and identified genetic diversity hotspots of high conservation importance. 2. Materials and Methodology 2.1 Study area: We conducted a literature survey and consulted with the forest department officials of Andhra Pradesh to sample pristine forest tracts in each forest range within the natural habitat of P. santalinus . The state of Andhra Pradesh has been divided into 5 territorial circles, one wildlife circle, and one project tiger circle for administration and forest management. At the divisional level, there are 32 territorial divisions, two wildlife divisions, and 13 social forestry divisions. There are also 10 social forestry divisions. The Andhra Pradesh Forest Department (APFD) has a total of 2,312 beats, 996 sections, and 295 ranges according to the available data [26]. The study was conducted in the Middle to Southern Eastern Ghats and covered five districts of Andhra Pradesh, located between latitude 13°32'14.1''N and longitude 79°36'04.1''E to 15°29'77.4''N and 79°12'81.7''E. We selected 22 forest ranges/populations under the Kurnool, Tirupati, and Guntur Circles in Andhra Pradesh, India, for sample collection (Table 1, Fig. 1). These circles include the endemic region of P. santalinus , which is categorized under dry deciduous forests [13]. The forests in these regions have both pure stands of P. santalinus and mixed associations, and we considered the distinctness of the forest patch in terms of altitude and the edaphic nature of the locality when sampling the closely located forest tracts. To facilitate efficient study management and organizational ease, we established each range (Table 1 and Fig. 1) as a distinct population unit. Leaf samples of Pterocarpus santalinus were collected from the Eastern Ghats of Andhra Pradesh, India. The plant material was identified by Divakara, BN, a scientist at IWST in Bengaluru, and a voucher specimen has been deposited at TDU/IWST, Bengaluru (IWST-NBA-01 to 400). Only leaf samples were collected without harming the tree, and their reproducibility. Collected samples were stored in deep freezers at IWST, Bengaluru. 2.2. Study material: From each forest range, an undisturbed natural forest area was selected for sampling. Fresh leaf samples were collected from four different girth classes. Seedlings and saplings with girth at breast height (GBH 1.37 m from the ground) up to 10 cm; young trees with a GBH of 10 to 20 cm; trees with a GBH of 20 to 30 cm; and mature trees with a GBH greater than 30 cm. A total of 4 to 5 plants were randomly selected for leaf sampling from each girth class. Eight to ten young leaves were selected per sample from each selected tree, and stored in a zip-lock cover containing silica gel. We collected ~16 to 20 individuals per population. A total of 361 individual leaf samples were collected from 22 populations. After the surface moisture in the silica gel was removed, the samples were transferred to -800°C for further storage and use. Geo-coordinates and altitudes were recorded using hand-held GPS instruments. The presence of the species at different altitudes and soil types was taken into account whenever the sampled forest patches of two different ranges were situated in proximity. Each sampled population was designated with acronyms formed with the first letter from the respective names of Forest Division, Forest Range, and Forest Beat (Table 1). 2.3. DNA isolation, PCR, and genotyping of SSR markers: We used the CTAB protocol described by Doyle and Doyle [16] to isolate DNA. For DNA amplification, we used 50–100 ng of genomic DNA and 5 picomoles of M13-tailed markers in a 20 µl reaction mixture. The amplified samples were subsequently subjected to fragment analysis. Our previous publication [63] described in detail the protocols for DNA isolation, PCR conditions, and fragment analysis. In the present study, 16 highly polymorphic SSR loci (Table S1) were used to analyze the 361 samples from 22 different populations of P. santalinus . These loci had a polymorphism information content (PIC) greater than 0.9 [63]. 2.4. Genetic diversity and population structure analysis: The raw genotyping data were analyzed via Peak Scanner software (Applied Biosystems, California, USA) [61]. The samples were categorized into different groups on the basis of their forest circle, division, population, girth class, and geographic distance (determined by their latitude and longitude). The allelic data for each group were then analyzed statistically. GenAlEx v.6.5. [49] was used to calculate various parameters, such as the number of alleles (Na), the number of effective alleles (Ne), the polymorphism information content (PIC), the observed heterozygosity (Ho), the expected heterozygosity (He), Shannon’s information index (I), the coefficient of genetic differentiation (F ST ), the gene flow (Nm) and analysis of molecular variance (AMOVA), to analyze genetic variation among the populations. Within populations, principal coordinate analysis (PCoA) based on the genetic distance matrix and the Mantel test were used to determine the correlation between geographic and genetic distances [49]. We applied Bayesian model-based cluster analysis via STRUCTURE 2.3.4 software [51] to determine population structure. The number of subgroups (K) was estimated to be 2 to 10 runs. Ten runs were performed on each K value, with a 10,000 iteration burn-in period followed by 10,000 Monte Carlo Markov chain (MCMC) replicates. The best K value was selected by Structure Harvester [17] based on the maximum ∆K [20] value. Cluster analysis was carried out by DARwin 6 software to construct a dendrogram via the unweighted neighbor-joining (UNJ) method with 10,000 bootstraps [50]. AMOVA was used to analyze the genetic variation among and within populations for all grouped data. Principal coordinate analysis (PCoA) was performed on the basis of the genetic distance matrix across 22 populations. A Mantel test was conducted using GenAlEx v.6.5 to determine the correlation between geographic and genetic distances [49]. 2.5. Genetic diversity combined with ecological factors: To comprehensively understand the ecological factors influencing genetic diversity and population clusters, we carefully examined several key factors. This involved considering factors such as elevation, soil type, annual precipitation, and temperature during the sampling process. We recorded GPS location and elevation data for each sample and determined the soil type through ground truth observations and a literature review. Additionally, we gathered information from NASA [29] regarding the mean annual precipitation, mean annual temperature, mean annual relative humidity, and mean annual wind direction for each population from 1981--2023. To identify the soil type in 22 sampling populations, we utilized a soil map available at https://www.fao.org [27]. Furthermore, we conducted a comparative analysis of genetic diversity parameters across environmental factors. 3. Results 3.1. Genetic variation: Twenty-two populations of P. santalinus from Eastern Ghats were analyzed for genetic diversity and population structure via 16 highly polymorphic SSR markers [63] (Table S1). Among these loci, PIN-82 presented the highest value for all diversity indices: number of alleles (Na) = 12.82, effective number of alleles (Ne) = 8.85, expected heterozygosity (He) = 0.87, and observed heterozygosity (Ho) = 0.70. On the other hand, the PSSSR-2 locus had the lowest values for the same indices: Na=3.77, Ne=2.34, He=0.36, and Ho=0.12. Across all the loci, the average expected value for He was 0.65, whereas the average Ho was 0.34. Additionally, the PSSSR-32 locus had the highest PIC value (0.96), whereas the PSSSR-2 locus had the lowest PIC value among the 16 loci (0.91) (Table 2). The CPV population presented the highest Na value at 13.44, whereas the TCT population presented the lowest Na value at 4.63. On the other hand, TTP had the highest Ne value at 9.21, whereas NRA had the lowest at 3.27. The average He was 0.65, with the CPV again having the highest value of 0.87 and the PVT having the lowest value of 0.44. The Ho values ranged from 0.673 (CPV) to 0.10 (TCT), with an average of 0.34 (Table 3). 3.2. Rare and private alleles across different populations : This study revealed rare alleles, which are common in less than 25% of populations, as well as population-specific alleles or private alleles (PAs), which are unique to a single population (Fig. 2). Loci PSSSR-24 and PSSSR-26 presented the greatest number of rare alleles (Fig S1). Among the populations, CVP had the highest number of rare alleles at 6.62, followed by TTP and CSM at 6.50 and 6.625, respectively. Across 16 highly polymorphic loci, 236 Pa were detected. The maximum number of Pa was found in the PSSSR-31, and the minimum was found in the PSSSR-18. On average, 0.67 private alleles (PAs) were found from 22 populations, ranging from 0.188 to 2.125. The NAG, TTP, CSM, and CPV populations contained the maximum number of Pa, with values of 2.12, 1.50, 1.44, and 1.31, respectively (Table 3). This study demonstrated clear genetic variation among populations from varying latitudes. Three primary groups, L1 (14.5--15.3°N), L2 (14.0--14.5°N), and L3 (13.0--13.9°N), were identified in this study, with each group having a cluster of alleles unique to the given latitude. The L1 group was composed of 105 alleles specific to this latitudinal group. These alleles are genetic variations that do not exist in other populations. The L2 group, in a similar vein, presented characteristics of 124 such alleles at this latitude, whereas the L3 group presented 142 alleles specific to its latitude. Compared with the other two groups, the L3 group presented a greater number of private alleles (Table S2; Fig S2). 3.3. Genetic differentiation : The inbreeding coefficient (Fis) ranged between 0.80 (PSSSR-72) and 0.19 (PIN-82), with a mean of 0.50. F statistics for each locus in the species revealed significant differences in the genetic differentiation coefficient (FST) and gene flow (Nm) at the locus level (Table 2). Furthermore, when the genetic differentiation coefficient (FST) and gene flow (Nm) among populations were compared, the average FST was 0.31, indicating moderate genetic differentiation. The Nm value ranged from 0.32 to 2.92, with a mean of 0.82, indicating a low rate of gene flow (Table 2). Analysis of molecular variance (AMOVA) with 999 permutations revealed 73% genetic variation within populations and 27% genetic variation between populations (Table 4). Additionally, FST =0.27 (P=0.001) indicated a significant genetic difference among the 22 populations of P. santalinus . The pairwise FST ranged between 0.049 and 0.427. The highest level appeared between PVT and TBB, whereas the lowest was between populations of TTP and CVP (Table S3). 3.4. Genetic Structure and Cluster Analysis: The structural analysis revealed a maximum ΔK=3. All 22 populations were grouped into three distinct genetic clusters (Fig. 3). Cluster I (red) contained 136 individuals from 8 populations (NRA, KOD, TBB, TCT, TTP, CSM, CPV, and NAK). Cluster II (green) contained 115 individuals from 7 populations (KVP, KSM, KRG, KKM, RRS, RCV, and NVV). Cluster III (blue) contained 110 individuals from 7 populations (PVT, PPT, PBB, RSJ RKK, GGS, and NVD). UNJ tree analysis also grouped the 361 individuals from 22 populations into three main clusters. Compared with the structure analysis, there was little difference in population grouping. Cluster I included four populations, Cluster II had seven, and Cluster III contained eleven populations (Fig. 4). An analysis of the codominant alleles via PCoA was conducted to compare the structural and UNJ analyses. The first two principal coordinates captured 35.56% of the information, with individual contributions of 16.04% and 9.95% (Fig. 5). Mantel tests were conducted to analyze the relationships between geographic distance and pairwise Fst (Fig. 7), uNeiP (Fig. S3a), and genetic distance (Supplementary Fig. 3 b, c and d) in 22 P. santalinus populations. The results indicated that genetic distance (90%) contributed more substantially to the genetic differentiation among the populations than did geographic distance (70%). Therefore, it is evident that there was no clear geographic origin-based structuring or predominant isolation by distance among the studied populations (Fig 6). 3.5. Genetic variation among the different girth classes: Genetic diversity analysis was conducted across four girth classes: seedlings and saplings, young trees with a GBH of 10--20 cm, young trees with a GBH of 20--30 cm, and mature trees (>30 cm). The purpose was to observe differences in genetic fitness among the four girth classes potentially impacted by the illegal harvesting of adult trees. The data revealed that the number of alleles (Na) ranged from 30.69 to 32.81, whereas the number of effective alleles (Ne) varied between 16.30 and 16.73 (Table 5). The Ho values ranged from 0.34 to 0.36, and He remained constant at 0.94. Additionally, the data revealed a mean fixation index (F) of 0.63. These findings suggest that there is no noteworthy difference in genetic diversity among the four girth classes. 3.6. Correlations between genetic diversity and environmental factors: A statistical analysis (Table 6) was used to explore the relationships between genetic diversity and environmental factors. Data collected on four environmental variables during the period 1980--2022 were plotted against populations (https://power.larc.nasa.gov/data-acce). The annual mean temperature varied from 26.23 0 C (RRS and RSJ) to 27.68 0 C (NAK) (Fig. S4a). There was a wide range of relative humidities between 62.86% (KKM/KOD/KRG/KSM/KVP) and 69.19% (TTP and CPV) ( Fig. S4b ) . The wind direction varied from 222.4 (GGS) to 264.6 degrees (TTP and CPV) ( Fig. S4c) . Between 0.32 mm (KOD) and 1.67 mm (TTP and CPV) of precipitation were recorded (Fig. S4d). Populations with high genetic diversity experienced mean temperatures ranging from 26.5°C (CPV and TTP) to 26.90°C (CSM). The altitude and latitude were not significantly correlated with most of the genetic parameters studied (Fig. S5a-f: Fig. S6 a-f). Similarly, the annual mean temperature did not significantly correlate with the genetic parameters (Fig. S7 a-f). The population of Na increased with increasing relative humidity (R2=0.30, p<0.05) and annual precipitation (R2=0.43, p<0.05) (Fig. S9a, 10a). Additionally, Shannon's information index (I) was correlated with relative humidity (R2=0.22, p<0.05) and annual precipitation (R2=0.34, p<0.05) (Fig. S9b, 10b). Between 0.32 mm (KOD) and 1.67 mm (TTP and CPV) of precipitation were recorded (Fig. S4d). Populations with high genetic diversity experienced mean temperatures ranging from 26.5°C (CPV and TTP) to 26.90°C (CSM). The altitude and latitude were not significantly correlated with most of the genetic parameters studied (Fig. S5a-f: Fig. S6 a-f). Similarly, the annual mean temperature did not significantly correlate with the genetic parameters (Fig. S7 a-f). The population of Na increased with increasing relative humidity (R2=0.30, p<0.05) and annual precipitation (R 2 =0.43, p<0.05) (Fig. S9a, S10a). Additionally, Shannon's information index (I) was correlated with relative humidity (R 2 =0.22, p<0.05) and annual precipitation (R 2 =0.34, p<0.05) (Fig. S8b, 9b). The Na population increased in correlation with both increasing relative humidity (R2=0.30, p<0.05) and annual precipitation (R2=0.43, p<0.05; Figures 8a and 9a). Similarly, the Shannon's information index (I) was correlated with relative humidity (R2=0.22, p<0.05) and annual precipitation (R2=0.34, p<0.05; Fig. S8b and S9b). However, there was no significant relationship between the Ho or fixation index and either the mean relative humidity or the annual precipitation (Fig. S8c, S9c; Fig. S9e). On the other hand, He was significantly related to annual precipitation (R 2 =0.25, p<0.05; Fig. S8d and S9d). Additionally, Pa was significantly correlated with both relative humidity (R 2 =0.21, p<0.05) and annual precipitation (R2=0.46, p<0.05; Figures S8f and 9f; Table 6). An analysis of the locations of different populations with a soil map revealed that 20 out of 22 populations were situated on Lithosols (Fig. 7a), with one population each on Chromic Luvisols (PPT) and Verticcambisols (TTP). A noticeable pattern emerged, revealing an increase in genetic diversity from Lithosols to Verticcambisols (Fig. 7 b-g). Interestingly, the three populations with the highest genetic diversity consisted of two populations (CPV and CSM) situated on Lithosols and one population (TTP) on Verticcambisols. This trend in genetic diversity parameters from Lithosols to Verticcambisols provides valuable preliminary insights (Fig. 7b-g). 3.7. Genetic diversity analysis was performed on the basis of the different forest classifications. The Forest Department of Andhra Pradesh classified the distribution of P. santalinus into different circles and divisions in Eastern Ghats (Fig. S11 and S12). Analysis of genetic diversity by circle revealed that the Tirupati circle had the highest Na (35.38), whereas the Guntur circle had the lowest (22.94). However, Guntur had a greater Ne of 11.60 than the Kurnool did, despite the latter having a slightly greater Ne (Table 7, Fig. S11). This trend was also observed in Ho. Despite the small difference in sample size between the Kurnool and Tirupati populations, the private alleles found differed significantly (5.69--10.88). Additionally, although the population size of the Guntur circle was half that of the Kurnool, all the genetic diversity parameters were nearly equal to or greater than those of the Kurnool circle. These results clearly indicate that Tirupati has the highest diversity, followed by the Guntur and Kurnool circles. There was a significant difference in the number of individuals (N) among the different divisions (Table 8, Fig. S12). Kadapa had the greatest population size, with 78 individuals, whereas Giddaluru and Nandyal had only 14 individuals. Divisions such as Chitoor, Nellore, and Rajampet had high N values, leading to higher allele frequencies than those of other divisions. As expected, Giddaluru and Nandyal presented relatively low Ne values. Among all the divisions, Chitoor had the highest He value (0.91), whereas Nandyal (0.53) had the lowest genetic diversity. The Chittoor division had a low (fixation index) F value of 0.36, whereas the Giddaluru division had a high F value of 0.75. The Nellore and Rajampet division populations had a high number of private alleles, which indicates a unique set of alleles in their genetic makeup. The Forest Department of Andhra Pradesh classified the distribution of P. santalinus into different circles and divisions in the Eastern Ghats (Figs. S11 and S12). Through genetic diversity analysis, it was found that the Tirupati circle had the highest Na (35.38), whereas the Guntur circle had the lowest (35.38). However, Guntur had a greater Ne (11.60) than did Kurnool, despite Kurnool having a slightly greater Ne (Table 7; Fig. S11). Despite the small difference in sample size between the Kurnool and Tirupati populations, the private alleles found differed significantly (5.69--10.88). This trend was also observed in Ho. Even though the population size of the Guntur circle was half that of the Kurnool, all the genetic diversity parameters were nearly equal to or greater than those of the Kurnool circle. Therefore, Tirupati clearly has the highest diversity, followed by the Guntur and Kurnool circles. There was a significant difference in the number of individuals among the different divisions (Table 8, Fig. S12). Kadapa had the greatest population size, whereas Giddaluru and Nandyal had the lowest. The Chitoor division had the highest He value (0.91), whereas the Nandyal division (0.53) had the lowest genetic diversity. The Chittoor division had a low F value of 0.36, whereas the Giddaluru division had a high F value of 0.75. The Nellore and Rajampet division populations had a high number of private alleles, indicating a unique set of alleles in their genetic makeup. 4. Discussion 4.1. Genetic diversity of P. santalinus : In India, P. santalinus is a valuable tree species that is in decline due to its valuable heartwood, compromising its genetic diversity . Genetic diversity is crucial for long-term survival and genetic improvement of a species through breeding [19, 34, 57]. To protect and preserve this species, effective conservation and management strategies have been developed using molecular markers [7, 5, 67]. Earlier studies focused on understanding genetic variations via dominant markers such as RAPD. Micropropagated P. santalinus individuals showed no genetic variation with RAPD markers [10], and significant DNA polymorphisms were detected in natural accessions [47] and nursery-grown plants [68]. These studies used small sample sizes, and dominant markers may have limitations in accurately capturing the total genetic diversity of the species. In this study, 16 highly polymorphic simple sequence repeats (SSRs) were used to assess the genetic diversity of P. santalinus across different populations. The present study revealed a total of 749 alleles among 361 individuals, which is considerably greater than the number of alleles obtained from 13 EST-SSRs. The genetic diversity values in this study were greater than those reported via EST-SSRs in P. santalinus and SSRs in P. erinaceous [1]. Two hundred thirty-seven alleles obtained from 17 SSRs were amplified across 365 individuals of P. erinaceus [31], as were the 54 alleles detected from 19 SSRs in 42 individuals of Dalbergia odorifera [38]. Our study revealed moderate genetic diversity values, with observed and expected heterozygosity values of 0.34 and 0.65, respectively. These values are relatively low compared with those of widely spread hardwood species such as Swietenia macrophylla (He=0.78) [36], Eucalyptus globulus Labill (He= 0.82) [66], E. grandis (He=0.77) [64], Tectona grandis (He=0.77) [21], and T. grandis L. (He=0.94) [39]. Low values coincide with the general belief that narrow-ranged species generally have lower genetic diversity than widespread congeners do [14]. These values were higher than those reported in studies within the genus Pterocarpus , specifically EST-SSRs in P. santalinus (He=0.322) [1] and SSRs in P. erinaceous (He= 0.57) [31]. Among the 22 populations studied, the CPV population presented the highest genetic diversity, whereas the TCT population presented the lowest genetic diversity. The low genetic diversity values in the TCT can be attributed to forest fragmentation, the presence of agricultural land near this population, and anthropological activities, which led to genetic bottlenecks and reduced genetic diversity due to the loss of natural habitat and gene flow barriers . Importantly, the value of Ho was much lower than that of He, indicating heterozygote deficiency in the populations of P. santalinus. The potential reasons for these findings could be attributed to the entomophilous cross-pollinating nature and wind dispersal of seeds [54, 55, 67], which restrict long-distance dispersal in P. santalinus . Additionally, this species is recognized for its abundant regeneration through coppice formation [30]. Similar characteristics have also been observed in the related genus Dalbergia [38, 43]. Alternatively, in smaller populations, there is a greater occurrence of mating between relatives than in larger populations [43]. 4.2. Rare and private alleles across the different populations: The frequency range of private alleles (PAs) varied significantly among different populations within the Eastern Ghats, with values ranging from 0.188 to 2.125. This wide range of variation suggests that some populations have a greater degree of genetic uniqueness than others do [24]. The unique alleles discovered in these populations could represent distinct evolutionary paths, as observed in rare plant species [32]. The presence of private alleles in a population is of evolutionary importance, and the evolutionary importance of a population is determined by both the number of alleles and the presence of private alleles [33, 48, 51]. Notably, the population with the highest Pa frequency (NAK) indicates significant genetic differentiation. These populations stand out as genetic reservoirs of unique alleles, indicating a greater degree of isolation or historical divergence that has led to the accumulation of distinctive genetics [32, 65], which might explain the long survival of P. Santalinus despite the enormous anthropological pressure. Hence, these trees are important genetic resources that can be used in tree breeding programs. 4.3. Genetic Differentiation and Population Structure According to the AMOVA, the majority (73%) of the genetic variation detected was within populations, whereas only 27% was between populations. This suggests that the primary contributor to total genetic variation can be attributed to variation within populations. Similar findings were reported in a recent study on P. marsupium [41], which used intersimple sequence repeat (ISSR) markers and reported that 91% of the genetic variation was within populations and that only 9% was found among populations. Amri and Mamboya [6] reported that genetic variation in P. angolensis 77.13% within the population and 28.86% among distinct populations. This aligns with previous research on long-lived, outcrossing, late-succession plant taxa, which have been shown to exhibit high levels of genetic diversity within populations [35]. The Shannon’s information index (I) of 1.52 and Nei’s gene diversity (2.31) obtained in the present study revealed high levels of genetic variation within the populations (Table 3). These findings are greater than those reported for P. angolensis (I=0.2769) [6], P. marsupium (I=0.46) [41] and D. odorifera (I= 0.65 and Nei’s genetic diversity 0.38) by Liu et al. [38]. Similarly, a significant pairwise F ST of 0.05 to 0.43 was observed among the P. santalinus populations (Table S2), which was greater than the F ST (0.042 to 0.115) of D. odorifera [38], indicating moderate genetic differentiation among the 22 P. santalinus populations. The highest level of genetic differentiation was found between the PVT and TBB populations (0.427), which were isolated at a distance of 150 km between them, and the lowest was found between the TTP and CPV populations (0.049), which were located at 34 km (Table S2). This finding revealed a decrease in gene flow with increasing geographic distance. Gene flow is vital for determining genetic differentiation and genetic drift among populations [58]. Gene flow in plant species occurs through the exchange of pollen, seeds, and spores, influencing the genetic variation in the population [72, 73]. A gene flow value greater than 1 can overcome genetic drift, whereas a value less than one indicates that genetic drift is the predominant factor affecting a population's genetic structure [62]. A mean Nm of 0.82 was observed in the present study, indicating low gene flow among the populations and indicating the occurrence of genetic drift in the populations. If not addressed, this will lead to the isolation of populations, leading to inbreeding depression, genetic bottlenecks and the extinction of populations/species from natural habitats. P. santalinus is pollinated mostly by Apis dorsata only during the night [54, 55]. The short distance of these bees from hives might be the primary reason for the low gene flow between populations and the fragmentation of the populations. An admixture model-based analysis was used to evaluate population structure. The genetic structure revealed the distribution pattern of genetic diversity within and between populations. Structural analysis revealed a maximum ΔK of 3, with 361 genotypes assigned to three clusters (Fig. 3). Cluster I included the populations in the Tirupati and Chittoor Circles, Cluster II included the populations in the Kadapa and Rajampet regions, and Cluster III included the populations from the Guntur and Nellore Circles. Some of the geographically close populations were placed in different clusters and vice versa, but the percentage of individuals with admixture was very low. The UNJ and PCoA results also supported the STRUCTURE analysis, which was attributed to differences in population clustering. Although all three analyses were successful in grouping 22 populations of P. santalinus into three subgroups, there were differences in the clustered populations and the number of populations. Overall, no apparent population clustering was observed, and a significant correlation was not found between genetic and geographic distances. The Mantel test results revealed that 68% of the genetic differences among the investigated populations were attributed to geographical distance (Fig. 6). The principle of isolation by distance, as described by Wright in 1943 [71], predicts that a positive correlation can be expected between genetic and geographic distances when populations reach equilibrium between gene flow and genetic drift. An analysis of the data revealed that there was a positive correlation between geographic distance and population differentiation, but it was not significant (Fig. 6). This differentiation is mostly attributed to genetic distance (Fig. 7b) rather than geographic distance. These findings indicate that human interference and the limited foraging distance of bees are the main factors influencing pollination differentiation. In the present study, low gene flow was detected even though the natural populations are located within a maximum distance of 250 km. This phenomenon eventually results in inbreeding and affects the fitness of the population. A possible reason could be habitat loss and fragmentation of populations by human interference, as reported by the NDF survey. 4.4. Genetic variation among the Girth classes: The analysis revealed that there were no significant differences in genetic diversity parameters such as Na, Ne, He, and Ho among the four girth classes (Table 7). This finding suggests that the genetic makeup of the population remained consistent regardless of the girth class. However, a noticeable upward trend in all genetic diversity parameters was observed from higher to lower girth classes. These results align with findings from other studies on tree species such as Pinus ponderosa [37], Koompassia malaccensis [45], and Dysoxylum malabaricum [12], which also revealed a similar pattern of genetic diversity between seedlings and adult plants. One possible explanation for this trend could be the occurrence of genetic drift or gene flow within the population [11]. In contrast, a study conducted on Manilkara multifida [70] in a highly fragmented habitat revealed a significant difference in Ho between adult individuals (EVC = 0.720, UBR = 0.736) and juveniles (EVC = 0.463, UBR = 0.560). Similarly, D. binectariferum reported a high level of allelic richness in adults compared with juveniles [11, 42]. These findings indicate that population fragmentation may have an impact on genetic diversity. However, our study did not find any such differences in genetic diversity parameters despite the selective pressure of logging on the population. The forest department's tremendous efforts to protect the species and the good amount of natural regeneration might be the factors influencing the maintenance of genetic diversity among girth classes. 4.5. Effects of ecological factors and edaphic factors: The genetic diversity of plant species depends on different factors, such as ecological, geographical, breeding system, and anthropogenic factors [56]. Higher genetic diversity is expected to reflect better adaptation to the changing environment of a species [23]. The P. santalinus distribution in Andhra Pradesh is restricted mainly to the Cuddapah landscape (13° 30’ and 15° 00’ North latitude and between 78° 45’ and 79° 39’ East longitude) [52]. Geographically, the region occupies approximately 5160 km2, and its geographical spread includes the Chittoor, Cuddapah, and Nellore districts of the Seshachalam Hill Range, which has altitudes ranging from 150–900 m [8]. Physiographically, the most favorable altitude is reported to be from 300--800 m [52]. However, our study included altitudes ranging from 124 m to 838 m (Table 1). The CSM (124 m), CPV (318 m), and TTP (602 m) populations presented high genetic diversity and were located in low- and medium-altitude regions. There was no clear pattern observed in genetic variation with increasing elevation. Overall, in this study, we observed a significant correlation between genetic diversity according to annual precipitation and relative humidity. The genetic diversity of P. santalinus is influenced by the type of soil and topography. This plant species grows on dry, hilly, and often rocky terrain, and it prefers lateritic and gravelly soil [60]. Approximately 80% of the red-sander growing area is occupied by outcrops of quartzites, whereas the remainder is occupied by shale geological formations [52]. The high potassium content of the quartzite soil could be a major factor in the localization of P. santalinus [52] . According to the soil distribution map of Eastern Ghats, which was created from data from bhukosh (https://bhukosh.gsi.gov.in/Bhukosh/Public), 20 out of 22 populations were found to be located on lithosols. One population was found on chromic luvisols (PPT), and one was found on vertic cambisols (TTP) (Fig. 8a). Additionally, we observed an increasing trend in genetic diversity parameters from Lithosols to vertic cambisols (Fig. 8b-g). Furthermore, to investigate the relationships between environmental factors and genetic diversity, detailed soil nutrient data and other environmental information are necessary. Further investigations of soil pH, nutrient levels, and microbial associations may help in understanding the influence of soil and other environmental factors on genetic diversity. 4.6. Genetic diversity analysis based on different forest classifications: The genetic diversity of P. santalinus in the Eastern Ghats of Andhra Pradesh shows significant variation across different circles and divisions. The analysis revealed notable variations in allele frequencies and diversity parameters. Compared with the other populations, the Tirupati circle presented the greatest genetic diversity, with the greatest number of alleles (Na) and private alleles having high precipitation, humidity, and low temperatures. Interestingly, despite differences in population size, the Guntur circle presents comparable or greater adequate population size (Ne) and diversity metrics than do larger circles such as Kurnool. Similarly, within divisions, genetic diversity correlates with population size, with greater Ne observed in larger populations. Divisions such as CTR are notable for their elevated genetic diversity, whereas others such as NLR and RJT have unique sets of private alleles. These findings highlight the need to consider population size and local environmental factors in conservation strategies for P. santalinus in the Eastern Ghats. Despite the stringent efforts of the APFD to combat unlawful deforestation practices, a noteworthy decline in the population of mature P. santalinus bearing trees available for harvesting has been detected in various forests [3]. This decline is most prominent in three forest department circles and eight divisions, where the Tirupati circle and Chittoor division exhibit significant variations. This could be due to P. santalinus natural populations prevailing in dry areas [9]. These populations hold immense potential as germplasms for future conservation initiatives aimed at safeguarding the species. 5. Conclusion This study represents the first comprehensive genetic diversity analysis covering the entire natural range of P. santalinus in Eastern Ghats, India. We used 16 highly polymorphic SSR markers to assess 22 natural populations in the region. Our findings revealed moderate genetic diversity, which is relatively low for a woody tree species, with a few populations displaying high levels of diversity, whereas others presented alarmingly low genetic variation. Most of the genetic variation was observed within populations, with moderate genetic differentiation and low gene flow among them. Among the 22 populations, Tirupati base-Sadashiva Kona (CPV), followed by Tirupati--Papanashini (TTP) and Chittoor East-Srikalahasti-Melachur (CSM), presented the highest genetic diversity (He=0.869), and the lowest was Chitaleti Pati Base Camp (PVT) (He=0.436). Additionally, many private alleles have been identified in populations Nellore Atmakuru-Kadarinaidupalli (NAK), Tirupati--Papanashini; (TTP), and Chittoor East-Srikalahasti-Melachur; (CSM), presenting opportunities for selective breeding to increase adaptation and resistance to changing environments. At the forest circle and division levels, the Tirupati circle and Chitoor divisions were identified as highly diverse, which is consistent with the findings at the population level. Despite habitat fragmentation and anthropogenic pressure on forest areas, no notable differences in genetic diversity parameters were observed between seedlings, saplings, and mature trees. The study also revealed significant correlations between genetic diversity parameters, annual precipitation, and relative humidity. Moreover, soil type and topography likely play major roles in species distributions. Notably, populations located at lower latitudes presented significant genetic diversity across their distribution range. These results underscore the need for further investigations into the effects of terrain, soil, and environmental factors to better understand the interaction between the environment and genetics on heartwood formation. In conclusion, the SSR loci identified in this study could serve as valuable tools for future tree improvement programs. Populations with high genetic diversity and unique alleles should be leveraged as germplasm resources and for seed material in both in situ and ex-situ conservation efforts, particularly to address the low gene flow rate among populations and manage those with low genetic diversity. Abbreviations APFD – Andhra Pradesh Forest Department CITES - Convention on International Trade in Endangered Species of Wild Fauna and Flora RAPD-Random Amplified Polymorphic DNA ISSR-Inter-Simple Sequence Repeat SSR- simple sequence repeats EST-SSR - expressed sequence tag-derived simple sequence repeat marker NGS- Next-Generation Sequencing DNA- Deoxyribonucleic Acid CTAB- Cetyltrimethylammonium bromide PCR- Polymerase chain reaction Na-Number of different alleles Ne-number of effective alleles Ho- observed heterozygosity He-Expected Heterozygosity PIC- Polymorphic Information Content I- Shannon's information index F- Fixation Index Fis- Inbreeding coefficient within an individual relative to the total Fit- Inbreeding coefficient within an individual relative to the total Fst- Inbreeding coefficient within a subpopulation relative to the total Nm-Gene Flow AMOVA - Analysis of Molecular Variance UNJ- Unweighted neighbor-joining PCoA-Principal Coordinate Analysis MCMC-Monte Carlo Markov Chain NDF- Non-Detrary Findings GBH- Girth at Breast Height GC – Girth class SiO 2 -Silicon dioxide K -Potassium Fe- Iron Ca- Calcium Na-Sodium A2cd- Declining population (past, present and/or projected) A2 -Population reduction observed, estimated, inferred, or suspected in the past where the causes of reduction may not have ceased OR may not be understood OR may not be reversible. (c) Declines in area of occupancy (AOO), extent of occurrence (EOO) and/or habitat quality (d) Actual or potential levels of exploitation Declarations Source of Funding: National Biodiversity Authority (NBA) (No. Tech./Genl./22/149/17/18-19/382). Conflict of interest: The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as potential conflicts of interest. All the authors declare that there are no conflicts of interest. Clinical trial number: Not applicable. Consent to Participate: Not applicable. This study does not involve any human or animal trials, nor does it include any genetic modification of the plant. Ethics statement: The plant material was identified by Divakara, BN, a scientist at IWST in Bengaluru, and a voucher specimen has been deposited at TDU/IWST, (IWST-NBA-01 to 400), FRLHT, Bengaluru. We have collected samples with the gracious permission of the Forest Department of Andhra Pradesh, India. Reference No. EF02-20051/33/2020 - Research SEC PCCF dated 10/20/2020 from the Forest Department, Government of Andhra Pradesh, India. We adhered to both local and national guidelines during the sample collection. Data Availability Statement: All data generated or analyzed during this study are included in this published article [and its supplementary information files]. Consent to publish: Consent to publish were obtained from all authors, and all the authors declare that there are no conflicts of interest. Plant reproducibility: Leaf samples of Pterocarpus santalinus were collected from the Eastern Ghats of Andhra Pradesh, India. Only leaf samples were collected without harming the tree, and ensuring their reproducibility. Author contribution statement : The project was conceptualized by MKP, PHR, and DBN. Sample collection was carried out by MKP, PHR, and DBN. Sample preparation, experiments, and data analysis were carried out by SMV, MAH, PHR, and MKP. Discussion of the data and MS preparation are performed by SMV, MAH, PHR, CJ, and MKP. The finalization of the manuscript was performed by PHR, CJ, SK, DBN, and MKP. Acknowledgments: We thank the National Biodiversity Authority (NBA) (No. Tech./Genl./22/149/17/18-19/382) for financial support. Dr. MKP also expresses his gratitude to the Department of Biotechnology (DBT) and the Science and Engineering Research Board (SERB) for their financial support. The collection of samples and other fieldwork was facilitated by the kind permission and cooperation of the State Forest Department, Government of Andhra Pradesh. We also dedicate this article to all the forest officers working in the Eastern Ghats region for their dedication to the protection and conservation of the Red Sanders. References Agasthikumar, S., Patturaj, M., Samji, A., Aiyer, B., Munusamy, A., Kannan, N., Arivazhagan, V., Warrier, R. R., Ramasamy, Y., 2022. De novo transcriptome assembly and development of EST-SSR markers for Pterocarpus santalinus L. f. (Red sanders), a threatened and endemic tree of India. Genetic Resources and Crop Evolution , Advance online publication.https://doi.org/10.1007/s10722-022-01385-8 Ahmed, M., and Nayar, M. P., 1984. Red Sanders tree ( Pterocarpus santalinusLinn .f.) on the verge of depletion. Bulletin of Botanical Survey of India , 26, 142-143. Ahmedullah, M., Rasingam, L., Swamy, J., Nagaraju, S., Shankara Rao, M., 2019. Non-Detriment Findings Report on the Red Sanders Tree (Pterocarpus santalinusL.f). Botanical Survey of India (Deccan Regional Centre), MoEFCC, Hyderabad. Allendorf, F. W., Luikart, G., Aitken, S. N., 2012. Conservation and the genetics of populations. John Wiley & Sons. Amiteye S., 2021. Basic concepts and methodologies of DNA marker systems in plant molecular breeding. Heliyon , 7(10), e08093. https://doi.org/10.1016/j.heliyon.2021.e08093 Amri, E., and Mamboya, F., 2012. Genetic diversity in Pterocarpus angolensis populations detected by random amplified polymorphic DNA markers. International Journal of Plant Breeding and Genetics , 6 (2), 105-114. Arif, I. A., Khan, H. A., Bahkali, A. H., Al Homaidan, A. A., Al Farhan, A. H., Al Sadoon, M., Shobrak, M., 2011. DNA marker technology for wildlife conservation. Saudi journal of biological sciences , 18(3), 219–225. https://doi.org/10.1016/j.sjbs.2011.03.002 Arunkumar, A. N., and Joshi, G. 2014. Pterocarpus santalinus (Red Sanders) an Endemic, Endangered Tree of India: Current Status, Improvement and the Future. Journal of Tropical Forestry and Environment , 4(2), 1-10.https://doi.org/10.31357/jtfe.v4i2.2063 Babar, S., Amarnath, G., Reddy, C.S., Jentsch, A., Sudhakar, S., 2012. Species distribution models: ecological explanation and prediction of an endemic and endangered plant species (Pterocarpus santalinus Lf). Current Science, 1157-1165. Balaraju, K., Agastian, P., Ignacimuthu, S., Park, K., 2011. A rapid in vitro propagation of red sanders (Pterocarpus santalinus L.) using shoot tip explants. Acta physiologiae plantarum , 33, 2501-2510. Bodare, S., Ravikanth, G., Ismail, S. A., Patel, M. K., Spanu, I., Vasudeva, R., Shaanker, R. U., Vendramin, G. G., Lascoux, M., Tsuda, Y., 2016. Fine- and local- scale genetic structure of Dysoxylum malabaricum, a late-successional canopy tree species in disturbed forest patches in the Western Ghats, India. Conservation Genetics , 18 (1), 1–15. https://doi.org/10.1007/s10592-016-0877-7 Bodare, S., Tsuda, Y., Ravikanth, G., Uma Shaanker, R., Lascoux, M., 2013. Genetic structure and demographic history of the endangered tree species Dysoxylum malabaricum (M eliaceae) in W estern G hats, I ndia: implications for conservation in a biodiversity hotspot. Ecology and Evolution , 3 (10), 3233-3248. Champion, H.G., Seth, S.K., 1968. A Revised Forest Types of India. Manager of Publications , Government of India, Delhi. Cole, C. T., 2003. Genetic Variation in Rare and Common Plants. Annual Review of Ecology, Evolution, and Systematics , 34, 213–237. doi:10.1146/annurev.ecolsys.34.030102.151717 Davey, J. W., Hohenlohe, P. A., Etter, P. D., Boone, J. Q., Catchen, J. M., Blaxter, M. L., 2011. Genome-wide genetic marker discovery and genotyping using next-generation sequencing. Nature Reviews Genetics , 12(7), 499-510. Doyle, J. J., and Doyle, J. L., 1990. Isolation of Plant DNA from Fresh Tissue. Earl, D. A., and VonHoldt, B. M., 2012. STRUCTURE HARVESTER: a website and program for visualizing STRUCTURE output and implementing the Evanno method. Conservation Genetic Resources , 4(2), 359–361. https://doi.org/10.1007/s12686-011-9548-7. Ellegren, H., 2004. Microsatellites: simple sequences with complex evolution. Nature Reviews Genetics , 5(6), 435-445. Ellegren, H., Galtier, N., 2016. Determinants of genetic diversity. Nature Reviews Genetics , 17, 422–433. https://doi.org/10.1038/nrg.2016.58 Evanno, G., Regnaut, S., Goudet, J. (2005). Detecting the number of clusters of individuals using the software structure: a simulation study. Molecular Ecology , 14, 2611-2620. https://doi.org/10.1111/j.1365-294X.2005.02553.x Fofana, I. J., Lidah, Y. J., Diarrassouba, N., N’guetta, S. P. A., Sangare, A., Verhaegen, D., 2008. Genetic Structure and Conservation of Teak (Tectona Grandis) Plantations in Côte d’Ivoire, Revealed by Site Specific Recombinase (SSR). Tropical Conservation Science , 1(3), 279-292. doi:10.1177/194008290800100308 Frankham, R., 2005. Genetics and extinction. Biological Conservation, 126(2), 131-140. Gadissa, F., Tesfaye, K., Dagne, K., Geleta, M., 2018. Genetic diversity and population structure analyses of Plectranthus edulis (Vatke) Agnew collections from diverse agro-ecologies in Ethiopia using newly developed EST-SSRs marker system. BMC Genetics , 19(1), 1-15. Hamrick, J. L., Godt, M. J. W., 1996. Effects of life history traits on genetic diversity in plant species. (1996b). Philosophical Transactions of the Royal Society B , 351 (1345), 1291–1298. https://doi.org/10.1098/rstb.1996.0112 Hegde, M., Singh, B. G., Krishnakumar, N., 2012. Non-Detriment Findings Study for Pterocarpus santalinus L. f. (Red Sanders) in India. Institute of Forest Genetics and Tree Breeding. https://forests.ap.gov.in/ https://www.fao.org. https://www.iucnredlist.org/search/list?query=Pterocarpus%20santalinus&searchType=species https://power.larc.nasa.gov/data-acce Indu, B. K., Kavyashree, R., Balasubramanya, S., Anuradha, M., 2019. Tree Improvement in Red Sanders, Red sanders: Silviculture and conservation,201-210.https://doi.org/10.1007/978-981-13-7627-6_15 Johnson, B. N., Quashie, M. L. A., Chaix, G., Camus‐Kulandaivelu, L., Adjonou, K., Segla, K. N., Vignes, H., 2020. Isolation and characterization of microsatellite markers for the threatened African endemic tree species Pterocarpus erinaceus Poir. Ecology and Evolution , 10(23), 13403-13411. Jump, A.S., Penuelas, J., 2005. Running to stand still: adaptation and the response of plants to rapid climate change. Ecology Letters , 8(9), 1010-1020. Kalinowski, S.T., 2004. Counting alleles with rarefaction: private alleles and hierarchical sampling designs. Conservation Genetics , 5, 539–543. Kardos, M., Armstrong, E. E., Fitzpatrick, S. W., Hauser, S., Hedrick, P. W., Miller, J. M., Tallmon, D. A., Funk, W. C., 2021. The crucial role of genome-wide genetic variation in conservation. Proceedings of the National Academy of Sciences , 118(48), e2104642118. https://doi.org/10.1073/pnas.2104642118 Kremer, A., Caron, H., Cavers, S., Colpaert, N., Gheysen, G., Gribel, R., Lemes, M., Lowe, A. J., Margis, R., Navarro, C., Salgueiro, F., 2005. Monitoring genetic diversity in tropical trees with multilocus dominant markers. Heredity , 95 (4), 274–280.https://doi.org/10.1038/sj.hdy.6800738 Lemes, M. R., Gribel, R., Proctor, J., Grattapaglia, D., 2003. Population genetic structure of mahogany ( Swietenia macrophylla King, Meliaceae) across the Brazilian Amazon, based on variation at microsatellite loci: implications for conservation. Molecular ecology , 12(11), 2875–2883. https://doi.org/10.1046/j.1365-294x.2003.01950.x Linhart, Y. B., Mitton, J. B., Sturgeon, K. B., Davis, M. L., 1981. Genetic variation in space and time in a population of ponderosa pine. Heredity , 46(3), 407-426. Liu, F., Hong, Z., Xu, D., Jia, H., Zhang, N., Liu, X., Yang, Z., & Lu, M. 2019b. Genetic diversity of the endangered Dalbergia odorifera revealed by SSR markers. Forests , 10(3), 225.https://doi.org/10.3390/f10030225 Maisuria, H. J., Dhaduk, H. L., Kumar, S., Sakure, A. A., Thounaojam, A. S., 2022. Teak population structure and genetic diversity in Gujarat, India. Current Plant Biology , 32, 100267. https://doi.org/10.1016/j.cpb.2022.100267 McNeely, J. A., Miller, K. R., Reid, W. V., Mittermeier, R. A., Werner, T. B., 1990. Conserving the world's biological diversity. Gland, Switzerland: IUCN; Washington, D.C.: WRI, CI, WWF-US, and the World Bank. Mohammad, N., Dahayat, A., Pardhi, Y., Rajkumar, M., 2022. Morpho-molecular diversity assessment of Indian kino ( Pterocarpus marsupium Roxb.). Journal of Applied Research on Medicinal and Aromatic Plants , 29, 100373. https://doi.org/10.1016/j.jarmap.2022.100373 Mohana Kumara, P., Dayanandan, S., Vasudeva, R., Ravikanth, G., Uma Shaanker, R., 2022. Population Genetic Diversity of Dysoxylum Binectariferum , an Economically Important Tree Species of the Western Ghats, India. In Molecular Genetics and Genomics Tools in Biodiversity Conservation (pp. 251-266). Singapore: Springer Nature Singapore. Moritsuka, E., Chhang, P., Tagane, S., Toyama, H., Sokh, H., Yahara, T., Tachida, H., 2017. Genetic variation and population structure of a threatened timber tree Dalbergia cochinchinensis in Cambodia. Tree genetics & genomes , 13, 1-11. Nawaz, M. A., Sahito, Z. A., Al-Arif, M. A., Kakar, M. S., Khan, S., 2017. Assessing genetic diversity and population structure of Pakistani rice germplasm. PLoS ONE , 12(9), e0183435. https://doi.org/10.1371/journal.pone.0183435 Noreen, A.M. and Webb, E.L., 2013. High genetic diversity in a potentially vulnerable tropical tree species despite extreme habitat loss. PLoS One , 8 (12), p.e82632. Oliveira, E. J., Padua, J. G., Zucchi, M. I., Vencovsky, R., Vieira, M. L. C., 2006. Origin, evolution and genome distribution of microsatellites. Genetics and Molecular Biology , 29(2), 294-307. Padmalatha, K., Prasad, M. N. V., 2007. Morphological and molecular diversity in Pterocarpus santalinusLf-an endemic and endangered medicinal plant. Medicinal and Aromatic Plant Science and Biotechnology , 1(2), 263-273. Parker, K.M., Sheffer, R.J., Hedrick, P.W., 1999. Molecular variation and evolutionarily significant units in the endangered Gila topminnow. Conservation Biology , 13, 108–116. Peakall, R., and Smouse, P.E., 2012. GenAlEx 6.5: genetic analysis in Excel. Population genetic software for teaching and research-an update. Bioinformatics , 28, 2537-2539. Perrier, X., Flori, A., Bonnot, F., 2003. Data analysis methods. In: Hamon, P., Seguin, M., Perrier, X., Glaszmann, J. C. Ed., Genetic diversity of cultivated tropical plants. Enfield, Science Publishers. Montpellier. pp 43 – 76. Pritchard, J.K., Stephens, M., Donnelly, P., 2000. Inference of population structure using multilocus genotype data. Genetics , 155(2), 945-959.https://doi.org/10.1093/genetics/155.2.945 Raju, K., and Nagaraju, A., 1999. Geobotany of red sanders (Pterocarpus santalinus) – a case study from the southeastern portion of Andhra Pradesh. Environmental Geology , 37, 340–344. https://doi.org/10.1007/s002540050393 Ramabrahmam, V., Sujatha., 2016. Red Sanders in Rayalaseema region of Andhra Pradesh: Importance to Commercial and Medicinal value. IOSR Journal of Pharmacy and Biological Sciences , 11, 57–60. Rao, S. P., Raju, A. J. S. 2002. Pollination ecology of the Red Sanders Pterocarpus santalinus (Fabaceae), an endemic and endangered tree species. Current Science , 83(9), 1144-1148. Rao, S.P., Atluri, J. B., Reddi, C.S., 2001. Intermittent mass blooming, midnight anthesis and rockbee pollination in Pterocarpus santalinus ( Fabaceae ). Nordic Journal of Botany , 21, 271-276. ISSN 0107-055X. Saeed, S., Barozai, M. Y., 2012. A review on genetic diversity of wild plants by using different genetic markers. Pure and Applied Biology , 1, 68-71. doi: 10.19045/bspab.2012.13004. Salgotra, R. K., Chauhan, B. S. 2023., Genetic Diversity, Conservation, and Utilization of Plant Genetic Resources. Genes , 14(1), 174. https://doi.org/10.3390/genes14010174 Schaal, B. A., Hayworth, D. A., Olsen, K. M., Rauscher, J. T., Smith, W. A., 1998. Phylogeographic studies in plants: problems and prospects. Molecular Ecology , 7 (4), 465-474. Selkoe, K. A., Toonen, R. J., 2006. Microsatellites for ecologists: a practical guide to using and evaluating microsatellite markers. Ecology Letters , 9(5), 615-629. Senthilkumar, N., Mayavel, A., Subramani, S. P., Balaji, K., Deenathayalan, P., 2015. Red sanders, Pterocarpus santalinus L. in Rajampet forest range, Rajampet forest division, Andhra Pradesh, India. Advances in Applied Science Research , 6(10), 130-134. Simko, I., 2009. Development of EST-SSR Markers for the Study of Population Structure in Lettuce (Lactuca sativa L.). Journal of Heredity , 100, 256–262. https://doi.org/10.1093/jhered/esn072 Slatkin, M., 1987. Gene flow and the geographic structure of natural populations. Science , 236(4803), 787-792. Sneha, M. V., Madhushree, A. H., Tapas, R. S., Divakara, B.N., Mohana, K.P., & Prabuddha, H. R., 2023. Genome sequencing and characterization of microsatellite markers of Pterocarpus santalinusL.f.: an economically important endangered tree of Eastern Ghats, India. Journal of Genetics , 102:35. Song, Z., Zhang, M., Li, F., et al., 2016. Genome scans for divergent selection in natural populations of the widespread hardwood species Eucalyptus grandis (Myrtaceae) using microsatellites. Scientific Reports , 6, 34941. https://doi.org/10.1038/srep34941 Sork, V.L., Smouse, P.E., Apsit, V.J., 2006. Genetic analysis of landscape connectivity in tree populations. Landscape Ecology , 21(5), 821-836. Steane, D. A., Conod, N., Jones, R. C., Vaillancourt, R. E., Potts, B. M. A., 2006. comparative analysis of population structure of a forest tree, Eucalyptus globulus (Myrtaceae), using microsatellite markers and quantitative traits. Tree Genet. Genomes , 2, 30–38 Teixeira da Silva, J. A., Kher, M. M., Soner, D., Nataraj, M. 2019. Red sandalwood (Pterocarpus santalinus L. f.): biology, importance, propagation and micropropagation. Journal of Forest Research , 30, 745-754. Usha, R., Rani, S. J., Prasuna, T. G. 2013. Genetic relationship between quality and nonquality wood of Pterocarpus santalinus L. (red sanders), an endemic tree species by using molecular markers. Journal of Chemical and Pharmaceutical Sciences , 6(3), 189-194. Vieira, M. L., Santini, L., Diniz, A. L., & Munhoz, C. F., 2016. Microsatellite markers: what they mean and why they are so useful. Genetics and Molecular Biology , 39(3), 312-328. doi: 10.1590/1678-4685-GMB-2016-0027. Waqar, Z., Moraes, R. C. S., Benchimol, M., Morante-Filho, J. C., Mariano-Neto, E., Gaiotto, F. A., 2021. Gene Flow and Genetic Structure Reveal Reduced Diversity between Generations of a Tropical Tree, Manilkara multifida Penn., in Atlantic Forest Fragments. Genes , 12 (12), 2025. https://doi.org/10.3390/genes12122025. Wright, S., 1943. Isolation by Distance. Genetics , 28 (2), 114–138. https://doi.org/10.1093/genetics/28.2.114 Woodruff, D. S., 2001. Populations, Species, and Conservation Genetics. In S. A. Levin (Ed.), Encyclopedia of Biodiversity (pp. 811-829). Elsevier. ISBN 9780122268656. https://doi.org/10.1016/B0-12-226865-2/00355-2. Zhang, D. M., Shen, X. H., Zhang, H. X., Shen, J. M. (2003). Advances in gene flow and paternity analysis of forest population. Forestry Research , 16, 488–494. doi:10.13275/j.cnki.lykxyj.2003.04.019 Tables Table 1: Sample collection data for 22 populations of Pterocarpus santalinus from various locations in Eastern Ghats, Andhra Pradesh, India. Forest Circle Division Range Beat Location Population ID Latitude (N) Longitude (E) Altitude (m) Sample size Guntur Giddaluru Giddaluru Singasanipalli PallugaoduThoka and Eluguddu shola GGS 15.2977 79.12817 512 16 Nellore Udayagiri Devammacheruvu Anasagarabodu and Badithala Bodu NUD 14.90691 79.16839 300 19 Nellore Atmakur Kadarinaidupalli Urlukonda Camp 410 NAK 14.67652 79.19965 157 20 Nellore Venkatagiri Vembaluru Mekalaguntha Camp 248 and Chinnakona Base Camp NVV 14.09043 79.47644 162 16 Kurnool Nandyal Rudravaram Ahobilam North Chinnakuchala NRA 15.15379 78.71711 305 16 Proddatur Porumamilla Tekurpeta Yerratichala PPT 14.99517 79.07484 398 16 Proddatur Vanipenta Tippireddypalli ChitaletiPati Base Camp PVT 14.96653 78.75828 315 16 Proddatur Badvel Balayapalli Bodabodu Camp 283 PBB 14.62871 78.97646 177 14 Kadapa Siddavatam Maddur Chinnadoddikona KSM 14.51345 79.00589 190 16 Kadapa Vempalli Polathala Bandennapadalu KVP 14.36888 78.67371 404 16 Camp 582 Kadapa Kadapa Maddimadugu East Inaparala gutta Camp 519 KKM 14.3371 78.78028 238 16 Kadapa Rayachoti Guvalacheruvu west Mangalam Bayalu road KRG 14.31187 78.76187 462 16 Kadapa Ontimitta Dasarala Doddi Utumora KOD 14.30738 78.99724 211 16 Tirupati Rajampet Rajampet Sri RangarajaPalem RollamadujuRastha Camp 889 RRS 14.12091 79.03636 367 16 Rajampet Sanipaya Jandrapenta Kuntathuvalu RSJ 14.12925 79.00255 351 16 Rajampet Chitvel Venkatarajpalli EtikuntoduBadava RCV 14.11746 79.39793 187 16 Rajampet Kodur K. V. bhavi (North) Bangla board RKK 13.91702 79.26148 151 16 Tirupati Balapalli Balapalli West Pangalachala TBB 13.78834 79.38422 355 16 Tirupati Chamala Talacona centra Rondavanka TCT 13.7736 79.17559 602 16 Tirupati Tirupati Papanashini and Timmala Papanashini Dam Camp 128 and Yerriganthalu Camp 127 TTP 13.71216 79.35739 790 16 Chittoor East WL Srikalahasti Melachur Savadugunta Camp 464 CSM 13.83461 79.49982 124 16 Chittoor East Puttur Vadamala Peta Sadashiva Kona CPV 13.53716 79.60114 318 20 GGS - GiddaluruGiddaluruSingasanipalli;NUD-Nellore Udayagiri Devammacheruvu; NAK- Nellore AtmakurKadarinaidupalli ; NVV- Nellore Venkatagiri Vembaluru; NRA- NandyalRudravaramAhobilam North; PPT- ProddaturPorumamillaTekurpeta; PVT- ProddaturVanipentaTippireddypalli; PBB- ProddaturBadvelBalayapalli; KSM- Kadapa SiddavatamMaddur; KVP- Kadapa VempalliPolathala; KKM- Kadapa KadapaMaddimadngu; KRG- Kadapa RayachotiGuvalacheruvu; KOD- Kadapa OntimittaDasarala Doddi; RRS- RajampetRajampet Sri RangarajaPalem; RSJ- RajampetSanipayaJandrapenta; RCV- RajampetChitvelVenkatarajpalli; RKK- Rajampet Kodur K. V. bhavi; TBB- Tirupati BalapalliBalapalli West; TCT- Tirupati ChamalaTalacona centra; TTP- Tirupati TirupatiPapanashini; CSM- Chittoor East SrikalahastiMelachur; CPV- Chittoor East Puttur Vadamala Peta. Table 2: Genetic diversity indices across 16 microsatellite loci for 22 populations of Pterocarpus santalinus Locus N Na Ne I Ho He PIC F F IS F ST Nm PIN-82 16 12.82 8.85 2.29 0.7 0.87 0.94 0.18 0.19 0.08 2.92 SSR-3 19 4.91 2.71 0.94 0.17 0.44 0.92 0.68 0.61 0.52 0.23 SSR-6 20 11.55 7.83 2.13 0.61 0.84 0.95 0.31 0.28 0.12 1.85 SSR-8 16 9 5.89 1.84 0.45 0.78 0.94 0.42 0.42 0.17 1.2 PSSSR-2 16 3.77 2.34 0.72 0.12 0.36 0.91 0.73 0.65 0.61 0.16 PSSSR-5 16 5.36 3.45 1.13 0.28 0.54 0.94 0.57 0.47 0.43 0.33 PSSSR-6 16 6.36 4.23 1.24 0.24 0.54 0.95 0.62 0.56 0.44 0.32 PSSSR-10 14 6.18 3.77 1.35 0.31 0.64 0.94 0.58 0.52 0.32 0.53 PSSSR-18 16 8.95 5.71 1.8 0.59 0.76 0.94 0.27 0.22 0.19 1.06 PSSSR-20 16 5.5 3.16 1.17 0.17 0.55 0.92 0.71 0.69 0.4 0.37 PSSSR-24 16 10.41 6.81 1.9 0.38 0.75 0.95 0.55 0.5 0.21 0.96 PSSSR-26 16 7.68 5.23 1.54 0.19 0.66 0.95 0.73 0.71 0.31 0.55 PSSSR-29 16 8.86 5.78 1.69 0.5 0.71 0.93 0.35 0.31 0.23 0.82 PSSSR-30 16 8.82 5.2 1.61 0.39 0.67 0.95 0.49 0.41 0.29 0.61 PSSSR-31 16 7.14 4.09 1.48 0.25 0.66 0.94 0.66 0.62 0.3 0.58 PSSSR-32 16 7.36 4.71 1.54 0.14 0.68 0.96 0.82 0.8 0.3 0.59 Mean 16 7.79 4.99 1.52 0.34 0.65 0.94 0.54 0.5 0.31 0.82 N: mean number of samples, Na: number of alleles, Ne: number of effective alleles, I: Shannon's Information Index, Ho: observed heterozygosity, He: expected heterozygosity, PIC: polymorphic information content, F: fixation index, F IS : inbreeding coefficient within individual relative to total, F ST : inbreeding coefficient within subpopulation relative to total, N m : gene flow. Table 3: Analysis of genetic diversity in 22 populations of Pterocarpus santalinus using 16 microsatellite markers. Population N Na Ne I Ho He F Pa PPL GGS 16 5.88 3.92 1.23 0.20 0.57 0.75 0.19 100% NUD 19 8.63 5.05 1.59 0.51 0.69 0.30 0.38 100% NAK 20 10.00 6.03 1.81 0.20 0.75 0.72 2.13 100% NVV 16 8.06 4.32 1.51 0.42 0.64 0.38 0.56 100% NRA 16 5.19 3.27 1.11 0.16 0.53 0.70 0.19 88% PPT 16 8.13 4.77 1.65 0.34 0.71 0.54 0.56 100% PVT 16 5.56 3.59 1.00 0.20 0.44 0.67 0.25 75% PBB 14 6.56 3.95 1.44 0.43 0.66 0.34 0.75 100% KSM 16 7.50 4.45 1.54 0.37 0.67 0.50 0.25 94% KVP 16 6.69 4.42 1.36 0.29 0.59 0.62 0.50 94% KKM 16 7.63 4.50 1.60 0.45 0.71 0.40 0.44 100% KRG 16 7.63 4.06 1.53 0.33 0.68 0.55 0.75 100% KOD 16 5.81 3.80 1.21 0.27 0.57 0.63 0.56 94% RRS 16 7.31 4.40 1.53 0.41 0.67 0.41 0.25 94% RSJ 16 6.81 3.99 1.32 0.29 0.57 0.63 0.19 94% RCV 16 9.94 6.82 1.96 0.52 0.81 0.34 0.75 100% RKK 16 7.00 4.64 1.28 0.27 0.55 0.67 1.13 94% TBB 16 4.94 3.55 1.03 0.13 0.49 0.81 0.25 81% TCT 16 4.63 3.46 1.01 0.10 0.49 0.88 0.44 88% TTP 16 12.31 9.21 2.27 0.52 0.86 0.40 1.50 100% CSM 16 11.81 9.12 2.20 0.46 0.84 0.47 1.44 100% CVP 20 13.44 8.39 2.29 0.67 0.87 0.22 1.31 100% Mean 16 7.79 4.99 1.52 0.34 0.65 0.54 0.67 0.95 N: number of samples Na: number of alleles, Ne: number of effective alleles, I: Shannon's Information Index, Ho: observed heterozygosity, He: expected heterozygosity, F: fixation index, Pa: number of private alleles, PPL: percent polymorphic loci. GGS - GiddaluruGiddaluruSingasanipalli;NUD-Nellore Udayagiri Devammacheruvu; NAK- Nellore AtmakurKadarinaidupalli ; NVV- Nellore Venkatagiri Vembaluru; NRA- NandyalRudravaramAhobilam North; PPT- ProddaturPorumamillaTekurpeta; PVT- ProddaturVanipentaTippireddypalli; PBB- ProddaturBadvelBalayapalli; KSM- Kadapa SiddavatamMaddur; KVP- Kadapa VempalliPolathala; KKM- Kadapa KadapaMaddimadngu; KRG- Kadapa RayachotiGuvalacheruvu; KOD- Kadapa OntimittaDasarala Doddi; RRS- RajampetRajampet Sri RangarajaPalem; RSJ- RajampetSanipayaJandrapenta; RCV- RajampetChitvelVenkatarajpalli; RKK- Rajampet Kodur K. V. bhavi; TBB- Tirupati BalapalliBalapalli West; TCT- Tirupati ChamalaTalacona centra; TTP- Tirupati TirupatiPapanashini; CSM- Chittoor East SrikalahastiMelachur; CPV- Chittoor East Puttur Vadamala Peta. Table 4: Analysis of molecular variance (AMOVA) for 361 individuals of Pterocarpus santalinus populations. Source Degree of freedom Sum of squares Mean of squares Variance components % of variation Among Populations 21 1591.32 75.77 2.14 28% Within Populations 700 3862.87 5.51 5.51 72% Total 721 5454.19 7.66 100% Table 5: Genetic variation in different girth classes of Pterocarpus santalinus. Girth Class (cm) N Na Ne I Ho He F GC-1 (0-10) 88 32.81 16.62 3.09 0.35 0.94 0.63 GC-2 (10-20) 88.44 32.44 16.73 3.08 0.35 0.94 0.63 GC-3 (20-30) 86.19 32.38 16.68 3.08 0.36 0.94 0.62 GC-4 (30->) 83.38 30.69 16.30 3.05 0.34 0.94 0.64 Mean 86.53 32.08 16.58 3.08 0.35 0.94 0.63 N: mean number of samples, Na: number of alleles, Ne: number of effective alleles, I: Shannon's Information Index, Ho: observed heterozygosity, He: expected heterozygosity, F: fixation index. Table 6: Pearson correlation analysis between genetic diversity and environmental factors. Variable Pearson’s Coefficient Latitude Altitude(m) Annual Temperature Annual Precipitation Relative Humidity Na r 0.405 0.036 0.318 0.655 0.544 p 0.061 0.874 0.149 0.001 0.009 Ho r 0.328 0.136 0.284 0.308 0.283 p 0.136 0.546 0.200 0.163 0.202 He r 0.320 0.083 0.206 0.502 0.391 p 0.146 0.713 0.357 0.017 0.072 I r 0.381 0.036 0.286 0.580 0.473 p 0.080 0.873 0.198 0.005 0.026 F r 0.193 0.217 0.187 0.146 0.130 p 0.391 0.332 0.403 0.517 0.564 Pa r 0.360 0.100 0.085 0.675 0.454 p 0.100 0.657 0.706 0.001 0.034 Na: number of alleles, Ho: observed heterozygosity, He: expected heterozygosity, I: Shannon's Information Index, F: fixation index, Pa: number of private alleles. Table 7: Genetic diversity analysis of Pterocarpus santalinus based on the different forest circlewise distributions in Eastern Ghats, Andhra Pradesh, India. Circle N Na Ne I Ho He F Pa Guntur 68 22.94 11.6 2.63 0.34 0.9 0.63 3.63 Kurnool 137 26.63 10.95 2.67 0.31 0.9 0.65 5.69 Tirupati 140 35.38 14.86 3.01 0.38 0.93 0.59 10.88 Mean 115 28.31 12.47 2.77 0.35 0.91 0.62 6.73 N: mean number of samples, Na: number of alleles, Ne: number of effective alleles, I: Shannon's Information Index, Ho: observed heterozygosity, He: expected heterozygosity, F: fixation index, Pa: number of private alleles. Table 8: Genetic diversity analysis of Pterocarpus santalinus based on the different forest divisionwise distributions in Eastern Ghats, Andhra Pradesh, India Division N Na Ne I Ho He F Pa CTR 33.44 19.69 11.68 2.67 0.58 0.91 0.36 3.19 NLR 53.50 20.62 10.44 2.52 0.37 0.88 0.58 3.37 GDR 14.50 5.87 3.92 1.23 0.20 0.57 0.75 0.19 KDP 78.06 18.56 8.00 2.32 0.34 0.86 0.60 3.19 NDL 15.56 5.19 3.27 1.11 0.16 0.53 0.70 0.19 PDT 44.12 15.69 7.50 2.18 0.32 0.82 0.63 1.69 RJT 61.50 19.56 9.30 2.46 0.37 0.88 0.59 2.44 TPT 45.49 17.62 6.92 2.12 0.25 0.77 0.69 2.50 Mean 43.27 15.35 7.63 2.08 0.32 0.78 0.61 2.09 CTR-Chitoor; NLR-Nellore; GDR-Giddaluru; KDP-Kadapa; NDL- Nandyal; PDT-Podratur; RJT-Rajampet; TPT-Tirupati N: mean number of samples, Na: number of alleles, Ne: number of effective alleles, I: Shannon's Information Index, Ho: observed heterozygosity, He: expected heterozygosity, F: fixation index, Pa: number of private alleles. Additional Declarations No competing interests reported. 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Also discoverable on Platform About Our Team In Review Editorial Policies Advisory Board Help Center Resources Author Services Accessibility API Access RSS feed Manage Cookie Preferences © Research Square 2026 | ISSN 2693-5015 (online) Privacy Policy Terms of Service Do Not Sell My Personal Information {"props":{"pageProps":{"initialData":{"identity":"rs-7357158","acceptedTermsAndConditions":true,"allowDirectSubmit":false,"archivedVersions":[],"articleType":"Research Article","associatedPublications":[],"authors":[{"id":508862694,"identity":"b2565847-e615-4b20-af49-851f52143219","order_by":0,"name":"Mohana Kumara P","email":"data:image/png;base64,iVBORw0KGgoAAAANSUhEUgAAAZAAAAAyAQMAAABI0h/eAAAABlBMVEX///8AAABVwtN+AAAACXBIWXMAAA7EAAAOxAGVKw4bAAABBElEQVRIiWNgGAWjYDADPgglIQciDzwgrMGAgQ2sNEHCGEKToIUhsQHEwKdFt7334OeCmj9ybNLtFz9//GGRPj/s8EOgVjs53QbsWszOnEuWnnHMwJhN5kyxBNBhuRtvpxkAtSQbmx3AoeVGjoE0D5tBYptETgJEy+wEkJYDidtwazH+zfPPoB6oJfkHUEu64ez0D4S0mEnzthkksEmkHwPZkiAvnUPAljNnzKxn9hkbtsmcYbM4kyZhuEE6p+BAggEevxzvMb5d8E1Onl+6/fGNCps6efnZ6Zs/fKiwk8OlBQSYwaQEjwGYNgCrNMCtHEkL+wMwLd+AX/UoGAWjYBSMPAAA4oBhwVFlRYYAAAAASUVORK5CYII=","orcid":"","institution":"University of Horticultural Sciences Bagalkot","correspondingAuthor":true,"prefix":"","firstName":"Mohana","middleName":"Kumara","lastName":"P","suffix":""},{"id":508862695,"identity":"989861de-aa72-43ab-8e0f-d4901bd648bd","order_by":1,"name":"Prabuddha H R","email":"","orcid":"","institution":"Institute of Wood Science and Technology (IWST)","correspondingAuthor":false,"prefix":"","firstName":"Prabuddha","middleName":"H","lastName":"R","suffix":""},{"id":508862696,"identity":"b9ebc756-61c3-4025-8569-63a97dc08f39","order_by":2,"name":"Divakara B N","email":"","orcid":"","institution":"Institute of Wood Science and Technology (IWST)","correspondingAuthor":false,"prefix":"","firstName":"Divakara","middleName":"B","lastName":"N","suffix":""},{"id":508862697,"identity":"2b04a9cf-2870-4c58-93a4-295274b1f50c","order_by":3,"name":"M V Sneha","email":"","orcid":"","institution":"The University of Transdisciplinary Health Sciences and Technology","correspondingAuthor":false,"prefix":"","firstName":"M","middleName":"V","lastName":"Sneha","suffix":""},{"id":508862698,"identity":"908cf9a9-e10e-4932-a665-ad230be9611c","order_by":4,"name":"A H Madhushree","email":"","orcid":"","institution":"The University of Transdisciplinary Health Sciences and Technology","correspondingAuthor":false,"prefix":"","firstName":"A","middleName":"H","lastName":"Madhushree","suffix":""},{"id":508862699,"identity":"277777b5-d7c8-48cf-b346-821ff6f5b0ba","order_by":5,"name":"Chetan H C","email":"","orcid":"","institution":"The University of Transdisciplinary Health Sciences and Technology","correspondingAuthor":false,"prefix":"","firstName":"Chetan","middleName":"H","lastName":"C","suffix":""},{"id":508862700,"identity":"ac0c69b8-48e5-421f-b2cd-7133f6bc7507","order_by":6,"name":"Subrahmanya Kumar K","email":"","orcid":"","institution":"The University of Transdisciplinary Health Sciences and Technology","correspondingAuthor":false,"prefix":"","firstName":"Subrahmanya","middleName":"Kumar","lastName":"K","suffix":""}],"badges":[],"createdAt":"2025-08-12 15:08:12","currentVersionCode":1,"declarations":"","doi":"10.21203/rs.3.rs-7357158/v1","doiUrl":"https://doi.org/10.21203/rs.3.rs-7357158/v1","draftVersion":[],"editorialEvents":[],"editorialNote":"","failedWorkflow":false,"files":[{"id":90667784,"identity":"dcaedf0f-80be-4eeb-86b2-8fa531ddefa6","added_by":"auto","created_at":"2025-09-05 13:02:04","extension":"png","order_by":1,"title":"Figure 1","display":"","copyAsset":false,"role":"figure","size":208867,"visible":true,"origin":"","legend":"\u003cp\u003eGeographical distribution of 22 populations of \u003cem\u003ePterocarpus santalinus\u003c/em\u003ein the Estern Ghats, Andhra Pradesh, India\u003c/p\u003e","description":"","filename":"1.png","url":"https://assets-eu.researchsquare.com/files/rs-7357158/v1/91623e30b59eb8bc117a3104.png"},{"id":90667433,"identity":"4ae83d07-9a99-4863-aefa-48cfa0b3c4b5","added_by":"auto","created_at":"2025-09-05 12:54:04","extension":"png","order_by":2,"title":"Figure 2","display":"","copyAsset":false,"role":"figure","size":122608,"visible":true,"origin":"","legend":"\u003cp\u003eNumber of rare and unique alleles among the 22 populations of \u003cem\u003ePterocarpus santalinus\u003c/em\u003e\u003c/p\u003e","description":"","filename":"2.png","url":"https://assets-eu.researchsquare.com/files/rs-7357158/v1/154c70d4c4b5162ae46b9a8a.png"},{"id":90667442,"identity":"50cb648a-a7b9-42e7-8bb5-89720fbc70a6","added_by":"auto","created_at":"2025-09-05 12:54:04","extension":"png","order_by":3,"title":"Figure 3","display":"","copyAsset":false,"role":"figure","size":485453,"visible":true,"origin":"","legend":"\u003cp\u003eSTRUCTURE bar graph representing three genetic clusters (ΔK = 3) among 22 populations of \u003cem\u003ePterocarpus santalinus\u003c/em\u003e. Each vertical bar represents an individual sample, and the color of the bar indicates the assignment probability of that individual belonging to one of the three identified clusters (designated by different colors).\u003c/p\u003e","description":"","filename":"3.png","url":"https://assets-eu.researchsquare.com/files/rs-7357158/v1/61323540a8d72de86566a128.png"},{"id":90667783,"identity":"e0d5db93-7472-4a19-961a-6a9c24e21d99","added_by":"auto","created_at":"2025-09-05 13:02:04","extension":"png","order_by":4,"title":"Figure 4","display":"","copyAsset":false,"role":"figure","size":870479,"visible":true,"origin":"","legend":"\u003cp\u003eNeighbor-joining tree for 361 individuals of \u003cem\u003ePterocarpus santalinus\u003c/em\u003e. Each color depicts a cluster. The numbers indicate the percentage of bootstrap support using 10000 replications.\u003c/p\u003e","description":"","filename":"4.png","url":"https://assets-eu.researchsquare.com/files/rs-7357158/v1/88af3592a5dc63bce610ed49.png"},{"id":90667445,"identity":"3cdfdfe9-7676-4b01-b1d3-c8de347677a9","added_by":"auto","created_at":"2025-09-05 12:54:05","extension":"png","order_by":5,"title":"Figure 5","display":"","copyAsset":false,"role":"figure","size":85633,"visible":true,"origin":"","legend":"\u003cp\u003ePrincipal coordinate analysis (PCoA) based on pairwise F\u003csub\u003eST\u003c/sub\u003e, Coord.1 (16.04%): The first principal coordinate explained 16.04% of the variation; Coord.2 (9.95%): The second principal coordinate explained 9.95% of the variation.\u003c/p\u003e","description":"","filename":"5.png","url":"https://assets-eu.researchsquare.com/files/rs-7357158/v1/3f73b1547bba1774850e3968.png"},{"id":90667416,"identity":"6943cd16-99c0-40ff-9234-ce2b590ff577","added_by":"auto","created_at":"2025-09-05 12:54:03","extension":"png","order_by":6,"title":"Figure 6","display":"","copyAsset":false,"role":"figure","size":53859,"visible":true,"origin":"","legend":"\u003cp\u003eMantel tests for relationships between pairwise F\u003csub\u003eST\u003c/sub\u003e matrix and geographic distance for \u003cem\u003ePterocarpus santalinus\u003c/em\u003e natural populations (R\u003csup\u003e2\u003c/sup\u003e = 0.6861, p \u0026gt; 0.05).\u003c/p\u003e","description":"","filename":"6.png","url":"https://assets-eu.researchsquare.com/files/rs-7357158/v1/b759d7f0fc57fc8e7d44b4e3.png"},{"id":90667420,"identity":"d147e66f-6eb4-4a29-a2db-eaae1705209a","added_by":"auto","created_at":"2025-09-05 12:54:03","extension":"png","order_by":7,"title":"Figure 7","display":"","copyAsset":false,"role":"figure","size":423515,"visible":true,"origin":"","legend":"\u003cp\u003eGenetic diversity indices across the different soil type (a to f) distributions of \u003cem\u003ePterocarpus santalinus\u003c/em\u003e populations. g. Distribution of \u003cem\u003ePterocarpus santalinus \u003c/em\u003epopulations with respect to soil type in Eastern Ghats, Andhra Pradesh, India.\u003c/p\u003e","description":"","filename":"7.png","url":"https://assets-eu.researchsquare.com/files/rs-7357158/v1/ce4a3fff4410412e8b13d9d4.png"},{"id":90668731,"identity":"e0acb8c4-a0f4-4136-8466-1c9523828c8d","added_by":"auto","created_at":"2025-09-05 13:10:05","extension":"pdf","order_by":0,"title":"","display":"","copyAsset":false,"role":"manuscript-pdf","size":4118792,"visible":true,"origin":"","legend":"","description":"","filename":"manuscript.pdf","url":"https://assets-eu.researchsquare.com/files/rs-7357158/v1/fbb380a4-2bd6-4cf3-bca2-e15d669070aa.pdf"},{"id":90667409,"identity":"b431e35d-896e-4504-9329-58bc15235263","added_by":"auto","created_at":"2025-09-05 12:54:01","extension":"docx","order_by":1,"title":"","display":"","copyAsset":false,"role":"supplement","size":4206337,"visible":true,"origin":"","legend":"","description":"","filename":"Figuressupply.docx","url":"https://assets-eu.researchsquare.com/files/rs-7357158/v1/7e08eeee98fceffca01652cb.docx"}],"financialInterests":"No competing interests reported.","formattedTitle":"Genetic diversity and population structure analysis of the endangered endemic and economically important plant, Red Sanders, distributed in the Eastern Ghats. India","fulltext":[{"header":"1. Introduction","content":"\u003cp\u003e\u003cem\u003ePterocarpus santalinus\u003c/em\u003e, commonly known as Red Sanders, is a forest tree species that is found exclusively in the Eastern Ghats of Andhra Pradesh, India. It is an endangered species with a naturally limited distribution range. \u003cem\u003eP. santalinus\u003c/em\u003e, a member of the Fabaceae family, is a slow-growing tree species that relies on cross-pollination and insects for reproduction [\u003cspan citationid=\"CR54\" class=\"CitationRef\"\u003e54\u003c/span\u003e]. In natural forests, it typically takes between 50 and 60 years for a pole-sized tree (measuring 30 cm girth at breast height or 173 cm from the ground) to achieve a harvestable girth of 70 cm. This species has been prized for centuries for its dyeing properties, traditional medicinal uses, and use as a source of timber. The heartwood of the tree boasts a reddish-brown hue, a distinctive wavy grain, and exceptional durability. Presently, \u003cem\u003eP. santalinus\u003c/em\u003e heart wood is highly valued on the global market [\u003cspan citationid=\"CR2\" class=\"CitationRef\"\u003e2\u003c/span\u003e, \u003cspan citationid=\"CR53\" class=\"CitationRef\"\u003e53\u003c/span\u003e, \u003cspan citationid=\"CR67\" class=\"CitationRef\"\u003e67\u003c/span\u003e]. The legal trade of seized wood is currently limited to occasional sales through the Forest Departments of Andhra Pradesh (APFD), Tamil Nadu, and Karnataka (NDF, 2019). This includes a range of products, such as wood chips, extracts, timber, and wood carvings. According to a report by the APFD, the auction of 8179.85 MT of seized wood from 2005\u0026ndash;2018-19 generated revenue of Rs.1688.24 crores. However, there is still a balance of 6285.909 MT of wood waiting for auctions in the APFD alone [\u003cspan citationid=\"CR26\" class=\"CitationRef\"\u003e26\u003c/span\u003e]. This species is highly vulnerable because of the overharvesting of mature trees from the wild due to the continued high demand for timber [\u003cspan citationid=\"CR2\" class=\"CitationRef\"\u003e2\u003c/span\u003e]. In 1988, the species was listed as endangered and categorized under the A2cd criterion [\u003cspan citationid=\"CR28\" class=\"CitationRef\"\u003e28\u003c/span\u003e, \u003cspan citationid=\"CR3\" class=\"CitationRef\"\u003e3\u003c/span\u003e], which explains habitat loss and population size reduction in the natural distributions of Eastern Ghats, India. The species is listed in Appendix II of the Convention for International Trade in Endangered Species of Wild Fauna and Flora (CITES) in 1995 because of its declining population and restricted distribution. Recently, a drastic decline (7.8\u0026ndash;3.9%) in the number of harvestable trees (GBH\u0026thinsp;\u0026gt;\u0026thinsp;70 cm) has been observed within the last six years [\u003cspan citationid=\"CR3\" class=\"CitationRef\"\u003e3\u003c/span\u003e, \u003cspan citationid=\"CR25\" class=\"CitationRef\"\u003e25\u003c/span\u003e]. One reason for the decline of this species is the hot and dry conditions of its natural habitat, which put its pollination ecology at risk. The tree blooms during the dry season. Its yellow flowers attract honey bees, especially \u003cem\u003eApis dorsata\u003c/em\u003e, which are the primary pollinators. The other two species, \u003cem\u003eA. indica\u003c/em\u003e and \u003cem\u003eA. florea\u003c/em\u003e, visit only in the early morning. This tree mainly prevents the growth of fruits from self-pollinated flowers, and only 6% of flowers grow into fruits due to various factors [\u003cspan citationid=\"CR55\" class=\"CitationRef\"\u003e55\u003c/span\u003e].\u003c/p\u003e\u003cp\u003eGenetic diversity plays a crucial role in biodiversity, influencing how well a species can adapt to environmental challenges and changes [\u003cspan citationid=\"CR22\" class=\"CitationRef\"\u003e22\u003c/span\u003e, \u003cspan citationid=\"CR40\" class=\"CitationRef\"\u003e40\u003c/span\u003e]. By measuring the genetic diversity within a species, we gain valuable insights into its evolution and the variations in its genetic makeup [\u003cspan citationid=\"CR4\" class=\"CitationRef\"\u003e4\u003c/span\u003e, \u003cspan citationid=\"CR44\" class=\"CitationRef\"\u003e44\u003c/span\u003e]. Genetic variation among and within populations of various plant species has been studied extensively molecular markers over the last three decades. In recent years, advanced molecular tools and next-generation sequencing (NGS) technologies have helped us discover robust molecular markers and use these markers to elucidate genetic variation in tree species [\u003cspan citationid=\"CR15\" class=\"CitationRef\"\u003e15\u003c/span\u003e]. Among the molecular markers available, microsatellites or simple sequence repeats (SSRs) are often preferred because they are highly mutated, generate multiple allelic forms and mutations per locus per generation, and are codominant [\u003cspan citationid=\"CR18\" class=\"CitationRef\"\u003e18\u003c/span\u003e, \u003cspan citationid=\"CR69\" class=\"CitationRef\"\u003e69\u003c/span\u003e]. The combination of both characteristics allows them to be used as a sensitive tool for assessing genetic diversity among species, determining population structure, reconstructing phylogenetics, genetic mapping, evolutionary analyses, and molecular breeding [\u003cspan citationid=\"CR59\" class=\"CitationRef\"\u003e59\u003c/span\u003e]. In practice, SSRs are popular, simple to implement, and reproducible in most research environments because they require minimal resources (i.e., technical skills, laboratory equipment, and consumables) [\u003cspan citationid=\"CR46\" class=\"CitationRef\"\u003e46\u003c/span\u003e]. Despite being a highly economically valuable tree species, very few studies have been reported on \u003cem\u003eP. santalinus\u003c/em\u003e via the use of DNA molecular markers. However, recent advancements in next-generation sequencing (NGS) have made it possible to sequence transcriptomes and whole genomes \u003cem\u003ede novo\u003c/em\u003e [\u003cspan citationid=\"CR1\" class=\"CitationRef\"\u003e1\u003c/span\u003e, \u003cspan citationid=\"CR63\" class=\"CitationRef\"\u003e63\u003c/span\u003e]. Previous genetic diversity studies have used molecular markers such as RAPD and ISSRs, which are dominant, nonlocus-specific, and have poor reproducibility. Moreover, past studies have used small sample sizes that do not represent the entire range of species distributions. However, this study emphasized covering the entire species distribution range of red sanders in close association with field officers of the Andhra Pradesh Forest Department. This study analyzed the genetic variation and population structure of \u003cem\u003eP. santalinus\u003c/em\u003e across 22 populations using 16 SSR markers and identified genetic diversity hotspots of high conservation importance.\u003c/p\u003e"},{"header":"2. Materials and Methodology","content":"\u003cp\u003e\u003cstrong\u003e2.1 Study area:\u003c/strong\u003e We conducted a literature survey and consulted with the forest department officials of Andhra Pradesh to sample pristine forest tracts in each forest range within the natural habitat of \u003cem\u003eP. santalinus\u003c/em\u003e. The state of Andhra Pradesh has been divided into 5 territorial circles, one wildlife circle, and one project tiger circle for administration and forest management. At the divisional level, there are 32 territorial divisions, two wildlife divisions, and 13 social forestry divisions. There are also 10 social forestry divisions. The Andhra Pradesh Forest Department (APFD) has a total of 2,312 beats, 996 sections, and 295 ranges according to the available data [26]. The study was conducted in the Middle to Southern Eastern Ghats and covered five districts of Andhra Pradesh, located between latitude 13\u0026deg;32\u0026apos;14.1\u0026apos;\u0026apos;N and longitude 79\u0026deg;36\u0026apos;04.1\u0026apos;\u0026apos;E to 15\u0026deg;29\u0026apos;77.4\u0026apos;\u0026apos;N and 79\u0026deg;12\u0026apos;81.7\u0026apos;\u0026apos;E. We selected 22 forest ranges/populations under the Kurnool, Tirupati, and Guntur Circles in Andhra Pradesh, India, for sample collection (Table 1, Fig. 1). These circles include the endemic region of \u003cem\u003eP. santalinus\u003c/em\u003e, which is categorized under dry deciduous forests [13]. The forests in these regions have both pure stands of \u003cem\u003eP. santalinus\u0026nbsp;\u003c/em\u003eand mixed associations, and we considered the distinctness of the forest patch in terms of altitude and the edaphic nature of the locality when sampling the closely located forest tracts.\u0026nbsp;To facilitate efficient study management and organizational ease, we established each range (Table 1 and Fig. 1) as a distinct population unit.\u0026nbsp;Leaf samples of\u003cstrong\u003e\u0026nbsp;\u003c/strong\u003e\u003cem\u003ePterocarpus santalinus\u003c/em\u003e were collected from the \u0026nbsp;Eastern Ghats of Andhra Pradesh, India. The plant material was identified by Divakara, BN, a scientist at IWST in Bengaluru, and a voucher specimen has been deposited at TDU/IWST, Bengaluru (IWST-NBA-01 to 400). Only leaf samples were collected without harming the tree, and their reproducibility. Collected samples were stored in deep freezers at IWST, Bengaluru.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e2.2. Study material:\u0026nbsp;\u003c/strong\u003eFrom each forest range, an undisturbed natural forest area was selected for sampling. Fresh leaf samples were collected from four different girth classes. Seedlings and saplings with girth at breast height (GBH 1.37 m from the ground) up to 10 cm; young trees with a GBH of 10 to 20 cm; trees with a GBH of 20 to 30 cm; and mature trees with a GBH greater than 30 cm. A total of 4 to 5 plants were randomly selected for leaf sampling from each girth class.\u0026nbsp;Eight to ten young leaves were selected per sample from each selected tree, and stored in\u0026nbsp;a zip-lock cover containing silica gel. We collected\u0026nbsp;~16 to 20 individuals per population. A total of 361 individual leaf samples were collected from 22 populations. After the surface moisture in the silica gel was removed, the samples were transferred to -800\u0026deg;C for further storage and\u0026nbsp;use. Geo-coordinates and altitudes\u0026nbsp;were recorded using hand-held GPS instruments.\u0026nbsp;The presence of the species at different altitudes and soil types was taken into account whenever the sampled forest patches of two different ranges were situated in proximity. Each sampled population was designated with acronyms formed with the first letter from the respective names of Forest Division, Forest Range, and Forest Beat (Table 1).\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e2.3. DNA isolation, PCR, and genotyping of SSR markers:\u0026nbsp;\u003c/strong\u003eWe used the CTAB protocol described by Doyle and Doyle [16] to isolate DNA. For DNA amplification, we used 50\u0026ndash;100 ng of genomic DNA and 5 picomoles of M13-tailed markers in a 20 \u0026micro;l reaction mixture. The amplified samples were subsequently subjected to fragment analysis. Our previous publication [63] described in detail the protocols for DNA isolation, PCR conditions, and fragment analysis. In the present study, 16 highly polymorphic SSR loci (Table S1) were used to analyze the 361 samples from 22 different populations of \u003cem\u003eP. santalinus\u003c/em\u003e. These loci had a polymorphism information content (PIC) greater than 0.9 [63].\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e2.4. Genetic diversity and population structure analysis:\u0026nbsp;\u003c/strong\u003eThe raw genotyping data were analyzed via Peak Scanner software (Applied Biosystems, California, USA) [61]. The samples were categorized into different groups on the basis of their forest circle, division, population, girth class, and geographic distance (determined by their latitude and longitude). The allelic data for each group were then analyzed statistically. GenAlEx v.6.5. [49] was used to calculate various parameters, such as the number of alleles (Na), the number of effective alleles (Ne), the polymorphism information content (PIC), the observed heterozygosity (Ho), the expected heterozygosity (He), Shannon\u0026rsquo;s information index (I), the coefficient of genetic differentiation (F\u003csub\u003eST\u003c/sub\u003e), the gene flow (Nm) and analysis of molecular variance (AMOVA), to analyze genetic variation among the populations. Within populations, principal coordinate analysis (PCoA) based on the genetic distance matrix and the Mantel test were used to determine the correlation between geographic and genetic distances [49].\u003c/p\u003e\n\u003cp\u003eWe applied Bayesian model-based cluster analysis via STRUCTURE 2.3.4 software [51] to determine population structure. The number of subgroups (K) was estimated to be 2 to 10 runs. Ten runs were performed on each K value, with a 10,000 iteration burn-in period followed by 10,000 Monte Carlo Markov chain (MCMC) replicates. The best K value was selected by Structure Harvester [17] based on the maximum ∆K [20] value. Cluster analysis was carried out by DARwin 6 software to construct a dendrogram via the unweighted neighbor-joining (UNJ) method with 10,000 bootstraps [50]. AMOVA was used to analyze the genetic variation among and within populations for all grouped data. Principal coordinate analysis (PCoA) was performed on the basis of the genetic distance matrix across 22 populations. A Mantel test was conducted using GenAlEx v.6.5 to determine the correlation between geographic and genetic distances [49].\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e2.5. Genetic diversity combined with ecological factors:\u0026nbsp;\u003c/strong\u003eTo comprehensively understand the ecological factors influencing genetic diversity and population clusters, we carefully examined several key factors. This involved considering factors such as elevation, soil type, annual precipitation, and temperature during the sampling process. We recorded GPS location and elevation data for each sample and determined the soil type through ground truth observations and a literature review. Additionally, we gathered information from NASA [29] regarding the mean annual precipitation, mean annual temperature, mean annual relative humidity, and mean annual wind direction for each population from 1981--2023. To identify the soil type in 22 sampling populations, we utilized a soil map available at https://www.fao.org [27]. Furthermore, we conducted a comparative analysis of genetic diversity parameters across environmental factors.\u003c/p\u003e"},{"header":"3. Results","content":"\u003cp\u003e\u003cstrong\u003e3.1. Genetic variation:\u0026nbsp;\u003c/strong\u003eTwenty-two populations of \u003cem\u003eP. santalinus\u0026nbsp;\u003c/em\u003efrom Eastern Ghats were analyzed for genetic diversity and population structure via 16 highly polymorphic SSR markers [63] (Table S1). Among these loci, PIN-82 presented the highest value for all diversity indices: number of alleles (Na) = 12.82, effective number of alleles (Ne) = 8.85, expected heterozygosity (He) = 0.87, and observed heterozygosity (Ho) = 0.70. On the other hand, the PSSSR-2 locus had the lowest values for the same indices: Na=3.77, Ne=2.34, He=0.36, and Ho=0.12. Across all the loci, the average expected value for He was 0.65, whereas the average Ho was 0.34. Additionally, the PSSSR-32 locus had the highest PIC value (0.96), whereas the PSSSR-2 locus had the lowest PIC value among the 16 loci (0.91) (Table 2). The CPV population presented the highest Na value at 13.44, whereas the TCT population presented the lowest Na value at 4.63. On the other hand, TTP had the highest Ne value at 9.21, whereas NRA had the lowest at 3.27. The average He was 0.65, with the CPV again having the highest value of 0.87 and the PVT having the lowest value of 0.44. The Ho values ranged from 0.673 (CPV) to 0.10 (TCT), with an average of 0.34 (Table 3).\u003c/p\u003e\n\u003cp\u003e3.2. \u003cstrong\u003eRare and private alleles across different populations\u003c/strong\u003e: This study revealed rare alleles, which are common in less than 25% of populations, as well as population-specific alleles or private alleles (PAs), which are unique to a single population (Fig. 2). Loci PSSSR-24 and PSSSR-26 presented the greatest number of rare alleles (Fig S1). Among the populations, CVP had the highest number of rare alleles at 6.62, followed by TTP and CSM at 6.50 and 6.625, respectively. Across 16 highly polymorphic loci, 236 Pa were detected. The maximum number of Pa was found in the PSSSR-31, and the minimum was found in the PSSSR-18. On average, 0.67 private alleles (PAs) were found from 22 populations, ranging from 0.188 to 2.125. The NAG, TTP, CSM, and CPV populations contained the maximum number of Pa, with values of 2.12, 1.50, 1.44, and 1.31, respectively (Table 3). This study demonstrated clear genetic variation among populations from varying latitudes. Three primary groups, L1 (14.5--15.3\u0026deg;N), L2 (14.0--14.5\u0026deg;N), and L3 (13.0--13.9\u0026deg;N), were identified in this study, with each group having a cluster of alleles unique to the given latitude. The L1 group was composed of 105 alleles specific to this latitudinal group. These alleles are genetic variations that do not exist in other populations. The L2 group, in a similar vein, presented characteristics of 124 such alleles at this latitude, whereas the L3 group presented 142 alleles specific to its latitude. Compared with the other two groups, the L3 group presented a greater number of private alleles (Table S2; Fig S2).\u003c/p\u003e\n\u003cp\u003e3.3. \u003cstrong\u003eGenetic differentiation\u003c/strong\u003e: The inbreeding coefficient (Fis) ranged between 0.80 (PSSSR-72) and 0.19 (PIN-82), with a mean of 0.50. F statistics for each locus in the species revealed significant differences in the genetic differentiation coefficient (FST) and gene flow (Nm) at the locus level (Table 2). Furthermore, when the genetic differentiation coefficient (FST) and gene flow (Nm) among populations were compared, the average FST was 0.31, indicating moderate genetic differentiation. The Nm value ranged from 0.32 to 2.92, with a mean of 0.82, indicating a low rate of gene flow (Table 2). Analysis of molecular variance (AMOVA) with 999 permutations revealed 73% genetic variation within populations and 27% genetic variation between populations (Table 4). Additionally, FST =0.27 (P=0.001) indicated a significant genetic difference among the 22 populations of \u003cem\u003eP. santalinus\u003c/em\u003e. The pairwise FST ranged between 0.049 and 0.427. The highest level appeared between PVT and TBB, whereas the lowest was between populations of TTP and CVP (Table S3).\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e3.4. Genetic Structure and Cluster Analysis:\u0026nbsp;\u003c/strong\u003eThe structural analysis revealed a maximum \u0026Delta;K=3. All 22 populations were grouped into three distinct genetic clusters (Fig. 3). Cluster I (red) contained 136 individuals from 8 populations (NRA, KOD, TBB, TCT, TTP, CSM, CPV, and NAK). Cluster II (green) contained 115 individuals from 7 populations (KVP, KSM, KRG, KKM, RRS, RCV, and NVV). Cluster III (blue) contained 110 individuals from 7 populations (PVT, PPT, PBB, RSJ RKK, GGS, and NVD). UNJ tree analysis also grouped the 361 individuals from 22 populations into three main clusters. Compared with the structure analysis, there was little difference in population grouping. Cluster I included four populations, Cluster II had seven, and Cluster III contained eleven populations (Fig. 4). An analysis of the codominant alleles via PCoA was conducted to compare the structural and UNJ analyses. The first two principal coordinates captured 35.56% of the information, with individual contributions of 16.04% and 9.95% (Fig. 5). Mantel tests were conducted to analyze the relationships between geographic distance and pairwise Fst (Fig. 7), uNeiP (Fig. S3a), and genetic distance (Supplementary Fig. 3 b, c and d) in 22 \u003cem\u003eP. santalinus\u0026nbsp;\u003c/em\u003epopulations. The results indicated that genetic distance (90%) contributed more substantially to the genetic differentiation among the populations than did geographic distance (70%). Therefore, it is evident that there was no clear geographic origin-based structuring or predominant isolation by distance among the studied populations (Fig 6).\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e3.5. Genetic variation among the different girth classes:\u0026nbsp;\u003c/strong\u003eGenetic diversity analysis was conducted across four girth classes: seedlings and saplings, young trees with a GBH of 10--20 cm, young trees with a GBH of 20--30 cm, and mature trees (\u0026gt;30 cm). The purpose was to observe differences in genetic fitness among the four girth classes potentially impacted by the illegal harvesting of adult trees. The data revealed that the number of alleles (Na) ranged from 30.69 to 32.81, whereas the number of effective alleles (Ne) varied between 16.30 and 16.73 (Table 5). The Ho values ranged from 0.34 to 0.36, and He remained constant at 0.94. Additionally, the data revealed a mean fixation index (F) of 0.63. These findings suggest that there is no noteworthy difference in genetic diversity among the four girth classes.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e3.6. Correlations between genetic diversity and environmental factors:\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eA statistical analysis (Table 6) was used to explore the relationships between genetic diversity and environmental factors. Data collected on four environmental variables during the period 1980--2022 were plotted against populations (https://power.larc.nasa.gov/data-acce). The annual mean temperature varied from 26.23\u003csup\u003e0\u003c/sup\u003eC (RRS and RSJ) to 27.68\u003csup\u003e0\u003c/sup\u003eC (NAK) (Fig. S4a). There was a wide range of relative humidities between 62.86% (KKM/KOD/KRG/KSM/KVP) and 69.19% (TTP and CPV)\u0026nbsp;\u003cstrong\u003e(\u003c/strong\u003eFig. S4b\u003cstrong\u003e)\u003c/strong\u003e. The wind direction varied from 222.4 (GGS) to 264.6 degrees (TTP and CPV)\u003cstrong\u003e\u0026nbsp;(\u003c/strong\u003e\u003cstrong\u003eFig. S4c)\u003c/strong\u003e. Between 0.32 mm (KOD) and 1.67 mm (TTP and CPV) of precipitation were recorded (Fig. S4d). Populations with high genetic diversity experienced mean temperatures ranging from 26.5\u0026deg;C (CPV and TTP) to 26.90\u0026deg;C (CSM). The altitude and latitude were not significantly correlated with most of the genetic parameters studied (Fig. S5a-f: Fig. S6 a-f). Similarly, the annual mean temperature did not significantly correlate with the genetic parameters (Fig. S7 a-f). The population of Na increased with increasing relative humidity (R2=0.30, p\u0026lt;0.05) and annual precipitation (R2=0.43, p\u0026lt;0.05) (Fig. S9a, 10a). Additionally, Shannon\u0026apos;s information index (I) was correlated with relative humidity (R2=0.22, p\u0026lt;0.05) and annual precipitation (R2=0.34, p\u0026lt;0.05) (Fig. S9b, 10b). Between 0.32 mm (KOD) and 1.67 mm (TTP and CPV) of precipitation were recorded (Fig. S4d). Populations with high genetic diversity experienced mean temperatures ranging from 26.5\u0026deg;C (CPV and TTP) to 26.90\u0026deg;C (CSM). The altitude and latitude were not significantly correlated with most of the genetic parameters studied (Fig. S5a-f: Fig. S6 a-f). Similarly, the annual mean temperature did not significantly correlate with the genetic parameters (Fig. S7 a-f). The population of Na increased with increasing relative humidity (R2=0.30, p\u0026lt;0.05) and annual precipitation (R\u003csup\u003e2\u003c/sup\u003e=0.43, p\u0026lt;0.05) (Fig. S9a, S10a). Additionally, Shannon\u0026apos;s information index (I) was correlated with relative humidity (R\u003csup\u003e2\u003c/sup\u003e=0.22, p\u0026lt;0.05) and annual precipitation (R\u003csup\u003e2\u003c/sup\u003e=0.34, p\u0026lt;0.05) (Fig. S8b, 9b). The Na population increased in correlation with both increasing relative humidity (R2=0.30, p\u0026lt;0.05) and annual precipitation (R2=0.43, p\u0026lt;0.05; Figures 8a and 9a). Similarly, the Shannon\u0026apos;s information index (I) was correlated with relative humidity (R2=0.22, p\u0026lt;0.05) and annual precipitation (R2=0.34, p\u0026lt;0.05; Fig. S8b and S9b). However, there was no significant relationship between the Ho or fixation index and either the mean relative humidity or the annual precipitation (Fig. S8c, S9c; Fig. S9e). On the other hand, He was significantly related to annual precipitation (R\u003csup\u003e2\u003c/sup\u003e=0.25, p\u0026lt;0.05; Fig. S8d and S9d). Additionally, Pa was significantly correlated with both relative humidity (R\u003csup\u003e2\u003c/sup\u003e=0.21, p\u0026lt;0.05) and annual precipitation (R2=0.46, p\u0026lt;0.05; Figures S8f and 9f; Table 6). An analysis of the locations of different populations with a soil map revealed that 20 out of 22 populations were situated on Lithosols (Fig. 7a), with one population each on Chromic Luvisols (PPT) and Verticcambisols (TTP). A noticeable pattern emerged, revealing an increase in genetic diversity from Lithosols to Verticcambisols (Fig. 7 b-g). Interestingly, the three populations with the highest genetic diversity consisted of two populations (CPV and CSM) situated on Lithosols and one population (TTP) on Verticcambisols. This trend in genetic diversity parameters from Lithosols to Verticcambisols provides valuable preliminary insights (Fig. 7b-g).\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e3.7. Genetic diversity analysis was performed on the basis of the different forest classifications.\u0026nbsp;\u003c/strong\u003eThe Forest Department of Andhra Pradesh classified the distribution of \u003cem\u003eP. santalinus\u003c/em\u003e into different circles and divisions in Eastern Ghats (Fig. S11 and S12). Analysis of genetic diversity by circle revealed that the Tirupati circle had the highest Na (35.38), whereas the Guntur circle had the lowest (22.94). However, Guntur had a greater Ne of 11.60 than the Kurnool did, despite the latter having a slightly greater Ne (Table 7, Fig. S11). This trend was also observed in Ho. Despite the small difference in sample size between the Kurnool and Tirupati populations, the private alleles found differed significantly (5.69--10.88). Additionally, although the population size of the Guntur circle was half that of the Kurnool, all the genetic diversity parameters were nearly equal to or greater than those of the Kurnool circle. These results clearly indicate that Tirupati has the highest diversity, followed by the Guntur and Kurnool circles. There was a significant difference in the number of individuals (N) among the different divisions (Table 8, Fig. S12). Kadapa had the greatest population size, with 78 individuals, whereas Giddaluru and Nandyal had only 14 individuals. Divisions such as Chitoor, Nellore, and Rajampet had high N values, leading to higher allele frequencies than those of other divisions. As expected, Giddaluru and Nandyal presented relatively low Ne values. Among all the divisions, Chitoor had the highest He value (0.91), whereas Nandyal (0.53) had the lowest genetic diversity. The Chittoor division had a low (fixation index) F value of 0.36, whereas the Giddaluru division had a high F value of 0.75. The Nellore and Rajampet division populations had a high number of private alleles, which indicates a unique set of alleles in their genetic makeup.\u003c/p\u003e\n\u003cp\u003eThe Forest Department of Andhra Pradesh classified the distribution of \u003cem\u003eP. santalinus\u003c/em\u003e into different circles and divisions in the Eastern Ghats (Figs. S11 and S12). Through genetic diversity analysis, it was found that the Tirupati circle had the highest Na (35.38), whereas the Guntur circle had the lowest (35.38). However, Guntur had a greater Ne (11.60) than did Kurnool, despite Kurnool having a slightly greater Ne (Table 7; Fig. S11).\u0026nbsp;Despite the small difference in sample size between the Kurnool and Tirupati populations, the private alleles found differed significantly (5.69--10.88). This trend was also observed in Ho. Even though the population size of the Guntur circle was half that of the Kurnool, all the genetic diversity parameters were nearly equal to or greater than those of the Kurnool circle.\u003c/p\u003e\n\u003cp\u003eTherefore, Tirupati clearly has the highest diversity, followed by the Guntur and Kurnool circles. There was a significant difference in the number of individuals among the different divisions (Table 8, Fig. S12). Kadapa had the greatest population size, whereas Giddaluru and Nandyal had the lowest. The Chitoor division had the highest He value (0.91), whereas the Nandyal division (0.53) had the lowest genetic diversity. The Chittoor division had a low F value of 0.36, whereas the Giddaluru division had a high F value of 0.75. The Nellore and Rajampet division populations had a high number of private alleles, indicating a unique set of alleles in their genetic makeup.\u003c/p\u003e"},{"header":"4. Discussion","content":"\u003cp\u003e\u003cstrong\u003e4.1. Genetic diversity of \u003cem\u003eP. santalinus\u003c/em\u003e:\u0026nbsp;\u003c/strong\u003e\u003cem\u003eIn India,\u0026nbsp;\u003c/em\u003e\u003cem\u003eP. santalinus\u003c/em\u003e\u003cem\u003e\u0026nbsp;is a valuable tree species that is in decline due to its valuable heartwood, compromising its genetic diversity\u003c/em\u003e\u003cem\u003e.\u0026nbsp;\u003c/em\u003eGenetic diversity is crucial for long-term survival and genetic improvement of a species through breeding [19, 34, 57]. To protect and preserve this species, effective conservation and management strategies have been developed using molecular markers [7, 5, 67]. Earlier studies focused on understanding genetic variations via dominant markers such as RAPD. Micropropagated \u003cem\u003eP. santalinus\u003c/em\u003e individuals showed no genetic variation with RAPD markers [10], and significant DNA polymorphisms were detected in natural accessions [47] and nursery-grown plants [68]. These studies used small sample sizes, and dominant markers may have limitations in accurately capturing the total genetic diversity of the species.\u0026nbsp;In this study, 16 highly polymorphic simple sequence repeats (SSRs) were used to assess the genetic diversity of \u003cem\u003eP. santalinus\u003c/em\u003e across different populations. The present study revealed a total of 749 alleles among 361 individuals, which is considerably greater than the number of alleles obtained from 13 EST-SSRs. The genetic diversity values in this study were greater than those reported via EST-SSRs in \u003cem\u003eP. santalinus\u0026nbsp;\u003c/em\u003eand SSRs in \u003cem\u003eP. erinaceous\u003c/em\u003e [1]. Two hundred thirty-seven alleles obtained from 17 SSRs were amplified across 365 individuals of \u003cem\u003eP. erinaceus\u0026nbsp;\u003c/em\u003e[31], as were the 54 alleles detected from 19 SSRs in 42 individuals of \u003cem\u003eDalbergia odorifera\u0026nbsp;\u003c/em\u003e[38].\u003c/p\u003e\n\u003cp\u003eOur study revealed moderate genetic diversity values, with observed and expected heterozygosity values of 0.34 and 0.65, respectively. These values are relatively low compared with those of widely spread hardwood species such as \u003cem\u003eSwietenia macrophylla\u003c/em\u003e (He=0.78) [36], \u003cem\u003eEucalyptus globulus Labill\u003c/em\u003e (He= 0.82) [66], \u003cem\u003eE. grandis\u003c/em\u003e (He=0.77) [64], \u003cem\u003eTectona grandis\u003c/em\u003e (He=0.77) [21], and \u003cem\u003eT. grandis\u003c/em\u003e L. (He=0.94) [39]. Low values coincide with the general belief that narrow-ranged species generally have lower genetic diversity than widespread congeners do [14]. These values were higher than those reported in studies within the genus \u003cem\u003ePterocarpus\u003c/em\u003e, specifically EST-SSRs in \u003cem\u003eP. santalinus\u0026nbsp;\u003c/em\u003e(He=0.322) [1] and SSRs in \u003cem\u003eP. erinaceous\u003c/em\u003e (He= 0.57) [31]. Among\u0026nbsp;the 22 populations studied,\u0026nbsp;the CPV\u0026nbsp;population\u0026nbsp;presented\u0026nbsp;the highest genetic diversity,\u0026nbsp;whereas\u0026nbsp;the TCT population\u0026nbsp;presented\u0026nbsp;the lowest genetic diversity. The low genetic diversity values in\u0026nbsp;the TCT can be attributed to forest fragmentation, the presence of agricultural land near this population, and anthropological activities,\u0026nbsp;which led\u0026nbsp;to genetic bottlenecks and reduced genetic diversity due to the loss of natural habitat and gene flow barriers\u003cem\u003e.\u0026nbsp;\u003c/em\u003eImportantly,\u0026nbsp;the value of Ho was\u0026nbsp;much lower than that of He, indicating heterozygote deficiency in the populations of \u003cem\u003eP. santalinus.\u0026nbsp;\u003c/em\u003eThe potential reasons for these findings could be attributed to the entomophilous cross-pollinating nature and wind dispersal of seeds [54, 55, 67], which restrict long-distance dispersal in \u003cem\u003eP. santalinus\u003c/em\u003e. Additionally, this species is recognized for its abundant regeneration through coppice formation [30]. Similar characteristics have also been observed in the related genus \u003cem\u003eDalbergia\u003c/em\u003e [38, 43]. Alternatively, in smaller populations, there is a greater occurrence of mating between relatives than in larger populations [43].\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e4.2. Rare and private alleles across the different populations:\u0026nbsp;\u003c/strong\u003eThe frequency range of private alleles (PAs) varied significantly among different populations within the Eastern Ghats, with values ranging from 0.188 to 2.125. This wide range of variation suggests that some populations have a greater degree of genetic uniqueness than others do [24]. The unique alleles discovered in these populations could represent distinct evolutionary paths, as observed in rare plant species [32]. The presence of private alleles in a population is of evolutionary importance, and the evolutionary importance of a population is determined by both the number of alleles and the presence of private alleles [33, 48, 51]. Notably, the population with the highest Pa frequency (NAK) indicates significant genetic differentiation. These populations stand out as genetic reservoirs of unique alleles, indicating a greater degree of isolation or historical divergence that has led to the accumulation of distinctive genetics [32, 65], which might explain the long survival of\u0026nbsp;\u003cem\u003eP. Santalinus\u0026nbsp;\u003c/em\u003edespite the enormous anthropological pressure. Hence, these trees are important genetic resources that can be used in tree breeding programs.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e4.3. Genetic Differentiation and Population Structure\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eAccording to the AMOVA, the majority (73%) of the genetic variation detected was within populations,\u0026nbsp;whereas only 27% was between populations. This suggests that the primary contributor to total genetic variation can be attributed to variation within populations. Similar findings were reported in a recent study on \u003cem\u003eP. marsupium\u0026nbsp;\u003c/em\u003e[41], which used intersimple sequence repeat (ISSR) markers and reported that 91% of the genetic variation was within populations and that only 9% was found among populations. Amri and Mamboya [6] reported that genetic variation in \u003cem\u003eP. angolensis\u0026nbsp;\u003c/em\u003e 77.13% within the population and 28.86% among distinct populations. This aligns with previous research on long-lived, outcrossing, late-succession plant taxa, which have been shown to exhibit high levels of genetic diversity within populations [35]. The\u0026nbsp;Shannon\u0026rsquo;s information index (I) of 1.52 and Nei\u0026rsquo;s gene diversity (2.31) obtained in the present study\u0026nbsp;revealed high levels of genetic variation within the populations (Table 3). These findings are greater than those reported for \u003cem\u003eP. angolensis\u0026nbsp;\u003c/em\u003e(I=0.2769) [6], \u003cem\u003eP. marsupium\u003c/em\u003e (I=0.46) [41] and \u003cem\u003eD. odorifera\u003c/em\u003e (I= 0.65 and Nei\u0026rsquo;s genetic diversity 0.38) by Liu et al. [38]. Similarly, a significant pairwise F\u003csub\u003eST\u0026nbsp;\u003c/sub\u003eof 0.05 to 0.43 was observed among the \u003cem\u003eP. santalinus\u0026nbsp;\u003c/em\u003epopulations\u0026nbsp;(Table S2), which was greater than the F\u003csub\u003eST\u0026nbsp;\u003c/sub\u003e(0.042 to 0.115) of\u003cem\u003e\u0026nbsp;D. odorifera\u0026nbsp;\u003c/em\u003e[38], indicating moderate genetic differentiation among the 22 \u003cem\u003eP. santalinus\u003c/em\u003e populations. The highest level of genetic differentiation was found between the PVT and TBB populations (0.427), which were isolated\u0026nbsp;at a distance of 150 km between them, and the lowest was found between the TTP and CPV populations (0.049), which were located at 34 km (Table S2). This finding revealed a decrease in gene flow with increasing geographic distance. Gene flow is vital for determining genetic differentiation and genetic drift among populations [58]. Gene flow in plant species occurs through the exchange of pollen, seeds, and spores, influencing the genetic variation in the population [72, 73]. A gene flow value greater than 1 can overcome genetic drift, whereas a value less than one indicates that genetic drift is the predominant factor affecting a population\u0026apos;s genetic structure [62]. A mean Nm of 0.82 was observed in the present study, indicating low gene flow among the populations and indicating the occurrence of genetic drift in the populations.\u0026nbsp;If not addressed, this will lead to the isolation of populations, leading to inbreeding depression, genetic bottlenecks and the extinction of populations/species from natural habitats.\u0026nbsp;\u003cem\u003eP. santalinus\u003c/em\u003e is pollinated mostly by \u003cem\u003eApis dorsata\u003c/em\u003e only during the night [54, 55]. The short distance of these bees from hives might be the primary reason for the low gene flow between populations and the fragmentation of the populations.\u003c/p\u003e\n\u003cp\u003eAn admixture model-based analysis was used to evaluate population structure. The genetic structure revealed the distribution pattern of genetic diversity within and between populations. Structural analysis revealed a maximum \u0026Delta;K of 3, with 361 genotypes assigned to three clusters (Fig. 3). Cluster I included the populations in the Tirupati and Chittoor Circles, Cluster II included the populations in the Kadapa and Rajampet regions, and Cluster III included the populations from the Guntur and Nellore Circles. Some of the geographically close populations were placed in different clusters and vice versa, but the percentage of individuals with admixture was very low. The UNJ and PCoA results also supported the STRUCTURE analysis, which was attributed to differences in population clustering. Although all three analyses were successful in grouping 22 populations of \u003cem\u003eP. santalinus\u003c/em\u003e into three subgroups, there were differences in the clustered populations and the number of populations. Overall, no apparent population clustering was observed, and a significant correlation was not found between genetic and geographic distances. The Mantel test results revealed that 68% of the genetic differences among the investigated populations were attributed to geographical distance (Fig. 6). The principle of isolation by distance, as described by Wright in 1943 [71], predicts that a positive correlation can be expected between genetic and geographic distances when populations reach equilibrium between gene flow and genetic drift. An analysis of the data revealed that there was a positive correlation between geographic distance and population differentiation, but it was not significant (Fig. 6). This differentiation is mostly attributed to genetic distance (Fig. 7b) rather than geographic distance. These findings indicate that human interference and the limited foraging distance of bees are the main factors influencing pollination differentiation.\u0026nbsp;In the present study, low gene flow was detected even though the natural populations are located within a maximum distance of 250 km. This phenomenon eventually results in inbreeding and affects the fitness of the population. A\u0026nbsp;possible reason could be habitat loss and fragmentation of populations by human interference, as reported by the NDF survey.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e4.4. Genetic variation among the Girth classes:\u0026nbsp;\u003c/strong\u003eThe analysis revealed that there were no significant differences in genetic diversity parameters such as Na, Ne, He, and Ho among the four girth classes (Table 7). This finding suggests that the genetic makeup of the population remained consistent regardless of the girth class. However, a noticeable upward trend in all genetic diversity parameters was observed from higher to lower girth classes. These results align with findings from other studies on tree species such as \u003cem\u003ePinus ponderosa\u003c/em\u003e [37], \u003cem\u003eKoompassia malaccensis\u0026nbsp;\u003c/em\u003e[45], and \u003cem\u003eDysoxylum malabaricum\u003c/em\u003e [12], which also revealed a similar pattern of genetic diversity between seedlings and adult plants. One possible explanation for this trend could be the occurrence of genetic drift or gene flow within the population [11]. In contrast, a study conducted on \u003cem\u003eManilkara multifida\u003c/em\u003e [70] in a highly fragmented habitat revealed a significant difference in Ho between adult individuals (EVC = 0.720, UBR = 0.736) and juveniles (EVC = 0.463, UBR = 0.560).\u0026nbsp;Similarly, \u003cem\u003eD. binectariferum\u0026nbsp;\u003c/em\u003ereported a high level of allelic richness in adults compared with juveniles [11, 42].\u0026nbsp;These findings indicate that population fragmentation may have an impact on genetic diversity. However, our study did not find any such differences in genetic diversity parameters despite the selective pressure of logging on the population. The forest department\u0026apos;s tremendous efforts to protect the species and the good amount of natural regeneration might be the factors influencing the maintenance of genetic diversity among girth classes.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e4.5. Effects of ecological factors and edaphic factors:\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThe genetic diversity of plant species depends on different factors, such as ecological, geographical, breeding system, and anthropogenic factors [56]. Higher genetic diversity is expected to reflect better adaptation to the changing environment of a species [23]. The \u003cem\u003eP. santalinus\u003c/em\u003e distribution in Andhra Pradesh is restricted mainly to the Cuddapah landscape (13\u0026deg; 30\u0026rsquo; and 15\u0026deg; 00\u0026rsquo; North latitude and between 78\u0026deg; 45\u0026rsquo; and 79\u0026deg; 39\u0026rsquo; East longitude) [52]. Geographically, the region occupies approximately 5160 km2, and its geographical spread includes the Chittoor, Cuddapah, and Nellore districts of the Seshachalam Hill Range, which has altitudes ranging from 150\u0026ndash;900 m [8]. Physiographically, the most favorable altitude is reported to be from 300--800 m [52]. However, our study included altitudes ranging from 124 m to 838 m\u0026nbsp;(Table 1). The CSM (124 m), CPV (318 m), and TTP (602 m) populations presented high genetic diversity and were located in low- and medium-altitude regions. There was no clear pattern observed in genetic variation with increasing elevation. Overall, in this study, we observed a significant correlation between genetic diversity according to annual precipitation and relative humidity. The genetic diversity of \u003cem\u003eP. santalinus\u003c/em\u003e is influenced by the type of soil and topography. This plant species grows on dry, hilly, and often rocky terrain, and it prefers lateritic and gravelly soil [60]. Approximately 80% of the red-sander growing area is occupied by outcrops of quartzites, whereas the remainder is occupied by shale geological formations [52]. The high potassium content of the quartzite soil could be a major factor in the localization of \u003cem\u003eP. santalinus\u0026nbsp;\u003c/em\u003e[52]\u003cem\u003e.\u003c/em\u003e According to the soil distribution map of Eastern Ghats, which was created\u0026nbsp;from data from bhukosh (https://bhukosh.gsi.gov.in/Bhukosh/Public), 20 out of 22 populations were found to be located on lithosols. One population was found on chromic luvisols (PPT), and one was found on vertic cambisols (TTP) (Fig. 8a). Additionally, we observed an increasing trend in genetic diversity parameters from Lithosols to vertic cambisols (Fig. 8b-g). Furthermore, to investigate the relationships between environmental factors and genetic diversity, detailed soil nutrient data and other environmental information are necessary. Further investigations of soil pH, nutrient levels, and microbial associations may help in understanding the influence of soil and other environmental factors on genetic diversity.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e4.6. Genetic diversity analysis based on different forest classifications:\u0026nbsp;\u003c/strong\u003eThe genetic diversity of \u003cem\u003eP. santalinus\u003c/em\u003e in the Eastern Ghats of Andhra Pradesh shows significant variation across different circles and divisions. The analysis revealed notable variations in allele frequencies and diversity parameters. Compared with the other populations, the Tirupati circle presented the greatest genetic diversity, with the greatest number of alleles (Na) and private alleles having high precipitation, humidity, and low temperatures.\u0026nbsp;Interestingly, despite differences in population size, the Guntur circle presents comparable or greater adequate population size (Ne) and diversity metrics than do larger circles such as Kurnool. Similarly, within divisions, genetic diversity correlates with population size, with greater Ne observed in larger populations. Divisions such as CTR are notable for their elevated genetic diversity, whereas others such as NLR and RJT have unique sets of private alleles. These findings highlight the need to consider population size and local environmental factors in conservation strategies for \u003cem\u003eP. santalinus\u003c/em\u003e\u003cem\u003e\u0026nbsp;\u003c/em\u003ein the Eastern Ghats. Despite the stringent efforts of the APFD to combat unlawful deforestation practices, a noteworthy decline in the population of mature \u003cem\u003eP. santalinus\u0026nbsp;\u003c/em\u003ebearing trees available for harvesting has been detected in various forests [3]. This decline is most prominent in three forest department circles and eight divisions, where the Tirupati circle and Chittoor division exhibit significant variations. This could be due to \u003cem\u003eP. santalinus\u0026nbsp;\u003c/em\u003enatural populations prevailing in dry areas [9]. These populations hold immense potential as germplasms for future conservation initiatives aimed at safeguarding the species.\u003c/p\u003e"},{"header":"5. Conclusion","content":"\u003cp\u003eThis study represents the first comprehensive genetic diversity analysis covering the entire natural range of \u003cem\u003eP. santalinus\u003c/em\u003e in Eastern Ghats, India. We used 16 highly polymorphic SSR markers to assess 22 natural populations in the region. Our findings revealed moderate genetic diversity, which is relatively low for a woody tree species, with a few populations displaying high levels of diversity, whereas others presented alarmingly low genetic variation. Most of the genetic variation was observed within populations, with moderate genetic differentiation and low gene flow among them.\u0026nbsp;Among the 22 populations, Tirupati base-Sadashiva Kona\u0026nbsp;(CPV), followed by\u0026nbsp;Tirupati--Papanashini\u0026nbsp;(TTP) and\u0026nbsp;Chittoor East-Srikalahasti-Melachur\u0026nbsp;(CSM), presented the highest genetic diversity (He=0.869), and the lowest was\u0026nbsp;Chitaleti Pati Base Camp (PVT) (He=0.436). Additionally, many private alleles have been identified in populations Nellore Atmakuru-Kadarinaidupalli (NAK), Tirupati--Papanashini; (TTP), and\u0026nbsp;Chittoor East-Srikalahasti-Melachur;\u0026nbsp;(CSM), presenting opportunities for selective breeding to increase adaptation and resistance to changing environments. At the forest circle and division levels, the Tirupati circle and Chitoor divisions were identified as highly diverse, which is consistent with the findings at the population level. Despite habitat fragmentation and anthropogenic pressure on forest areas, no notable differences in genetic diversity parameters were observed between seedlings, saplings, and mature trees. The study also revealed significant correlations between genetic diversity parameters, annual precipitation, and relative humidity. Moreover, soil type and topography likely play major roles in species distributions. Notably, populations located at lower latitudes presented significant genetic diversity across their distribution range. These results underscore the need for further investigations into the effects of terrain, soil, and environmental factors to better understand the interaction between the environment and genetics on heartwood formation. In conclusion, the SSR loci identified in this study could serve as valuable tools for future tree improvement programs. Populations with high genetic diversity and unique alleles should be leveraged as germplasm resources and for seed material in both \u003cem\u003ein situ\u003c/em\u003e and \u003cem\u003eex-situ\u003c/em\u003e conservation efforts, particularly to address the low gene flow rate among populations and manage those with low genetic diversity.\u003c/p\u003e\n\u003cp\u003e\u003cbr\u003e\u003c/p\u003e"},{"header":"Abbreviations","content":"\u003cp\u003eAPFD \u0026ndash; Andhra Pradesh Forest Department\u003c/p\u003e\n\u003cp\u003eCITES - Convention on International Trade in Endangered Species of Wild Fauna and Flora\u003c/p\u003e\n\u003cp\u003eRAPD-Random Amplified Polymorphic DNA\u003c/p\u003e\n\u003cp\u003eISSR-Inter-Simple Sequence Repeat\u003c/p\u003e\n\u003cp\u003eSSR-\u0026nbsp;simple sequence repeats\u003c/p\u003e\n\u003cp\u003eEST-SSR - expressed sequence tag-derived simple sequence repeat marker\u003c/p\u003e\n\u003cp\u003eNGS-\u0026nbsp;Next-Generation Sequencing\u003c/p\u003e\n\u003cp\u003eDNA- Deoxyribonucleic Acid\u003c/p\u003e\n\u003cp\u003eCTAB-\u0026nbsp;Cetyltrimethylammonium\u0026nbsp;bromide\u003c/p\u003e\n\u003cp\u003ePCR- Polymerase chain reaction\u003c/p\u003e\n\u003cp\u003eNa-Number of different alleles\u003c/p\u003e\n\u003cp\u003eNe-number of effective alleles\u003c/p\u003e\n\u003cp\u003eHo-\u0026nbsp;observed heterozygosity\u003c/p\u003e\n\u003cp\u003eHe-Expected Heterozygosity\u003c/p\u003e\n\u003cp\u003ePIC- Polymorphic Information Content\u003c/p\u003e\n\u003cp\u003eI- Shannon\u0026apos;s information index\u003c/p\u003e\n\u003cp\u003eF- Fixation Index\u003c/p\u003e\n\u003cp\u003eFis- Inbreeding coefficient within an individual relative to the total\u003c/p\u003e\n\u003cp\u003eFit- Inbreeding coefficient within an individual relative to the total\u003c/p\u003e\n\u003cp\u003eFst- Inbreeding coefficient within a subpopulation relative to the total\u003c/p\u003e\n\u003cp\u003eNm-Gene Flow\u003c/p\u003e\n\u003cp\u003eAMOVA -\u0026nbsp;Analysis of Molecular Variance\u003c/p\u003e\n\u003cp\u003eUNJ- Unweighted neighbor-joining\u003c/p\u003e\n\u003cp\u003ePCoA-Principal Coordinate Analysis\u003c/p\u003e\n\u003cp\u003eMCMC-Monte Carlo Markov Chain\u003c/p\u003e\n\u003cp\u003eNDF- Non-Detrary Findings\u003c/p\u003e\n\u003cp\u003eGBH- Girth at Breast Height\u003c/p\u003e\n\u003cp\u003eGC \u0026ndash; Girth class\u003c/p\u003e\n\u003cp\u003eSiO\u003csub\u003e2\u0026nbsp;\u003c/sub\u003e-Silicon dioxide\u003c/p\u003e\n\u003cp\u003eK -Potassium\u003c/p\u003e\n\u003cp\u003eFe- Iron\u003c/p\u003e\n\u003cp\u003eCa- Calcium\u003c/p\u003e\n\u003cp\u003eNa-Sodium\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eA2cd-\u0026nbsp;\u003c/strong\u003eDeclining population (past, present and/or projected)\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eA2\u003c/strong\u003e-Population reduction observed, estimated, inferred, or suspected in the past where the causes of reduction may not have ceased OR may not be understood OR may not be reversible.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e(c)\u003c/strong\u003e Declines in area of occupancy (AOO), extent of occurrence (EOO) and/or habitat quality\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003e(d)\u003c/strong\u003e Actual or potential levels of exploitation\u003c/p\u003e"},{"header":"Declarations","content":"\u003cp\u003e\u003cstrong\u003eSource of Funding:\u003c/strong\u003e National Biodiversity Authority (NBA) (No. Tech./Genl./22/149/17/18-19/382).\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eConflict of interest:\u0026nbsp;\u003c/strong\u003eThe authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as potential conflicts of interest. All the authors declare that there are no conflicts of interest.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eClinical trial number:\u003c/strong\u003e Not applicable.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eConsent to Participate:\u003c/strong\u003e \u003cstrong\u003eNot applicable.\u003c/strong\u003e This study does not involve any human or animal trials, nor does it include any genetic modification of the plant.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eEthics statement:\u0026nbsp;\u003c/strong\u003eThe plant material was identified by Divakara, BN, a scientist at IWST in Bengaluru, and a voucher specimen has been deposited at TDU/IWST, (IWST-NBA-01 to 400), FRLHT, Bengaluru. \u003cstrong\u003e\u0026nbsp;\u003c/strong\u003eWe have collected samples with the gracious permission of the Forest Department of Andhra Pradesh, India. Reference No. EF02-20051/33/2020 - Research SEC PCCF dated 10/20/2020 from the Forest Department, Government of Andhra Pradesh, India. We adhered to both local and national guidelines during the sample collection.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eData Availability Statement:\u003c/strong\u003e All data generated or analyzed during this study are included in this published article [and its supplementary information files].\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eConsent to publish:\u003c/strong\u003e Consent to publish were obtained from all authors, and\u0026nbsp;all the authors declare that there are no conflicts of interest.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003ePlant reproducibility:\u0026nbsp;\u003c/strong\u003eLeaf samples of\u003cstrong\u003e\u0026nbsp;\u003c/strong\u003e\u003cem\u003ePterocarpus santalinus\u003c/em\u003e were collected from the \u0026nbsp;Eastern Ghats of Andhra Pradesh, India. Only leaf samples were collected without harming the tree, and ensuring their reproducibility.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eAuthor contribution statement\u003c/strong\u003e: The project was conceptualized by MKP, PHR, and DBN. Sample collection was carried out by MKP, PHR, and DBN. Sample preparation, experiments, and data analysis were carried out by SMV, MAH, PHR, and MKP. Discussion of the data and MS preparation\u003cstrong\u003e\u0026nbsp;\u003c/strong\u003e\u003cstrong\u003eare performed by\u0026nbsp;\u003c/strong\u003eSMV, MAH, PHR, CJ, and MKP. The finalization of the manuscript was performed by PHR, CJ, SK, DBN, and MKP.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eAcknowledgments:\u003c/strong\u003e We thank the National Biodiversity Authority (NBA) (No. Tech./Genl./22/149/17/18-19/382) for financial support. Dr. MKP also expresses his gratitude to the Department of Biotechnology (DBT) and the Science and Engineering Research Board (SERB) for their financial support. The collection of samples and other fieldwork was facilitated by the kind permission and cooperation of the State Forest Department, Government of Andhra Pradesh. We also dedicate this article to all the forest officers working in the Eastern Ghats region for their dedication to the protection and conservation of the Red Sanders.\u003c/p\u003e"},{"header":"References","content":"\u003col\u003e\n\u003cli\u003eAgasthikumar, S., Patturaj, M., Samji, A., Aiyer, B., Munusamy, A., Kannan, N., Arivazhagan, V., Warrier, R. R., Ramasamy, Y., 2022. De novo transcriptome assembly and development of EST-SSR markers for \u003cem\u003ePterocarpus santalinus\u003c/em\u003e L. f. (Red sanders), a threatened and endemic tree of India. \u003cem\u003eGenetic Resources and Crop Evolution\u003c/em\u003e, Advance online publication.https://doi.org/10.1007/s10722-022-01385-8\u003c/li\u003e\n\u003cli\u003eAhmed, M., and Nayar, M. P., 1984. Red Sanders tree (\u003cem\u003ePterocarpus santalinusLinn\u003c/em\u003e.f.) on the verge of depletion. \u003cem\u003eBulletin of Botanical Survey of India\u003c/em\u003e, 26, 142-143.\u003c/li\u003e\n\u003cli\u003eAhmedullah, M., Rasingam, L., Swamy, J., Nagaraju, S., Shankara Rao, M., 2019. Non-Detriment Findings Report on the Red Sanders Tree (Pterocarpus santalinusL.f). Botanical Survey of India (Deccan Regional Centre), MoEFCC, Hyderabad.\u003c/li\u003e\n\u003cli\u003eAllendorf, F. W., Luikart, G., Aitken, S. N., 2012. Conservation and the genetics of populations. John Wiley \u0026amp; Sons.\u003c/li\u003e\n\u003cli\u003eAmiteye S., 2021. Basic concepts and methodologies of DNA marker systems in plant molecular breeding. \u003cem\u003eHeliyon\u003c/em\u003e, 7(10), e08093. https://doi.org/10.1016/j.heliyon.2021.e08093\u003c/li\u003e\n\u003cli\u003eAmri, E., and Mamboya, F., 2012. Genetic diversity in Pterocarpus angolensis populations detected by random amplified polymorphic DNA markers. \u003cem\u003eInternational Journal of Plant Breeding and Genetics\u003c/em\u003e, \u003cem\u003e6\u003c/em\u003e(2), 105-114.\u003c/li\u003e\n\u003cli\u003eArif, I. A., Khan, H. A., Bahkali, A. H., Al Homaidan, A. A., Al Farhan, A. H., Al Sadoon, M., Shobrak, M., 2011. DNA marker technology for wildlife conservation. \u003cem\u003eSaudi journal of biological sciences\u003c/em\u003e, 18(3), 219\u0026ndash;225. https://doi.org/10.1016/j.sjbs.2011.03.002\u003c/li\u003e\n\u003cli\u003eArunkumar, A. N., and Joshi, G. 2014. Pterocarpus santalinus (Red Sanders) an Endemic, Endangered Tree of India: Current Status, Improvement and the Future. \u003cem\u003eJournal of Tropical Forestry and Environment\u003c/em\u003e, 4(2), 1-10.https://doi.org/10.31357/jtfe.v4i2.2063\u003c/li\u003e\n\u003cli\u003eBabar, S., Amarnath, G., Reddy, C.S., Jentsch, A., Sudhakar, S., 2012. Species distribution models: ecological explanation and prediction of an endemic and endangered plant species (Pterocarpus santalinus Lf). \u003cem\u003eCurrent Science,\u003c/em\u003e 1157-1165.\u003c/li\u003e\n\u003cli\u003eBalaraju, K., Agastian, P., Ignacimuthu, S., Park, K., 2011. A rapid in vitro propagation of red sanders (Pterocarpus santalinus L.) using shoot tip explants. \u003cem\u003eActa physiologiae plantarum\u003c/em\u003e, 33, 2501-2510.\u003c/li\u003e\n\u003cli\u003eBodare, S., Ravikanth, G., Ismail, S. A., Patel, M. K., Spanu, I., Vasudeva, R., Shaanker, R. U., Vendramin, G. G., Lascoux, M., Tsuda, Y., 2016. Fine- and local- scale genetic structure of Dysoxylum malabaricum, a late-successional canopy tree species in disturbed forest patches in the Western Ghats, India. \u003cem\u003eConservation Genetics\u003c/em\u003e, \u003cem\u003e18\u003c/em\u003e(1), 1\u0026ndash;15. https://doi.org/10.1007/s10592-016-0877-7\u003c/li\u003e\n\u003cli\u003eBodare, S., Tsuda, Y., Ravikanth, G., Uma Shaanker, R., Lascoux, M., 2013. Genetic structure and demographic history of the endangered tree species Dysoxylum malabaricum (M eliaceae) in W estern G hats, I ndia: implications for conservation in a biodiversity hotspot. \u003cem\u003eEcology and Evolution\u003c/em\u003e, \u003cem\u003e3\u003c/em\u003e(10), 3233-3248.\u003c/li\u003e\n\u003cli\u003eChampion, H.G., Seth, S.K., 1968. A Revised Forest Types of India. \u003cem\u003eManager of Publications\u003c/em\u003e, Government of India, Delhi.\u003c/li\u003e\n\u003cli\u003eCole, C. T., 2003. Genetic Variation in Rare and Common Plants. \u003cem\u003eAnnual Review of Ecology, Evolution, and Systematics\u003c/em\u003e, 34, 213\u0026ndash;237. doi:10.1146/annurev.ecolsys.34.030102.151717\u003c/li\u003e\n\u003cli\u003eDavey, J. W., Hohenlohe, P. A., Etter, P. D., Boone, J. Q., Catchen, J. M., Blaxter, M. L., 2011. Genome-wide genetic marker discovery and genotyping using next-generation sequencing. \u003cem\u003eNature Reviews Genetics\u003c/em\u003e, 12(7), 499-510.\u003c/li\u003e\n\u003cli\u003eDoyle, J. J., and Doyle, J. L., 1990. Isolation of Plant DNA from Fresh Tissue.\u003c/li\u003e\n\u003cli\u003eEarl, D. A., and VonHoldt, B. M., 2012. STRUCTURE HARVESTER: a website and program for visualizing STRUCTURE output and implementing the Evanno method. \u003cem\u003eConservation Genetic Resources\u003c/em\u003e, 4(2), 359\u0026ndash;361. https://doi.org/10.1007/s12686-011-9548-7.\u003c/li\u003e\n\u003cli\u003eEllegren, H., 2004. Microsatellites: simple sequences with complex evolution. \u003cem\u003eNature Reviews Genetics\u003c/em\u003e, 5(6), 435-445.\u003c/li\u003e\n\u003cli\u003eEllegren, H., Galtier, N., 2016. Determinants of genetic diversity. \u003cem\u003eNature Reviews Genetics\u003c/em\u003e, 17, 422\u0026ndash;433. https://doi.org/10.1038/nrg.2016.58\u003c/li\u003e\n\u003cli\u003eEvanno, G., Regnaut, S., Goudet, J. (2005). Detecting the number of clusters of individuals using the software structure: a simulation study. \u003cem\u003eMolecular Ecology\u003c/em\u003e, 14, 2611-2620. https://doi.org/10.1111/j.1365-294X.2005.02553.x\u003c/li\u003e\n\u003cli\u003eFofana, I. J., Lidah, Y. J., Diarrassouba, N., N\u0026rsquo;guetta, S. P. A., Sangare, A., Verhaegen, D., 2008. Genetic Structure and Conservation of Teak (Tectona Grandis) Plantations in C\u0026ocirc;te d\u0026rsquo;Ivoire, Revealed by Site Specific Recombinase (SSR). \u003cem\u003eTropical Conservation Science\u003c/em\u003e, 1(3), 279-292. doi:10.1177/194008290800100308\u003c/li\u003e\n\u003cli\u003eFrankham, R., 2005. Genetics and extinction. Biological Conservation, 126(2), 131-140.\u003c/li\u003e\n\u003cli\u003eGadissa, F., Tesfaye, K., Dagne, K., Geleta, M., 2018. Genetic diversity and population structure analyses of Plectranthus edulis (Vatke) Agnew collections from diverse agro-ecologies in Ethiopia using newly developed EST-SSRs marker system. \u003cem\u003eBMC Genetics\u003c/em\u003e, 19(1), 1-15.\u003c/li\u003e\n\u003cli\u003eHamrick, J. L., Godt, M. J. W., 1996. Effects of life history traits on genetic diversity in plant species. (1996b). \u003cem\u003ePhilosophical Transactions of the Royal Society B\u003c/em\u003e, \u003cem\u003e351\u003c/em\u003e(1345), 1291\u0026ndash;1298. https://doi.org/10.1098/rstb.1996.0112\u003c/li\u003e\n\u003cli\u003eHegde, M., Singh, B. G., Krishnakumar, N., 2012. Non-Detriment Findings Study for \u003cem\u003ePterocarpus santalinus\u003c/em\u003e L. f. (Red Sanders) in India. Institute of Forest Genetics and Tree Breeding.\u003c/li\u003e\n\u003cli\u003ehttps://forests.ap.gov.in/\u003c/li\u003e\n\u003cli\u003ehttps://www.fao.org.\u003c/li\u003e\n\u003cli\u003ehttps://www.iucnredlist.org/search/list?query=Pterocarpus%20santalinus\u0026amp;searchType=species\u003c/li\u003e\n\u003cli\u003ehttps://power.larc.nasa.gov/data-acce\u003c/li\u003e\n\u003cli\u003eIndu, B. K., Kavyashree, R., Balasubramanya, S., Anuradha, M., 2019. Tree Improvement in Red Sanders, Red sanders: Silviculture and conservation,201-210.https://doi.org/10.1007/978-981-13-7627-6_15\u003c/li\u003e\n\u003cli\u003eJohnson, B. N., Quashie, M. L. A., Chaix, G., Camus‐Kulandaivelu, L., Adjonou, K., Segla, K. N., Vignes, H., 2020. Isolation and characterization of microsatellite markers for the threatened African endemic tree species \u003cem\u003ePterocarpus erinaceus\u003c/em\u003e Poir. \u003cem\u003eEcology and Evolution\u003c/em\u003e, 10(23), 13403-13411.\u003c/li\u003e\n\u003cli\u003eJump, A.S., Penuelas, J., 2005. Running to stand still: adaptation and the response of plants to rapid climate change. \u003cem\u003eEcology Letters\u003c/em\u003e, 8(9), 1010-1020.\u003c/li\u003e\n\u003cli\u003eKalinowski, S.T., 2004. Counting alleles with rarefaction: private alleles and hierarchical sampling designs. \u003cem\u003eConservation Genetics\u003c/em\u003e, 5, 539\u0026ndash;543.\u003c/li\u003e\n\u003cli\u003eKardos, M., Armstrong, E. E., Fitzpatrick, S. W., Hauser, S., Hedrick, P. W., Miller, J. M., Tallmon, D. A., Funk, W. C., 2021. The crucial role of genome-wide genetic variation in conservation. \u003cem\u003eProceedings of the National Academy of Sciences\u003c/em\u003e, 118(48), e2104642118. https://doi.org/10.1073/pnas.2104642118\u003c/li\u003e\n\u003cli\u003eKremer, A., Caron, H., Cavers, S., Colpaert, N., Gheysen, G., Gribel, R., Lemes, M., Lowe, A. J., Margis, R., Navarro, C., Salgueiro, F., 2005. Monitoring genetic diversity in tropical trees with multilocus dominant markers. \u003cem\u003eHeredity\u003c/em\u003e, \u003cem\u003e95\u003c/em\u003e(4), 274\u0026ndash;280.https://doi.org/10.1038/sj.hdy.6800738\u003c/li\u003e\n\u003cli\u003eLemes, M. R., Gribel, R., Proctor, J., Grattapaglia, D., 2003. Population genetic structure of mahogany (\u003cem\u003eSwietenia macrophylla\u003c/em\u003e King, Meliaceae) across the Brazilian Amazon, based on variation at microsatellite loci: implications for conservation. \u003cem\u003eMolecular ecology\u003c/em\u003e, 12(11), 2875\u0026ndash;2883. https://doi.org/10.1046/j.1365-294x.2003.01950.x\u003c/li\u003e\n\u003cli\u003eLinhart, Y. B., Mitton, J. B., Sturgeon, K. B., Davis, M. L., 1981. Genetic variation in space and time in a population of ponderosa pine. \u003cem\u003eHeredity\u003c/em\u003e, 46(3), 407-426.\u003c/li\u003e\n\u003cli\u003eLiu, F., Hong, Z., Xu, D., Jia, H., Zhang, N., Liu, X., Yang, Z., \u0026amp; Lu, M. 2019b. Genetic diversity of the endangered \u003cem\u003eDalbergia odorifera\u003c/em\u003e revealed by SSR markers. \u003cem\u003eForests\u003c/em\u003e, 10(3), 225.https://doi.org/10.3390/f10030225\u003c/li\u003e\n\u003cli\u003eMaisuria, H. J., Dhaduk, H. L., Kumar, S., Sakure, A. A., Thounaojam, A. S., 2022. Teak population structure and genetic diversity in Gujarat, India. \u003cem\u003eCurrent Plant Biology\u003c/em\u003e, 32, 100267. https://doi.org/10.1016/j.cpb.2022.100267\u003c/li\u003e\n\u003cli\u003eMcNeely, J. A., Miller, K. R., Reid, W. V., Mittermeier, R. A., Werner, T. B., 1990. Conserving the world\u0026apos;s biological diversity. Gland, Switzerland: IUCN; Washington, D.C.: WRI, CI, WWF-US, and the World Bank.\u003c/li\u003e\n\u003cli\u003eMohammad, N., Dahayat, A., Pardhi, Y., Rajkumar, M., 2022. Morpho-molecular diversity assessment of Indian kino (\u003cem\u003ePterocarpus marsupium\u003c/em\u003e Roxb.). \u003cem\u003eJournal of Applied Research on Medicinal and Aromatic Plants\u003c/em\u003e, 29, 100373. https://doi.org/10.1016/j.jarmap.2022.100373\u003c/li\u003e\n\u003cli\u003eMohana Kumara, P., Dayanandan, S., Vasudeva, R., Ravikanth, G., Uma Shaanker, R., 2022. Population Genetic Diversity of \u003cem\u003eDysoxylum Binectariferum\u003c/em\u003e, an Economically Important Tree Species of the Western Ghats, India. In \u003cem\u003eMolecular Genetics and Genomics Tools in Biodiversity Conservation\u003c/em\u003e (pp. 251-266). Singapore: Springer Nature Singapore.\u003c/li\u003e\n\u003c/ol\u003e\n\n\u003col start=\"43\"\u003e\n\u003cli\u003eMoritsuka, E., Chhang, P., Tagane, S., Toyama, H., Sokh, H., Yahara, T., Tachida, H., 2017. Genetic variation and population structure of a threatened timber tree \u003cem\u003eDalbergia cochinchinensis\u003c/em\u003e in Cambodia. \u003cem\u003eTree genetics \u0026amp; genomes\u003c/em\u003e, 13, 1-11.\u003c/li\u003e\n\u003cli\u003eNawaz, M. A., Sahito, Z. A., Al-Arif, M. A., Kakar, M. S., Khan, S., 2017. Assessing genetic diversity and population structure of Pakistani rice germplasm. \u003cem\u003ePLoS ONE\u003c/em\u003e, 12(9), e0183435. https://doi.org/10.1371/journal.pone.0183435\u003c/li\u003e\n\u003cli\u003eNoreen, A.M. and Webb, E.L., 2013. High genetic diversity in a potentially vulnerable tropical tree species despite extreme habitat loss. \u003cem\u003ePLoS One\u003c/em\u003e, \u003cem\u003e8\u003c/em\u003e(12), p.e82632.\u003c/li\u003e\n\u003cli\u003eOliveira, E. J., Padua, J. G., Zucchi, M. I., Vencovsky, R., Vieira, M. L. C., 2006. Origin, evolution and genome distribution of microsatellites. \u003cem\u003eGenetics and Molecular Biology\u003c/em\u003e, 29(2), 294-307.\u003c/li\u003e\n\u003cli\u003ePadmalatha, K., Prasad, M. N. V., 2007. Morphological and molecular diversity in Pterocarpus santalinusLf-an endemic and endangered medicinal plant. \u003cem\u003eMedicinal and Aromatic Plant Science and Biotechnology\u003c/em\u003e, 1(2), 263-273.\u003c/li\u003e\n\u003cli\u003eParker, K.M., Sheffer, R.J., Hedrick, P.W., 1999. Molecular variation and evolutionarily significant units in the endangered Gila topminnow. \u003cem\u003eConservation Biology\u003c/em\u003e, 13, 108\u0026ndash;116.\u003c/li\u003e\n\u003cli\u003ePeakall, R., and Smouse, P.E., 2012. GenAlEx 6.5: genetic analysis in Excel. Population genetic software for teaching and research-an update. \u003cem\u003eBioinformatics\u003c/em\u003e, 28, 2537-2539.\u003c/li\u003e\n\u003cli\u003ePerrier, X., Flori, A., Bonnot, F., 2003. Data analysis methods. In: Hamon, P., Seguin, M., Perrier, X., Glaszmann, J. C. Ed., Genetic diversity of cultivated tropical plants. Enfield, Science Publishers. Montpellier. pp 43 \u0026ndash; 76.\u003c/li\u003e\n\u003cli\u003ePritchard, J.K., Stephens, M., Donnelly, P., 2000. Inference of population structure using multilocus genotype data. \u003cem\u003eGenetics\u003c/em\u003e, 155(2), 945-959.https://doi.org/10.1093/genetics/155.2.945\u003c/li\u003e\n\u003cli\u003eRaju, K., and Nagaraju, A., 1999. Geobotany of red sanders (Pterocarpus santalinus) \u0026ndash; a case study from the southeastern portion of Andhra Pradesh. \u003cem\u003eEnvironmental Geology\u003c/em\u003e, 37, 340\u0026ndash;344. https://doi.org/10.1007/s002540050393\u003c/li\u003e\n\u003cli\u003eRamabrahmam, V., Sujatha., 2016. Red Sanders in Rayalaseema region of Andhra Pradesh: Importance to Commercial and Medicinal value. \u003cem\u003eIOSR Journal of Pharmacy and Biological Sciences\u003c/em\u003e, 11, 57\u0026ndash;60.\u003c/li\u003e\n\u003cli\u003eRao, S. P., Raju, A. J. S. 2002. Pollination ecology of the Red Sanders Pterocarpus santalinus (Fabaceae), an endemic and endangered tree species. \u003cem\u003eCurrent Science\u003c/em\u003e, 83(9), 1144-1148.\u003c/li\u003e\n\u003cli\u003eRao, S.P., Atluri, J. B., Reddi, C.S., 2001. Intermittent mass blooming, midnight anthesis and rockbee pollination in \u003cem\u003ePterocarpus santalinus\u003c/em\u003e (\u003cem\u003eFabaceae\u003c/em\u003e). \u003cem\u003eNordic Journal of Botany\u003c/em\u003e, 21, 271-276. ISSN 0107-055X.\u003c/li\u003e\n\u003cli\u003eSaeed, S., Barozai, M. Y., 2012. A review on genetic diversity of wild plants by using different genetic markers. \u003cem\u003ePure and Applied Biology\u003c/em\u003e, 1, 68-71. doi: 10.19045/bspab.2012.13004.\u003c/li\u003e\n\u003cli\u003eSalgotra, R. K., Chauhan, B. S. 2023., Genetic Diversity, Conservation, and Utilization of Plant Genetic Resources. \u003cem\u003eGenes\u003c/em\u003e, 14(1), 174. https://doi.org/10.3390/genes14010174\u003c/li\u003e\n\u003cli\u003eSchaal, B. A., Hayworth, D. A., Olsen, K. M., Rauscher, J. T., Smith, W. A., 1998. Phylogeographic studies in plants: problems and prospects. \u003cem\u003eMolecular Ecology\u003c/em\u003e, \u003cem\u003e7\u003c/em\u003e(4), 465-474.\u003c/li\u003e\n\u003cli\u003eSelkoe, K. A., Toonen, R. J., 2006. Microsatellites for ecologists: a practical guide to using and evaluating microsatellite markers. \u003cem\u003eEcology Letters\u003c/em\u003e, 9(5), 615-629.\u003c/li\u003e\n\u003cli\u003eSenthilkumar, N., Mayavel, A., Subramani, S. P., Balaji, K., Deenathayalan, P., 2015. Red sanders, Pterocarpus santalinus L. in Rajampet forest range, Rajampet forest division, Andhra Pradesh, India. \u003cem\u003eAdvances in Applied Science Research\u003c/em\u003e, 6(10), 130-134.\u003c/li\u003e\n\u003cli\u003eSimko, I., 2009. Development of EST-SSR Markers for the Study of Population Structure in Lettuce (Lactuca sativa L.). \u003cem\u003eJournal of Heredity\u003c/em\u003e, 100, 256\u0026ndash;262. https://doi.org/10.1093/jhered/esn072\u003c/li\u003e\n\u003cli\u003eSlatkin, M., 1987. Gene flow and the geographic structure of natural populations. \u003cem\u003eScience\u003c/em\u003e, 236(4803), 787-792.\u003c/li\u003e\n\u003cli\u003eSneha, M. V., Madhushree, A. H., Tapas, R. S., Divakara, B.N., Mohana, K.P., \u0026amp; Prabuddha, H. R., 2023. Genome sequencing and characterization of microsatellite markers of Pterocarpus santalinusL.f.: an economically important endangered tree of Eastern Ghats, India. \u003cem\u003eJournal of Genetics\u003c/em\u003e, 102:35.\u003c/li\u003e\n\u003cli\u003eSong, Z., Zhang, M., Li, F., et al., 2016. Genome scans for divergent selection in natural populations of the widespread hardwood species Eucalyptus grandis (Myrtaceae) using microsatellites. \u003cem\u003eScientific Reports\u003c/em\u003e, 6, 34941. https://doi.org/10.1038/srep34941\u003c/li\u003e\n\u003cli\u003eSork, V.L., Smouse, P.E., Apsit, V.J., 2006. Genetic analysis of landscape connectivity in tree populations. \u003cem\u003eLandscape Ecology\u003c/em\u003e, 21(5), 821-836.\u003c/li\u003e\n\u003cli\u003eSteane, D. A., Conod, N., Jones, R. C., Vaillancourt, R. E., Potts, B. M. A., 2006. comparative analysis of population structure of a forest tree, Eucalyptus globulus (Myrtaceae), using microsatellite markers and quantitative traits. \u003cem\u003eTree Genet. Genomes\u003c/em\u003e, 2, 30\u0026ndash;38\u003c/li\u003e\n\u003cli\u003eTeixeira da Silva, J. A., Kher, M. M., Soner, D., Nataraj, M. 2019. Red sandalwood (Pterocarpus santalinus L. f.): biology, importance, propagation and micropropagation. \u003cem\u003eJournal of Forest Research\u003c/em\u003e, 30, 745-754.\u003c/li\u003e\n\u003cli\u003eUsha, R., Rani, S. J., Prasuna, T. G. 2013. Genetic relationship between quality and nonquality wood of Pterocarpus santalinus L. (red sanders), an endemic tree species by using molecular markers. \u003cem\u003eJournal of Chemical and Pharmaceutical Sciences\u003c/em\u003e, 6(3), 189-194.\u003c/li\u003e\n\u003cli\u003eVieira, M. L., Santini, L., Diniz, A. L., \u0026amp; Munhoz, C. F., 2016. Microsatellite markers: what they mean and why they are so useful. \u003cem\u003eGenetics and Molecular Biology\u003c/em\u003e, 39(3), 312-328. doi: 10.1590/1678-4685-GMB-2016-0027.\u003c/li\u003e\n\u003cli\u003eWaqar, Z., Moraes, R. C. S., Benchimol, M., Morante-Filho, J. C., Mariano-Neto, E., Gaiotto, F. A., 2021. Gene Flow and Genetic Structure Reveal Reduced Diversity between Generations of a Tropical Tree, \u003cem\u003eManilkara multifida\u003c/em\u003e Penn., in Atlantic Forest Fragments. \u003cem\u003eGenes\u003c/em\u003e, \u003cem\u003e12\u003c/em\u003e(12), 2025. https://doi.org/10.3390/genes12122025.\u003c/li\u003e\n\u003cli\u003eWright, S., 1943. Isolation by Distance. \u003cem\u003eGenetics\u003c/em\u003e, \u003cem\u003e28\u003c/em\u003e(2), 114\u0026ndash;138. https://doi.org/10.1093/genetics/28.2.114\u003c/li\u003e\n\u003cli\u003eWoodruff, D. S., 2001. Populations, Species, and Conservation Genetics. In S. A. Levin (Ed.), \u003cem\u003eEncyclopedia of Biodiversity\u003c/em\u003e (pp. 811-829). Elsevier. ISBN 9780122268656. https://doi.org/10.1016/B0-12-226865-2/00355-2.\u003c/li\u003e\n\u003cli\u003eZhang, D. M., Shen, X. H., Zhang, H. X., Shen, J. M. (2003). Advances in gene flow and paternity analysis of forest population. \u003cem\u003eForestry Research\u003c/em\u003e, 16, 488\u0026ndash;494. doi:10.13275/j.cnki.lykxyj.2003.04.019\u003c/li\u003e\n\u003c/ol\u003e"},{"header":"Tables","content":"\u003cp\u003e\u003cstrong\u003eTable 1:\u0026nbsp;\u003c/strong\u003eSample collection data for 22 populations of \u003cem\u003ePterocarpus santalinus\u003c/em\u003e from various locations in Eastern Ghats, Andhra Pradesh, India.\u003c/p\u003e\n\u003ctable border=\"1\" cellspacing=\"0\" cellpadding=\"0\" width=\"925\"\u003e\n \u003ctbody\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eForest Circle\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eDivision\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eRange\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eBeat\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eLocation\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePopulation ID\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eLatitude (N)\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eLongitude (E)\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eAltitude (m)\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eSample\u0026nbsp;\u003c/strong\u003e\u003c/p\u003e\n \u003cp\u003e\u003cstrong\u003esize\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003eGuntur\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eGiddaluru\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eGiddaluru\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eSingasanipalli\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003ePallugaoduThoka and Eluguddu shola\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eGGS\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e15.2977\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.12817\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e512\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eNellore\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eUdayagiri\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eDevammacheruvu\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eAnasagarabodu and Badithala Bodu\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eNUD\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.90691\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.16839\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e300\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e19\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eNellore\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eAtmakur\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eKadarinaidupalli\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eUrlukonda Camp 410\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eNAK\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.67652\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.19965\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e157\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e20\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eNellore\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eVenkatagiri\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eVembaluru\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eMekalaguntha Camp 248 and Chinnakona Base Camp\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eNVV\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.09043\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.47644\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e162\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003eKurnool\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eNandyal\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eRudravaram\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eAhobilam North\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eChinnakuchala\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eNRA\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e15.15379\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e78.71711\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e305\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eProddatur\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003ePorumamilla\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eTekurpeta\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eYerratichala\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003ePPT\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.99517\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.07484\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e398\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eProddatur\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eVanipenta\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eTippireddypalli\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eChitaletiPati Base Camp\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003ePVT\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.96653\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e78.75828\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e315\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eProddatur\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eBadvel\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eBalayapalli\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eBodabodu Camp 283\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003ePBB\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.62871\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e78.97646\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e177\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e14\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eKadapa\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eSiddavatam\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eMaddur\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eChinnadoddikona\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eKSM\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.51345\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.00589\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e190\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd rowspan=\"2\" valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eKadapa\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd rowspan=\"2\" valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eVempalli\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd rowspan=\"2\" valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003ePolathala\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eBandennapadalu\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd rowspan=\"2\" valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eKVP\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd rowspan=\"2\" valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.36888\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd rowspan=\"2\" valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e78.67371\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd rowspan=\"2\" valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e404\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd rowspan=\"2\" valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eCamp 582\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eKadapa\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eKadapa\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eMaddimadugu East\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eInaparala gutta Camp 519\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eKKM\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.3371\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e78.78028\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e238\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eKadapa\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eRayachoti\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eGuvalacheruvu west\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eMangalam Bayalu road\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eKRG\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.31187\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e78.76187\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e462\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eKadapa\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eOntimitta\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eDasarala Doddi\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eUtumora\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eKOD\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.30738\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e78.99724\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e211\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003eTirupati\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eRajampet\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eRajampet\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eSri RangarajaPalem\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eRollamadujuRastha Camp 889\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eRRS\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.12091\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.03636\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e367\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eRajampet\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eSanipaya\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eJandrapenta\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eKuntathuvalu\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eRSJ\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.12925\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.00255\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e351\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eRajampet\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eChitvel\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eVenkatarajpalli\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eEtikuntoduBadava\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eRCV\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e14.11746\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.39793\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e187\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eRajampet\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eKodur\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eK. V. bhavi (North)\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eBangla board\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eRKK\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e13.91702\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.26148\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e151\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eTirupati\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eBalapalli\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eBalapalli West\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003ePangalachala\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eTBB\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e13.78834\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.38422\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e355\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eTirupati\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eChamala\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eTalacona centra\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eRondavanka\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eTCT\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e13.7736\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.17559\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e602\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eTirupati\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eTirupati\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003ePapanashini and Timmala\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003ePapanashini Dam Camp 128 and Yerriganthalu Camp 127\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eTTP\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e13.71216\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.35739\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e790\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eChittoor East WL\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003eSrikalahasti\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eMelachur\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eSavadugunta Camp 464\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eCSM\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e13.83461\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.49982\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e124\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"bottom\" style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eChittoor East\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 102px;\"\u003e\n \u003cp\u003ePuttur\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 108px;\"\u003e\n \u003cp\u003eVadamala Peta\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 168px;\"\u003e\n \u003cp\u003eSadashiva Kona\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 90px;\"\u003e\n \u003cp\u003eCPV\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 84px;\"\u003e\n \u003cp\u003e13.53716\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 78px;\"\u003e\n \u003cp\u003e79.60114\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 72px;\"\u003e\n \u003cp\u003e318\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"bottom\" style=\"width: 66px;\"\u003e\n \u003cp\u003e20\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd colspan=\"10\" valign=\"bottom\" style=\"width: 925px;\"\u003e\n \u003cp\u003eGGS\u003cstrong\u003e-\u003c/strong\u003eGiddaluruGiddaluruSingasanipalli;NUD-Nellore Udayagiri \u0026nbsp;Devammacheruvu; NAK- Nellore \u0026nbsp;AtmakurKadarinaidupalli ; NVV- Nellore Venkatagiri \u0026nbsp;Vembaluru; NRA- NandyalRudravaramAhobilam North; PPT- ProddaturPorumamillaTekurpeta; PVT- ProddaturVanipentaTippireddypalli; PBB- ProddaturBadvelBalayapalli; KSM- Kadapa SiddavatamMaddur; KVP- Kadapa VempalliPolathala; KKM- Kadapa KadapaMaddimadngu; KRG- Kadapa RayachotiGuvalacheruvu; KOD- Kadapa OntimittaDasarala Doddi; RRS- RajampetRajampet Sri RangarajaPalem; RSJ- RajampetSanipayaJandrapenta; RCV- RajampetChitvelVenkatarajpalli; RKK- Rajampet Kodur K. V. bhavi; TBB- Tirupati BalapalliBalapalli West; TCT- Tirupati ChamalaTalacona centra; TTP- Tirupati TirupatiPapanashini; CSM- Chittoor East SrikalahastiMelachur; CPV- Chittoor East Puttur Vadamala Peta.\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003e\u003cstrong\u003eTable 2:\u0026nbsp;\u003c/strong\u003eGenetic diversity indices across 16 microsatellite loci for 22 populations of \u003cem\u003ePterocarpus santalinus\u003c/em\u003e\u003c/p\u003e\n\u003ctable border=\"1\" cellspacing=\"0\" cellpadding=\"0\" width=\"616\"\u003e\n \u003ctbody\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eLocus\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eN\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNa\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNe\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eI\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eHo\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eHe\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePIC\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eF\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eF\u003csub\u003eIS\u003c/sub\u003e\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eF\u003csub\u003eST\u003c/sub\u003e\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNm\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePIN-82\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e12.82\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e8.85\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e2.29\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.7\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.87\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.18\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.08\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e2.92\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eSSR-3\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e4.91\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e2.71\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.17\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.92\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.68\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.61\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.52\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.23\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eSSR-6\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e20\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e11.55\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e7.83\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e2.13\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.61\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.84\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.95\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.31\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.28\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.12\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e1.85\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eSSR-8\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e9\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e5.89\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.84\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.45\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.78\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.42\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.42\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.17\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e1.2\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-2\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e3.77\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e2.34\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.72\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.12\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.36\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.91\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.73\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.65\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.61\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.16\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-5\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e5.36\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e3.45\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.13\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.28\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.54\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.57\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.47\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.43\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.33\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-6\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e6.36\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e4.23\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.24\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.24\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.54\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.95\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.62\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.56\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.32\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-10\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e14\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e6.18\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e3.77\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.35\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.31\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.64\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.58\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.52\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.32\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.53\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-18\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e8.95\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e5.71\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.8\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.59\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.76\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.27\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.22\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e1.06\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-20\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e5.5\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e3.16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.17\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.17\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.55\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.92\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.71\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.69\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.4\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.37\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-24\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e10.41\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e6.81\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.9\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.38\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.75\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.95\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.55\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.5\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.21\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.96\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-26\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e7.68\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e5.23\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.54\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.66\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.95\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.73\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.71\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.31\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.55\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-29\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e8.86\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e5.78\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.69\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.5\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.71\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.93\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.35\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.31\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.23\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.82\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-30\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e8.82\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e5.2\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.61\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.39\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.67\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.95\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.49\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.41\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.29\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.61\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-31\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e7.14\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e4.09\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.48\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.25\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.66\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.66\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.62\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.3\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.58\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePSSSR-32\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e7.36\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e4.71\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e1.54\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e0.14\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e0.68\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e0.96\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e0.82\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e0.8\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.3\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e0.59\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 85px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eMean\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 50px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 51px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e7.79\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e4.99\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e1.52\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 45px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e0.34\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 55px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e0.65\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 47px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e0.94\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 52px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e0.54\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 53px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e0.5\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e0.31\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 44px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e0.82\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd colspan=\"12\" valign=\"top\" style=\"width: 616px;\"\u003e\n \u003cp\u003eN: mean number of samples, Na: number of alleles, Ne: number of effective alleles, I: Shannon\u0026apos;s Information Index, Ho: observed heterozygosity, He: expected heterozygosity, PIC: polymorphic information content, F: fixation index, F\u003csub\u003eIS\u003c/sub\u003e: inbreeding coefficient within individual relative to total, F\u003csub\u003eST\u003c/sub\u003e: inbreeding coefficient within subpopulation relative to total, N\u003csub\u003em\u003c/sub\u003e: gene flow.\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003e\u003cstrong\u003eTable 3:\u0026nbsp;\u003c/strong\u003eAnalysis of genetic diversity in 22 populations of \u003cem\u003ePterocarpus santalinus\u003c/em\u003e using 16 microsatellite markers.\u003c/p\u003e\n\u003ctable border=\"1\" cellspacing=\"0\" cellpadding=\"0\" width=\"645\"\u003e\n \u003ctbody\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePopulation\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eN\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNa\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNe\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eI\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eHo\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eHe\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eF\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePa\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePPL\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eGGS\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e5.88\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e3.92\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.23\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.20\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.57\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.75\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNUD\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e8.63\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e5.05\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.59\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.51\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.69\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.30\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.38\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNAK\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e20\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e10.00\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e6.03\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.81\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.20\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.75\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.72\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e2.13\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNVV\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e8.06\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.32\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.51\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.42\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.64\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.38\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.56\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNRA\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e5.19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e3.27\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.11\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.53\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.70\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e88%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePPT\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e8.13\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.77\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.65\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.34\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.71\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.54\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.56\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePVT\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e5.56\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e3.59\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.00\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.20\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.67\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.25\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e75%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePBB\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e14\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e6.56\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e3.95\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.43\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.66\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.34\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.75\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eKSM\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e7.50\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.45\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.54\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.37\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.67\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.50\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.25\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e94%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eKVP\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e6.69\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.42\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.36\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.29\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.59\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.62\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.50\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e94%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eKKM\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e7.63\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.50\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.60\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.45\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.71\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.40\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eKRG\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e7.63\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.06\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.53\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.33\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.68\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.55\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.75\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eKOD\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e5.81\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e3.80\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.21\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.27\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.57\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.63\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.56\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e94%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eRRS\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e7.31\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.40\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.53\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.41\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.67\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.41\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.25\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e94%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eRSJ\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e6.81\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e3.99\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.32\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.29\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.57\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.63\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e94%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eRCV\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e9.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e6.82\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.96\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.52\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.81\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.34\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.75\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eRKK\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e7.00\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.64\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.28\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.27\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.55\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.67\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.13\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e94%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eTBB\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e3.55\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.03\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.13\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.49\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.81\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.25\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e81%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eTCT\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.63\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e3.46\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.01\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.10\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.49\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.88\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e88%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eTTP\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e12.31\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e9.21\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e2.27\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.52\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.86\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.40\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.50\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eCSM\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e11.81\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e9.12\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e2.20\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.46\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.84\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.47\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eCVP\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e20\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e13.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e8.39\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e2.29\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.67\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.87\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.22\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.31\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 69px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eMean\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e16\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e7.79\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e4.99\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e1.52\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.34\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.65\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.54\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.67\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 64px;\"\u003e\n \u003cp\u003e0.95\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003eN: number of samples Na: number of alleles, Ne: number of effective alleles,\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eI: Shannon\u0026apos;s Information Index, Ho: observed heterozygosity, He: expected heterozygosity,\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eF: fixation index, Pa: number of private alleles, PPL: percent polymorphic loci.\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eGGS\u003cstrong\u003e-\u003c/strong\u003eGiddaluruGiddaluruSingasanipalli;NUD-Nellore Udayagiri \u0026nbsp;Devammacheruvu; NAK- Nellore \u0026nbsp;AtmakurKadarinaidupalli ; NVV- Nellore Venkatagiri \u0026nbsp;Vembaluru; NRA- NandyalRudravaramAhobilam North; PPT- ProddaturPorumamillaTekurpeta; PVT- ProddaturVanipentaTippireddypalli; PBB- ProddaturBadvelBalayapalli; KSM- Kadapa SiddavatamMaddur; KVP- Kadapa VempalliPolathala; KKM- Kadapa KadapaMaddimadngu; KRG- Kadapa RayachotiGuvalacheruvu; KOD- Kadapa OntimittaDasarala Doddi; RRS- RajampetRajampet Sri RangarajaPalem; RSJ- RajampetSanipayaJandrapenta; RCV- RajampetChitvelVenkatarajpalli; RKK- Rajampet Kodur K. V. bhavi; TBB- Tirupati BalapalliBalapalli West; TCT- Tirupati ChamalaTalacona centra; TTP- Tirupati TirupatiPapanashini; CSM- Chittoor East SrikalahastiMelachur; CPV- Chittoor East Puttur Vadamala Peta.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eTable 4:\u0026nbsp;\u003c/strong\u003eAnalysis of molecular variance (AMOVA) for 361 individuals of \u003cem\u003ePterocarpus\u0026nbsp;\u003c/em\u003e\u003cem\u003esantalinus\u003c/em\u003e populations.\u003c/p\u003e\n\u003ctable border=\"0\" cellspacing=\"0\" cellpadding=\"0\" width=\"487\"\u003e\n \u003ctbody\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 161px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eSource\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 71px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eDegree of freedom\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 74px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eSum of squares\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 67px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eMean of squares\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 96px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eVariance components\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 18px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e% of variation\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 161px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eAmong Populations\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 71px;\"\u003e\n \u003cp\u003e21\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 74px;\"\u003e\n \u003cp\u003e1591.32\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 67px;\"\u003e\n \u003cp\u003e75.77\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 96px;\"\u003e\n \u003cp\u003e2.14\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 18px;\"\u003e\n \u003cp\u003e28%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 161px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eWithin Populations\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 71px;\"\u003e\n \u003cp\u003e700\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 74px;\"\u003e\n \u003cp\u003e3862.87\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 67px;\"\u003e\n \u003cp\u003e5.51\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 96px;\"\u003e\n \u003cp\u003e5.51\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 18px;\"\u003e\n \u003cp\u003e72%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 161px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eTotal\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 71px;\"\u003e\n \u003cp\u003e721\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 74px;\"\u003e\n \u003cp\u003e5454.19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 67px;\"\u003e\n \u003cp\u003e\u0026nbsp;\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 96px;\"\u003e\n \u003cp\u003e7.66\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 18px;\"\u003e\n \u003cp\u003e100%\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003e\u003cstrong\u003eTable 5:\u0026nbsp;\u003c/strong\u003eGenetic variation in different girth classes of \u003cem\u003ePterocarpus santalinus.\u003c/em\u003e\u003c/p\u003e\n\u003ctable border=\"0\" cellspacing=\"0\" cellpadding=\"0\" width=\"469\"\u003e\n \u003ctbody\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 113px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eGirth Class (cm)\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 50px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eN\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 53px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNa\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNe\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 52px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eI\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eHo\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eHe\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 48px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eF\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 113px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eGC-1 (0-10)\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 50px;\"\u003e\n \u003cp\u003e88\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 53px;\"\u003e\n \u003cp\u003e32.81\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e16.62\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 52px;\"\u003e\n \u003cp\u003e3.09\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e0.35\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 48px;\"\u003e\n \u003cp\u003e0.63\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 113px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eGC-2 (10-20)\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 50px;\"\u003e\n \u003cp\u003e88.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 53px;\"\u003e\n \u003cp\u003e32.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e16.73\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 52px;\"\u003e\n \u003cp\u003e3.08\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e0.35\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 48px;\"\u003e\n \u003cp\u003e0.63\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 113px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eGC-3 (20-30)\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 50px;\"\u003e\n \u003cp\u003e86.19\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 53px;\"\u003e\n \u003cp\u003e32.38\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e16.68\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 52px;\"\u003e\n \u003cp\u003e3.08\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e0.36\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 48px;\"\u003e\n \u003cp\u003e0.62\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 113px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eGC-4 (30-\u0026gt;)\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 50px;\"\u003e\n \u003cp\u003e83.38\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 53px;\"\u003e\n \u003cp\u003e30.69\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e16.30\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 52px;\"\u003e\n \u003cp\u003e3.05\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e0.34\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 48px;\"\u003e\n \u003cp\u003e0.64\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 113px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eMean\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 50px;\"\u003e\n \u003cp\u003e86.53\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 53px;\"\u003e\n \u003cp\u003e32.08\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e16.58\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 52px;\"\u003e\n \u003cp\u003e3.08\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e0.35\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 51px;\"\u003e\n \u003cp\u003e0.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 48px;\"\u003e\n \u003cp\u003e0.63\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003eN: mean number of samples, Na: number of alleles, Ne: number of effective alleles,\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eI: Shannon\u0026apos;s Information Index, Ho: observed heterozygosity, He: expected heterozygosity,\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eF: fixation index.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eTable 6:\u0026nbsp;\u003c/strong\u003ePearson correlation analysis between genetic diversity and environmental factors.\u003c/p\u003e\n\u003ctable border=\"1\" cellspacing=\"0\" cellpadding=\"0\" width=\"642\"\u003e\n \u003ctbody\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 74px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eVariable\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePearson\u0026rsquo;s\u003c/strong\u003e\u003c/p\u003e\n \u003cp\u003e\u003cstrong\u003eCoefficient\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 73px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eLatitude\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 94px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eAltitude(m)\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 105px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eAnnual Temperature\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 103px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eAnnual Precipitation\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 103px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eRelative Humidity\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd rowspan=\"2\" valign=\"top\" style=\"width: 74px;\"\u003e\n \u003cp\u003eNa\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003er\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.405\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.036\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.318\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.655\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.544\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003ep\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.061\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.874\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.149\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.001\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.009\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd rowspan=\"2\" valign=\"top\" style=\"width: 74px;\"\u003e\n \u003cp\u003eHo\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003er\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.328\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.136\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.284\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.308\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.283\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003ep\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.136\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.546\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.200\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.163\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.202\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd rowspan=\"2\" valign=\"top\" style=\"width: 74px;\"\u003e\n \u003cp\u003eHe\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003er\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.320\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.083\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.206\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.502\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.391\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003ep\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.146\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.713\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.357\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.017\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.072\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd rowspan=\"2\" valign=\"top\" style=\"width: 74px;\"\u003e\n \u003cp\u003eI\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003er\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.381\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.036\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.286\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.580\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.473\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003ep\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.080\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.873\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.198\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.005\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.026\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd rowspan=\"2\" valign=\"top\" style=\"width: 74px;\"\u003e\n \u003cp\u003eF\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003er\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.193\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.217\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.187\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.146\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.130\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003ep\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.391\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.332\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.403\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.517\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.564\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd rowspan=\"2\" valign=\"top\" style=\"width: 74px;\"\u003e\n \u003cp\u003ePa\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003er\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.360\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.100\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.085\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.675\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.454\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd valign=\"top\" style=\"width: 89px;\"\u003e\n \u003cp\u003ep\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 73px;\"\u003e\n \u003cp\u003e0.100\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 94px;\"\u003e\n \u003cp\u003e0.657\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 105px;\"\u003e\n \u003cp\u003e0.706\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.001\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 103px;\"\u003e\n \u003cp\u003e0.034\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003eNa: number of alleles, Ho: observed heterozygosity, He: expected heterozygosity, I: Shannon\u0026apos;s Information Index, F: fixation index, Pa: number of private alleles.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eTable 7:\u0026nbsp;\u003c/strong\u003eGenetic diversity analysis of \u003cem\u003ePterocarpus santalinus\u003c/em\u003e based on the different forest circlewise distributions in Eastern Ghats, Andhra Pradesh, India.\u003c/p\u003e\n\u003ctable border=\"0\" cellspacing=\"0\" cellpadding=\"0\" width=\"576\"\u003e\n \u003ctbody\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eCircle\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eN\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNa\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNe\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eI\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eHo\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eHe\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eF\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePa\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003eGuntur\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e68\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e22.94\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e11.6\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e2.63\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e0.34\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e0.9\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e0.63\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e3.63\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003eKurnool\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e137\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e26.63\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e10.95\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e2.67\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e0.31\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e0.9\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e0.65\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e5.69\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003eTirupati\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e140\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e35.38\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e14.86\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e3.01\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e0.38\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e0.93\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e0.59\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e10.88\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eMean\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e115\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e28.31\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e12.47\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e2.77\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e0.35\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e0.91\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e0.62\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003e6.73\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003c/tbody\u003e\n\u003c/table\u003e\n\u003cp\u003eN: mean number of samples, Na: number of alleles, Ne: number of effective alleles,\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eI: Shannon\u0026apos;s Information Index, Ho: observed heterozygosity, He: expected heterozygosity, F: fixation index, Pa: number of private alleles.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eTable 8:\u0026nbsp;\u003c/strong\u003eGenetic diversity analysis of \u003cem\u003ePterocarpus santalinus\u003c/em\u003e based on the different forest divisionwise distributions in Eastern Ghats, Andhra Pradesh, India\u003c/p\u003e\n\u003ctable border=\"0\" cellspacing=\"0\" cellpadding=\"0\" width=\"576\"\u003e\n \u003ctbody\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eDivision\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eN\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNa\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eNe\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eI\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eHo\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eHe\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eF\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003ePa\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003c/tr\u003e\n \u003ctr\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e\u003cstrong\u003eCTR\u003c/strong\u003e\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e33.44\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e19.69\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e11.68\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e2.67\u003c/p\u003e\n \u003c/td\u003e\n \u003ctd style=\"width: 64px;\"\u003e\n \u003cp\u003e0.58\u003c/p\u003e\n \u003c/td\u003e\n 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Nandyal; PDT-Podratur; RJT-Rajampet; TPT-Tirupati\u003c/p\u003e\n\u003cp\u003eN: mean number of samples, Na: number of alleles, Ne: number of effective alleles,\u0026nbsp;\u003c/p\u003e\n\u003cp\u003eI: Shannon\u0026apos;s Information Index, Ho: observed heterozygosity, He: expected heterozygosity, F: fixation index, Pa: number of private alleles.\u003c/p\u003e"}],"fulltextSource":"","fullText":"","funders":[],"hasAdminPriorityOnWorkflow":false,"hasManuscriptDocX":true,"hasOptedInToPreprint":true,"hasPassedJournalQc":"","hasAnyPriority":false,"hideJournal":false,"highlight":"","institution":"","isAcceptedByJournal":true,"isAuthorSuppliedPdf":false,"isDeskRejected":"","isHiddenFromSearch":false,"isInQc":false,"isInWorkflow":false,"isPdf":false,"isPdfUpToDate":true,"isWithdrawnOrRetracted":false,"journal":{"display":true,"email":"
[email protected]","identity":"discover-forests","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":false,"externalIdentity":"","sideBox":"Learn more about [Discover Forests](https://link.springer.com/journal/44415)","snPcode":"44415","submissionUrl":"https://submission.nature.com/new-submission/44415/3","title":"Discover Forests","twitterHandle":"","acdcEnabled":true,"dfaEnabled":true,"editorialSystem":"stoa","reportingPortfolio":"Springer Open","inReviewEnabled":true,"inReviewRevisionsEnabled":true},"keywords":"Pterocarpus santalinus, Red Sader, Eastern Ghats, Genetic diversity, Microsatellite, Population structure","lastPublishedDoi":"10.21203/rs.3.rs-7357158/v1","lastPublishedDoiUrl":"https://doi.org/10.21203/rs.3.rs-7357158/v1","license":{"name":"CC BY 4.0","url":"https://creativecommons.org/licenses/by/4.0/"},"manuscriptAbstract":"\u003cp\u003e\u003cem\u003ePterocarpus santalinus\u003c/em\u003e, or Red Sanders, is an Indian native tree species that is under threat of decline in natural populations due to illicit felling in Eastern Ghats. In the present study, we assessed the genetic variation and population structure across 22 natural populations 16 highly polymorphic SSR markers in 361 individuals. The average number of alleles (Na) was 7.79, with an expected heterozygosity (He) of 0.65, which is lower than that of other woody plants. Interestingly, the Tirupati base-Sadashiva Kona population presented the greatest genetic diversity (He\u0026thinsp;=\u0026thinsp;0.87), whereas the Chitaleti Pati base Camp population presented the least genetic diversity (He\u0026thinsp;=\u0026thinsp;0.44). The analysis revealed that extensive genetic variation among populations (72%) contrasted with that within populations (28%). The Tirupati circle (He\u0026thinsp;=\u0026thinsp;0.93) and Chittor divisions (He\u0026thinsp;=\u0026thinsp;0.91) presented high genetic diversity. The FST values revealed considerable genetic differentiation among the populations, with a value of 0.31 and poor gene flow (Nm\u0026thinsp;=\u0026thinsp;0.82). Cluster analysis of 361 samples from 22 populations revealed three main genetic groups. Populations located at lower latitudes presented greater genetic diversity than those located at higher latitudes did, and geographical and genetic distances were positively correlated. The population as a whole presented moderate level of genetic diversity, with clear variation between the populations at lower and higher latitudes and positive geographical and genetic correlations. These results indicate the importance of conserving \u003cem\u003eP. santalinus\u003c/em\u003e.\u003c/p\u003e","manuscriptTitle":"Genetic diversity and population structure analysis of the endangered endemic and economically important plant, Red Sanders, distributed in the Eastern Ghats. India","msid":"","msnumber":"","nonDraftVersions":[{"code":1,"date":"2025-09-05 12:53:50","doi":"10.21203/rs.3.rs-7357158/v1","editorialEvents":[{"type":"communityComments","content":0},{"type":"decision","content":"Revision requested","date":"2025-11-13T21:24:46+00:00","index":"","fulltext":""},{"type":"editorInvitedReview","content":"","date":"2025-10-07T02:12:08+00:00","index":"hide","fulltext":""},{"type":"editorInvitedReview","content":"","date":"2025-10-03T22:32:40+00:00","index":"hide","fulltext":""},{"type":"reviewerAgreed","content":"14163217813953287469636632113954428289","date":"2025-10-02T11:55:36+00:00","index":"hide","fulltext":""},{"type":"reviewerAgreed","content":"262708790454179063068796831435295047871","date":"2025-09-30T19:43:01+00:00","index":"hide","fulltext":""},{"type":"reviewerAgreed","content":"186267480443447535349672285340517346203","date":"2025-09-26T10:24:51+00:00","index":"hide","fulltext":""},{"type":"reviewerAgreed","content":"59578088546609500215509917669384440436","date":"2025-09-10T02:12:59+00:00","index":"hide","fulltext":""},{"type":"editorInvitedReview","content":"","date":"2025-08-31T15:15:26+00:00","index":"hide","fulltext":""},{"type":"reviewerAgreed","content":"47931959086379014291456288466173586870","date":"2025-08-30T06:30:19+00:00","index":"hide","fulltext":""},{"type":"reviewersInvited","content":"","date":"2025-08-29T06:55:00+00:00","index":"","fulltext":""},{"type":"editorAssigned","content":"","date":"2025-08-26T09:35:03+00:00","index":"","fulltext":""},{"type":"editorInvited","content":"","date":"2025-08-25T08:00:21+00:00","index":"","fulltext":""},{"type":"checksComplete","content":"","date":"2025-08-22T16:46:42+00:00","index":"","fulltext":""},{"type":"submitted","content":"Discover Forests","date":"2025-08-22T16:41:27+00:00","index":"","fulltext":""}],"status":"published","journal":{"display":true,"email":"
[email protected]","identity":"discover-forests","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":false,"externalIdentity":"","sideBox":"Learn more about [Discover Forests](https://link.springer.com/journal/44415)","snPcode":"44415","submissionUrl":"https://submission.nature.com/new-submission/44415/3","title":"Discover Forests","twitterHandle":"","acdcEnabled":true,"dfaEnabled":true,"editorialSystem":"stoa","reportingPortfolio":"Springer Open","inReviewEnabled":true,"inReviewRevisionsEnabled":true}}],"origin":"","ownerIdentity":"368c685c-a806-468b-bf57-9e6057406930","owner":[],"postedDate":"September 5th, 2025","published":true,"recentEditorialEvents":[],"rejectedJournal":[],"revision":"","amendment":"","status":"under-review","subjectAreas":[],"tags":[],"updatedAt":"2026-05-15T21:38:47+00:00","versionOfRecord":[],"versionCreatedAt":"2025-09-05 12:53:50","video":"","vorDoi":"","vorDoiUrl":"","workflowStages":[]},"version":"v1","identity":"rs-7357158","journalConfig":"researchsquare"},"__N_SSP":true},"page":"/article/[identity]/[[...version]]","query":{"redirect":"/article/rs-7357158","identity":"rs-7357158","version":["v1"]},"buildId":"8U1c8b4HqxoKbykW_rLl7","isFallback":false,"isExperimentalCompile":false,"dynamicIds":[84888],"gssp":true,"scriptLoader":[]}
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