Next Article in Journal
Osteichthyan Fishes from the uppermost Norian (Triassic) of the Fuchsberg near Seinstedt, Lower Saxony (Germany)
Previous Article in Journal
Is the Arbuscular Mycorrhizal Fungus Funneliformis mosseae a Suitable Agent to Control Criconematid Populations?
Previous Article in Special Issue
Genome-Wide Screening for SNPs Associated with Stature in Diverse Cattle Breeds
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Genome-Wide SNP Analysis Reveals the Genetic Diversity and Population Structure of the Domestic Reindeer Population (Rangifer tarandus) Inhabiting the Indigenous Tofalar Lands of Southern Siberia

by
Veronika Ruslanovna Kharzinova
1,*,
Arsen Vladimirovich Dotsev
1,
Anastasiya Dmitrievna Solovieva
1,
Larisa Delger-Oolovna Shimit
2,
Anton Pavlovich Kochkarev
3,
Henry Reyer
4 and
Natalia Anatolievna Zinovieva
1
1
L.K. Ernst Federal Research Center for Animal Husbandry, Dubrovitsy, Podolsk Municipal District, Podolsk 142132, Russia
2
Department of Veterinary Medicine and Animal Science, FGBOU VPO Tuvan State University, Kyzyl 663246, Russia
3
FSBI “State Reserve Central Siberian”, Turukhansky District, Bor 663246, Russia
4
Institute of Genome Biology, Research Institute for Farm Animal Biology (FBN), Mecklenburg-Vorpommern, 18196 Dummerstorf, Germany
*
Author to whom correspondence should be addressed.
Diversity 2022, 14(11), 900; https://doi.org/10.3390/d14110900
Submission received: 31 August 2022 / Revised: 29 September 2022 / Accepted: 20 October 2022 / Published: 25 October 2022

Abstract

:
Operating under the assumption that decline in population size increases the threat of loss of genetic diversity, herein, our first aim was to monitor and document the genetic diversity and population structure of the endemic Tuva–Tofalar reindeer, the number of which has seen a dramatic decrease. Second, we were interested in understanding of Tuva reindeer genetic relationship with four officially recognized reindeer breeds, whose wild populations inhabit the Far North of Russia, as well as with the domestic reindeer making up the Mongolian population. Our results, based on the genome-wide SNP genotypes generated by the BovineHD BeadChip, revealed a low level of genetic variability of Tuva population in terms of the values of both allelic and genetic diversity. The ADMIXTURE analysis, the PCA plot, and the Neighbor Net network results, showed that Tuva population shared genetic background with reindeer inhabiting Mongolia, an implication of their common origin. Moreover, all statistic approaches used in our study showed a distinctive shared genetic structure revealed in independent clusters found in the composition of: an admixed cluster of Tuvan and Mongolian populations, a cluster of domestic reindeer breeds, and a cluster of the wild populations—all of which indirectly points to the possibility of the independent origins (with regard to the domestication) of the reindeer groups studied herein. We believe that our findings will contribute to the formation of a rational basis for solving problems related to the conservation of domestic Tuva-Tofalar reindeer in order to increase the number of this substantial reindeer population which will contribute to the sustainable functioning of ecosystems and the lives and culture of indigenous peoples inhabiting the southern sections of Eastern Siberia.

1. Introduction

More than 50% of the territory of the Russian Federation is located in the regions of the Far North, where traditional nature management forms the basis for the lives of indigenous ethnic groups. The traditional occupation of these indigenous peoples is reindeer herding, which is closely interrelated with their survival in their native land [1].
The Republic of Tuva is the southernmost habitat of reindeer populations and is divided into 16 districts. It borders the Republics of Buryatia and Khakassia, and it includes the territories of Irkutsk, Krasnoyarsk, and Altai as well as Mongolia. The well-being of Tuvans, Tofalars, and other peoples of Southern Siberia has historically strictly depended on hunting, which required the means of proper transportation. Thus, the reindeer proved to be the only animal that would allow indigenous people to explore the vast expanses of the taiga. As a result, the local Tuva–Tofalar group of reindeer was created (reindeer of the Todzhinsky District of the Republic of Tuva and the Nizhneudinsky District of the Irkutsk Region) [2]. Reindeer of the Tuva–Tofalar population are tall with rather long bodies, deep chests, well-developed muscles, and are light in color (Figure 1).
Currently, 77% of the total number of domestic reindeer in the Republic of Tuva is in the Todzhinsky District, where reindeer herding is the traditional occupation of the small northern community of Tuvans-Todzhans. This district is included in the Eastern Sayan Mountain Region and borders the territories inhabited by small ethnic groups, such as the Tofa (Tofalars, in the Irkutsk Region), the Soyots (the Republic of Buryatia), and the Dukha (also known as Tsaatan, the Khubsugul Province of Mongolia), who are also engaged in reindeer herding. These unique and endangered reindeer-herding cultures of Inner Asia represent some of the oldest cultures who maintain the northern reindeer as their totem animal.
Unlike the large-scale reindeer and caribou ranchers of Scandinavia, northern Siberia, Alaska, and Canada, who live in tundra areas and raise large herds of reindeer primarily for meat, these cultures practice a peculiar form of reindeer husbandry, raising small herds of reindeer in mountainous forest areas (taiga) for their milk and to be used as a means of transport, while wild game is the principal source of food. Moreover, it is important to note that the four representative cultures in question developed based on reindeer domestication in the remote, fragile, and ecologically diverse transition belt between the Siberian boreal forest and the Inner Asia steppes. Given this fact, they can be considered “cultures of reindeer habitat”, in other words, peoples directly related to the high mountain reindeer habitats, where they have lived under the conditions dictated by the natural ebb and flow of the ecology of their region [2,3,4,5].
Despite the fact that the local Tuva–Tofalar population of reindeer still occupies an important place in the social and cultural activities of the indigenous peoples and is characterized by distinctive morphological features, this population has not been selected as an officially recognized breed, unlike the other four reindeer populations [6].
The census determined population size of domestic reindeer in Russia’s Far North, as of 1 September 2021, was confirmed to be 1,900,000 individuals [7]. However, recent attention has been drawn to a reduction in the Tuva reindeer population from 15,000 in 1990 to 1400 individual animals in 2019. It is believed that intense global factors, such as climate change and habitat degradation, may have led to the decline in the Tuvan reindeer population. The current higher winter temperatures cause snow to melt and refreeze or to fall as rain, which also refreezes. This causes an icy sheet to encase the lichen on the ground, which is the reindeers’ main winter food supply. The reindeer simply cannot dig through the ice, and often the ice freezes over such a large area that they starve while wandering, trying to reach the plants that they can smell right beneath them. Thus, reindeer have less and less to eat, and their migration routes are being broken apart by roads, fences, and railway lines. The effects of climate change in addition to all this make an already difficult situation worse. Many reindeer herders now need to purchase feed for their reindeer during winter, an extra cost that may be difficult for owners of smaller herds to afford.
An additional explanation of the domestic Tuvan reindeer decline may lie in the classifying of this population as a peripheral one. According to Kesić et al. [8], the peripheral populations are defined as populations on the edge of species distribution that usually represent reservoirs of biodiversity. Growing under stronger selection pressures than core populations, rear-edge populations are frequently subjected to various biotic and abiotic stress factors, which negatively affect their reproductive success and survival.
Considering the assumption that a decreasing population size increases the threat of loss of genetic diversity by reducing the ability of a population to adapt to environmental changes [9], this implies the increasing importance of gaining insights into the nuclear genetic diversity of the Tuva population.
Molecular genetic techniques have revolutionized our ability to characterize genetic variation [10]. The employment of nuclear markers is one of the most powerful means for studying the genetic diversity, the calculation of genetic distances, the detection of bottlenecks and admixture due to a high degree of polymorphism, random distribution across the genome, codominance, and neutrality with respect to selection [11]. The power provided by single nucleotide polymorphism (SNP) markers detected using genome-wide sequencing approaches led to their increased use in genetic conservation studies [12]. SNPs are popular for investigating levels of genetic differentiation among remnant populations and for comparing levels and patterns of genetic variation within populations [13,14], which provide information on the adaptive potential of populations [15], as well as patterns of inbreeding and relatedness [16]. Results from SNP studies are being interpreted for use in management decisions that include genetic rescue, genetic mixing, and founder selection in threatened species programs [17,18].
The successful application of SNP genotyping arrays to study the genetic biodiversity of members of the Cervidae family has already been proven and is evidenced by an abundance of scientific papers [19,20,21,22] on the matter. In fact, we have previously presented data on the current genetic composition and population structure of domestic and wild populations inhabiting the Russian Far North using SNP array [23,24]. Despite the relevance of the previous articles, the Tuvan population has not been covered, leaving questions regarding its genetic structure and diversity wide open. In this regard, the current study was undertaken in order to answer the above issues under question.
In the current research, on the basis of the genotypes generated by the Bovine HD BeadChip, we sought to achieve two goals: first, to shed light on the current state of genetic diversity and population structure of domestic Tuva reindeer; and second, to establish the population genetic relationship with four officially recognized breeds and wild populations inhabiting the Russian Far North and domestic reindeer inhabiting Mongolia. Moreover, by studying the Tuva–Tofalar reindeer and their potential, our core intention was to draw attention to the vulnerability of global genetic resources and the necessity of taking timely action to protect these resources, something that will enhance humankind’s capability to adapt to future climate changes.

2. Experiments

2.1. Ethics Statement

The current study does not involve any endangered or protected animals and all procedures were conducted according to the ethical guidelines of the L.K. Ernst Federal Science Center for Animal Husbandry. The protocol for the study, No. 2 (28 April 2022), was approved by the Commission on the Ethics of Animal Experiments of the L.K. Ernst Federal Science Center for Animal Husbandry.
The tissue samples of domestic reindeer were collected by trained personnel under strict veterinary rules in accordance with the rules for conducting laboratory research (tests) in the implementation of the veterinary control (supervision) approved by a Council Decision of the Eurasian Economic Commission No. 80 (10 November 2017) during the corral work on the herd. The muscle tissue samples of the wild reindeer were collected during scientific expeditions after obtaining collection permits granted by the Department of Hunting of the Republic of Sakha and by the Ministry of Ecology and Rational Nature Management of the Krasnoyarsk Territory in compliance with Russian Federation Law No. 209-FZ of 24 July 2009.
SNP genotypes of all domestic breeds, domestic Mongolian population, and wild reindeer samples involved in this study were taken from the Bioresource collection of the L.K. Ernst Federal Research Center for Animal Husbandry.

2.2. Sample Collection, DNA Extraction, and Dataset Generation

The biomaterial of the Tuva–Tofalar population of reindeer (TUVA, n = 28) was taken from a herd bred in the northeast of the Tuva Republic (Todzhinsky District) during the corral work and was stored at –20 °C until DNA extraction. Genomic DNA was extracted with commercial DNA-Extran-2 kits (JSC Syntol, Russia) following the manufacturer’s instructions. The DNA samples were quantified using a method of visualization in bands by 1% agarose gel electrophoresis. The concentration of the dsDNA was measured on a Qubit 3.0 fluorimeter (Thermo Fisher Scientific (formerly Life Technologies Waltham, MA, USA), Wilmington, DE, USA). DNA purity was determined by evaluating the absorption ratio of A260/A280 on a NanoDrop2000 spectrophotometer (Thermo Fisher Scientific, Wilmington, DE, USA). The concentration of DNA, on average, was 67.15 ng/μL.
To determine the possible genetic contribution to the Tuva reindeer population’s structure, we employed the SNP genotypes dataset of all officially recognized breeds in Russia: the Nenets breed from the Nenets Autonomous District (NEN, n = 33); the Even breed from the Republic of Sakha (Yakutia) (EVN, n = 19); the Evenk breed from both breeding regions, the Republic of Sakha (Yakutia) (EVK_Y, n = 20) and the Krasnoyarsk Territory (EVK_K, n = 20); and the Chukotka breed from the Chukotka Autonomous District (CHU, n = 25). Since the Tuva Republic borders Mongolia in the south, the SNP genotypes of domestic Mongolian population samples (MONG, n = 11) were included in the dataset.
Additionally, the genotypes of wild reindeer of the taiga (TG, n = 16) and tundra (TU, n = 11) populations inhabiting the territory of the Krasnoyarsk Territory and Yakutia, respectively, were included in our dataset as an outgroup. The coordinate range of the covered area in the Krasnoyarsk Territory was from 64 to 69° N and from 113 to 117° E and in Yakutia from 64 to 69° N and from 113 to 117° E. A map of breeding zones of domestic reindeer and the sampling sites where specimens used in this study were collected is presented in Figure 2.
The R packages maps and mapdata [25] were applied for plotting the geographic map of the reindeer sampling areas.

2.3. SNP Genotyping and Data Processing

A total of 183 DNA samples were genotyped using the Illumina BovineHD Genotyping BeadChip. The quality control of the SNP-genome sequencing of the reindeer samples was performed by setting a cutoff of 0.5 for the GenCall and GenTrain scores [26] using PLINK v1.90 [27]. The SNP dataset was filtered to remove loci located on the sex chromosomes of the UMD 3.1 assembly [28], as well as loci genotyped in <90% of individuals and rare alleles with geno 0.1—mind 0.1—maf 0.05 plink commands. SNPs with a value of linkage disequilibrium (LD) between a pair of single-nucleotide polymorphisms equal to r2 > 0.05 were also excluded from further analyses. After conducting all filtering steps, the final dataset included 183 individuals and comprised 6786 SNPs.
Calculation of diversity statistics, including the observed heterozygosity (HO), the unbiased expected heterozygosity (UHE) [29], the inbreeding coefficient (FIS) based on the unbiased expected heterozygosity, the rarefied allelic richness (AR), and pairwise genetic differentiation values (FST) [30], was conducted using the R package “diveRsity” [31].
The resulting relationships obtained based on the pairwise distance matrix of FST measures were graphical represented by the Neighbor Net network using the SplitsTree 4.14.5 software [32].
The genetic population structure of the reindeer was analyzed using principal component analysis (PCA) in PLINK v1.90 and depicted with the R package “ggplot2” [33].
The estimation of individual ancestry derived from our genetic data was performed using the ADMIXTURE v1.3 software [34], while proposing a number of K values ranging from 1 to 10 and visualized using the R package “pophelper” [35]. The optimal value of K value was set as the one having the lowest cross-validation (CV) error.
All input files were created in R version 3.3.2 [36].

3. Results

An assessment of the genetic diversity parameters of the Tuvan reindeer in comparison with domestic breeds, domestic Mongolian, and wild reindeer populations is shown in Table 1.
As per the data in Table 1, the reindeer of TUVA as well as MONG and WLD_TG had the lowest values of allelic richness (AR): 1.507, 1.516, and 1.582, respectively, while the highest values were distributed among the tundra population of the wild reindeer (1.684) and in the Yakut Evenk breed of domestic reindeer (1.679). The observed heterozygosity (HO) ranged between 0.150 in TUVA and 0.185 in EVK_Y. The lowest values of unbiased heterozygosity (UHE) were found in the MONG (0.154) and the TUVA (0.155) as compared with the EVK_Y, the EVN and the WLD_TU, which had practically equal and, in fact, the highest values of the index: 0.189, 0.187, and 0.187, respectively. For almost all the reindeer groups studied, the expected unbiased heterozygosity was higher than the observed heterozygosity with exception of the Mongolian population. Consequently, domestic Mongolian reindeer alone were found to possess excessive heterozygotes as evidenced by the UFIS values: −0.006 [−0.014; 0.002]. The remaining groups of reindeer had a positive UFIS value, but then NEN and EVK_K maintained a 95% confidence interval very close to zero: 0.006 [0.001; 0.011] and 0.012 [0.006; 0.018], respectively.
The ADMIXTURE analysis estimated K = 4 as the best number of ancestors with the lowest cross-validation value (CV, 0.358) (Supplementary Materials, Figure S1). Despite this, we ran ADMIXTURE for value of K = 5, which showed more detailed results (Figure 3).
We found that as K was increased to K  =  5, the Tuvan reindeer showed a common genetic background with the Mongolian population. Meanwhile, at K = 3, in the Tuva population admixed individuals appeared to carry genetic components of two clusters: CHU/WLD_TU/WLD_TG and EVN/EVK_Y/EVK_K/NEN. Furthermore, the proportion of the wild component decreased (K = 4 and K = 5), while admixed individuals with the domestic reindeer cluster retained ancestral background only with EVN/EVK_Y. Among officially recognized breeds, CHU and NEN were revealed to be the most genetically structured, while two breeds inhabiting the Yakutia Region (EVN and EVK_Y) demonstrated a common genetic background. The Evenk breed of the Krasnoyarsk Region disclosed no independent structure representing an admixed genetic component composed of those of reindeer breeds from neighboring geographic regions: the Republic of Sakha (Yakutia) and the Nenets Autonomous District. Wild tundra population revealed a low proportion of admixture from the domestic reindeer, as opposed to the taiga population in which all but one individual showed a total genetic similarity to their assigned cluster.
Further, the genetic structure of Tuva–Tofalar population of reindeer was investigated by the principal component analysis with the results presented in Figure 4.
Initially, we extracted PCA for all of the studied reindeer groups (Figure 4A). PC1 explained the greatest possible variance in the data between two axes (17.42%), detaching the cluster formed by the Tuvan and Mongolian populations from the remaining reindeer. Meanwhile, at PC2 (11.63% of the variance), the location of the TUVA and MONG clusters were intermediate between the two domestic and wild populations. Interestingly, PC2 also placed the Chukotka breed on the same plane as wild populations. To learn more about this finding, we excluded the Tuvan and Mongolian samples from further analysis (Figure 4B,C), as well as that of the wild individuals (Figure 4C). In Figure 4B, PC1 (13.28% of the variance) united all breeds with the exception of those of the Chukotka, separating it along with the independent clusters of the wild populations. The PC2 (12.35% of the variance) distinguished cluster formed by the two breeds of the Yakutia Region (EVN and EVK_Y) and the Chukotka breed from the remaining reindeer groups. The genetic relationship between reindeer breeds is more accurately visualized in Figure 4C. The first principal component (16.14% of the variance) placed in a quadrant is the distinct cluster of the Chukotka breed, while a mixing cluster formed by the Even and the Evenk reindeer of the Yakutia Region fell into a different quadrant. Likewise, the genetic detachment of the Chukotka individuals was reflected by the second principal component (8.87% of the variance) which also revealed a distinct cluster in the Nenets breed in close proximity to the cluster of the Evenk breed inhabiting the Krasnoyarsk Region, placing it on the axis.
Figure 5 presents the results of the neighbor-net analysis which was conducted based on pairwise FST values calculated from SNP genotypes. FST estimates between each pair of reindeer groups are shown in Table S1 (Supplementary Materials, Table S1).
The Tuvan population showed the closest relationship with the Mongolian population, being located at one node (FST = 0.042), while all other domestic and wild reindeer occupied the opposite node on the tree. Among the reindeer breeds, EVN and EVK_Y revealed the lowest genetic distance (FST = 0.014), forming one cluster from which the Chukotka breed branched out. The second cluster consisted of the breeds from the Nenets and Krasnoyarsk Regions (NEN/EVK_K, FST = 0.023). The third cluster is composed of a branch of the tundra and taiga wild populations, which was positioned between the two clusters of the reindeer breeds.

4. Discussion

The last few decades have been marked by comprehensive studies on genetic resources of natural populations of various species in order to conserve and rationally exploit them. This is due to the fact that species may have, or are, experiencing declines in population sizes [37]. Increasing arctic temperatures, precipitation, and an anthropogenic landscape change have affected the decrease in number of caribou and reindeer herds across their circumpolar range. Despite the widespread occurrence of the domestic reindeer in the regions of the Far North Russia, the population census size over the last few decades shifted dramatically from a maximum of 2.5 million heads to a minimum of 1.9 [24,38]. Among all domestic reindeer, the domestic population inhabiting the indigenous Tofalar lands of southern Siberia is considered the smallest one. A sharp reduction of the Tuva reindeer population occurred after the Soviet Union collapse. Then, it kept declining gradually and, as of 2019, it was confirmed to consist of 1400 individuals. Operating under the assumption that the decrease in population size increases the threat of loss of genetic diversity, our research in this study aimed to identify the level of genetic diversity of the Tuva–Tofalar population of reindeer. Furthermore, we intended to find out which niche this domestic population occupies among the reindeer of all officially recognized breeds, including wild populations as well as the domestic reindeer of the Mongolian population. In order to efficiently address these research targets, we used the Illumina BovineHD Genotyping BeadChip to estimate both genetic diversity parameters and the population structure of the Tuva population based on 6786 SNPs. As we had assumed, the Tuva reindeer showed a low level of genetic diversity, as evidenced by the values of both allelic and genetic diversity (Table 1). The pattern revealed was consistent with previous results reported by Stolpovsky et al. [6] based on STR markers. The authors explained the identified patterns in the Tuva population as being based on low migratory activity, which is indicated by its relatively isolated habitat and the process of domestication. A rather high level of genetic diversity in the Tuva population was found by this research through the examination of the mtDNA control region, conducted in 2006 by Kol et al. [39]. Incongruence between our data and that mentioned above may indicate a decrease in the genetic diversity of this reindeer population over the course of time. However, the fact that those results were obtained using a different methodological approach should be noted. As referred to by Petit-Marty et al. [37] a mitochondrial genome evolution has different characteristics than one which is nuclear-genomic in nature, such as haploidy, lack of recombination, and uniparental inheritance.
The low level of genetic diversity of the Tuva population revealed in this study could also be caused by the geographical features of the population organization of this group of reindeer, with reference to the peripheral population, as we assumed and stated in the introduction. The expectation that peripheral populations have little genetic diversity was supported by several ensuing findings. For example, Lewontin [40] reported that small populations are likely to maintain little genetic diversity because of genetic drift. Some authors stated that strong selective forces at the edge of the species’ distribution could erode the genetic diversity of peripheral populations [40,41]. Nevertheless, as referred to by Channell [42], while these expectations of low genetic diversity in peripheral populations are reasonable, they rely on patterns or assumptions that have been accepted uncritically. A closer examination of these patterns or assumptions is, therefore, necessary.
In our findings, the low genetic diversity of the Tuvan reindeer was relatively predictable, whereas the population–genetic relationships of this group with the other domestic and wild reindeer populations turned out to be unforeseen.
With the ADMIXTURE analysis, the common ancestral origin of the genomes of the Tuvan and Mongolian reindeer was seen from K = 2, and this structure did not break down when the number of K was raised (Figure 2). One alternative possibility for the observed pattern might have been caused by both the origin of reindeer herding and the historical events of the two countries. The ethnic composition of the population of modern Mongolia consists of various ethnic groups, including the Tsaatans or Tuvans (or Dukha as they call themselves) who live along the border region of Tuva and Mongolia (the Khubsugul Province) [43]. According to researchers, the term “Tsaatan” appeared in official documents in the 1920s. They were named Tsaatans because they were engaged in reindeer herding [2]. It should be noted that “Tsaa” in Mongolian means: “reindeer”, while “Tsaatan” is “owning a reindeer”. This ethnic group has been seen as being a part of Mongolia at different times in history. In 1926–1927, a border between Mongolia and Tuva was formally established, dividing the pasture territories where the Dukha roamed into two parts. Nevertheless, a strict division of the people occurred only in 1947, when Tuva became a part of the Soviet Union. The state border totally separated the Dukha leaving them on the Soviet side. According to historical data, at that time, many of the older generation of this ethnic group moved with their reindeer from Tuva to Mongolia and settled down there. According to ethnographers, the Dukha and the Tozhu-Tuvan still carry out fully nomadic and semi-nomadic lifestyles in the taiga with their reindeer, subsisting almost entirely on hunting, gathering, and fishing [2,4,44].
Despite the fact that the two ethnic groups have been separated since the Russia–Mongolia border formed in the Eastern Sayan Mountains, a genetic heterogeneity of the Tuvan and Mongolian reindeer population has not been revealed in our study. Furthermore, we noted that the close relationship of the two populations was reflected in both the PCA plot (Figure 4A) and the NeighborNet network (Figure 5).
Nevertheless, our special attention was drawn to the intermediate location of the Tuva and Mongolia reindeer groups with regard to the second principal component of PCA (Figure 4A). As referred to by McVean [45], with PCA, a projection of non-admixed individuals can lead to their placement (location) being intermediate and between two original populations. For example, samples from a third population that either diverged from population A after a split from population B, or one that come from a population that diverged before the A/B split, will (in both cases) be projected between the locations of samples from populations A and B.
A statement that was discovered indirectly points to the possibility of the independent domestication origins of the reindeer groups studied in the current research. This assumption was additionally supported by a distinctive genetic structure manifested by independent clusters composed of an admixed cluster of Tuvan and Mongolian populations, a cluster of domestic reindeer breeds and a cluster of wild populations (Figure 3 and Figure 5).
Our results are, in fact, complementary to previous work with regard to revealing the independent origin of domestic reindeer in Russia and Fennoscandia based on mitochondrial sequences and nuclear microsatellites [46]. The authors have also concluded that some wild reindeer populations have not contributed to the domestic gene pool, suggesting variation in the domestication potential among populations. Moreover, Weldenegodguad et al. [47] applying population genomics analysis, suggested at least two independent reindeer domestication events with genetic lineages originating from different refugial regions after the Last Glacial Maximum.
An explanation of admixed individuals with the genetic component of the domestic reindeer in the cluster of Tuvan and Mongolian populations (Figure 3) has no documented evidence. However, one possible explanation for the observed pattern might be the reindeer exchanges between regions, which are well known.
In the present study, although we used SNPs genotypes that were not included in our previous work [24], the pattern of distribution of the genetic diversity values (the Evenk and Even breeds of Yakutia Region), as well as independent ancestry (the Nenets, the Even and the Chukotka breeds) and the clear admixture proportions between breeds (the EVK_YAK and EVK_KRA), did not change. Moreover, all statistical approaches used in our study more considerably divided domestic and wild populations, which was consistent with previously published results obtained on a different sample set of animals [23]. Additionally, PCA and NeighborNet analysis (Figure 4 and Figure 5) revealed a different genetic structure of the taiga reindeer from their counterparts inhabiting the tundra. In the present study, these differences were more evident than those previously described [23]. Behavioral differences and restrictions in seasonal migration patterns apparently caused divergence in genetic structure between tundra and taiga reindeer.

5. Conclusions

In this study, using a high-density SNP genotypes analysis, we first attempted to fill in missing information with regard to the status of the population genetics of the domestic Tuva–Tofalar local group of reindeer inhabiting the south of Eastern Siberia, along with its genetic relationship to all officially recognized breeds, including the domestic reindeer of the Mongolian population and wild reindeer.
The low level of genetic diversity that was revealed in the Tuvan population was our main concern, since its further loss may lead to a decrease in the adaptive capabilities of the species, as long as genetic diversity is the raw material for natural selection allowing species to adapt to new environmental conditions. Moreover, we observed that the Tuva population shared genetic background with reindeer inhabiting Mongolia implying their common origin, while a singular structure of Tuvan reindeer differs from domestic and wild populations inhabiting country.
In this regard, we believe that our findings will be useful for solving problems related to conservation in order to increase the number of this substantial reindeer population, which is vital for the normal functioning of ecosystems and for the life and culture of the indigenous peoples living in the region. In addition, the disclosure of the genetic characteristics of the Tuvan reindeer obtained in this study may also be functional for implementing genetic diversity databases accumulated from breeds and populations with two different goals: the conservation and the sustainable use and exploitation of the Rangifer tarandus species worldwide.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/d14110900/s1, Figure S1: The cross-validation value; Table S1: FST estimates between each pair of reindeer groups.

Author Contributions

Conceptualization, V.R.K., A.V.D., and N.A.Z.; methodology, A.V.D., A.D.S., and H.R.; software, A.V.D. and H.R.; validation, A.V.D.; formal analysis, V.R.K. and N.A.Z.; investigation, V.R.K. and A.V.D.; resources, V.R.K., L.D.-O.S., and A.P.K.; data curation, V.R.K.; writing—original draft preparation, V.R.K.; writing—review and editing, N.A.Z.; visualization, A.V.D.; supervision, V.R.K. and N.A.Z.; project administration, V.R.K. and N.A.Z.; funding acquisition, V.R.K. and A.V.D. All authors have read and agreed to the published version of the manuscript.

Funding

This study was supported by the Russian Science Foundation (RSF) within Project nos. 21-16-00071 (the 777k SNP genotyping of the Tuva reindeer. The studies of the Mongolian and wild populations as well as the Chukotka, the Even and the Evenk breeds) and the Ministry of Science and Higher Education of the Russian Federation (theme No. FGGN-2022-0002) (the studies of the Nenets breed).

Institutional Review Board Statement

The study was approved by the Commission on the Ethics of Animal Experiments of the L.K. Ernst Federal Science Center for Animal Husbandry (the protocol No. 2 (28 April 2022)).

Informed Consent Statement

Not applicable.

Data Availability Statement

The SNP genotypes for all the reindeer individuals used in our study are available on request to the corresponding author.

Acknowledgments

The authors thank the reindeer herders for their permission to collect samples. The authors would like to express gratitude to the reviewers for their attention to this paper and for their constructive suggestions. The equipment of the Center for Biological Resources and Bioengineering of Agricultural Animals (Ernst Federal Science Center for Animal Husbandry) was used in the research.

Conflicts of Interest

The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript; or in the decision to publish the results.

References

  1. Nosov, S.I.; Bondarev, B.E.; Gladkov, A.A.; Gassiy, V. Land resources evaluation for damage compensation to indigenous peoples in the arctic (case-study of anabar region in Yakutia). Resources 2019, 8, 143. [Google Scholar] [CrossRef] [Green Version]
  2. Chuluun, S.; Aiygy, E. State policy of Russian Federation and mongolian people’s republic concerning tuvan reindeer breedersin modern period. Bull. Kalmyk Univ. 2016, 4, 40–49. (In Russian) [Google Scholar]
  3. Kol, N.V. Genetic Polymorphism in the Population of the Reindeer (Rangifer tarandus) of the Tuva Republic (Todzhinsky district). Ph.D. Thesis, Institute of General Genetics, N.I. Vavilov RAS, Moscow, Russia, 19 December 2006. [Google Scholar]
  4. Requiem-or-Recovery-21st-Century-Fate-Reindeer-Herding. Cultural Survival Quarterly Magazine. Available online: https://www.culturalsurvival.org/publications/cultural-survival-quarterly/ (accessed on 25 June 2022).
  5. Bicheool, S.M.; Samdan, A.A. Reindeer herders of the Eastern Sayans of the Republic of Tuva and Mongolia. Bull. Tuva State Univ. 2012, 1, 31–37. (In Russian) [Google Scholar]
  6. Stolpovsky, Y.A.; Babayan, O.V.; Kashtanov, S.N.; Piskunov, A.K.; Semina, M.T.; Kholodova, M.V.; Layshev, K.A.; Yuzhakov, A.A.; Romanenko, T.M.; Lisichkina, M.G.; et al. Genetic evaluation of the breeds of reindeer (Rangifer tarandus) and their wild ancestor using a new panel of STR markers. Russ. J. Genet. 2020, 12, 1469–1483. [Google Scholar] [CrossRef]
  7. The Government of the Russian Federation Presented a Roadmap for the Digitalization of Reindeer Farms. Available online: https://www.tadviser.ru/index.php/ (accessed on 25 June 2022).
  8. Kesić, L.; Cseke, K.; Orlović, S.; Stojanović, D.B.; Kostić, S.; Benke, A.; Borovics, A.; Stojnić, S.; Avramidou, E.V. Genetic diversity and differentiation of pedunculate oak (Quercus robur L.) populations at the Southern Margin of its distribution range—Implications for conservation. Diversity 2021, 13, 371. [Google Scholar] [CrossRef]
  9. Frankham, R.; Ballou, J.D.; Ralls, K.; Eldridge, M.D.B.; Dudash, M.R.; Fenster, C.B.; Lacy, R.C.; Sunnucks, P. A Practical Guide for Genetic Management of Fragmented Animal and Plant Populations, 1st ed.; Oxford University Press: Oxford, UK, 2019; pp. 115–121. [Google Scholar] [CrossRef]
  10. Barcaccia, G.; Felicetti, M.; Galla, G.; Capomaccio, S.; Cappelli, K.; Albertini, E.; Buttazzoni, L.; Pieramati, C.; Silvestrelli, M.; Supplizi, A.V. Molecular analysis of genetic diversity, population structure and inbreeding level of the Italian Lipizzan horse. Livest. Sci. 2013, 151, 124–133. [Google Scholar] [CrossRef]
  11. Putman, A.; Carbone, I. Challenges in analysis and interpretation of microsatellite data for population genetic studies. Ecol. Evol. 2014, 4, 4399–4428. [Google Scholar] [CrossRef]
  12. Garner, B.A.; Hand, B.K.; Amish, S.J.; Bernatchez, L.; Foster, J.T.; Miller, K.M.; Morin, P.A.; Narum, S.R.; O’Brien, S.J.; Roffler, G.; et al. Genomics in conservation: Case studies and bridging the gap between data and application. Trends Ecol. Evol. 2016, 31, 81–83. [Google Scholar] [CrossRef] [Green Version]
  13. Campbell, M.R.; Vu, N.V.; LaGrange, A.P.; Hardy, R.S.; Ross, T.J.; Narum, S.R. Development and application of single-nucleotide polymorphism (SNP) genetic markers for conservation monitoring of Burbot populations. Trans. Am. Fish. Soc. 2019, 148, 661–670. [Google Scholar] [CrossRef]
  14. Maroso, F.; Franch, R.; Rovere, G.D.; Arculeo, M.; Bargelloni, L. RAD SNP markers as a tool for conservation of dolphinfish Coryphaena hippurus in the Mediterranean Sea: Identification of subtle genetic structure and assessment of populations sex-ratios. Mar. Genom. 2016, 28, 57–62. [Google Scholar] [CrossRef]
  15. Ørsted, M.; Hoffmann, A.A.; Sverrisdóttir, E.; Nielsen, K.L.; Kristensen, T.N. Genomic variation predicts adaptive evolutionary responses better than population bottleneck history. PLoS Genet. 2019, 15, e1008205. [Google Scholar] [CrossRef] [PubMed]
  16. Mulvena, S.R.; Pierson, J.C.; Farquharson, K.A.; McLennan, E.A.; Hogg, C.J.; Grueber, C.E. Investigating inbreeding in a free-ranging, captive population of an Australian marsupial. Conserv. Genet. 2020, 21, 665–675. [Google Scholar] [CrossRef]
  17. Fitzpatrick, S.W.; Bradburd, G.S.; Kremer, C.T.; Salerno, P.E.; Angeloni, L.M.; Funk, W.C. Genomic and fitness consequences of genetic rescue in wild populations. Curr. Biol. 2020, 30, 517–522. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  18. Schmidt, T.L.; Jasper, M.E.; Weeks, A.R.; Hoffmann, A.A. Unbiased population heterozygosity estimates from genome-wide sequence data. Methods Ecol. Evol. 2021, 12, 1888–1898. [Google Scholar] [CrossRef]
  19. Kharzinova, V.R.; Sermyagin, A.A.; Gladyr, E.A.; Okhlopkov, I.M.; Brem, G.; Zinovieva, N.A. A study of applicability of SNP chips developed for bovine and ovine species to whole-genome analysis of reindeer Rangifer tarandus. J. Hered. 2015, 106, 758–761. [Google Scholar] [PubMed]
  20. Haynes, G.D.; Latch, E.K. Identification of novel single nucleotide polymorphisms (SNPs) in deer (Odocoileus spp.) using the BovineSNP50 BeadChip. PLoS ONE 2012, 7, e36536. [Google Scholar] [CrossRef] [Green Version]
  21. Kharzinova, V.R.; Dotsev, A.V.; Solovieva, A.D.; Fedorov, V.I.; Okhlopkov, I.M.; Wimmers, K.; Reyer, H.; Brem, G.; Zinovieva, N.A. Population-genetic characteristics of domestic reindeer of Yakutia based on whole-genome SNP analysis. Sel’skokhozyaistvennaya Biol. 2017, 52, 669–678. [Google Scholar] [CrossRef] [Green Version]
  22. Kasarda, R.; Moravčíková, N.; Židek, R.; Mészáros, G.; Kadlečík, O.; Trakovická, A.; Pokorádi, J. Investigation of the genetic distances of bovids and cervids using BovineSNP50k BeadChip. Arch. Anim. Breed 2015, 58, 57–63. [Google Scholar] [CrossRef] [Green Version]
  23. Kharzinova, V.R.; Dotsev, A.V.; Deniskova, T.E.; Solovieva, A.D.; Fedorov, V.I.; Layshev, K.A.; Romanenko, T.M.; Okhlopkov, I.M.; Wimmers, K.; Reyer, H.; et al. Genetic diversity and population structure of domestic and wild reindeer (Rangifer Tarandus l. 1758): A novel approach using bovinehd beadchip. PLoS ONE 2018, 13, e0207944. [Google Scholar] [CrossRef] [Green Version]
  24. Kharzinova, V.; Dotsev, A.; Solovieva, A.; Sergeeva, O.; Bryzgalov, G.; Reyer, H.; Wimmers, K.; Brem, G.; Zinovieva, N. Insight into the current genetic diversity and population structure of domestic reindeer (Rangifer tarandus) in Russia. Animals 2020, 10, 1309. [Google Scholar] [CrossRef]
  25. Becker, R.A.; Wilks, A.R.; Brownrigg, R.; Minka, T.P.; Deckmyn, A. Maps: Draw Geographical Maps. R Package Version 3.2.0. 2017. Available online: https://www.rdocumentation.org/packages/maps/versions/3.3.0 (accessed on 25 March 2022).
  26. Fan, J.; Oliphant, A.; Shen, R.; Kermani, B.G.; García, F.; Gunderson, K.L.; Hansen, M.S.; Steemers, F.; Butler, S.L.; Deloukas, P.; et al. Highly parallel SNP genotyping. Cold Spring Harb. Symp. Quant. Biol. 2003, 68, 69–78. [Google Scholar] [CrossRef] [PubMed]
  27. Chang, C.C.; Chow, C.C.; Tellier, L.C.; Vattikuti, S.; Purcell, S.M.; Lee, J.J. Second-generation PLINK: Rising to the challenge of Larger and Richer Datasets. Gigascience 2015, 4, 7. [Google Scholar] [CrossRef] [PubMed]
  28. Zimin, A.V.; Delcher, A.L.; Florea, L.; Kelley, D.R.; Schatz, M.C.; Puiu, D.; Hanrahan, F.; Pertea, G.; Van Tassell, C.P.; Sonstegard, T.S.; et al. A whole-genome assembly of the domestic cow, Bos taurus. Genome Biol. 2009, 10, R42. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  29. Nei, M. Estimation of average heterozygosity and genetic distance from a small number of individuals. Genetics 1978, 89, 583–590. [Google Scholar] [CrossRef]
  30. Weir, B.S.; Cockerham, C.C. Estimating F-statistics for the analysis of population structure. Evolution 1984, 38, 1358–1370. [Google Scholar]
  31. Keenan, K.; McGinnity, P.; Cross, T.F.; Crozier, W.W.; Prodoh, P.A. DiveRsity: An R package for the estimation of population genetics parameters and their associated errors. Methods Ecol. Evol. 2013, 4, 782–788. [Google Scholar] [CrossRef] [Green Version]
  32. Huson, D.H.; Bryant, D. Application of phylogenetic networks in evolutionary studies. Mol. Biol. Evol. 2006, 23, 254–267. [Google Scholar] [CrossRef]
  33. Wickham, H. Ggplot2: Elegant Graphics for Data Analysis, 2nd ed.; Springer: New York, NY, USA, 2009; p. 213. [Google Scholar]
  34. Alexander, D.H.; Novembre, J.; Lange, K. Fast model-based estimation of ancestry in unrelated individuals. Genome Res. 2009, 19, 1655–1664. [Google Scholar] [CrossRef] [Green Version]
  35. Francis, R.M. Pophelper: An R package and web app to analyse and visualize population structure. Mol. Ecol. Resour. 2017, 17, 27–32. [Google Scholar] [CrossRef] [Green Version]
  36. R Core Team. R: A Language and Environment for Statistical Computing; R Foundation for Statistical Computing: Vienna, Austria, 2012. [Google Scholar]
  37. Petit-Marty, N.; Liu, M.; Tan, I.Z.; Chung, A.; Terrasa, B.; Guijarro, B.; Ordines, F.; Ramírez-Amaro, S.; Massutí, E.; Schunter, C. Declining population sizes and loss of genetic diversity in commercial fishes: A simple method for a first diagnostic. Front. Mar. Sci. 2022, 9, 872537. [Google Scholar] [CrossRef]
  38. Klokov, K. Reindeer husbandry in Russia. Int. J. Entrep. Small Bus. 2007, 4, 726. [Google Scholar] [CrossRef]
  39. Kol, N.; Korolev, A.; Zakharov, I. Mitochondrial DNA polymorphism in Tuvinian population of reindeer Rangifer tarandus L. Genetika 2006, 42, 110–112. (In Russian) [Google Scholar] [CrossRef] [PubMed]
  40. Lewontin, R.C. The Genetic Basis of Evolutionary Change; Columbia University Press: New York, NY, USA, 1974; pp. 341–346. [Google Scholar]
  41. Mayr, E. Populations, Species, and Evolution; Harvard University Press: Cambridge, MA, USA, 1970; pp. 449–453. [Google Scholar]
  42. Channell, R. The conservation value of peripheral populations: The supporting science. In Proceedings of the Species at Risk 2004 Pathways to Recovery Conference Organizing Committee, Victoria, BC, Canada, 2–6 March 2004; pp. 1–17. [Google Scholar]
  43. Aiyzhy, E.; Kanunnikov, D.; Mongush, S. The tsaatans borderline life (based on field research). Opcion 2018, 34, 88–116. [Google Scholar]
  44. Mongush, M.V. Tuvans outside of Tuva: The problem of ethnic self-conservation. Senri Ethnol. Stud. 2014, 86, 197–213. [Google Scholar]
  45. McVean, G. A genealogical interpretation of principal components analysis. PLoS Genet. 2009, 5, e1000686. [Google Scholar] [CrossRef] [Green Version]
  46. Røed, K.H.; Flagstad, O.; Nieminen, M.; Holand, O.; Dwyer, M.J.; Røv, N.; Vilà, C. Genetic analyses reveal independent domestication origins of Eurasian reindeer. Proc. Biol. Sci. 2008, 275, 1849–1855. [Google Scholar] [CrossRef] [Green Version]
  47. Weldenegodguad, M.; Pokharel, K.; Ming, Y.; Honkatukia, M.; Peippo, J.; Reilas, T.; Røed, K.H.; Kantanen, J. Genome sequence and comparative analysis of reindeer (Rangifer tarandus) in northern Eurasia. Sci. Rep. 2020, 10, 8980. [Google Scholar] [CrossRef]
Figure 1. The male reindeer of the Tuva–Tofalar population (the photo provided by Shimit L. D. and Demkina S. A.).
Figure 1. The male reindeer of the Tuva–Tofalar population (the photo provided by Shimit L. D. and Demkina S. A.).
Diversity 14 00900 g001
Figure 2. The map of breeding and inhabiting zones of domestic and wild reindeer and the sampling sites where specimens used in this study were collected. Tuva population—TUVA; Nenets breed—NEN; Even breed—EVN; Evenk breed of the Yakutia region—EVK_Y; Evenk breed of the Krasnoyarsk region—EVK_K; Chukotka breed—CHU; Mongolian population—MONG; wild reindeer of the Krasnoyarsk Territory—WLD_TG; and wild reindeer of Northern Yakutia—WLD_TU.
Figure 2. The map of breeding and inhabiting zones of domestic and wild reindeer and the sampling sites where specimens used in this study were collected. Tuva population—TUVA; Nenets breed—NEN; Even breed—EVN; Evenk breed of the Yakutia region—EVK_Y; Evenk breed of the Krasnoyarsk region—EVK_K; Chukotka breed—CHU; Mongolian population—MONG; wild reindeer of the Krasnoyarsk Territory—WLD_TG; and wild reindeer of Northern Yakutia—WLD_TU.
Diversity 14 00900 g002
Figure 3. The Admixture analysis depicting genetic structure of the Tuvan population among officially recognized breeds, domestic Mongolian, and wild reindeer populations. Tuva population—TUVA; Nenets breed—NEN; Even breed—EVN; Evenk breed of the Yakutia region—EVK_Y; Evenk breed of the Krasnoyarsk region—EVK_K; Chukotka breed—CHU; Mongolian population—MONG; wild reindeer of the Krasnoyarsk Territory—WLD_TG; and wild reindeer of Northern Yakutia—WLD_TU.
Figure 3. The Admixture analysis depicting genetic structure of the Tuvan population among officially recognized breeds, domestic Mongolian, and wild reindeer populations. Tuva population—TUVA; Nenets breed—NEN; Even breed—EVN; Evenk breed of the Yakutia region—EVK_Y; Evenk breed of the Krasnoyarsk region—EVK_K; Chukotka breed—CHU; Mongolian population—MONG; wild reindeer of the Krasnoyarsk Territory—WLD_TG; and wild reindeer of Northern Yakutia—WLD_TU.
Diversity 14 00900 g003
Figure 4. The principal component analysis of the Tuvan population among officially recognized breeds, domestic Mongolian, and wild reindeer populations: (A)-PCA for all of the studied reindeer groups; (B)- PCA for all officially recognized breeds and wild populations of reindeer; (C)- PCA for all officially recognized reindeer breeds. Tuva population—TUVA; Nenets breed—NEN; Even breed—EVN; Evenk breed of the Yakutia region—EVK_Y; Evenk breed of the Krasnoyarsk region—EVK_K; Chukotka breed—CHU; Mongolian population—MONG; wild reindeer of the Krasnoyarsk Territory—WLD_TG; and wild reindeer of Northern Yakutia—WLD_TU.
Figure 4. The principal component analysis of the Tuvan population among officially recognized breeds, domestic Mongolian, and wild reindeer populations: (A)-PCA for all of the studied reindeer groups; (B)- PCA for all officially recognized breeds and wild populations of reindeer; (C)- PCA for all officially recognized reindeer breeds. Tuva population—TUVA; Nenets breed—NEN; Even breed—EVN; Evenk breed of the Yakutia region—EVK_Y; Evenk breed of the Krasnoyarsk region—EVK_K; Chukotka breed—CHU; Mongolian population—MONG; wild reindeer of the Krasnoyarsk Territory—WLD_TG; and wild reindeer of Northern Yakutia—WLD_TU.
Diversity 14 00900 g004
Figure 5. The NeighborNet network of the Tuvan population among officially recognized breeds, domestic Mongolian, and wild reindeer populations based on pairwise FST values. Tuva population—TUVA; Nenets breed—NEN; Even breed—EVN; Evenk breed of the Yakutia region—EVK_Y; Evenk breed of the Krasnoyarsk region—EVK_K; Chukotka breed—CHU; Mongolian population—MONG; wild reindeer of the Krasnoyarsk Territory—WLD_TG; and wild reindeer of Northern Yakutia—WLD_TU.
Figure 5. The NeighborNet network of the Tuvan population among officially recognized breeds, domestic Mongolian, and wild reindeer populations based on pairwise FST values. Tuva population—TUVA; Nenets breed—NEN; Even breed—EVN; Evenk breed of the Yakutia region—EVK_Y; Evenk breed of the Krasnoyarsk region—EVK_K; Chukotka breed—CHU; Mongolian population—MONG; wild reindeer of the Krasnoyarsk Territory—WLD_TG; and wild reindeer of Northern Yakutia—WLD_TU.
Diversity 14 00900 g005
Table 1. The parameters of the genetic diversity of the Tuvan population in comparison with domestic breeds, domestic Mongolian, and wild populations of reindeer calculated based on SNP genotypes.
Table 1. The parameters of the genetic diversity of the Tuvan population in comparison with domestic breeds, domestic Mongolian, and wild populations of reindeer calculated based on SNP genotypes.
Breed/Population 1N 2AR 3HO 4UHE5UFIS6
TUVA281.516 ± 0.0050.150 ± 0.0020.155 ± 0.0020.032 [0.026; 0.038]
NEN331.617 ± 0.0050.180 ± 0.0020.181 ± 0.0020.006 [0.001; 0.011]
EVN191.666 ± 0.0050.182 ± 0.0020.187 ± 0.0020.027 [0.021; 0.033]
EVK_Y201.679 ± 0.0050.185 ± 0.0020.189 ± 0.0020.019 [0.013; 0.025]
EVK_K201.634 ± 0.0050.181 ± 0.0020.184 ± 0.0020.012 [0.006; 0.018]
CHU251.606 ± 0.0050.171 ± 0.0020.176 ± 0.0020.027 [0.021; 0.033]
MONG111.507 ± 0.0060.156 ± 0.0020.154 ± 0.002−0.006 [−0.014; 0.002]
WLD_TG161.582 ± 0.0060.168 ± 0.0020.172 ± 0.0020.016 [0.009; 0.023]
WLD_TU111.684 ± 0.0060.184 ± 0.0020.187 ± 0.0020.023 [0.011; 0.035]
1 Tuva population—TUVA; Nenets breed—NEN; Even breed—EVN; Evenk breed of the Yakutia region—EVK_Y; Evenk breed of the Krasnoyarsk region—EVK_K; Chukotka breed—CHU; Mongolian population—MONG; wild reindeer of the Krasnoyarsk Territory—WLD_TG; and wild reindeer of Northern Yakutia—WLD_TU; 2 n, sample size; 3 AR, allelic richness; 4 HO, observed heterozygosity; 5 UHE, unbiased expected heterozygosity; and 6 FIS, inbreeding coefficient based on the difference between UHE and HO with a 95% confidence interval (CI; in square brackets).
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Kharzinova, V.R.; Dotsev, A.V.; Solovieva, A.D.; Shimit, L.D.-O.; Kochkarev, A.P.; Reyer, H.; Zinovieva, N.A. Genome-Wide SNP Analysis Reveals the Genetic Diversity and Population Structure of the Domestic Reindeer Population (Rangifer tarandus) Inhabiting the Indigenous Tofalar Lands of Southern Siberia. Diversity 2022, 14, 900. https://doi.org/10.3390/d14110900

AMA Style

Kharzinova VR, Dotsev AV, Solovieva AD, Shimit LD-O, Kochkarev AP, Reyer H, Zinovieva NA. Genome-Wide SNP Analysis Reveals the Genetic Diversity and Population Structure of the Domestic Reindeer Population (Rangifer tarandus) Inhabiting the Indigenous Tofalar Lands of Southern Siberia. Diversity. 2022; 14(11):900. https://doi.org/10.3390/d14110900

Chicago/Turabian Style

Kharzinova, Veronika Ruslanovna, Arsen Vladimirovich Dotsev, Anastasiya Dmitrievna Solovieva, Larisa Delger-Oolovna Shimit, Anton Pavlovich Kochkarev, Henry Reyer, and Natalia Anatolievna Zinovieva. 2022. "Genome-Wide SNP Analysis Reveals the Genetic Diversity and Population Structure of the Domestic Reindeer Population (Rangifer tarandus) Inhabiting the Indigenous Tofalar Lands of Southern Siberia" Diversity 14, no. 11: 900. https://doi.org/10.3390/d14110900

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop