Research Article | Open Access
Elijah K. Githui, David N. Thuo, Joshua O. Amimo, Nyamu M. Njagi, Maryanne M. Gitari, "Mitochondrial DNA Phylogenetics of Black Rhinoceros in Kenya in relation to Southern Africa Population", International Journal of Biodiversity, vol. 2017, Article ID 8326361, 6 pages, 2017. https://doi.org/10.1155/2017/8326361
Mitochondrial DNA Phylogenetics of Black Rhinoceros in Kenya in relation to Southern Africa Population
Black rhinoceros (Diceros bicornis) are highly endangered due to poaching and other anthropological reasons and their protection to rebound the numbers and genetic improvement are necessary remedial measures defined by Rhino International Union of Conservation for the Nature Red List (IUCN). In Kenya black rhino numbers declined from approximately 20,000 in the 1970s to fewer than 400 in 1982. Wildlife conservation managers effected strategies to manage/breed the remaining rhinoceros populations in Eastern and Southern Africa within regional sanctuaries. This study analyzes the genetic variability of these remnant rhinoceros using Mitochondrial DNA (mtDNA). Majority of the rhinoceros in both Kenyan and Southern Africa group are monophyletic clusters with insignificant genetic variations while some lineages are underrepresented. The Eastern Africa rhinoceros forms a distinct clade from the Sothern Africa counterpart while Tanzania population has admixtures. Tajima-D test showed that these two populations are under different selection pressure possibly due to different history of adverse anthropologic activities. Similarly, the Southern Africa rhinoceros have low genetic diversity compared to the Eastern African population due to extended periods of game hunting during Africa colonization. This study suggests that managed translocations of individual rhinoceros across the separated fragments can be applied to improve their genetic diversity.
Black rhinoceros (Diceros bicornis) has suffered dramatic decline of all mammals in the recent history and the species is currently categorized as critically endangered in the International Union of Conservation for the Nature Red List (IUCN) [1, 2]. Between 1960s and 1980s wanton illegal poaching and loss of habitat due to increased human developments in areas that were formerly wilderness resulted in approximately 96% decline (65,000 to 3,800 individuals) in population black rhinoceros across their range in Africa [3, 4]. In recent years, conservation measures have resulted in increase of in situ black rhino numbers from of 2475 individuals in 1993 to approximately 4880 in 2010 [2, 5, 6].
Kenya Wildlife Service (KWS) records show that these impacts reflected on Kenyan black rhinoceros numbers where catastrophic decline was from an estimated 20,000 individuals in 1970 to 398 in 1991 and then this slightly rebounded to about 631 in 2014 [7, 8]. This was through conservation strategy developed to intensively manage the remaining rhinos within small rhino sanctuaries where KWS periodical translocated the surviving rhinoceros into the high security sanctuaries to limit poaching and enhance breeding [9, 10].
Majority of the extant black rhinoceros belong to subspecies Diceros bicornis minor and Diceros bicornis michaeli. Other subspecies include Diceros bicornis longipes and Diceros bicornis bicornis. The D. b. michaeli (eastern black rhino) is found in Kenya and Tanzania while D. b. minor is found in Tanzania to South Africa [3, 11]. Although there are apparently no marked geographic or reproductive barriers between the subspecies, they occupy different ecological zones. There have not been any rigorous studies on migration and reproductive gene flow between the subspecies although some authors suggest that each subspecies may have distinct genetic or behavioral adaptations to their local environments [3, 12].
Genetic differences between related populations can also result from strong genetic drift caused by population fragmentation and declining population sizes [13, 14]. When the genetic structure and historic pattern of gene flow of a species had been described, reintroduction methods can be used to secure locally adapted populations or restocking used for genetic supplementation. Mitochondrial DNA (mtDNA) phylogeny sheds light on founder female populations and can be applied in determining black rhinoceros population relationships across the ecological and geographic zones [15, 16]. The measure of variability within and between groups is an essential step in determining robust numbers of individuals in a sanctuary that preserves genetic diversity of these populations [12, 17]. In this study we analyzed mtDNA genetic relationships between Kenyan black rhinoceros population and the Southern Africa counterpart to assess gene flow between the populations.
2. Materials and Methods
2.1. Sample Collections
Samples were collected during rhino translocations exercises between sanctuaries within Kenya between years 2008 and 2012, conducted by KWS rangers and scientist at Nairobi National Park. Blood and ear snips were collected by KWS veterinary officer from anaesthetized animals and preserved in absolute ethanol in cryovials instantly. Materials for laboratory analysis were transported to Molecular Genetics Laboratory, National Museums of Kenya, and preserved.
2.2. DNA Extraction
Portion of skin tissue sample and blood sample precipitates were centrifuged briefly and ethanol aspirated. The samples were left to air-dry then washed in 3 volumes of 1x PBS to rehydrate. DNA was subsequently extracted using Qiagen Kit according to manufacturer’s manual (Qiagen Inc., Germantown, MD, USA) essentially involving lysis, binding of DNA to silica matrix, and elution in 200 ul TE (10 mM Tris HCL, 1 mM EDTA, and pH 8.0). For tissues that were difficult to completely lyse, phenol: chloroform method was applied . The blood/tissue was incubated in 50 ug/ml proteinase K, 1% SDS in STE buffer (150 mM NaCl, 100 mM EDTA, 10 mM Tris HCl, and pH 7.4) at 55°C for 3 hrs. The lysate was subjected to phenol: chloroform phase separation and the upper aqueous phase containing DNA aspirated to a new tube. DNA precipitated from the aqueous phase by adding 2-3 volumes of absolute ethanol. The pellet was suspended in 50 to 100 ul TE (10 mM Tris HCL, 1 mM EDTA, and pH 8.0). DNA concentration was measured by absorbance at 260 nm/280 nm and the quality analyzed by electrophoresis in 1% Agarose gel in 1x TAE buffer (40 mM Tris acetate, 1 mM EDTA, and pH 8.0). The respective tubes with DNA were appropriately labeled and stored at −20°C.
2.3. PCR and Product Purification Procedures
In this study 28 DNA samples representing rhinoceros from within Kenya sanctuaries and national parks were analyzed. Polymerase chain reaction was carried out using the following parameters: denaturation at 94°C, 1 min annealing at 54°C, 45 sec., and extension at 72°C for 1 min. The primers flanking region of 3′ end of cytochrome b and D-loop middle region were applied. The amplification product was verified on 1% agarose gels and the fragment excised from the gel solubilized in sodium iodide solution then bound to (silica) column in the gene clean procedure. Bound DNA was eluted in 30 ul nuclease free ddH2O.
Gene cleaned DNA of the amplified fragments were sequenced at Macrogen Inc., Europe (Netherlands), using Sanger’s fluorescent dye chain terminator method. Each of the samples was independently sequenced three times and the raw sequences analyzed in Clustal-W program in BioEdit (Version 7.05) to give the consensus but five of the sample sequences did not yield good data and were excluded. The edited raw sequences were submitted to National Center for Biotechnology Information (NCBI: https://www.ncbi.nlm.nih.gov) nucleotide database, GenBank accession numbers: KU569499-KU569508 and KP247507-KP247521.
2.5. Sequence Alignment and Phylogenetic Analysis
Sequences from the dataset were initially aligned utilizing the Clustal-W program in BioEdit and the phylogenetic relationships inferred from the aligned nucleotide sequences by the NJ method (bootstrap 1000 replicates) implemented in the MEGA suite version 6 [19, 20].
Test of neutrality was performed using Tajima’s D software implemented in MEGA suite [21, 22] and the analysis of allele diversity haplotypes and population divergence done in DNA sequence polymorphism statistics packages implemented in DnaSP V5 software [23, 24].
3.1. Distant Phylogenetic Relationship in Rhinoceros Family
Phylogenetic tree clusters generated by NJ method at bootstrap 1000 replicates were rooted against outgroup Dicerorhinus sumatrensis harrissoni indicating long distance evolutionary separation between the white rhinoceros (Ceratotherium simum simum) and the black rhinoceros (D. bicornis) clusters. The two clusters of black rhinoceros (D. b. minor and D. b. michaeli) are phylogenetically closely related. Majority of the rhinoceros in both Kenyan and Southern Africa group are monophyletic clusters with insignificant genetic variations while some of the representative lineages have only a few rhinoceros. The Tanzanian rhinoceros population (Figure 1, shown in grey) is an independent lineage of D. b. michaeli with some admixtures from Kenya population and possible lineage variant represented by D. b. rovumae voucher sample. Some rhinoceros from the South Western Africa (D. b. bicornis) cluster together with the D. b. minor population of Southern Africa while other independent lineages from South Western African population represented by D. b. angolensis and D. b. occidentallis are monophyletic (Figure 1). In each black rhinoceros population, tree clusters are monophyletic.
3.2. Population Departure from Neutrality
When population is at equilibrium neutrality the nucleotide diversity () and the number of nucleotide segregating sites () are indistinguishable and this is seen in both Southern Africa (D. b. minor) and Kenyan (D. b. michaeli) rhinoceros. Tajima-D analysis of Southern Africa rhinoceros dataset showed a positive value while Kenyan group subset had a weak negative value (Table 1).
|The analysis involved 16 nucleotide sequences. There were a total of 255 positions () in the final dataset of each population, D. b. minor and D. b. michaeli. = number of sequences, = total number of sites, = number of segregating sites, , , = nucleotide diversity, and is the Tajima test statistic ( and both estimate , where (expected) and ), software default significant at . Analyses were conducted in MEGA6.|
3.3. DNA Diversity and Divergence between Populations
DNA diversity analysis of similar region of mtDNA of the Kenyan and Southern African rhinoceros showed that the two populations are distinct with only one shared mutation and nine fixed differences. The Southern Africa rhinoceros population had lower haplotype diversity and nucleotide diversity relative to the Kenyan population (Table 2).
|Between populations: number of fixed differences: 7; mutations polymorphic in population 1 but monomorphic in population 2: 9; mutations polymorphic in population 2 but monomorphic in population 1: 5; shared mutations: 1.|
Black rhinoceros became critically endangered species in the 1970s mainly due to poaching and historical game hunting during colonial era and also due to expansion of agricultural land in Africa [25–27], prompting implementation of remedial conservation strategies to intensively manage the remaining population within high security sanctuaries [5, 9]. These management fragments started with low numbers of founding population with periodical translocation between the sanctuaries managed in coordination with local government wild life services [7, 28]. The low numbers of founding population have implications in genetic variability and resilience of the subspecies.
The Eastern Africa black rhinoceros (D. b. michaeli) is historically separated from the southern population (D. b. minor) although there is no real geographical barrier to limit movement between the two regions. Some authors suggest that each subspecies population may have behavioral adaptations to their local environments [3, 12]. The two subspecies are not genetically reproductively separated and there have been no rigorous studies on migration and reproductive gene flow between these populations . In this study, phylogenetic analysis of these populations using mtDNA D-loop region (Figure 1) shows that the two populations fall into two different clades that have further separated into monophyla clusters over time. This is concurrent with previous observations that the D. b. michaeli and D. b. minor populations become distinct genetically [27, 29, 30]. However, the phylogenetic tree branch lengths of two clades of black rhinoceros are closely linked and are distantly related to white rhinoceros, C. s. simum, and Sumatran rhinoceros, D. s. harrissoni , indicating that the Eastern Africa and Southern Africa black rhinoceros separation is recent. The Tanzanian D. b. michaeli cluster has admixtures populations with lineages from Kenya likely at the geographic areas separated by national boundary but also has lineages close to southern black rhinoceros. The voucher specimen, AF187834 (Figure 1), was born in Cincinnati zoo, Ohio, USA, from a Kenya lineage  while D. b. rovumae voucher is now extinct but has closely related lineages in the southern black rhinoceros that can be used in genetic supplementation [27, 31]. Southwestern Africa black rhinoceros (D. b. bicornis) from Namibia and Angola clustered within the D. b. minor clade. The Southwestern Africa monophyla lineages, for example, D. b. congolensis and D. b. occidentalis, can further be studied with the aim of providing source of heterogeneity in genetic supplementation of the Southern Africa black rhinoceros population.
Inbreeding depression versus outbreeding depression are concerns in management policies of rhinoceros populations in sanctuaries [32, 33]. The current sanctuaries hold fragmented pockets of rhinoceros after near demise in the 1970s due to anthropologic issues but mainly poaching. Previous studies based mtDNA diversity showed that D. b. minor population in Southern Africa had only a few haplotypes raising the question of whether these remnant populations lost genetic diversity recently as a result of management fragments gene flow bottleneck or have been a genetically separate lineage for longer time . Tajima’s D test analysis in this study showed a positive value for the southern D. b. minor population while the Eastern Africa D. b. michaeli population had negative value (Table 1) indicating that the two populations are experiencing different selection pressure. Based on the recent history of demise and restocking of African rhinoceros, it is plausible that the positive Tajima’s D value reflects recent bottleneck in these fragmented population while the Eastern African negative Tajima’s D value is a result of recent population expansion from few founding individual rhinoceroses.
For the same sample size the Eastern African D. b. michaeli had higher genetic diversity (haplotypes = 10) compared to the Southern Africa D. b. minor (haplotypes = 6) with seven fixed differences and only one shared mutation (Table 2). The apparent low diversity in the Southern Africa black rhinoceros infer a population bottleneck [27, 29]. For the mtDNA region analyzed, the fixed nucleotide polymorphic site differences between the two populations were seven with only one shared polymorphic site indicating that gene flow between the Eastern and Southern African and rhinoceros populations is restricted. Since mtDNA is maternally inherited, this may imply that the female rhinoceros founding population has behavioral restricted movements within an ecological range.
There is need to readjust current conservation management paradigms for the black rhinoceros where precaution strategies in the translocation of endangered species bring only small, incremental improvements [27, 28, 34]. Rhinoceros are herbivores without substantial predators and are resilient to ecological challenges ; therefore their translocation for restocking to improve genetic diversity is feasible. Since there is no reproductive barrier in African black rhinoceroses, the genetic diversity improvement will involve pilot outbreeding programs among the fragmented populations across the ecological range [5, 27, 29].
Conflicts of Interest
The authors declare that there are no conflicts of interest regarding the publication of this paper.
This research project was supported by Molecular Genetics Laboratory at National Museums of Kenya and subgrant from Professor Thomas Gilbert, University of Copenhagen, Natural History Museums, Denmark, to support Masters of Arts Program for Nyamu M. Njagi and Masters of Science dissertation project for David N. Thuo.
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