Literature DB >> 32298359

Revisiting the Woolly wolf (Canis lupus chanco) phylogeny in Himalaya: Addressing taxonomy, spatial extent and distribution of an ancient lineage in Asia.

BheemDutt Joshi1, Salvador Lyngdoh1, Sujeet Kumar Singh1, Reeta Sharma1, Vinay Kumar1, Ved Prakash Tiwari1, S A Dar1, Aishwarya Maheswari1, Ranjana Pal1, Tawqir Bashir1, Hussain Saifee Reshamwala1, Shivam Shrotriya1, S Sathyakumar1, Bilal Habib1, Laura Kvist2, Surendra Prakash Goyal1.   

Abstract

Of the sub-species of Holarctic wolf, the Woolly wolf (Canis lupus chanco) is uniquely adapted to atmospheric hypoxia and widely distributed across the Himalaya, Qinghai Tibetan Plateau (QTP) and Mongolia. Taxonomic ambiguity still exists for this sub-species because of complex evolutionary history anduse of limited wild samples across its range in Himalaya. We document for the first time population genetic structure and taxonomic affinity of the wolves across western and eastern Himalayan regions from samples collected from the wild (n = 19) using mitochondrial control region (225bp). We found two haplotypes in our data, one widely distributed in the Himalaya that was shared with QTP and the other confined to Himachal Pradesh and Uttarakhand in the western Himalaya, India. After combining our data withpublished sequences (n = 83), we observed 15 haplotypes. Some of these were shared among different locations from India to QTP and a few were private to geographic locations. A phylogenetic tree indicated that Woolly wolves from India, Nepal, QTP and Mongolia are basal to other wolves with shallow divergence (K2P; 0.000-0.044) and high bootstrap values. Demographic analyses based on mismatch distribution and Bayesian skyline plots (BSP) suggested a stable population over a long time (~million years) with signs of recent declines. Regional dominance of private haplotypes across its distribution range may indicate allopatric divergence. This may be due to differences in habitat characteristics, availability of different wild prey species and differential deglaciation within the range of the Woolly wolf during historic time. Presence of basal and shallow divergence within-clade along with unique ecological requirements and adaptation to hypoxia, the Woolly wolf of Himalaya, QTP, and Mongolian regions may be considered as a distinct an Evolutionary Significant Unit (ESU). Identifying management units (MUs) is needed within its distribution range using harmonized multiple genetic data for effective conservation planning.

Entities:  

Year:  2020        PMID: 32298359      PMCID: PMC7162449          DOI: 10.1371/journal.pone.0231621

Source DB:  PubMed          Journal:  PLoS One        ISSN: 1932-6203            Impact factor:   3.240


Introduction

Resolving species and sub-species ambiguity has been a key issue in conservation biology, especially in widely distributed and species having the large home ranges [1]. Such ambiguity of classification into species or sub-species has often been debated in the literature for extant mammalsof the Central Asian region as well. Some examples of the debated species in Qinghai Tibetan Plateau (QTP) and Himalayan regions are musk deer (Moschus spp.) [2], blue sheep [3], wolf [4], brown bear [5]and snow leopard [6,7]. This region is known to have undergone various climatic changes in the past and differences in uplift since the Pleistocene. These events may have even lead to distinctpaleo-ecological niches because of differences in major geophysical events in these two (QTP and Himalaya) regions[3] and could have resulted in distinct evolutionary significant units (ESU)/management units. Of the medium sized carnivores of the world, the grey wolf (Canis lupus) is one of the most widely distributed species in different bioclimatic zones and it is divided into many discrete populations and subspecies across the world [8]. Several studies have addressed the issues of phylogeography, genetic diversity, taxonomy and evolutionary history in the northern hemisphere[4,9-11]. However, the Woolly wolf (Canis lupus chanco) of the Qinghai Tibetan Plateau-Himalaya region has not caught much attention. It is one of the sub-species of Holarctic wolf (Canis lupus) and is widely distributed in Central Asia ranging from Chinese Turkestan and the Tian Shan throughout Tibet to Mongolia, North China, Shensi, Szechwan, Yunnan and the western Himalaya [12]. This sub-species is also known by different names across its range. Several types for different localities have been reported, such as “chanco” in Chinese Tartary; “laniger” in Tibet; “niger” near Hanle in S.E. Kashmir; “filchneri” in Si-nung-fu, Kansu; “karanorensis” in Kara-nor, the Gobi; and tschiliensis” in the coast of Chihli [12]. The taxonomic status of the Himalayan and peninsular wolves (wolf distributed in peninsular India)has been revised several times, based on the ecological and morphological studies, and accorded as a sub-species ora species. The Woolly wolf from the Himalayan region was designated as distinct species called C. laniger [13]which later on was merged with the C. lupus[14], whereas the lowland Indian wolf was assigned as a species named C. pallipes Blanford (1888)[14]. Further, these both were designated as sub-species of C. lupus and named as C. l. chanco and C.l. pallipes respectively.Subsequently, it was also agreed on the taxonomic classification of the Himalayan wolf[15][16]that was proposed as C. l. chanco[13]and Peninsular wolf as C. l. pallipes[14]. Currently, the taxonomic classification of the Woolly wolf is still under debate [16] and is pending due to limited data from contemporary wild population across Himalaya. The limited studies undertaken on the Woolly wolf from Himalaya, QTP and Mongolia have assigned it at a basal position in an evolutionary cladogram and considered it as an ancient lineage [10,15,17]. Later on samples analysed [15]from Nepal, Tibet, Jammu and Kashmir and mentioned that wolves from the Himalayan region formeda separate clade[15]. They further suggested that the Pleistocene geological events may have shaped the observed phylogeographic pattern. Subsequently, the taxonomic status of the wolf of the Indian sub-continent was examined using mitochondrial control region sequences[18] and suggested new species’ named C. himalayensis for the Himalayan wolf and C. indica for the Peninsular Indian wolf. However, most of these studies have relied mostly on limited samples that originated from either zoos or museums and, for example, the relatedness of the zoo individuals was not studied [16]. A recent study using wild-caught samples of the Woolly wolf of the Himalayan region from Nepal suggested phylogenetic distinction and old divergence from the Holarctic wolf [11]. Likewise, Werhahn et al. [4,19]suggested distinctiveness of the Woolly wolf from other wolves and advocated that their geographic range is not restricted to the Himalaya. They also recommended that the Woolly wolf should be classified as a distinct taxon of special conservation concern. However, all these studies have used limited samples across distribution range of wild wolves from the Himalayan region. In the current study, we re-examine the phylogeny and population genetic structure of the Woolly wolf based on a wide coverage of samples collected from the wild across the Himalayan region of India and compare the data with the published literature available for the Himalayan region of Nepal, QTP, and Mongolia. We also examine the possible extent of the Woolly wolf lineage relationship within Holarctic grey wolf [4,19].

Material and methods

Ethical statement

All the samples were non-invasively collected from the different states of Indian Himalayan region. Fecal samples of wolf were collected noninvasively without any animal capture or handling. Therefore, sample collection did not require any handling permission from the respective department. However, permission for procuring, processing and preserving scat samples were obtained from the from the Ministry of Forest, Environment and Climate Change, Uttarakhand with letter vide no 1/29/2003-PT, Department of Forest, Environment and Wildlife Management, Government of Sikkim vide No. 2081778 Dated 18/04/2012, Department of Forest and Environment and Climate Change of Himachal Pradesh, vide no. WL/Research Study/WLM/4671 dated 24/11/2015 and WL/Research Study/WLM 87 dated 07/04/2010.

Sample collection and DNA extraction

We collected putative wild wolf scat samples (n = 132) from Indian Himalayan range covering four regions of Jammu and Kashmir (JK) (n = 5), Himachal Pradesh (HP) (n = 120), Uttarakhand (UK) (n = 4) and Sikkim (SK) (n = 3) during 2003–2015 with an elevation ranges from 3000 to 4500 m (Fig 1). DNA was extracted from the samples using the QiagenDN easy Stool Kit, Qiagen, Germany, according to the manufacturer’s instructions. To detect any contamination in the DNA extraction procedure and reagents, we performed the extraction procedure with two independent negative controls.
Fig 1

Median Joining network of different haplotypes of Canis lupus chanco from different geographical regions.

Circle sizes are proportional to the number of samples with that haplotype using the mitochondrial control regions. Circle on the map represent the sampling locations (map not to scale).

Median Joining network of different haplotypes of Canis lupus chanco from different geographical regions.

Circle sizes are proportional to the number of samples with that haplotype using the mitochondrial control regions. Circle on the map represent the sampling locations (map not to scale).

Selection of primer

Various molecular markers such as microsatellites, mitochondrial regions, whole-genome sequencing (WGS), single nucleotide polymorphism (SNPs) have been suggested for identifying management units (MU), Evolutionary Significant Units (ESU) and Distinct Population Segment (DPS) for effective conservation planning across species’ range [20-22]. With the advances in molecular genomics, WGS has been a preferred a genomic approach in conservation studies but requires good quality of samples [23-25]. Obtaining adequate number of invasive samples such as blood or tissue for WGS studies from the widely distributed species of low density are not cost-effective in comparison to fecal DNA [26,27] and also lacks comparable data at present to document variations due to microevolution. Woolly wolf have several “Eco-morph” and obtaining adequate invasive samples across its range would be a challenge for planning WGS studies. Besides, bringing compatible harmonized microsatellite data for defining conservation units has also been a challenge for species having transboundary range [28]. However, the control region (CR) of the mitochondrial genome ‘is the highly variable’region and 250 to 450 bp have been used in several phylogenetic/phylogeographic studies on wolves [4,29,30]. Therefore, we preferred to use CR region of 250 bp in the present study, which is easy to amplify with faecal DNA. This covers maximum variability and extensive comparable data are available from almost throughout the range, including the study of Nepal and others [11,15,19,31].

PCR amplification and DNA sequencing

Species of each scat was identified using mitochondrial cytochrome b gene with primers widely used in carnivores species [32]. Cytochrome b gene was amplified in 20 μl PCR, containing 2.0 μl DNA template, 1.6 mM MgCl2, 2x Buffer, 0.5 unit Tag DNA polymerase, 2.4 μldNTPs and 1.0 μM each primer. PCR cycling was performed with an initial denaturation for 5 minutes at 94 °C, followed by 40 cycles of denaturation for 45 s at 94 °C annealing for 60 s at 55 °C and 1 min extension at 72 °C with a final extension of 72 °C for 10 min. Only scats confirmed to be of Canis lupus (n = 19) were used for further analysis. These were from Jammu and Kashmir (n = 1), Himachal Pradesh (n = 15), Uttarakhand (n = 2) and Sikkim (n = 1). Mitochondrial control region (CR) was amplified with primers in [33] as above, except the annealing temperature was 56 °C for 45 s. The cycle sequencing of PCR products were cleaned using the BigDye Terminator kit (Applied Biosystems, USA) and purified products were subjected to DNA sequencing on the ABI 3730 Genetic Analyzer (Applied Biosystems, USA).

Data analysis

DNA sequences of cytochrome b and control region were examined and edited, and aligned using CLUSTAL W [34] as implemented in BioEdit v.7.2.5[35]. All electropherograms were inspected by eye for quality, especially for the observed variable sites and validated using Sequencher 4.7 (Gene Codes Corporation, USA). Generated sequences were also validated using reference data from the NCBI, BLAST at GenBank (http://www.ncbi.nlm.nih.gov). Besides sequences generated in this study, we also retrieved total 66 sequences of Canis lupus sub-species control region from the GenBank originating from Peoples Republic of China (PRC), Mongolia, Japan and India, and which were defined as C.l. chanco. We also retrieved one sequence that was assigned as Canis lupus laniger from Tibet. List of sequences used in this study are provided in the electronic supplementary file in S1 Table. All further analysis were done with control region data only. Divergence of sequences was calculated using the Kimura 2 parameters (K2P)distance matrix in the MEGA 6[36]. Genetic diversity was estimated by computing nucleotide (π) and haplotype (h) diversity in DnaSP 5.10 [37] which was used for neutrality tests (Tajima D and Fu’s Fs) as well. Nucleotide diversity calculated as the average number of nucleotide differences per site whereas haplotype diversity is the probability how two randomly sampled haplotypes are different[38]. Tajima D statistic used to measure the observed variation of a population with respect to variation expected in a randomly evolving population[39]. Fu’s Fs statistics is used to point the discrepancy between nucleotide differences observed in the samples[40]. Population differentiation (FST) as a measure of structure in natural population, ruggedness indices and mismatch distributions, implying size changes or stationarity of populations, were calculated using Arlequin v. 3.1.1[41]. The models for nucleotide substitution were selected comparing Akaike Information Criterion 2 scores implemented in the Model Generator [42]Patterns of historical demography can also be inferred from estimates of the effective population size over time using theBayesian skyline plot(BSP) method implemented in BEAST v. 2.1.3[43]. This method estimates a posterior distribution of effective population sizes through time via MCMC procedures, by moving backward in time until the most recent common ancestor is reached. The constant population size coalescent model was the basic assumption used for this approach. The among-site rate heterogeneity across all branches model, a strict molecular clock and a substitution rate of 0.04 × 10−9 /site/year[44]. Markov chains were run for 2.5 × 107 generations and were sampled every 1000 generations, with the first 2500 samples discarded as burn-in. Other parameters were set as default values and results were visualized in the TRACER v. 1.6 [45]. For the phylogenetic analysis, Bayesian inferences (BI), Maximum Likelihood (ML) and Neighbor-Joining (NJ) trees were reconstructed in MEGA [36] and the BEAST v.2.1.3 [46]. Nodal support was estimated using bootstrap analysis with 1000 replicates. Evolutionary relationships between sequences were assessed also with median-joining networks constructed with the program NETWORK v.4.5.1.0 (www.fluxus-engineering.com/network_terms.htm) using a median-joining algorithm and default settings as in Bandelt et al. (1999)[47]. Further, final phylogenetic tree were constructed using the Bayesian method using the sequences of all wolf sub-species distributed throughout the globe (S1 Table). Phylogenetic analyses were performed for 20 million generations while sampling every 1000th tree, and the first 10% of trees sampled were treated as burn in, and FigTree v.1.3.1 [48]was used to display and summarized annotated phylogenetic trees yielded by BEAST.

Results

Sequence variability, sequence divergence and haplotypes

We sequenced total 292 bp of the mitochondrial control region (mtCR) throughout the distribution range of Woolly wolf in the Himalayan region, resulting into an alignment of 263 bp. After merging our data with the sequences retrieved from the GenBank, a total 246 bp long alignment was retained for subsequent analysis. A total of 18 variable sites were observed resulting into 15 haplotypes (Table 1, Fig 1). We found two haplotypes in our data (Table 2). Haplotype 2was shared between the Himachal Pradesh and Uttarakhand, whereas haplotype 3was found in the Jammu and Kashmir, Uttarakhand and Sikkim (Tables 1 and 2; Fig 2). The sequence divergence between the haplotypes ranged from 0.000 to 0.044. The least divergent (0.001) were betweenH14 and H8 whereas highest divergence (0.044) was between H9 and H15 (S2 Table). The inter species sequence divergence was found between the 0.09–0.15 between the canids species (S4 Table). The sequence divergence between the Tibetan wolf and wolf of mainland was 0.09 which is slightly lower (0.13–0.16) than the sequence divergence observed in other canid species.
Table 1

Nucleotide variability between different haplotypesobserved from the wild collected samples of Indian Himalayan region and other published sequences of Woolly wolf (Canis lupus chanco) using a mitochondrial control region (246 bp).

HaplotypesNucleotide position
1111111111111111111
5555555555555555555
4445555555556666667
8890112455563344550
1855466614853846240
H1GTTGGGTGTGCCC-GACAG
H2.........A...-A..G.
H3....A....A...-A....
H4.........A...TA..G.
H5.....A...A...-A..GA
H6.........AT..TA..G.
H7AC.......A...-A....
H8.........A...-A....
H9..GA.A.CAA...-T....
H10.........A...-.....
H11.............-.GT..
H12....A.A..A...-A....
H13.........A...TT....
H14.........A...TA....
H15.........A.T.T.GT..
Table 2

Observed haplotypes in Woolly wolf (Canis lupus chanco) across its range in relation to geographical areas.

ZonesGeographical regionsNo. of samples usedHaplotypesReference
Himalayan RegionH1H2H3H4H5H6H7H8H9H10H11H12H13H14H15
JK, India211**Present study and Sharma et al. 2004
HP, India1515Present study
HP, India (Zoo)1717***Aggarwal et al. 2007
UK, India211Present study
Sikkim, India11Present study
Nepal31**1*1**Chetri et al. 2016
QTPTibet31*1**1**Meng, 2009
Unknown location, PRC92*1*3*1*1*1*GenBank
Qinghai Lake, PRC132*2*1*4*1*1*1*1*GenBank
MongoliaMongolia22*GenBank

JK = Jammu and Kashmir; HP = Himachal Pradesh; UK = Uttarakhand; China UK = China Unknown locations; China QL = China, Qinghai Lake

PRC = People’s Republic of China; QTP = Qinghai Tibetan Plateau

* Observed in earlier studies (published sequences)

** Observed in museum samples

*** Observed in captive samples

Fig 2

Haplotype distribution frequency of Canis lupus chanco from different geographical regions using the mitochondrial control regions (map not to scale).

JK = Jammu and Kashmir; HP = Himachal Pradesh; UK = Uttarakhand; China UK = China Unknown locations; China QL = China, Qinghai Lake PRC = People’s Republic of China; QTP = Qinghai Tibetan Plateau * Observed in earlier studies (published sequences) ** Observed in museum samples *** Observed in captive samples

Diversity and neutrality indices

The nucleotide (π) and haplotype (h) diversity among the Indian samples of the Woolly wolf were 0.00270 and 0.588, respectively. These values were relatively higher in PRC (π = 0.01278 and h = 0.888) than the Himalayan region including Nepal (π = 0.00344 and h = 0.606) (Table 3). The overall nucleotide and haplotype diversity of the Woolly wolf were 0.00851 and 0.777, respectively (Table 3). The two widely used neutrality tests, Tajima’s D and Fu’s Fs, were found positive, but statistically non-significant for the Indian samples. For all samples, the Tajima’s D and Fu’s Fs statistics values were negative, with only Tajima’s D value statistically significant (P<0.05) (Table 3). The mismatch distribution graphs from all the data and from our samples indicate a multimodal pattern (S1 Fig). For all the data, there was a high ruggedness (r) value (0.03157; P = 0.68000) and sum of square deviation (SSD; 0.00392 P = 0.69000), which are statistically non-significant (Table 3). The Bayesian skyline plots show a stable population size over the time except for a recent decline (Fig 3).
Table 3

Mitochondrial diversity indices and neutrality tests observed using sequences of the present study and so far reported from other areas for mitochondrial control region (246 bp) in Woolly wolf (Canis lupus chanco).

Sampling locationsNNhNucleotide Diversity (π)Haplotype diversity (h)Tajima value (D)Fu’ FsSSDr
India (UK, JK, HP, SK)3730.002700.5880.736360.7820.02870 (0.03000)0.20666 (0.02000)
Himalayan region4040.003440.606-0.49014-0.0550.02870 (0.03000)0.20666 (0.02000)
QTP, PRC25110.012780.888-0.95919-1.936
Mongolia21------
Overall66150.008780.790-1.65226*-4.1750.00392 (0.69000)0.03157 (0.68000)

N = number of samples, Nh = number of haplotype diversity,

JK = Jammu and Kashmir; HP = Himachal Pradesh; UK = Uttarakhand; QTP = Qinghai Tibetan Plateau; PRC = People’s Republic of China

*Statistically significant; values in parentheses are significance values

Fig 3

Bayesian skyline plot of Canis lupus chanco using mitochondrial control region.

N = number of samples, Nh = number of haplotype diversity, JK = Jammu and Kashmir; HP = Himachal Pradesh; UK = Uttarakhand; QTP = Qinghai Tibetan Plateau; PRC = People’s Republic of China *Statistically significant; values in parentheses are significance values

Network and phylogenetic tree analysis

Median-Joining network spanned a total of 15 haplotypes with two median vectors which show the missing connecting haplotypes (Fig 1). Most of the haplotypes are separated with 1–3 mutations, except H 9 in PRC that is separated by five mutations. Bayesian (BI) phylogenetic tree used with HKY model which were second suitable model for the interpretation as all the methods have shown similar topology. In the tree, the haplotypes form six major clades. In most clades, the haplotypes originate from multiple locations (S2 Fig), except in clades 1, 2 and 3. No clear phylogeographic pattern was seen in population genetic differentiation either. In overall, phylogenetic tree of all wolf subspecies splits in two major clade one as Woolly wolf clade and second is wolf-dog clade (Fig 4). These clades indicates that Woolly wolf and wolf-dog clades adequately diverged with the mean genetic divergence (0.08 SD). FST values calculated between the clades ranged from 0.533–1.00 (Table 4), however, they were not significant when calculated between geographic areas and higher values may be artifact of sample size. Significant differences were observed between clade 1 and 2 and between clades 5 and 6 when compared to the other clades (Table 4). The AMOVA, partitioned 71.35% of variation among the populations and 28.65 within the populations (S3 Table), with a highly significant FST (P = 0.0000; S3 Table).
Fig 4

Overall phylogenetic relationships of Woolly wolf and wolf-dog clade using the mitochondrial control region Cuon alpinus and Chrysocyon brachyurus are as the out-group.

Clade highlighted in red are the samples marked as C. l. chanco [49] and [50]. Blue lines indicates samples collected from the Himalayan range.

Table 4

Estimate of FST values in the different geographic areas and clades using a mitochondrial control region of Woolly wolf (Canis lupus chanco).

(a) Between geographic areas in Himalayan region
HPQTPUKNepalJKSK
Himachal Pradesh (HP)
QTP0.74432
Uttarakhand (UK)0.776120.04545
Nepal0.798660.142860.7956
Jammu and Kashmir (JK)0.8783-0.11628-0.2-0.0625
Sikkim (SK)1-0.2-1-0.875-10
(b) Between the clades
AreasClade1Clade2Clade3Clade4Clade5Clade6
Clade10
Clade20.66667*0
Clade31.00000.533980
Clade41.00000.818871.00000
Clade50.88664*0.87110*0.81872*0.94174*0
Clade60.80408*0.84528*0.63844*0.92004*0.67279*0

The FST values marked with * are significant (P = 0.05).

Clade 1: People’s Republic of China (PRC); Clade 2 Mongolia; Clade 3: PRC; Clade 4 India and PRC; Clade 5: India and PRC; Clade 6: India, QTP, Nepal and PRC.

Overall phylogenetic relationships of Woolly wolf and wolf-dog clade using the mitochondrial control region Cuon alpinus and Chrysocyon brachyurus are as the out-group.

Clade highlighted in red are the samples marked as C. l. chanco [49] and [50]. Blue lines indicates samples collected from the Himalayan range. The FST values marked with * are significant (P = 0.05). Clade 1: People’s Republic of China (PRC); Clade 2 Mongolia; Clade 3: PRC; Clade 4 India and PRC; Clade 5: India and PRC; Clade 6: India, QTP, Nepal and PRC.

Discussion

Phylogenetic or taxon status of the Woolly wolf from the Himalayan region in relation to QTP and Mongolia has been poorly known due to lack of samples from the wild [15,18]except in recent studies from Nepal [4,10,11,19]. By combining sequences from other studies, altogether seven haplotypes have been detected in the Himalayan region (Tables 1 and 2). The overall nucleotide diversity of the Woolly wolf across its range in Central Asia (0.00878;Table 3) was lower than in other wolf species of India and Central Asia (π 0.04-.012; Hd 0.11–0.94)[31] and golden jackal (π 0.0161)[51]. The nucleotide and haplotype diversities in the Woolly wolf of Himalaya were lower than at the QTP region (Table 3). Such higher mtDNA diversity in QTP region has also been reported among other species [52,53]. In corroboration to earlier findings [4,10,11,15,18,19], Woolly wolves from western to eastern Himalayan region were basal and monophyletic in the phylogenetic tree of Holarctic wolf and wolf-dog clades. The present-day monophyletic lineages of the Woolly wolf from Central Asia clustered in six sub-clades (S2 Fig). The Median-Joining (MJ) Network analysis revealed H8 and H2 as core haplotypes (Fig 1). The topology in Median-Joining (MJ) Network indicates intermixing of different populations, supported by the low FST-values among regions (Table 4). AMOVA analysis reveals a relatively higher variation between populations than within population (S3 Table). Harp ending’s raggedness index, multimodal mismatch distributions, high SSD-value and lack of a star-like Median-Joining Network together with the Bayesian Skyline result support stable long-term population size [54,55]of the Woolly wolf in this area. A similar trend was also reported in Golden Jackal [51]. The Bayesian Skyline analysis also indicated a decline of the effective population size in the recent time (Fig 3). Such a recent decline has also been reported from the brown bear [56], Tibetan antelope (Pantholops hodgsonii) and Tibetan gazelle (Procaprapicticaudata) [53] in this landscape. The lack of geographic affinity of haplotypes observed within the sub-clades of C. l. chanco (S2 Fig) has also observed at the global scale for wolves from the different parts of Eurasia[10]. The shallow divergence within the Woolly wolf clade indicates that all the populations in Central Asia probably emerged within a very short period from ancestor. Our analyses (S2 Fig; S2 Table) indicate that the ancestor of present-day Woolly wolf lineage probably had ranging behavior covering longer distances across its range during the glaciation-deglaciation periods and the population was quite stable despite of climatic oscillation (Fig 3).

Presence of regional private haplotypes and paleo-ecological perspective

Even though the Woolly wolf has extremely large territories(6670–26619 km2) in Mongolia [57] and 800–1000 km2 in the Himalayan region (Lyngdoh et al. unpublished), and therefore same haplotypes were found over the large areas, however, some regional geographic affinity was also observed (Table 2; Fig 5). Of the two haplotypes (H2 and H3) collected from the wild along Indian Himalaya, H3 was shared among the locations in Jammu and Kashmir, Uttarakhand, Sikkim, and QTP (Table 2) and may be ancient haplotype. This indicates connectivity of populations through the rugged terrains of southern QTP which is similar to Himalayan region (Fig 5) and may have probably facilitated the movement of the female wolf between western and eastern Himalaya in the past. Presence of similar genetic connectivity between Jammu and Kashmir to Sikkim has also been observed in the snow leopard based on mtDNA and nuclear markers (Singh et al. unpublished). The observed Haplotype H2 in the present study was restricted to Himachal Pradesh (HP) and Uttarakhand. Similarly, in the Himalayan Brown bear which is sympatric with Woolly wolf in this landscape has also shared a haplotype only between HP and Uttarakhand in the western Himalayan region (Goyal et al. unpublished). These observations may indicate the presence of suitable corridor connecting habitats between HP and Uttarakhand, whereas such connectivity may probably lacking with other parts, especially with JK in the northern region. However, this should be validated by monitoring GPS tagged Woolly wolf individual and GIS analysis. Haplotype H7 was also restricted to the wild population of Nepal and has not been reported from anywhere else (Table 2). Absence of QTP haplotypes in Mongolia may be due to Quilon mountains (Fig 2), which have been a barrier for some species after deglaciation periods may be due to differences in availability of the wild prey species across these two regions (Fig 5). Observed private regional haplotypes may indicate multi-stage population divergence in the past(Fig 5), as these areas are well known for differential glacial and interglacial periods across Himalaya and QTP even after the LGM [58,59]. This may have been the reason of different ectomorphs of the Woolly wolf reported at different parts of its range [12]. Similar divergence from multiple refugia has been reported for Himalayan snow cock (Tetraogallus himalayensis) in this landscape [60].
Fig 5

Distribution of haplotypes in relation to terrain profile of Himalayan region (HR), QTP and Mongolia.

(SQTP = South QTP; SW = Southwest; SE = Southeast). Red colour represent the haplotype distributed only in the QTP, PRC green represent the haplotype only distributed in the Himalaya and QTP.

Distribution of haplotypes in relation to terrain profile of Himalayan region (HR), QTP and Mongolia.

(SQTP = South QTP; SW = Southwest; SE = Southeast). Red colour represent the haplotype distributed only in the QTP, PRC green represent the haplotype only distributed in the Himalaya and QTP. Presence of private haplotypes (Table 2; Fig 5) may indicate that there are some restrictions to dispersal. This may indicate significance of some physical, ecological or biological factors that limit the spread of haplotypes to areas, which would be within the dispersal ability of the Woolly wolf[57](Lyngdoh et al unpublished). The time used to search and pursue for prey influences the foraging strategy of a predator and this behavior has been found to differ across terrain complexities and dominate prey species [61]. Wolves occur in varied topographies and differ significantly in the type, density and selection of prey species across the world[62-65]. We also noted that different terrain complexities (Fig 5) and variation in the availability of the wild prey species guilds affect the dietary habits of the Woolly wolf across its range (Fig 5). Medium to large sized species were major prey species in the Himalayan range, whereas small sized species were preferred in QTP and Mongolia (Fig 6).
Fig 6

Variation in terrain complexities and wild prey species in the diet of Woolly wolf based on different studies (1–9) across its range in Central Asia.

(1: [66]; 2: [67]; 3: [68]; 4: [69]; 5: [70]; 6: [71]; 7: [72]; 8: [73]; 9: [74]).

Variation in terrain complexities and wild prey species in the diet of Woolly wolf based on different studies (1–9) across its range in Central Asia.

(1: [66]; 2: [67]; 3: [68]; 4: [69]; 5: [70]; 6: [71]; 7: [72]; 8: [73]; 9: [74]). Genetic structuring have been observed in wolves despite the absence of topographic barriers limiting dispersal. Known drivers for this have been familiarization to natal habitat, prey specialization [17,75-78]and probably hunting skills to particular wild prey species that were passed on from parents to their offspring[78]. In the absence of information on species’ ranging and foraging behavior and in concurrence with the literature, we speculate that these drivers and the past paleoclimatic conditions over Himalaya-QTP-Mongolia regions might have been the reasons for the observed private haplotypes (Table 2; Fig 6). The haplotypes which have been detected either in the museum or zoo samples (Table 2), have so far not been reported in wild samples in spite of reasonably extensive sampling in the present study (n = 19) and in Nepal (n = 72)[4,19]. We suggest a need of extensive sampling in the Himalayan region to find for the haplotypes reported from museums or zoos in the wild. Moreover, such sampling strategies may shed light on existing barriers of gene flow in the Himalayas.

Sequence ambiguity in Woolly wolf: Are they Himalayan or Tibetan or Mongolian?

Earlier study indicated that the Himalayan wolf is a separate basal clade among the other wolves of the world[18]. In their analysis, samples of Grey wolf from peninsular India (C. l.pallipes) and a total of five sequences of C. l. chanco originating from Mongolia and also used in a another study [49]clustered in the same clade, whereas Himalayan wolf sequences generated by them were in a separate ancient lineage. Therefore, it was suggested that the Himalayan wolf should be considered as a separate species C. himalayensis[18]. However, sequences of the present study along with all available sequences of the C. l. chanco and C. himalayensis clustered in a single Woolly wolf clade whereas sequences of C. l. chanco used in another study[49] were clustered in Dog-wolf clade (Fig 4). We, therefore, believe that these sequences may not be of the Woolly wolf. Such ambiguity in the sequences has also been reported in other related canids[29,79]. When these sequences were removed, we found no evidence for Canis lupus chanco to be distinct from the Himalayan wolf. Therefore, we advocate that there is only one extant sub-species C. l. chanco throughout the Himalayan and Central Asian Highlands (Fig 4).

A need for classifying Woolly wolf as separate conservation unit

Available evidence also suggests the presence of genetic and ecological adaptations that are unique to Woolly wolf across Himalaya, QTP, and Mongolia compared to other wolves. We believe that positive selection of hypoxia-related genetic selection [80] and the placement of all the studied populations of Himalaya, QTP and Mongolia in the same distinct ancient lineage, C.l. chanco ~ C.l. laniger ~ C.lhimalayensis need special conservation and recognition as a separate Evolutionary Significant Unit (ESU). Due to the presence of private regional haplotypes and ecological specialization, as a result from differences in terrain characteristics and differences in the availability of prey species, we advocate further studies using different genetic markers to identify Management Units [81] or Evolutionary Significant Units across range of this sub-species. These conservation units would form a basis for planning effective conservation strategies and would provide scientific support for retaining the regional level genetic integrity and avoid any mixing of gene pool among populations of different ecological specialization. Therefore, we suggest a need of trans-boundary studies using harmonized multi genetic markers so as to ascertain whether Woolly wolf may be designated as a separate species i.e.Canischanco or not. “Chanco” is a latinised pronunciation for wolf among the Tibeto-Mongoloid community in Central Asia, encompassing a large proportion of the Woolly wolf range. A recent study on Woolly wolf from Nepal, based on different molecular markers also suggested considering it as a distinct species [4,19].

Conclusion

Woolly wolf samples from the wild from the western to eastern Himalayan region along with other samples from Nepal, QTP, and Mongolia were placed within the same basal clade in phylogenetic analyses reconfirming that the Woolly wolf clade is ancient to wolf and wolf-dog clades. Because of shallow divergence, non-significant FST values and low genetic distances among the sub-clades within the monophyletic clade, our study suggest that Woolly wolf is, in fact, Canis lupus chanco and not Canishimalyansis or C.l.laniger. We observed lower genetic diversity in the populations of the Himalayan region than in QTP. Our analysis reveals that the Woolly wolf deserved recognition as an ESU due to its distinct evolution from paleo-ecological times, adaptation to hypoxic conditions, terrain complexities and unique wild prey assemblage in comparison to other Holarctic wolf populations[64,82]. Furthermore, wolves are known to range longer distances, therefore, there is also a need for trans-boundary efforts in research and conservation management for (i) identifying critical habitats and connectivity corridors through harmonized methods and genetic markers [19,28] in order to ensure long-term survival of this ancient lineage and (ii) use of harmonized multi genetic markers to ascertain whether the Woolly wolf may be designated as separate species or not. Besides the area has the long-standing history of persecution of wolves that is still prevalent. Therefore, a need for effective protection to minimize the wolf-human conflict due to livestock depredation is needed for ensuring viable population for effective conservation in this landscape.

Details of samples and Sequences used in this study.

(DOCX) Click here for additional data file.

Sequence divergence between the different haplotypes (H1-H15) of Woolly wolf (Canis lupus chanco) using a mitochondrial control region.

(DOCX) Click here for additional data file.

AMOVA results of Woolly wolf in phylogenetic tree of different clades.

(DOCX) Click here for additional data file.

Inter species genetic distance of the family canidae using control regions marker.

(DOCX) Click here for additional data file.

Pairwise mismatch distribution graph of Canis lupus chanco using a mitochondrial control region.

(DOCX) Click here for additional data file.

Phylogenetic analysis based on Bayesian inferences (BI) tree constructed of Canis lupus chanco using mitochondrial control region of Cuon alpines and Chrysocyon brachyurus as the out group.

Map showing the clade wise distribution of samples in their distribution range. Values above the nodes are posterior probabilities. (DOCX) Click here for additional data file. 5 Feb 2020 PONE-D-20-00939 Revisiting the Woolly wolf (Canis lupus chanco) phylogeny in Himalaya: Addressing taxonomy, spatial extent and distribution of an ancient lineage in Asia PLOS ONE Dear Dr. Goyal, Thank you for submitting your manuscript to PLOS ONE. After careful consideration, we feel that it has merit but does not fully meet PLOS ONE’s publication criteria as it currently stands. Therefore, we invite you to submit a revised version of the manuscript that addresses the points raised during the review process. Please address the minor issues. There is no need to produce more data, but rephrase the species status accordingly. The data are not sufficient to draw definite conclusions at this point. We would appreciate receiving your revised manuscript by Mar 21 2020 11:59PM. 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Any typographical or grammatical errors should be corrected at revision, so please note any specific errors here. Reviewer #1: No Reviewer #2: Yes ********** 5. Review Comments to the Author Please use the space provided to explain your answers to the questions above. You may also include additional comments for the author, including concerns about dual publication, research ethics, or publication ethics. (Please upload your review as an attachment if it exceeds 20,000 characters) Reviewer #1: The authors investigated the phylogenetic status of the woolly wolf, a type of wolf that inhabits the Himalayan Region, the Qinghai Tibetan Plateau (QTP) and Mongolia. The authors sequenced the mt control regions of 19 individuals from the Himalayan Region, namely from Jammu and Kashmir (JK, n=1), Himachal Pradesh (HP, n=15), Uttarakhand (UK, n=2) and Sikkim (n=1)). They compared these sequences to 48 wolf mt control region sequences downloaded from Genbank, originating from the Himalayan Region (21), the QTP (Tibet, Qinghai Lake, and unknown location, n = 25) and Mongolia (2). There objectives were twofold: to study population structuring of the woolly wolf, and to reexamine the taxonomic status of the woolly wolf, as previous studies have suggested that the status of the woolly wolf should be elevated to the species level. In my opinion the authors meet the first objective satisfactorily, but don’t provide enough new data or analyses to meet the second objective. They argue that Himalayan, QTP and Mongolian wolves group together in a basal wolf lineage, and that in addition these wolves are uniquely adapted to height. On these two grounds the authors argue that the woolly wolf should be considered as a separate species. Although I don’t necessarily disagree, I think more new data and more solid evidence is needed to justify this claim. Since the taxonomic status of the woolly wolf is not the main theme of the paper, the authors could consider downplaying these statements. Alternatively, the authors could expand in the discussion on the species concept discussion (if they really want to go down that road), and discuss how the observed genetic distance of woolly wolves and other wolves compares to the genetic divergence of other carnivore subspecies/species pairs. In addition, figure S3 should became a main figure, and be discussed more thoroughly (both in the methods and the results section). Considering the presentation of the data, the high number of location names causes a bit of confusion for the reader, at least for me. For the figures, I suggest to use colour coding and/or labelling to clarify whether sampling locations belong to either of the three/four main geographical regions (i.e. India/Himalaya, Qinghai Tibetan Plateau and Mongolia). Additionally, figures could be shrinked and presented as a multi tile plot to facilitate comparisons. As a final point: although the text is clearly written and easy to follow, there are typo’s and grammar errors (such as the wrong use of ‘also’ and ‘the’) which need to be improved prior to publication. I listed some typo's below, but just a random selection. Please ensure that during revision all typo's and grammatical errors (also the ones not listed below) are corrected. Title: what do you mean with 'spatial extent'? Line 41: most studies agree, that… No comma Line 43: a separate species by some… Remove ‘by some’ Line 52: By combining our data to…. After combining our data with Line 54: the number of observed haplotypes depends on sample size. Why not use another, sample size independent, estimate for genetic diversity? Line 56: shallow divergence (0.000-0.044). which estimator? Line 58: over a long time. How long is long? Line 58: over the a long…. Remove ‘the’ Line 61: within the range of the Woolly wolf’s…. Remove ‘s Line 63-65: adaptation is in itself not sufficient to validate species status. As an example: the arctic wolf is uniquely adapted to the polar habitat, but is considered a subspecies and not a species, and many more examples can be given. Line 67: there is an urgent need of transboundary efforts in identifying management units (MUs) to help conservation. How does this follow from the results? Line 76: what do you mean with long-ranging mammals? Line 134-136: I think the objectives could be stated a bit more precisely. I wonder how the objective stated in lines 134_36 differ from re-examining the taxonomy of the woolly wolf, which you already mentioned in the previous sentence? For phylogeography you have not much data to work on. Maybe it is more correct to say that you study the population structure of the Himalayan wolf? Line 161: and size too? Line 163: remove ‘a’ Line169: ‘is the highly variable’ Line 181-182: Jammu and Kashmir (n=1), Himachal Pradesh (n=15), Uttarakhand (n=2) and Sikkim (n=1). Does this uneven distribution somehow affect the study outcomes? Line 193-196: Specify in main text and in abstract how many additional samples. I inferred from the tables that the number is 48 if I didn’t make a calculation error, but this information should be more easy to find. Line 203: ruggedness indices Line 217: For the phylogenetic analysis… start new paragraph. Line: 255 why Fst values so high? Line 250-252. Only Bayesian (BI) phylogenetic tree used for the interpretation as all the methods have shown similar topology. This explains why you chose so show one tree building method, but not why you choose Bayesian method in particular. Line 365: Why is figure S3 not mentioned in the results section? TABLES AND FIGURES Table 1. what is the meaning of PRC? (stand-alone test: can you understand the figure without reading the main text?) Table 2: concerning the captive samples, inbreeding could affect the result and is maybe worth a few lines of discussion in either the methods or the discussion section Figure 1. Could you make the labels a bit bigger? Also, since in table 1 you refer to Himachal Pradesh, for consistency I suggest to replace on the map the text Spiti Valley with Himachal Pradesh or HP. It took me a long time to work out the location of HP samples. Also, the number of colours is quite overwhelming. As I suggested above, it might make it easier for the reader if you use colour coding based on the main geographical regions. Figure2. I would suggest to make the piecharts a bit bigger, and to crop the map (currently no samples in right third and upper part of the map). Would be even better if the size of the piecharts would be relative to the number of samples. Figure 4. What do the colours red and green represent? Figure S1. Is the deviation between expected and observed mismatch distribution significant? Reviewer #2: This is a well-written and easy to follow manuscript which presents some new results and insight into the taxonomy, phylogeography and conservation genetics of the wolly wolf. The paper has used a non-invasive sampling approach, by collecting faeces in the Field, and also include previously published data/sequences from other geographic areas. Therefore, the results are representative for most of the Himalayan region. I find the study useful, and I only have a few suggestions/questions. Astract: ok, but is perhaps unncessesarily long? I would recommend to shorten it . Main text: All parts are well written and relatively easy to follow, at least if you have a background in genetics. However, the Data analysis section in the Methods might be hard to read if you dont have a specialist background. I would recommend to add a few sentences to explain/describe in words what purpose the different statistical analyses have in your study (and perhaps even some expectations/predictions), so that a wider readership can follow and understand the results, e.g. non-geneticist interested in predators and/or Conservation issues. If neccesary, to the same aim, follow up and add a few half sentences in the results too, so that everything connects nicely. Other than that I find the study well written and interesting. ********** 6. PLOS authors have the option to publish the peer review history of their article (what does this mean?). If published, this will include your full peer review and any attached files. If you choose “no”, your identity will remain anonymous but your review may still be made public. Do you want your identity to be public for this peer review? For information about this choice, including consent withdrawal, please see our Privacy Policy. Reviewer #1: No Reviewer #2: No [NOTE: If reviewer comments were submitted as an attachment file, they will be attached to this email and accessible via the submission site. Please log into your account, locate the manuscript record, and check for the action link "View Attachments". If this link does not appear, there are no attachment files to be viewed.] While revising your submission, please upload your figure files to the Preflight Analysis and Conversion Engine (PACE) digital diagnostic tool, https://pacev2.apexcovantage.com/. PACE helps ensure that figures meet PLOS requirements. To use PACE, you must first register as a user. Registration is free. Then, login and navigate to the UPLOAD tab, where you will find detailed instructions on how to use the tool. If you encounter any issues or have any questions when using PACE, please email us at figures@plos.org. Please note that Supporting Information files do not need this step. 21 Mar 2020 Point to point authors response to the Reviewers’ comments Manuscript ID: PONE-D-20-00939 Manuscript title: Joshi et al. -Revisiting the Woolly wolf (Canis lupus chanco) phylogeny in Himalaya: Addressing taxonomy, spatial extent and distribution of an ancient lineage in Asia Please use the space provided to explain your answers to the questions above. You may also include additional comments for the author, including concerns about dual publication, research ethics, or publication ethics. (Please upload your review as an attachment if it exceeds 20,000 characters) The authors would like express thanks to the reviewer for considering our manuscript interesting and accepting it for publication after revision. We have incorporated all suggestions raised by the reviewer’s for each of the questions in preparation of revised version of manuscript. Reviewer #1: Comments:The authors investigated the phylogenetic status of the woolly wolf, a type of wolf that inhabits the Himalayan Region, the Qinghai Tibetan Plateau (QTP) and Mongolia. The authors sequenced the mt control regions of 19 individuals from the Himalayan Region, namely from Jammu and Kashmir (JK, n=1), Himachal Pradesh (HP, n=15), Uttarakhand (UK, n=2) and Sikkim (n=1)). They compared these sequences to 48 wolf mt control region sequences downloaded from Genbank, originating from the Himalayan Region (21), the QTP (Tibet, Qinghai Lake, and unknown location, n = 25) and Mongolia (2). There objectives were twofold: to study population structuring of the woolly wolf, and to reexamine the taxonomic status of the woolly wolf, as previous studies have suggested that the status of the woolly wolf should be elevated to the species level. Author response: We appreciate reviewer to evaluate the manuscript carefully. Earlier studies are in support of present study but lack of comprehensive data across Indian Himalayan range previous studies (Aggarwal et al. 2007) suggested that wolf found in the Himalayan region should be designated as separate species. The present study generates largest available samples size of wild Woolly wolf across Himalayas and analysis suggests that Woolly wolf distributed across Mongolia, QTP and India is a single sub-species. We claim that the sub-species may be considered as an ESU though existing studies support the view that the species deserves recognition as a Taxon. Comments: In my opinion the authors meet the first objective satisfactorily, but don’t provide enough new data or analyses to meet the second objective. They argue that Himalayan, QTP and Mongolian wolves group together in a basal wolf lineage, and that in addition these wolves are uniquely adapted to height. On these two grounds the authors argue that the woolly wolf should be considered as a separate species. Author response: We agree with reviewer and have rephrased the species status accordingly (line no. 28-30). However, we suggest that the Woolly wolf may be uplifted to species level from the grey wolf found in the main land of Indian, Pakistan and other regions. Comments: Although I don’t necessarily disagree, I think more new data and more solid evidence is needed to justify this claim. Since the taxonomic status of the woolly wolf is not the main theme of the paper, the authors could consider downplaying these statements. Alternatively, the authors could expand in the discussion on the species concept discussion (if they really want to go down that road), and discuss how the observed genetic distance of woolly wolves and other wolves compares to the genetic divergence of other carnivore subspecies/species pairs. In addition, figure S3 should became a main figure, and be discussed more thoroughly (both in the methods and the results section). Author response: We have downplayed our statements and compared genetic distances within the canids (line no 276-279) and found sequence divergence between the subspecies from 0.03-0.06 of dog wolf clade. Whereas, sequences of dog-wolf clade showed the higher sequence divergence with wooly wolf. Inter species sequences divergence of different canid species were found 0.135-0.163 which is slightly higher than the observed (0.078-090) between the wooly wolf– (Canis lupus chanco) and Grey wolf (Canis lupus lupus/ Canis lupus lupus/ Canis lupus lupus). We brought the figure in main text as Figure 4 and discussed this appropriately both in methods and results section. Comments: Considering the presentation of the data, the high number of location names causes a bit of confusion for the reader, at least for me. For the figures, I suggest to use color coding and/or labelling to clarify whether sampling locations belong to either of the three/four main geographical regions (i.e. India/Himalaya, Qinghai Tibetan Plateau and Mongolia). Additionally, figures could be shrinked and presented as a multi tile plot to facilitate comparisons. Author response: We have changed all suggested figures to readable and increased the size (Figure 1 and Figure 2). As a final point: although the text is clearly written and easy to follow, there are typo’s and grammar errors (such as the wrong use of ‘also’ and ‘the’) which need to be improved prior to publication. I listed some typo's below, but just a random selection. Please ensure that during revision all typo's and grammatical errors (also the ones not listed below) are corrected. Author response: Agreed and manuscript has carefully checked. Title: what do you mean with 'spatial extent'? Author response: Spatial extent is geographical extent of the sample coverage Line 41: most studies agree, that… No comma Author response: Corrected as per suggestion Line 43: a separate species by some… Remove ‘by some’ Author response: Corrected as per suggestion Line 52: By combining our data to…. After combining our data with Author response: Corrected as per suggestion Line 54: the number of observed haplotypes depends on sample size. Why not use another, sample size independent, estimate for genetic diversity? Author response: Corrected as per suggestion Line 56: shallow divergence (0.000-0.044). Which estimator? Author response: Corrected as per suggestion and provided in details of all parameters. Line 58: over a long time. How long is long? Author response: Corrected as per suggestion Line 58: over the a long…. Remove ‘the’ Author response: Corrected as per suggestion Line 61: within the range of the Woolly wolf’s…. Remove ‘s Author response: Corrected as per suggestion Line 63-65: adaptation is in itself not sufficient to validate species status. As an example: the arctic wolf is uniquely adapted to the polar habitat, but is considered a subspecies and not a species, and many more examples can be given. Author response: Apart from adaptation, there are other factors that can be argued in this context, i.e isolation in a large area and time, in the line of African Wolf. Also there are morphological traits that are distinct and not found in many closely related sister species. Even their howls are distinct (Hennelly et al 2017). So there are various other studies which support this finding (Werhan et al 2020). There are also dietary factors which make this wolf uniquely adapted to preying on high altitude species (Lyngdoh et al 2020). There are different species concepts that can fit this justification however, as agreed with the reviewer we advocate a single species in the entire region distinct from the Holarctic wolf and do not recognize Himalayan Wolf as separate from Tibetan Wolf. There lines have modified now Line 67: there is an urgent need of transboundary efforts in identifying management units (MUs) to help conservation. How does this follow from the results? Author response: This follows from the recognition of the species as a single entity distinct from Holarctic wolves. The Woolly wolves are well adapted ecological, biologically and morphologically. From available literature, it seems wolves range long distances and often cross political boundaries. In trans-Himalayas and Tibetan Region, prey populations are depressed (Lyngdoh et al 2019). These regions support wolves which may be in huge conflict due to practices that prevail and legislative mechanisms in countries. Therefore, following our data and field data, we know that wolves are distinct yet long ranging, hence trans-boundary conservation efforts are essential for the natural gene flow amongst these individuals. Line 76: what do you mean with long-ranging mammals? Author response: The species has large home range (> 1000 sq. km) across trans-boundary and displays altitudinal migratory behavior from field data behviour such as Tibetan wolf have recorded as larger home ranges (6670–26619 km2 in Mongolia (Kaczensky et al., 2008) and 800–1000 km2 in the Himalayan region (Lyngdoh et al. unpublished). Line 134-136: I think the objectives could be stated a bit more precisely. I wonder how the objective stated in lines 134_36 differ from re-examining the taxonomy of the woolly wolf, which you already mentioned in the previous sentence? For phylogeography you have not much data to work on. Maybe it is more correct to say that you study the population structure of the Himalayan wolf? Author response: Necessary changes made as suggested in line number 124-128. Line 161: and size too? Author response: Corrected as per suggestion Line 163: remove ‘a’ Author response: Corrected as per suggestion Line169: ‘is the highly variable’ Author response: Corrected as per suggestion Line 181-182: Jammu and Kashmir (n=1), Himachal Pradesh (n=15), Uttarakhand (n=2) and Sikkim (n=1). Does this uneven distribution somehow affect the study outcomes? Author response: No these may lead to increase of some haplotype but will not change overall assignment and population structure Line 193-196: Specify in main text and in abstract how many additional samples. I inferred from the tables that the number is 48 if I didn’t make a calculation error, but this information should be more easy to find. Author response: All the details have been given in text in the line no. 213 Line 203: ruggedness indices Author response: Corrected as per suggestion Line 217: For the phylogenetic analysis… start new paragraph. Author response: Corrected as per suggestion Line: 255 why Fst values so high? Author response: This may be due to small samples size Line 250-252. Only Bayesian (BI) phylogenetic tree used for the interpretation as all the methods have shown similar topology. This explains why you chose so show one tree building method, but not why you choose Bayesian method in particular. Author response: As Bayesian tree widely used and also the best suitable nucleotide substitution modes HKY were available with BEAST package and reasons have been provided in the methods in details. Line 365: Why is figure S3 not mentioned in the results section? Author response: As suggested, this has been brought as main figure and discussed accordingly in line no 302-314. TABLES AND FIGURES Table 1. what is the meaning of PRC? (stand-alone test: can you understand the figure without reading the main text?) Author response: All abbreviation have been provided carefully and clarity of text have been given Table 2: concerning the captive samples, inbreeding could affect the result and is maybe worth a few lines of discussion in either the methods or the discussion section Author response: Use of maternal inherited genetic markers is not affected by inbreeding because the respective haplotype would be present in next progeny. Therefore, inclusion of captive samples in our analysis may not affect our conclusion. Figure 1. Could you make the labels a bit bigger? Also, since in table 1 you refer to Himachal Pradesh, for consistency I suggest to replace on the map the text Spiti Valley with Himachal Pradesh or HP. It took me a long time to work out the location of HP samples. Also, the number of colours is quite overwhelming. As I suggested above, it might make it easier for the reader if you use colour coding based on the main geographical regions. Author response: Yes Agreed Author response: We have made appropriate changes 1) Increased the labels size, changed spiti valley to Himachal Pradesh and subsequent in the text. In this figure 1 we would like show the individually haplotypes of wild and museum/zoo samples therefore the haplotype coloring pattern is given in map as per Haplotype Network. However we have changed size and labels for the clarity. Figure 2. I would suggest to make the piecharts a bit bigger, and to crop the map (currently no samples in right third and upper part of the map). Would be even better if the size of the piec harts would be relative to the number of samples. Author response: Necessary changes were made in Figure. Figure 4. What do the colours red and green represent? Author response: Labels have been provided. Figure S1. Is the deviation between expected and observed mismatch distribution significant? Author response: No there is no significant deviation. Reviewer #2: This is a well-written and easy to follow manuscript which presents some new results and insight into the taxonomy, phylogeography and conservation genetics of the Woolly wolf. The paper has used a non-invasive sampling approach, by collecting faeces in the Field, and also include previously published data/sequences from other geographic areas. Therefore, the results are representative for most of the Himalayan region. I find the study useful, and I only have a few suggestions/questions. Author response: We thank reviewer for positive response. Astract: ok, but is perhaps unncessesarily long? I would recommend to shorten it . Author response: The abstract is reduced as suggested Main text: All parts are well written and relatively easy to follow, at least if you have a background in genetics. However, the Data analysis section in the methods might be hard to read if you do not have a specialist background. I would recommend to add a few sentences to explain/describe in words what purpose the different statistical analyses have in your study (and perhaps even some expectations/predictions), so that a wider readership can follow and understand the results, e.g. non-geneticist interested in predators and/or Conservation issues. If necessary, to the same aim, follow up and add a few half sentences in the results too, so that everything connects nicely. Author response: All required suggestion has been incorporated. Other than that I find the study well written and interesting. Author response: We thanks to reviewers for reviewing the manuscript from line 223-237. Submitted filename: Authors response.docx Click here for additional data file. 30 Mar 2020 Revisiting the Woolly wolf (Canis lupus chanco) phylogeny in Himalaya: Addressing taxonomy, spatial extent and distribution of an ancient lineage in Asia PONE-D-20-00939R1 Dear Dr. Goyal, We are pleased to inform you that your manuscript has been judged scientifically suitable for publication and will be formally accepted for publication once it complies with all outstanding technical requirements. Please follow my instructions in the comments to the authors. They are not mandatory,  but in your own interest to improve the value of the fascinating study. Within one week, you will receive an e-mail containing information on the amendments required prior to publication. When all required modifications have been addressed, you will receive a formal acceptance letter and your manuscript will proceed to our production department and be scheduled for publication. Shortly after the formal acceptance letter is sent, an invoice for payment will follow. To ensure an efficient production and billing process, please log into Editorial Manager at https://www.editorialmanager.com/pone/, click the "Update My Information" link at the top of the page, and update your user information. If you have any billing related questions, please contact our Author Billing department directly at authorbilling@plos.org. If your institution or institutions have a press office, please notify them about your upcoming paper to enable them to help maximize its impact. If they will be preparing press materials for this manuscript, you must inform our press team as soon as possible and no later than 48 hours after receiving the formal acceptance. Your manuscript will remain under strict press embargo until 2 pm Eastern Time on the date of publication. For more information, please contact onepress@plos.org. With kind regards, Axel Janke Academic Editor PLOS ONE Additional Editor Comments (optional): Dear Authors 1) the abstract is not shortened as suggested by one reviewer. I opted to accept the paper, because I _trust_ that you will shorten it to a standard size. Abstracts typically have 200-300 Words. It almost 500 words now! 2) I also trust that you go carefully through the MS again and implement and add a few explanations that you provided to reviewer's one questions to improve the MS, e.g. what is a long-ranging species, what you you mean by spatial and so on. While you have dutifully answered the questions in the reply, some of that did not make it into the MS. This is not crucial and at your discretion, but it is in your own interest. Reviewers' comments: 3 Apr 2020 PONE-D-20-00939R1 Revisiting the Woolly wolf (Canis lupus chanco) phylogeny in Himalaya: Addressing taxonomy, spatial extent and distribution of an ancient lineage in Asia Dear Dr. Goyal: I am pleased to inform you that your manuscript has been deemed suitable for publication in PLOS ONE. Congratulations! Your manuscript is now with our production department. If your institution or institutions have a press office, please notify them about your upcoming paper at this point, to enable them to help maximize its impact. If they will be preparing press materials for this manuscript, please inform our press team within the next 48 hours. Your manuscript will remain under strict press embargo until 2 pm Eastern Time on the date of publication. For more information please contact onepress@plos.org. For any other questions or concerns, please email plosone@plos.org. Thank you for submitting your work to PLOS ONE. With kind regards, PLOS ONE Editorial Office Staff on behalf of Dr. Axel Janke Academic Editor PLOS ONE
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Authors:  L E Carmichael; J A Nagy; N C Larter; C Strobeck
Journal:  Mol Ecol       Date:  2001-12       Impact factor: 6.185

2.  DnaSP v5: a software for comprehensive analysis of DNA polymorphism data.

Authors:  P Librado; J Rozas
Journal:  Bioinformatics       Date:  2009-04-03       Impact factor: 6.937

3.  SNP Discovery from Single and Multiplex Genome Assemblies of Non-model Organisms.

Authors:  Phillip A Morin; Andrew D Foote; Christopher M Hill; Benoit Simon-Bouhet; Aimee R Lang; Marie Louis
Journal:  Methods Mol Biol       Date:  2018

4.  RADSeq: next-generation population genetics.

Authors:  John W Davey; John L Davey; Mark L Blaxter; Mark W Blaxter
Journal:  Brief Funct Genomics       Date:  2010-12       Impact factor: 4.241

5.  Phylogeography of Tibetan snowcock (Tetraogallus tibetanus) in Qinghai-Tibetan Plateau.

Authors:  Bei An; Lixun Zhang; Stephen Browne; Naifa Liu; Luzhang Ruan; Sen Song
Journal:  Mol Phylogenet Evol       Date:  2008-12-11       Impact factor: 4.286

6.  A robust, simple genotyping-by-sequencing (GBS) approach for high diversity species.

Authors:  Robert J Elshire; Jeffrey C Glaubitz; Qi Sun; Jesse A Poland; Ken Kawamoto; Edward S Buckler; Sharon E Mitchell
Journal:  PLoS One       Date:  2011-05-04       Impact factor: 3.240

7.  Genetic variability of the grey wolf Canis lupus in the Caucasus in comparison with Europe and the Middle East: distinct or intermediary population?

Authors:  Małgorzata Pilot; Michał J Dąbrowski; Vahram Hayrapetyan; Eduard G Yavruyan; Natia Kopaliani; Elena Tsingarska; Barbara Bujalska; Stanisław Kamiński; Wiesław Bogdanowicz
Journal:  PLoS One       Date:  2014-04-08       Impact factor: 3.240

8.  Top predators constrain mesopredator distributions.

Authors:  Thomas M Newsome; Aaron C Greenville; Duško Ćirović; Christopher R Dickman; Chris N Johnson; Miha Krofel; Mike Letnic; William J Ripple; Euan G Ritchie; Stoyan Stoyanov; Aaron J Wirsing
Journal:  Nat Commun       Date:  2017-05-23       Impact factor: 14.919

9.  Hypoxia adaptations in the grey wolf (Canis lupus chanco) from Qinghai-Tibet Plateau.

Authors:  Wenping Zhang; Zhenxin Fan; Eunjung Han; Rong Hou; Liang Zhang; Marco Galaverni; Jie Huang; Hong Liu; Pedro Silva; Peng Li; John P Pollinger; Lianming Du; XiuyYue Zhang; Bisong Yue; Robert K Wayne; Zhihe Zhang
Journal:  PLoS Genet       Date:  2014-07-31       Impact factor: 5.917

10.  Ancient Himalayan wolf (Canis lupus chanco) lineage in Upper Mustang of the Annapurna Conservation Area, Nepal.

Authors:  Madhu Chetri; Yadvendradev V Jhala; Shant R Jnawali; Naresh Subedi; Maheshwar Dhakal; Bibek Yumnam
Journal:  Zookeys       Date:  2016-04-21       Impact factor: 1.546

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