Fisheries and Aquatic Sciences
The Korean Society of Fisheries and Aquatic Science

Mitochondrial DNA-based investigation of dead rorqual (Cetacea: Balaenopteridae) from the west coast of India

Shantanu Kundu1, Manokaran Kamalakannan2, Dhriti Banerjee2,3, Flandrianto Sih Palimirmo4, Arif Wibowo4, Hyun-Woo Kim1,5,6,*
1Department of Marine Biology, Pukyong National University, Busan 48513, Korea
2Mammal & Osteology Section, Zoological Survey of India, Kolkata 700053, India
3Zoological Survey of India, Kolkata 700053, India
4Research Center for Conservation of Marine and Inland Water Resources, National Research and Innovation Agency, Cibinong 16911, Indonesia
5Research Center for Marine Integrated Bionics Technology, Pukyong National University, Busan 48513, Korea
6Marine Integrated Biomedical Technology Center, National Key Research Institutes in Universities, Pukyong National University, Busan 48513, Korea
*Corresponding author: Hyun-Woo Kim, Department of Marine Biology, Pukyong National University, Busan 48513, Korea, Tel: +82-51-629-5926, Fax: +82-51-629-5931,

Copyright © 2024 The Korean Society of Fisheries and Aquatic Science. This is an Open Access article distributed under the terms of the Creative Commons Attribution Non-Commercial License ( which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited.

Received: Aug 03, 2023; Revised: Sep 12, 2023; Accepted: Nov 06, 2023

Published Online: Jan 31, 2024


The study assessed the utility of mitochondrial DNA for identifying a deceased rorqual discovered off the western coast of India. Both the COI and Cytb genes exhibited remarkable 99-100% similarity with the GenBank sequence of Balaenoptera musculus through a global BLAST search, confirming their affiliation with this species. Inter-species genetic distances for COI and Cytb genes ranged from 6.75% to 9.80% and 7.37% to 10.96% respectively, compared with other Balaenopteridae species. The Bayesian phylogenies constructed based on both COI and Cytb genes demonstrated clear and separate clustering for all Balaenopteridae species, further reaffirming their distinctiveness, while concurrently revealing a cohesive clustering pattern of the generated sequences within the B. musculus clade. Beyond species confirmation, this study provides valuable insights into the presence of live and deceased B. musculus individuals within Indian marine ecosystems. This information holds significant potential for guiding conservation efforts aimed at safeguarding Important Marine Mammal Areas (IMMAs) in India over the long term.

Keywords: Indian Ocean; Cetaceans; Matrilineal phylogeny; Important Marine Mammal Areas (IMMAs); Conservation


The order Cetartiodatyla, specifically the Infraorder Cetacea, encompasses a diverse group of marine mammals, includes whales, dolphins and porpoises. Among them, rorquals, classified under the family Balaenopteridae, are generally the largest, while dolphins are smaller and porpoises are the smallest in size (Wilson & Mittermeier, 2014). In addition to external morphological characteristics, one key distinguishing feature of whales is the presence of keratinaceous baleen plates, used for filter feeding, in contrast to the conical-shaped teeth of dolphins and spade-shaped teeth of porpoises (Jefferson et al., 1993). The family Balaenopteridae comprises nine species under the genus Balaenoptera and a single species under the genus Megaptera. These enigmatic marine mammals face several anthropogenic threats including direct exploitation through deck-mounted harpoon cannons, exposure to pollutants, and vessel strikes (Kemper et al., 2005). Consequently, live sightings of these animals are becoming increasingly rare (Sutaria et al., 2016). Nevertheless, occasionally, deceased cetaceans wash up on the Indian coastline, which extends for 7,516 km, encompassing nine coastal states, two union territories, and two island territories in India.

These stranded animal carcasses often provide invaluable insights into the natural history, ecology, and population genetics of these species (Bilgmann et al., 2011; Tucker et al., 2019). Moreover, records of marine mammal strandings along coastlines contribute relevant information for conservation efforts and offer insights into the status of marine ecosystems (Coombs et al., 2019). Furthermore, the long-term monitoring and detailed autopsy examinations of these stranded animals are crucial for determining the cause of death and guiding future conservation measures (Arbelo et al., 2013). However, identifying species from deteriorated biological samples in the maritime environment can be a challenging process.

To overcome the taxonomic challenges associated with species identification, molecular approaches have proven effective in whale species recognition and systematics research (Ross et al., 2003). The DNA sequences of the mitochondrial genome have provided new insights into cetacean origin and evolution (Arnason et al., 2004). Notably, two mitochondrial ribosomal RNA genes, as well as the protein-coding genes COI and Cytb, have been demonstrated to effectively discriminate major cetacean groups (Milinkovitch et al., 1994; Sholl et al., 2008; Viricel & Rosel, 2012). Additionally, the mitochondrial control region has been evaluated for estimating the population genetics of whales (Arnason et al., 1993; LeDuc et al., 2017). Combining various nuclear and mitochondrial loci has proved useful in identifying whale phylogeny and divergence periods (Jackson et al., 2009; McGowen et al., 2009; Sasaki et al., 2005). Whole-genome sequencing of blue whales and other rorquals has revealed evidence of introgressive gene flow in the marine environment, as well as insights on their lifespan and adaptability (Árnason et al., 2018; Yim et al., 2014). Therefore, this study aims to identify a morphologically unknown rorqual by analyzing mitochondrial DNA. To confirm the species’ identity, we calculate genetic distances and look at the phylogenetic relationship. Our generated data may serve as a reference sequence for population genetic analyses of rorquals in Indian marine waters. Additionally, historical records of blue whales spanning ~90 years will enhance our understanding and contribute to long-term conservation action plans for cetaceans in the Indian marine ecosystem.

Materials and Methods

Survey and sampling

A single deceased individual of rorquals was detected along the western coast of India, near Kozhikode, Kerala, at coordinates 10.949N 75.875E (Fig. 1). The external morphological features of the specimen were extensively degraded, rendering taxonomic-based species identification unfeasible. To mitigate potential surface contamination, an aseptic tissue sample was carefully extracted and thoroughly rinsed with 70% ethanol before preservation. The tissue sample was vouchered and cataloged in the National Zoological Collections of the Western Ghat Regional Centre (WGRC), Zoological Survey of India (ZSI), Kozhikode, India, under registration number ZSI/WGRC/V.3628. In an effort to gain insights into the conservation priorities for rorquals in Indian marine waters, Important Marine Mammal Area (IMMA) shapefiles and associated metadata were acquired from the IUCN Joint SSC/WCPA Marine Mammal Protected Areas Task Force (IUCN MMPATF, 2018).

Fig. 1. Map showing the live and dead records of blue whales in Indian Marine waters. The bar diagram shows the frequency of Balaenoptera musculus sighting (dead or alive) from 1931–2023. Red pin showing the collection locality of biological samples of the rorqual carcass washes up on the west coast of India. IUCN SSC-designated Important Marine Mammal Areas (IMMAs) have been identified to understand the areas where cetacean conservation is prioritized by the Indian conservation agencies.
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Molecular screening

Total genomic DNA was extracted using the standard phenol–chloroform isoamyl alcohol method (Sambrook & Russell, 2001). Two primer pairs, LCO-HCO and mcb398-mcb869, were employed to amplify the partial segments of COI and Cytb genes, respectively (Folmer et al., 1994; Verma & Singh, 2002). Each 25 mL PCR reaction mixture contained 10 pmol of each primer, 20 ng of template DNA, 1X PCR buffer, 1.0–1.5 mM of MgCl2, 0.25 mM of each dNTPs, and 1 U of High-fidelity Platinum Taq DNA Polymerase (Invitrogen, Carlsbad, CA, USA). PCR reactions were carried out in a Veriti Thermal Cycler (Applied Bio Systems, Foster City, CA, USA) following standard thermal profiles. PCR products were purified using the QIAquick Gel Extraction Kit (QIAGEN, Germantown, MD, USA) according to the provided protocol. Cycle sequencing was performed with the BigDye Terminator ver. 3.1 Cycle Sequencing Kit (Applied Biosystems, Foster City, CA, USA), and bi-directional Sanger sequencing was conducted using the Genetic Analyzer (Applied Biosystems) located at Rajiv Gandhi Centre for Biotechnology, Thiruvananthapuram, Kerala, India.

Dataset construction

Forward and reverse chromatograms were carefully screened using the SeqScanner Version 1.0 (Applied Biosystems) to eliminate noisy segment from each sequence. Consensus sequences were subsequently subjected to nucleotide BLAST searches (, accessed on 21 July 2023) and ORF finder screening (, accessed on 21 July 2023) for validation. Finally, the generated sequences were deposited in the GenBank database to obtain unique accession numbers. Additionally, a total of 43 COI sequences and 35 Cytb sequences from various Balaenopteridae species were retrieved from GenBank to facilitate confirmatory analyses. The DNA sequence (NC_000889) of Hippopotamus amphibius (Artiodactyla: Hippopotamidae) was used as an outgroup taxon in the ensuing analyses. Generated and database sequences were aligned using ClustalX software to create two distinct datasets (Thompson et al., 1997).

Genetic distance and phylogenetic analyses

Kimura-2-parameter (K2P) genetic distances were computed for both COI and Cytb datasets using MEGAX (Kumar et al., 2018). To conduct phylogenetic analyses, the best fit models were determined using JModelTest v2 based on the lowest Bayesian Information Criterion scores (Darriba et al., 2012). Bayesian inference topologies were constructed using Mr. Bayes 3.1.2, employing nst = 6 with one cold and three hot chains (Metropolis-coupled Markov chain Monte Carlos). The program was executed for 100,000 generations, with tree sampling performed at every 100 generations and 25% of samples discarded as burn-in (Ronquist & Huelsenbeck, 2003). The resulting topologies were edited using the iTOL v6.8 webserver (, accessed on 21 July 2023) (Letunic & Bork, 2021).

Results and Discussion

The four nucleotides (A, T, G, and C) wield significant power in identifying organisms across various life forms and stages, particularly when morphology alone proves inadequate for the task (Hebert et al., 2003). This innovative approach, seamlessly integrated with traditional morphology-based species identification, has demonstrated its effectiveness, particularly in the context of Marine Metazoans (Steinke et al., 2016). In the present study, molecular techniques were employed to examine a deceased rorqual specimen. The generated sequences of two mitochondrial genes, COI (OQ704238) and Cytb (OQ718808), exhibited striking similarities of 100% and 99.56%, respectively, with the references mitochondrial genome sequence (MF409242) of B. musculus (Árnason et al., 2018). Among the nine studied Balaenopteridae species, the partial COI gene (612 bp) displayed 20.75% variable nucleotides, with a mere 0.33% variability observed in B. musculus. Similarly, the partial Cytb gene (450 bp) exhibited 24.22% variable nucleotides, with 0.44% variation in B. musculus. Both COI and Cytb genes depicted mean genetic distances of 7% and 8%, respectively, within the present datasets. Specifically, in the COI gene, inter-species genetic distances ranged from 3.83% (between B. bonaerensis and B. acutorostrata) to 10.42% (between B. borealis and B. acutorostrata) (Table 1). Notably, the targeted species, B. musculus, including the generated sequence, maintained inter-species genetic distances of 6.75% (with B. borealis) to 9.80% (with B. acutorostrata) when compared to other Balaenopteridae species. Intra-species genetic distances among the Balaenopteridae species ranged from 0% (between B. edeni and B. omurai) to 1.2% (for B. physalus). In the Cytb gene, inter-species genetic distances spanned from 2.66% (between B. borealis and B. edeni) to 12.78% (between Megaptera novaeangliae and B. bonaerensis) (Table 1). The blue whale, B. musculus exhibited inter-species genetic distances ranging from 7.37% to 10.96% when compared to other Balaenopteridae species. In contrast to COI, the Cytb gene displayed negligible intra-species genetic distances, ranging from 0% to 1.1%, as observed in COI. Both COI- and Cytb-based Bayesian phylogenies exhibited distinct segregation and monophyletic clustering for all Balaenopteridae species. The generated sequences from the unidentified deceased rorqual formed cohesive clusters within the B. musculus clade in both COI- and Cytb-based species trees, with robust posterior probability support (Fig. 2). Based on this molecular investigation, the present study confirms the identity of the deceased rorquals as blue whales, B. musculus.

Table 1. Mitochondrial COI and Cytb genes based genetic distances of Balaenopteridae species
Species Inter-species genetic distances (COI/Cytb) Intra-species
Balaenoptera musculus 0.10/0
Balaenoptera borealis 6.75/7.37 0.70/0
Balaenoptera edeni 7.39/8.77 4.32/2.66 0/0.20
Balaenoptera brydei 7.51/8.98 4.97/4.31 4.36/4.73 0.20/0
Balaenoptera omurai 7.52/9.74 7.58/11.14 7.10/11.60 8.93/12.09 0/0.70
Megaptera novaeangliae 7.59/7.84 7.95/8.12 7.33/10.20 8.04/8.44 8.44/12.57 0.30/0.20
Balaenoptera bonaerensis 7.95/11.50 8.71/8.82 7.89/8.93 8.31/9.15 8.80/11.93 7.13/12.78 0.20/0.80
Balaenoptera physalus 8.05/8.79 7.76/8.14 7.60/8.90 9.25/8.46 7.74/12.02 6.28/10.23 7.78/10.51 1.20/1.10
Balaenoptera acutorostrata 9.80/10.96 10.42/8.31 9.26/8.56 9.19/8.63 10.22/12.67 8.66/11.19 3.83/4.27 9.86/9.91 0.70/0.40
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Fig. 2. Mitochondrial COI- and Cytb-based Bayesian phylogenies clearly discriminated all the Balaenopteridae species and clustered the generated sequences (marked by red stars) into the B. musculus clades. The posterior probability supports of each node are overlaid with the topologies.
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Despite their crucial role in marine ecosystems, whales, and especially in India, have received scant attention from conservation biologists and taxonomists (Bijukumar et al., 2012). Marine mammals frequently strand along the Indian coast, yet due to a dearth of local taxonomic expertise and the often-compromised condition of specimens, accurate species identification is not consistently achieved (George et al., 2011). Given the pivotal role of all cetaceans in conservation endeavors, precise documentation of their presence can yield vital insights into the distribution and migratory patterns of numerous species in the oceans surrounding India. The blue whale, B. musculus (cf. Linnaeus 1758), stands as the largest baleen whale and indeed, the largest known animal on Earth. This colossal mammal boasts a cosmopolitan distribution across major oceans worldwide, with the exception of the Arctic, Mediterranean, Okhotsk, and Bering Seas. It encompasses four recognized subspecies, namely B. m. musculus, B. m. indica, B. m. intermedia, and B. m. brevicauda (Reeves et al., 1998). In the Indian Ocean, blue whales (B. m. indica) have been recorded on numerous occasions along both the east and west coasts, from Okhamandal in Gujarat to Andhra Pradesh and West Bengal states in India. These records are based on strandings, acoustic detections, and live sightings (Chandrasekar et al., 2021; Marine Mammal Research & Conservation, 2023; Sutaria et al., 2016). It is worth noting that the blue whale (B. musculus) is currently categorized as ‘Endangered’ by the IUCN Red List of Threatened Species (IUCN, 2023).

Blue whales face a myriad of anthropogenic threats that hinder their population recovery, including historical whaling, climate-induced pollution, noise pollution, and vessel collisions. The causes of marine mammal strandings can be attributed to both natural and human-induced factors, and the information gleaned from strandings can be instrumental in understanding the geographical distribution of marine mammal populations, their seasonal migrations, and the factors contributing to mortality. While the effects of noise pollution on blue whales are not yet fully understood, it has the potential to disrupt mating activities, leading to population-level consequences and harm or mortality (Croll et al., 2001). Although a recent study has focused on a significant mass mortality event among large baleen whales, linked to harmful toxic algal blooms (Häussermann et al., 2017), the natural causes of mortality among blue whales are well-documented. However, the specific reasons for mortality in stranded marine animals are often inadequately studied, and extensive necropsy research and postmortem examinations would greatly contribute to understanding the impact of anthropogenic interactions. Blue whales, like other baleen whales, undertake extensive migrations between breeding areas in low-latitude regions where they mate and give birth during the winter, and feeding grounds in high-latitude areas during the summer (Corkeron & Connor, 1999). The energy expended during these activities, including fasting, migration, calving, and raising young, increases the risk of mortality during these voyages. The southern range of the Indian Ocean boasts the largest acoustic diversity of blue whales (Torterotot et al., 2020). Given the recent establishment of IMMAs in Indian marine waters, both the east and west coasts feature high-priority zones, representing critical habitat portions for marine mammal species that have the potential to be delineated and managed for conservation purposes. Beyond the realm of DNA data, blue whale sightings in Indian seas are on the rise, underscoring India’s ongoing conservation efforts. Furthermore, the Marine Mammal Research and Conservation Network of India ( has compiled the most comprehensive information on Indian cetaceans, undoubtedly facilitating conservation management planning.

Competing interests

No potential conflict of interest relevant to this article was reported.

Funding sources

This work was supported by a Research Grant from Pukyong National University (2023).


The first author (S.K.) thanks the Pukyong National University’s Global Postdoc Program in South Korea. The authors are thankful to Dr. Arun Sathyam, Veterinary Officer, Forest Department, Kozhikode, Kerala for sampling the carcass. M.K. is grateful to Dr. V.D. Hegde, Scientist-E & Officer-in-Charge, Western Ghat Regional Centre, Zoological Survey of India, Kozhikode, Kerala for the encouragement and facilities.

Availability of data and materials

The mitochondrial gene sequence data that support the findings of this study are freely accessible in NCBI GenBank at, under the accession no. OQ704238 and OQ718808.

Ethics approval and consent to participate

Not applicable.



Arbelo M, de Los Monteros AE, Herráez P, Andrada M, Sierra E, Rodríguez F, et al. Pathology and causes of death of stranded cetaceans in the Canary Islands (1999−2005). Dis Aquat Organ. 2013; 103:87-99


Arnason U, Gullberg A, Janke A. Mitogenomic analyses provide new insights into cetacean origin and evolution. Gene. 2004; 333:27-34


Arnason U, Gullberg A, Widegren B. Cetacean mitochondrial DNA control region: sequences of all extant baleen whales and two sperm whale species. Mol Biol Evol. 1993; 10:960-70.


Árnason Ú, Lammers F, Kumar V, Nilsson MA, Janke A. Whole-genome sequencing of the blue whale and other rorquals finds signatures for introgressive gene flow. Sci Adv. 2018; 4:eaap9873


Bijukumar A, Jijith SS, Suresh Kumar U, George S. DNA barcoding of the Bryde’s whale Balaenopteraedeni Anderson (Cetacea: Balaenopteridae) washed ashore along Kerala coast, India. J Threat Taxa. 2012; 4:2436-43


Bilgmann K, Möller LM, Harcourt RG, Kemper CM, Beheregaray LB. The use of carcasses for the analysis of cetacean population genetic structure: a comparative study in two dolphin species. PLOS ONE. 2011; 6e20103


Chandrasekar K, Saravanane N, Cubelio SS, Sudhakar M. Live observation of great blue whale (Balaenopteramusculus) from northern Arabian Sea, off Gujarat, India. Curr Sci. 2021; 120:470-1.


Coombs EJ, Deaville R, Sabin RC, Allan L, O’Connell M, Berrow S, et al. What can cetacean stranding records tell us? A study of UK and Irish cetacean diversity over the past 100 years. Mar Mamm Sci. 2019; 35:1527-55


Corkeron PJ, Connor RC. Why do baleen whales migrate?. Mar Mamm Sci. 1999; 15:1228-45


Croll DA, Clark CW, Calambokidis J, Ellison WT, Tershy BR. Effect of anthropogenic low-frequency noise on the foraging ecology of Balaenoptera whales. Anim Conserv. 2001; 4:13-27


Darriba D, Taboada GL, Doallo R, Posada D. jModelTest 2: more models, new heuristics and parallel computing. Nat Methods. 2012; 9:772


Folmer O, Black M, Hoeh W, Lutz R, Vrijenhoek R. DNA primers for amplification of mitochondrial cytochrome c oxidase subunit I from diverse metazoan invertebrates. Mol Mar Biol Biotechnol. 1994; 3:294-9.


George S, Meenakshi K, Bijukumar A. Molecular taxonomy of marine mammals stranded along Kerala coast, India. Curr Sci. 2011; 100:117-20.


Häussermann V, Gutstein CS, Bedington M, Cassis D, Olavarria C, Dale AC, et al. Largest baleen whale mass mortality during strong El Niño event is likely related to harmful toxic algal bloom. PeerJ. 2017; 5e3123


Hebert PDN, Cywinska A, Ball SL, deWaard JR. Biological identifications through DNA barcodes. Proc R Soc B Biol Sci. 2003; 270:313-21


International Union for Conservation of Nature [IUCN]. The IUCN red list of threatened species. Version 2022-2IUCN 2023.[cited 2023 Jul 21]


International Union for Conservation of Nature Marine Mammal Protected Areas Task Force [IUCN MMPATF]. Global dataset of important marine mammal areas (IUCN-IMMA) [Internet]. Made available under agreement on terms of use by the IUCN Joint SSC/WCPA IUCN MMPATF 2018.[cited 2023 Mar 20]


Jackson JA, Baker CS, Vant M, Steel DJ, Medrano-González L, Palumbi SR. Big and slow: phylogenetic estimates of molecular evolution in baleen whales (suborder Mysticeti). Mol Biol Evol. 2009; 26:2427-40


Jefferson TA, Leatherwood S, Webber MA. FAO species identification guide. Marine mammals of the world. Rome: FAO. 1993.


Kemper CM, Flaherty A, Gibbs SE, Hill M, Long M, Byard RW. Cetacean captures, strandings and mortalities in South Australia 1881-2000, with special reference to human interactions. Aust Mammal. 2005; 27:37-47


Kumar S, Stecher G, Li M, Knyaz C, Tamura K. MEGA X: molecular evolutionary genetics analysis across computing platforms. Mol Biol Evol. 2018; 35:1547-9


Leduc RG, Archer FI, Lang AR, Martien KK, Hancock-Hanser B, Torres-Florez JP, et al. Genetic variation in blue whales in the eastern pacific: implication for taxonomy and use of common wintering grounds. Mol Ecol. 2017; 26:740-51


Letunic I, Bork P. Interactive tree of life (iTOL) v5: an online tool for phylogenetic tree display and annotation. Nucleic Acids Res. 2021; 49:W293-6


Marine Mammal Research & Conservation. Marine Mammals of India database [Internet]. 2023.[cited 2023 Mar 20]


McGowen MR, Spaulding M, Gatesy J. Divergence date estimation and a comprehensive molecular tree of extant cetaceans. Mol Phylogenet Evol. 2009; 53:891-906


Milinkovitch MC, Meyer A, Powell JR. Phylogeny of all major groups of cetaceans based on DNA sequences from three mitochondrial genes. Mol Biol Evol. 1994; 11:939-48.


Reeves RR, Clapham PJ, Brownell RL, Silber GK. Recovery plan for the blue whale (Balaenoptera musculus). Silver Spring, MD: National Marine Fisheries Service. 1998.


Ronquist F, Huelsenbeck JP. MrBayes 3: Bayesian phylogenetic inference under mixed models. Bioinformatics. 2003; 19:1572-4


Ross HA, Lento GM, Dalebout ML, Goode M, Ewing G, McLaren P, et al. DNA surveillance: web-based molecular identification of whales, dolphins, and porpoises. J Hered. 2003; 94:111-4


Sambrook J, Russell DW. Molecular cloning: a laboratory manual. 3rd ed New York, NY: Cold Spring Harbor Laboratory Press. 2001.


Sasaki T, Nikaido M, Hamilton H, Goto M, Kato H, Kanda N, et al. Mitochondrial phylogenetics and evolution of mysticete whales. Syst Biol. 2005; 54:77-90


Sholl TGC, Nascimento FF, Leoncini O, Bonvicino CR, Siciliano S. Taxonomic identification of dolphin love charms commercialized in the Amazonian region through the analysis of cytochrome b DNA. J Mar Biol Assoc UK. 2008; 88:1207-10


Steinke D, Prosser SWJ, Hebert PDN. DNA barcoding of marine metazoans. Methods Mol Biol. 2016; 1452:155-68


Sutaria D, Sule M, Jog K, Bopardikar I, Jamalabad A, Panicker D. Baleen whale records from the Arabian Sea, India from June 2015 to May 2016. Bled: International Whaling Commission. 2016Report No.: SC/66b/34/SH.


Thompson JD, Gibson TJ, Plewniak F, Jeanmougin F, Higgins DG. The CLUSTAL_X windows interface: flexible strategies for multiple sequence alignment aided by quality analysis tools. Nucleic Acids Res. 1997; 25:4876-82


Torterotot M, Samaran F, Stafford KM, Royer JY. Distribution of blue whale populations in the Southern Indian Ocean based on a decade of acoustic monitoring. Deep Sea Res II Top Stud Oceanogr. 2020; 179:104874


Tucker JP, Vercoe B, Santos IR, Dujmovic M, Butcher PA. Whale carcass scavenging by sharks. Glob Ecol Conserv. 2019; 19e00655


Verma SK, Singh L. Novel universal primers establish identity of an enormous number of animal species for forensic application. Mol Ecol Notes. 2002; 3:28-31


Viricel A, Rosel PE. Evaluating the utility of cox1 for cetacean species identification. Mar Mamm Sci. 2012; 28:37-62


Wilson DE, Mittermeier RA. Handbook of the mammals of the world. Barcelona: Sea mammals Lynx Edicions. 2014.


Yim HS, Cho YS, Guang X, Kang SG, Jeong JY, Cha SS, et al. Minke whale genome and aquatic adaptation in cetaceans. Nat Genet. 2014; 46:88-92