Research Article Volume 2 Issue 4
1Department of Ocean Studies and Marine Biology, Pondicherry University off Campus, India
1Department of Ocean Studies and Marine Biology, Pondicherry University off Campus, India
Correspondence: Mohan PM, Department of Ocean Studies and Marine Biology, Pondicherry University off Campus, India
Received: July 21, 2018 | Published: August 10, 2018
Citation: Mohan PM, Sojitra MU. Whales and dugong sighting in Andaman Sea, off Andaman and Nicobar islands. Open Access J Sci. 2018;2(4):274-280. DOI: 10.15406/oajs.2018.02.00086
The sighting of whales and the dugong was one of the important methods of the survey on its distribution. A study was initiated to understand this survey results in and around the Andman and Nicobar waters. The source for the study was considered from the existing database from the published literature, unpublished reports from the different Government Agencies related to this study and personal interview with the fisher folk. Based on this survey it was found that there were total eight species of whale and one species of dugong had been recorded from this survey in Andaman waters. Among the sighted species, the sperm whale is the most abundant species were observed. While there is only one species record, from Family Balaenopteridae of Bryde’s whale and from Family Ziphiidae of Blainville’s beaked whale. Killer whale has been the most frequently recorded species during this survey. There was only one mass stranding occurred in Andaman and Nicobar Islands of 40 individuals of Short-finned pilot whale. Based on this it is recommended that various stakeholders, both within and outside the academic and government research communities, engage in more active collaboration and information sharing to better synergize research, conservation, and management efforts throughout the Andaman and Nicobar Islands.
Keywords: fisher folk, synergize research, marginal sea, species record, fishermen, polar bears, pinnipeds, dolphins and porpoises, manatees and dugong, pilot whale
Andaman and Nicobar Islands are one of the biodiversity hotspots of the world, located between Lat. 06°45’ to 13°41’N and Long. 92°12’ to 93°57’E in Bay of Bengal. This archipelago comprised of 572 islands with a coastline of about 1,962km and total area of 8,249 km². The Andaman Sea is a marginal sea of the eastern Indian Ocean, separated from the Bay of Bengal (to its west) by the Andaman and Nicobar Islands and touching Myanmar, Thailand and the Malay Peninsula. Its southernmost end is defined by Breueh Island, an island just north of Sumatra. The maximum length of the Andaman Sea is 1,200 km and maximum width is 645 km. The surface area of the sea is 600,000 km². The average depth of the sea is 1,096 m while the maximum depth is 4,198 m. The Andaman Sea extends over 92⁰ E to 100⁰ E and 4⁰ N to 20⁰ N, Occupies a very significant position in the Indian Ocean, yet remained unexplored for a long period of time. Marine mammals are important components and occupy elevated trophic level in the oceanic environment. They are generally classified under three major Orders, namely Cetacea (whales, dolphins and porpoises), Sirenia (manatees and dugong), and Carnivora (sea otters, polar bears, and pinnipeds). Till date, there are 129 marine mammals Species of these three Groups and are known to occur in the world ocean.1 Many cetaceans have fully adapted to live in almost all marine ecosystems and have evolved to exploit a wide variety of prey species. Being apex predators, cetaceans have the potential to be important barometers of marine diversity and give them significant role as indicators of marine ecosystem conservation state. Cetaceans are thought to have a major influence on marine food webs as well as the structure and function of some aquatic communities because of their large body size, high metabolic rates, and large numbers.2,3 Therefore, an understanding the role of cetaceans in the marine ecosystem is imperative because it provides a context to evaluate the potential impact of their predation on prey population, prey community structure and variation in prey population.2
Cetaceans are highly mobile animals with complex habitat requirements and are distributed unevenly across oceans, ranging from temperate, tropical, subtropical, and polar water of the deep ocean. These apart, estuaries and the tributaries of some of the world’s largest rivers act potential habitat for few cetaceans (river dolphin) and sirenians group (dugong). Some habitats, such as tropical, subtropical and temperate, maintain extremely diverse cetacean species assemblages, whereas Polar Regions support a restricted range of species (Gaston, 2003). Among the different marine habitats, tropical water occupies vast part of the world ocean and covers nearly 50% of the world’s oceans, which supports a wide range of distribution of tropical cetacean species.4,5 Dugongs were common in the Andaman and Nicobar Islands until the 1950s, but currently there are only sporadic sightings.6 A first study on the distribution of seagrass meadows was carried out in 1995. This study estimated, the presence of 40 dugongs based on interviews with fishermen and regular divers6–8 sighted three dugongs in the wild at Neil, Havelock and Kodiaghat Islands in the southern Andaman Islands and three dugongs were sighted near Neil Island by.9 The year 2008, it was collated all available information on dugong occurrences from records available since 1956 and found that there were 58 records of mortality in the past 50 years and in the past 20 years there were 10 records of mortality indicating a possibility of a further decline in numbers since the 1999 report.
Based on the above review it was decided to bring out the status of sighting on whales and dugong in the Andaman Sea. This study was carried out in Andaman Sea extended from off Andaman and Nicobar Islands (Figure1). Whales and Dugong distribution status are important for the conservation and protection purposes. However, in general, this study was limited due to no catch of these species by the fisherfolk. So, their biodiversity may be understood only through the existing records as well as seafarer’s information. This aspect, the existing records and information was collected from different review of literature and agencies like, State Fishery Departments, Zoological Survey of India, Fishery Survey of India, NGO’s and Department of Environment and Forest. The cetaceans of the southern and northern parts of the Indian Ocean have also been well studied relative to those of the other cetaceans, resulting in a basic understanding of distribution and abundance.10–17 Contrast to these parts of the Indian Ocean, studies on cetacean in the northeastern part of the Indian Ocean, in particular, in the Indian peninsula is very little due to complete lack of systematic program in the last century. There is no uniformity among different authors as to the exact number of cetacean species occurrence in Indian water. Recent advancement in fishing has extended fishing activity to oceanic waters and thereby has added new species to cetacean community in the Indian Sea. Information from incidental catch (by-catch) in fisheries and sightings indicate that Indo-Pacific bottlenose (Tursiops aduncus), humpback (Sousa chinensis) and spinner dolphins (Stenella longirostris) are the most common species in India.18–20 A few species such as Cuvier beaked whale (Ziphius cavirostris), Melon headed whale and Killer whale (Orcinus orca) have been recorded very rarely in the last 200 years and raises uncertainty as to the distribution of these species in Indian waters.19
Cetacean entanglement in fishing gear represents one of the most immediate threats to their diversity in India.21 Bycatch of several species of marine mammals are reported regularly in the Indian fisheries during all the season. Cetaceans entanglement has been observed in a wide range of fishing gear including pelagic driftnets,22 bottom-set gillnets,23 trawl nets24 and purse seines.20 Such an entanglement causes physical damages to fishing gear and also causes injuries to cetaceans or death through drowning. Among many gears used in Indian fisheries, gillnet is the main cause for massive cetacean entanglement. The Indian gillnet fishery is one of the largest driftnet fisheries in the world with around 14,800 operational fleets across the Indian Seas. Sea cow (Dugong dugon) is the only extant species in the Family Dugongidae and true herbivorous marine mammal. Currently dugongs are classified as vulnerable to extinction under the 1996 World Conservation Union (IUCN) Red List of Threatened Species. This classification describes taxon that faces a high-risk of extinction in the wild in the medium-term future. In the case of the dugong, it is deemed population reduction in the form of the following: an observed, estimated, inferred or suspected reduction of at least 20% over the last 10 years or three generations, whichever is the longer.25
India, dugongs have been reported from the Gulf of Kutch in the north-west, Gulf of Mannar and Palk Bay in the southeast and the Andaman and Nicobar Islands.26–38 There are no records from further north along the east coast of India or from the Sunderbans,39 although there are records from the Chittagong coast of Bangladesh and Burmese waters.40 They were previously reported (as seals) along the west coast of India,29 from salt water inlets of the south Malabar and Konkan coasts as far north as Canara (which corresponds to southern Maharashtra, Goa, Karnataka and Kerala today). The occurrence of dugongs along the Malabar Coast was also mentioned in the Imperial Gazetteer.33 Dugongs have also been reported from the Maldives and Laccadive Islands41 but are now believed to be extinct.9 Indian seas, the main threats to dugong populations are habitat loss and degradation, fishing pressure, indigenous hunting and use and naturally occurring diseases. Global warming is an indirect threat to the dugong. The United Nation's Intergovernmental Panel on Climate Change (IPCC) has speculated that climate change due to increasing amounts of anthropogenic "greenhouse" gases may result in increased tropical sea surface temperatures (SSTs) and increased tropical rainfall associated with a slightly stronger inter-tropical convergence zone (ITCZ).42–44
The oral interaction surveys were carried out from December 2017 to March 2018 with fisher-folks of Port Blair and Campbell Bay of Andaman and Nicobar Islands. The data were collected from 1902 to 2018. Out of 13 sighting, five belongs to 1902 to 2002 and remaining 08 data from 2009 to 2018. The purpose of such interview was to create a database of the whales and to collect information on local cetacean species. Additionally, the behavioural remarks also were considered with fishermen while they are at the sea fishing in different areas. The data suggested that the Bryde’s Whale, Sperm Whale, Killer Whale, False Killer Whale, Short – Finned –Pilot whale and Dugong dugong were the most sighted along with stranded species. Apart from that, secondary data on the reports of whales and dugong in these islands were collected through published literature and unpublished reports from different scientific organizations. Consultations and interactions were made by scientific departments as well as fisher-folk communities and local inhabitants to confirm the collected literature information along with the information on sightings and the stranding of whales and dugong in the past. Additionally, there are some personal reports also have been included while sailing from Port Blair to Campbell Bay. Along with that, sailor of the passenger ships also have been interviewed for the sightings of whales along with sea route from Port Blair to other destinations such as Hut Bay, Car Nicobar, Kamorta and Campbell Bay.
These collected data were tabulated as well as visual graphic were made to understand the distribution as well as it distributional status. Based on these interpretations, the final report was developed.
The Andaman Sea, off Andaman and Nicobar Coasts, represented eight species of whales and one species of dugong as per the survey conducted during the period December 2017 to March 2018 among the fisher folk and sailors (Table 1). The secondary data on this aspect suggested that these records were meager and not up to the serious level to upkeep this record due to lack of interest or knowledge (Table 2) and (Figure 2) & (Figure 3). The fisher folk data was suggested that the sighting was a regular phenomenon in the coastal waters as well as in the insular shelf regions (Figure 4) & (Table 3). Further, it was also observed that the whales were swimming away from the boat generated noise. The whale stranding was another major observation was identified in this sector during this study. Till date, the stranding incidence of five species of whale and one species of dugon were recorded (Table 2). Out of these six incidences, only one major stranding was occurred of Short Finned Pilot Whales. The causes for this stranding incidence may be due to the undersea earthquake, geomagnetic error, strong tidal currents, sonic waves, following the fast moving prey such as dolphin, school of fishes, etc., rough weather, weakness of whale due to ageing or infection, etc.,. There were some observations also suggested that entanglement in a ghost net for this creature, which leads to death or injured (Figure 5). The dugong was also observed in almost all over the length and breadth of the Andaman and Nicobar coastal regions. The report suggested that its observation was from North Landfall islands to South Indira Point Figure 6 & Figure 7. This distribution suggested that the Ritchie’s Archipelago and Great Nicobar regions may be the most probable sighting were done (Table 4) & (Figure 8).45–48
Sr.No. |
Species |
Number |
Date |
Location |
1 |
Bryde’s Whale |
1 |
15 May 1988 |
Sighted in Andaman sea |
2 |
Sperm Whale |
1 |
March & April 1920 |
Sightings off the Andaman and Nicobar Islands |
3 |
Sperm Whale |
2 |
30 November 2012 |
Ten degree Channel |
4 |
Killer Whale |
1 |
12 April, 1983 |
One sighted north of Andamans |
5 |
Killer Whale |
1 |
February 1902 |
Sighted Pulomilo Island near Little Nicobar |
6 |
Killer Whale |
1 |
April 2009 |
Little Andaman |
7 |
Killer Whale |
4 |
23 September 2010 |
Great Nicobar |
8 |
False Killer Whale |
4 |
June 2010 |
Andaman Sea |
9 |
Short-finned Pilot Whale |
30 |
May 2010 |
Andaman sea |
10 |
Blainville's Beaked Whale |
1 |
? |
Recorded from the Nicobar |
11 |
Unidentified Whale |
1 |
27 December 2017 |
Ross Island |
12 |
Unidentified Whale |
1 |
28 December 2017 |
Car Nicobar |
13 |
Unidentified Whale |
10 |
28 December 2017 |
Great Nicobar Island |
14 |
Dugong dugon |
40 |
1990 - 1995 |
Sightings in the Andaman islands: 6 Dugongs near Landfall Island, 6 near Ritchie’s Archipelago and 5 near Little Andaman and Dugong Creek; in the Nicobars, 5 Dugongs near Katchall, 10 near Camorta Island, 4 specimens around Little Nicobar and 4 around Great Nicobar Island |
15 |
Dugong dugon |
1 |
Feb 2007 – Mar 2008 |
2 m, Havlock Island, Andaman |
16 |
Dugong dugon |
1 |
Feb 2007 – Mar 2008 |
2.5 m, Neil Island, Andaman |
17 |
Dugong dugon |
1 |
Feb 2007 – Mar 2008 |
3 m, Kodiaghat, Andaman |
|
Total |
101 |
|
|
Table 1 Sighting of Whales and Dugongs
Sr. No. |
Species |
Number |
Date |
Location |
1 |
Pygmy Sperm Whale |
1 |
8 July 1988 |
A 1.95 m long specimen from |
2 |
Killer Whale |
1 |
? |
Skull from the Nicobar Islands in the Bombay Natural History |
3 |
False Killer Whale |
2 |
27 July 1976 |
Entangled in gillnets off Madhuban, Port Blair; one escaped |
4 |
False Killer Whale |
1 |
9 June 1977 |
Caught in gillnet off |
5 |
False Killer Whale |
1 |
7 March 1983 |
Shastri Nagar, Great Nicobar |
6 |
Melon-headed Whale |
1 |
Before 1971 |
Car Nicobar |
7 |
Short-finned Pilot Whale |
40 |
21 October 2012 |
Elizabeth Bay, North Andaman |
8 |
Dugong dugon |
1 |
8 March 1929 |
Female carrying a young, |
9 |
Dugong dugon |
1 |
8 July 1977 |
One caught in gillnets off Port Blair |
10 |
Dugong dugon |
1 |
March 1989 |
Hut Bay, Little Andaman |
11 |
Dugong dugon |
1 |
July 1989 |
One dead Dugong found near Pilo Kunji of the Great Nicobars |
12 |
Dugong dugon |
1 |
19 February 1997 |
2.63 m long female Dugong caught and brought dead to shore at Hut Bay, Little Andamans |
13 |
Dugong dugon |
1 |
25 December 2008 |
Stranded, Neil Island, Andaman |
|
Total |
53 |
|
|
Table 2 Stranding and Ghost Net Entanglement of Whales and Dugongs
Sr. No. |
Whale |
Numbers |
Date |
Location |
Behavioural notes |
1 |
Sperm Whale |
1 |
2016 |
Inglish Island |
Lob-tailing, Diving |
2 |
Big Whale |
1 |
2002 |
Chowra |
|
3 |
Big Whale |
1 |
2010 |
Mayabandar |
Specimen approached the boat, Feeding |
4 |
Big Whale |
2 |
1998 |
Mayabandar |
Feeding |
5 |
Big Whale |
3 |
2017 |
South Sentinal Island |
Specimens approached the boat |
6 |
Big Whale |
1 |
2016 |
Interview Island |
|
7 |
Big Whale |
1 |
? |
Hut Bay |
Disturbed by the approaching boat |
8 |
Big Whale |
1 |
2001 |
North Sentinal Island |
Breaching, Disturbed by the approaching boat |
9 |
Big Whale |
1 |
2017 |
Mayabandar |
|
10 |
Big Whale |
1 |
2015 |
Ross Island |
|
11 |
Big Whale |
1 |
2003 |
Interview Island |
Entangled in fishing net |
12 |
Big Whale |
1 |
2015 |
North Sentinal Island |
Specimen approached the boat |
13 |
Big Whale |
1 |
2014 |
South Sentinal Island |
|
14 |
Black Fish |
20 |
2013 |
Indira Point |
Feeding |
15 |
Balck Fish |
1 |
2000 |
Mayabandar |
Feeding |
16 |
Black Fish |
4 |
2014 |
Hut Bay |
|
|
Total |
41 |
|
|
|
Table 3 Sightings of Whales – Fisherfolk Survey
Sr. No. |
Species |
Numbers |
Date |
Location |
1 |
Black Fish |
1 |
2013 |
Panchvati beach, Rangat |
2 |
Big whale |
1 |
Approx. 2003 |
Havelock |
3 |
Big whale |
1 |
2004 |
27 Km beach, Great Nicobar |
Total |
|
3 |
|
|
Table 4 Stranding of Whales – Fisherfolk Survey
There are total eight species of whale and one species of dugong had been recorded from this survey in Andaman waters. The distribution of these species lies all over EEZ and coastal waters of Andaman and Nicobar Islands. Among the large whales, the sperm whale is the most abundant species. While there is only one species record, from Family Balaenopteridae of Bryde’s whale and from Family Ziphiidae of Blainville’s beaked whale, which suggests the low abundance of these to Families. Among the toothed whales Family Delphinidae is most diverse one with four species have been reported from the study area. Killer whale has been the most frequently recorded species during this survey, while the number of individuals was recorded of short-finned pilot whale. The stranding data show that the false killer whale was most frequently getting caught in ghost nets. There was only one mass stranding occurred in Andaman and Nicobar Islands of 40 individuals of Short-finned pilot whale. The death of whale and dugong are less by stranding compare to the ghost net entanglement. There have been also reports of stranding which do not have any authentic handling and supervision of carcasses, which could be a great opportunity to collect the morphological and anatomical data and distribution data. This Survey had provided a useful means for collection of whales sighting and stranding data as secondary data and most importantly fisher-folks interview survey data. The data generated on species occurrence and distribution will be useful for assisting with the estimation of the abundance of whale in the Andaman waters in the future. For this, the oceanic survey research needs to be supplemented with coastal surveys with smaller boats and most frequent survey. It is recommended that various stakeholders, both within and outside the academic and government research communities, engage in more active collaboration and information sharing to better synergize research, conservation, and management efforts throughout the Andaman and Nicobar Islands. There should have better coordinate the handling of stranding events and facilitate valuable data collection through examination and sampling of stranded carcasses. Only through such collaboration can adequate research, conservation, and management take place.
The authors gratefully thank the local fisher-folk of South Andaman and Campbell Bay for their valuable time and information they had provided for the survey. Further, they also like to express thanks to Governmental Organizations, such as Fishery Survey of India, Zoological Survey of India and Forest Department located at Andaman and Nicobar Islands, for their information extended to this study. Over and above, the authors extend their grateful acknowledgement for the authorities of Pondicherry University, Pudcherry, India for their constant support to this work.
The author declares there is no conflict of interest.
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