MARINE MAMMAL SCIENCE, 23(3): 688–693 (July 2007) C 2007 by the Society for Marine Mammalogy DOI: 10.1111/j.1748-7692.2007.02373.x SPITSBERGEN BOWHEAD WHALES REVISITED ØYSTEIN WIIG LUTZ BACHMANN Natural History Museum, University of Oslo, POB 1172 Blindern, N-0318 Oslo, Norway E-mail: oystein.wiig@nhm.uio.no VINCENT M. JANIK Sea Mammal Research Unit, Gatty Marine Lab, School of Biology, University of St Andrews, Fife KY16 8LB, United Kingdom KIT M. KOVACS CHRISTIAN LYDERSEN Norwegian Polar Institute, N-9226 Tromsø, Norway Bowhead whales (Balaena mysticetus) are endemic to arctic and subarctic regions of the Atlantic Ocean, and the Bering, Beaufort, Chukchi, and Okhotsk seas (Moore and Reeves 1993) and often live in close association with the sea-ice edge. Five geographically separated stocks are currently recognized: (1) the Bering/Chukchi/Beaufort Seas stock, (2) the Okhotsk Sea stock, (3) the Davis Strait stock, (4) the Hudson Bay stock, and (5) the Spitsbergen stock distributed in the Greenland, Barents, and Kara seas. Exploitation over several centuries dramatically reduced the population size of this once abundant species (Woodby and Botkin 1993). Commercial hunting of bowhead whales commenced in the early 1600s in the North Atlantic region around Svalbard and spread out into other regions when this stock became depleted. The pre-exploitation population size of the Spitsbergen stock has been estimated to be between 25,000 and more than 100,000 individuals (Allen and Keay 2006). After cessation of the hunt, bowhead whales around Svalbard were considered to be extinct a (JonsgArd 1981). Today, the Spitsbergen stock of bowhead whales is believed to 688 NOTES 689 Figure 1. Survey track line and sightings of bowhead whales in the Fram Strait between Svalbard and Greenland. All tracks except the one going from Svalbard to the west at 80◦ N are along the ice edge. The ice was distributed west and north of the track line and changed during the survey. Sightings of whales: (1) 17 April, 1 whale; (2) 18 April, 7+ whales; (3) 25 April, 1 whale; (4) 26 April, 1 whale; (5) 26 April, 1 whale; (6) 26 April, 3 whales; (7) 28 April, 1 whale; (8) 28 April, 3 whales. number in the tens (Christensen et al. 1992) and is considered critically endangered by the IUCN (Cetacean Specialist Group 2006). Systematic surveys for monitoring the Spitsbergen stock have never been conducted. Here, we report results from a survey for bowhead whales in the North Atlantic along the ice edge between Svalbard and Greenland in April 2006. From 17 to 28 April 2006, we searched north and northwest of Svalbard for bowhead whales (Fig. 1) from the research vessel Lance (Norwegian Polar Institute). The survey started from Spitsbergen, Svalbard, and headed west along 80◦ N toward the edge of the drifting pack ice, which on 17 April 2006 was located at approximately 0◦ longitude. We proceeded north along the ice to about 82◦ N and then southeast to 80.12◦ N, 11.27◦ E north of Svalbard. On 25 April we went straight back through open waters toward the western ice edge at 80◦ N where we continued our search effort. The total distance of the survey lines was approximately 2,000 km. Throughout the survey, we continuously monitored the sea acoustically, and in addition, at least two persons equipped with binoculars were actively searching for whales from the bridge of the vessel (∼10 m above seal level) at all times. During 149 h of the surveying time we towed two custom-made hydrophones 280 m and 380 m, respectively, behind the vessel. The first hydrophone consisted of a PC5TUBE 690 MARINE MAMMAL SCIENCE, VOL. 23, NO. 3, 2007 piezoelectric ceramic by Morgan Electro Ceramics (Stourport, UK) and a Magrec (Devon, UK) HP/02 amplifier enclosed in a Pirelli (Milano, Italy) Resin Kit. The second hydrophone consisted of a Benthos (North Falmouth, MA, USA) AQ4 hydrophone and a Magrec HP/01 amplifier suspended in a 1-in. diameter polyurethane tube filled with Isopar M hydrophone oil. The frequency response of both systems was approximately 100 Hz to 15 kHz ± 3 dB. Both hydrophones were attached to the same Kevlar-strengthened towing cable. At speed of 10 knt, this array tows at approximately 5–6 m below the surface (Gillespie 1997). If ice conditions did not permit towing of the acoustic gear, or when Lance was cruising at very low speeds, Dowty (London, UK) SSQ906 A(D) or Plessey (Cowes, UK) SSQ906 sonobuoys were deployed for acoustic monitoring (hydrophone depth set to 40 m). The sonobuoys were used for a total of 19 h of surveying and during 4 h when small boats were engaged in attempting to biopsy the whales. Sonobuoys were deployed from the ship and the signal was monitored while the ship cruised away from the buoy. While cruising we deployed one buoy every 30 min. Sonobuoy signals were received on a modified ICOM (Bellevue, WA, USA) VHF receiver that received the full audio bandwidth of the signal. All acoustic signals were high-pass filtered at 100 Hz using an F-J Electronics (Holte, Danmark) A/S AFF450 filter and then digitized at 50 kHz using an Avisoft (Berlin, Germany) Ultrasoundgate 416 digitizer connected to a Toshiba Tecra S1 laptop computer. Monitoring was conducted by researchers listening continuously to the input on Sennheiser (Wedemark, Germany) HD280 Pro headphones and watching real-time spectrograms (FFT length: 1024 points) produced by Avisoft Recorder software. The upper frequency limit of the spectrograms was set to 4 kHz on the screen to enlarge the relevant frequency band for this study. We had eight observation events that included 17–20 bowhead whales (Table 1, Fig. 1). All whales were detected visually from the vessel’s bridge and all observations were made in a relatively small area of the Fram Strait over the continental slope at depths between 1,030 and 2,785 m. Age and sex of the animals were not determined, but those whales we got close to with small boats for biopsy darting were at least 15-m long. Habitat selection by bowhead whales is believed to change with season. During spring and summer, bowheads reside in continental-slope waters (Moore et al. 2000). This is consistent with our spring sightings, which were made on the continental slopes of Svalbard. In this region, warm Atlantic water of the West Spitsbergen Current meets cold arctic water of the East Greenland Current (Schauer et al. 2004). When the annually formed winter sea ice melts in this region during the spring, phytoplankton begins to grow vigorously (Smith et al. 1987) making an abundant food source for copepods (Hirche and Niehoff 1996). Bowhead whales feed mainly on calanoid copepods and euphausiids (Lowry 1993, Lowry et al. 2004). We observed a dense layer that was consistent with a zooplankton signal at 80–100 m depth on a 120 kHz echo sounder (Simrad EK60) in those areas where whales were observed. Møller et al. (2006) found that the biomass of copepods in the upper 60 m of the Greenland Sea increased during spring to peak in June. We suggest that the whales we observed in the Fram Strait were feeding on copepods along the ice edge. NOTES 691 We expected to hear singing or other calls from bowhead whales at this time of the year (Würsig and Clark 1993) but had no success in recording sound of any kind from the whales. Our recording system was tested with a variety of marine mammal sounds before this study. During our cruise we recorded our own ship engine, that of another vessel, and songs of bearded seals. Because bearded seals use the same frequency range as bowhead whales we are confident that the lack of vocal activity cannot be explained by problems with our recording equipment. It is, however, possible that bowhead sounds were masked by engine noise at large distances and that the whales ceased vocalizing when the ship got close. We cannot rule out that the presence of our ship (and our three small satellite boats) may have influenced the vocal behavior of the animals, although avoidance responses were not evident prior to deployments of the small boats. R/V Lance is an ice-going vessel that uses a variable-pitch propeller. These propellers create considerably more noise than those with blades that are fixed in one position. Although we did not measure the source level of our engine, the noise it created could be recorded with sonobuoys at distances of up to 10 km. Disturbance reactions of bowheads to loud noise have been well documented and include the temporary cessation of vocalizing (Richardson et al. 1995). Further studies are needed to investigate the acoustic behavior of bowhead whales in the North Atlantic. The distribution of bowheads in the Fram Strait is well documented for the 17th and 18th century (Reeves 1980, Sanger 1991, Hacquebord 1999). There was a “bay” of ice-free water in the area between Svalbard and Greenland that was maintained by the warm Atlantic water of the West Spitsbergen Current. The location of the northern extension of this bay varied considerably interannually but in some years reached up to 80◦ N in late April. It was thought that the bowhead whales moved from the south into this ice bay in April. A huge number of whales were caught in this area, which whalers referred to as Whaler’s Bay or the Northern Whaling Ground. The spring ice conditions in 2006 differed dramatically from those in historical whaling reports; there was open water as far north as 82◦ N in April. For the surveyed area, we conclude that during April 2006 bowhead whales within the western range of the Spitsbergen stock were concentrated in the area 80◦ –81◦ N, 0◦ –2◦ E. Obviously, the occurrence of copepods that congregate to feed on the algal bloom along the ice edge, as well as the sea current systems that keeps this part of the Fram Strait more or less consistently open, make the area a favorable habitat for bowhead whales during early spring. Records of bowhead whales have been sporadic but persistent for some time in the Svalbard area (Reeves 1980) and in the eastern part of the Barents Sea, particularly in the Franz Josef Land area (Wiig 1991, Moore and Reeves 1993, de Korte and Belikov 1994). In addition, reports of bowhead sightings have been received annually in the last few years from Spitsbergen fjords during summer (Norwegian Polar Institute, unpublished data). There is also an apparent increase in the number of occasional observations of bowheads in Northeast Greenland during the last decades (Gilg and Born 2005). Preliminary results from aerial surveys conducted in the Canadian eastern Arctic from 2002 to 2004 suggest that the Davis Strait and Hudson Bay stocks may be in the order of several thousand whales, rather than the few hundred 692 MARINE MAMMAL SCIENCE, VOL. 23, NO. 3, 2007 that were estimated for this stock prior to this recent work (COSEWIC 2005). Currently, it is not known whether the observed bowhead whales in the Svalbard area are stragglers from the Northwest Atlantic or survivors of the Spitsbergen stock. Planned comparative genetic analyses of West Greenland bowheads (Heide-Jørgensen et al. 2003) with biopsies obtained during our Svalbard survey will allow us to address this question. ACKNOWLEDGMENTS We are grateful to the crew of R/V Lance for help during the survey. We are also grateful to C. Freitas, R. Pike, G. Westereng, and J. R. Wiig for their participation in the survey team. C. Freitas also helped with making the figure. We acknowledge funding by the Norwegian Polar Institute, the Research Council of Norway (grant no.: 153028/S40; 146515/420), and the Strategic University Program “National Centre for Biosystematics” (Project nr. 146515/420), co-funded by the Research Council of Norway and the NHM, University of Oslo. VMJ was supported by a UK Royal Society University Research Fellowship. LITERATURE CITED ALLEN, R. C., AND I. KEAY. 2006. Bowhead whales in the Eastern Arctic, 1611–1911: Population reconstruction with historical whaling records. Environment and History 12:89–113. CETACEAN SPECIALIST GROUP. 2006. Balaena mysticetus (Spitsbergen stock). IUCN 2006 IUCN Red List of Threatened Species (Available from www.iucnredlist.org). CHRISTENSEN, I., T. HAUG AND N. ØIEN. 1992. Seasonal distribution, exploitation and present abundance of stocks of large baleen whales (Mysticeti) and sperm whales (Physeter macrocephalus) in Norwegian and adjacent waters. International Council for Exploration of the Seas, Journal of Marine Science 49:341–355. COSEWIC. 2005. COSEWIC assessment and update status report on the bowhead whales Balaena mysticetus in Canada. Committee on the Status of Endangered Wildlife in Canada, Ottawa. Viii + 51 pp (Available from www.sararegistry. gc.ca/status/status e.cfm). DE KORTE, J., and S. E. BELIKOV. 1994. Observations of Greenland whales (Balaena mysticetus), Zemlya Frantsa-Iosifa. Polar Record 30:135–136. GILG, O., AND E. W. BORN. 2005. Recent sightings of the bowhead whale (Balaena mysticetus) in northeast Greenland and the Greenland Sea. Polar Biology 28:796–801. GILLESPIE, D. 1997. An acoustic survey for sperm whales in the Southern Ocean Sanctuary conducted from the RV Aurora Australis. Report of the International Whaling Commission 47:897–907. HACQUEBORD, L. 1999. The hunting of Greenland right whale in Svalbard, its interaction with climate and its impact on the marine ecosystem. Polar Research 18:375– 382. HEIDE-JøRGENSEN, M. P., K. L. LAIDRE, Ø. WIIG, M. V. JENSEN, L. DUECK, L. D. MAIERS, H. C. SCHMIDT AND R. C. HOBBS. 2003. First successful satellite tracking of bowhead whales, Balaena mysticetus, in Baffin Bay: From Greenland to Canada in ten days. Arctic 56:21–31. HIRCHE, H.-J., AND B. NIEHOFF. 1996. Reproduction of the Arctic copepod Calanus hyperboreus in the Greenland Sea—Field and laboratory observations. Polar Biology 16:209– 219. a a JONSGARD, A. 1981. Bowhead whales, Balaena mysticetus, observed in arctic waters of the eastern North Atlantic after the Second World War. Report of the International Whaling Commission 31:38–92. NOTES 693 LOWRY, L. F. 1993. Foods and feeding ecology. Pages 201–238 in J. J. Burns, J. J. Montague AND C. J. Cowles, eds. The bowhead whale. Special Publication Number 2, Society for Marine Mammalogy, Lawrence, KS. LOWRY, L. F., G. SHEFfiELD AND J. C. GEORGE. 2004. Bowhead whale feeding in the Alaskan Beaufort Sea, based on stomach contents analyses. Journal of Cetacean Research and Management 6:215–223. MOORE, S. E., AND R. R. REEVES. 1993. Distribution and movement. Pages 313–386 in J. J. Burns, J. J. Montague AND C. J. Cowles, eds. The bowhead whale. Special Publication Number 2, Society for Marine Mammalogy, Lawrence, KS. MOORE, S. E., D. P. DEMASTER AND P. K. DAYTON. 2000. Cetacean habitat selection in the Alaskan Arctic during summer and autumn. Arctic 53:432–447. MøLLER, E. F., T. G. NIELSEN AND K. RICHARDSON. 2006. The zooplankton community in the Greenland Sea: Composition and role in carbon turnover. Deep-Sea Research I 53:76–93. REEVES, R. R. 1980. Spitsbergen bowhead stock: A short review. Marine Fisheries Review 42:65–69. RICHARDSON, W. J., C. R. GREENE, C. I. MALME AND D. H. THOMSON. 1995. Marine mammals and noise. Academic Press, San Diego, CA. SANGER, C. W. 1991. Environmental factors affecting 17th–19th century whaling in the Greenland Sea. Polar Record 27:77–86. SCHAUER, U., E. FAHRBACK, S. OSTERHUS AND G. ROHARDT. 2004. Arctic warming through the Fram Strait: Oceanic heat transport from 3 years of measurements. Journal of Geophysical Research 109:1–14. SMITH, W. O., M. E. M. BAUMANN, D. L. WILSON AND L. ALETSEE. 1987. Phytoplankton biomass and productivity in the marginal ice zone of the Fram Strait during summer 1984. Journal of Geophysical Research 92:6777–6786. WIIG, Ø. 1991. Seven bowhead whales (Balaena mysticetus L.) observed at Franz Josef Land in 1990. Marine Mammal Science 7:316–319. WOODBY, D. A., AND D. B. BOTKIN. 1993. Stock sizes prior to commercial whaling. Pages 387–407 in J. J. Burns, J. J. Montague and C. J. Cowles, eds. The bowhead whale. Special Publication Number 2, Society for Marine Mammalogy, Lawrence, KS. WÜRSIG, B., AND C. CLARK. 1993. Behavior. Pages 157–199 in J. J. Burns, J. J. Montague and C. J. Cowles, eds. The bowhead whale. Special Publication Number 2, Society for Marine Mammalogy, Lawrence, KS. Received: 26 September 2006 Accepted: 18 December 2006