How is acoustics used to monitor Arctic marine mammals?
Warming in the Arctic is occurring at a much faster rate than the global mean. Sea ice loss will have direct and indirect impacts on many Arctic species, including marine mammals. Many of these species are especially vulnerable to climate change due to their close association with, and in some cases dependence on, sea ice (for reproduction, resting, and feeding). Changing Arctic climate conditions are also impacting species distributions and migration patterns. Subarctic species, such as gray, humpback, and fin whales, may expand their range into Arctic waters during extended, ice-free months, increasing competition for resources with other Arctic species. The reduction in Arctic sea ice also provides humans with unprecedented access to the region. Extended ice-free periods have stimulated plans for shipping, oil and gas development, tourism, commercial fishing, and other offshore activities. Given the potential rise in human activities, there is growing concern regarding the potential effects of anthropogenic noise on marine mammals.
Marine mammal vulnerability to anthropogenic sound in the Arctic needs to be characterized. Maps of marine mammal movement patterns and habitat use are central to this effort. However, abundance estimates, habitat assessments, migration patterns, and other key, baseline data are limited or undescribed for many Arctic marine mammals. Also, the effects of noise will vary dramatically between regions, and species-specific responses to climate change are not likely to be consistent. Assessing the status and trends of marine mammal populations in the Arctic is difficult, though, due to species’ distributions, cryptic behaviors, seasonal movements, and the logistical challenges of surveying in remote environments. Passive acoustic monitoring (PAM) is a versatile, non-invasive, and cost-effective method to detect, classify, and track marine mammals over large areas for long periods. Acoustic recorders can be mounted to fixed moorings, floats, gliders, and autonomous underwater vehicles (AUVs).
Passive acoustics has greatly increased the detection of marine mammals in the Arctic when compared with previous visual observations. It has been used since the 1980s to monitor the migration of the Bering-Chukchi-Beafort (BCB) population of bowhead whales in the western Arctic. Since 2008, over 100 recorders have been deployed. This strong sampling effort is associated with oil and gas exploration in the northeast Chukchi and western Beaufort Seas.
Another study determining fin whale presence in the southern Chukchi Sea via passive acoustics found fin whales to remain longer in the area than previously reported. The whales remained in the area until there was a decrease in water temperature and sea ice formed. Thus, if Arctic sea ice losses continue to extend in time and geographic space, with associated increases in water temperature, scientists believe the range of fin whales into the Arctic will also expand.
Autonmous acoustic recorders and hydrophones deployed from small boats have provided data on the acoustic repertoire of several Arctic pinniped species, including ribbon, ringed, and bearded seals. Multiple studies have investigated the movement patterns, sea ice interactions, and reproductive strategies of bearded seals. Male bearded seals are highly vocal during the breeding season, producing elaborate, underwater “trill” vocalizations. These sounds travel long distances and can be used to provide at-sea locations for vocalizing males. Calling activity is significantly correlated with higher sea ice concentrations. This suggests that losses in ice cover may negatively impact bearded seals, which depend on sea ice habitats for breeding, resting, and foraging.
Passive acoustics is also a valuable tool for long-term monitoring. Acoustic recorders were simultaneously deployed in the Fram Strait (the passage between Greenland and Svalbard, Norway) and on the Chukchi Plateau (a large subsea formation extending north from Alaska into the Arctic), representing the first coordinated, year-round sampling of underwater acoustic habitats at two sites in the High Arctic. The collected data provide a baseline to which other Arctic sites can be compared, and showed distinctly different acoustic habitats at each site. The Fram Strait site was more acoustically complex, with calls from bowhead whales and toothed whales (belugas and narwhals), as well as airgun pulses, recorded year-round. Calls from blue whales and fin whales were also recorded. At the Chukchi Plateau, beluga and bowhead whales, ribbon seals, and airgun pulses were detected seasonally. No marine mammal calls were recorded at all from December through February. Bearded seal calls were recorded at both sites during spring and summer, corresponding with the mating season for the species. Scientists attributed the differences in soundscapes to differences in sea ice cover, temperature, patterns of ocean circulation, and anthropogenic noise sources. The year-round detection of bowhead whales in the Fraim Strait suggest that this area is an overwintering ground, and potentially a mating area, for this endangered population of baleen whales.
It is important to note that these studies have been conducted on distinct populations, and a wider understanding of Arctic marine mammal spatial and temporal distributions is still needed. PAM studies are also limited in that they rely on vocally active marine mammals and the knowledge of vocal rates of a particular species. PAM data, however, are still critical in developing an understanding of the Arctic ecosystem, from which future changes in ambient noise can be monitored, and potential impacts on Arctic marine mammals investigated and understood. Integrating passive acoustic systems into ocean observing initiatives will also provide a means to track changes in the underwater acoustic environment. A hydrophone has been incorporated into the underwater sensor platform maintained by Ocean Networks Canada’s Cambridge Bay Observatory.
Additional Links on DOSITS
- Science of Sound: How does sea ice affect how sound travels?
- Audio Gallery: Bowhead Whale
- Audio Gallery: Fin Whale
- Audio Gallery: Bearded Seal
- NOAA Fisheries. Listening for Change in the Arctic
- Baumgartner, M. F., Stafford, K. M., Winsor, P., Statscewich, H., & Fratantoni, D. M. (2014). Glider-based passive acoustic monitoring in the Arctic. Marine Technology Society Journal, 48(5), 40–51. https://doi.org/10.4031/MTSJ.48.5.2
- Marcoux, M., Auger-Méthé, M., Chmelnitsky, E. G., Ferguson, S. H., & Humphries, M. M. (2011). Local passive acoustic monitoring of narwhal presence in the Canadian Arctic: A pilot project. Arctic, 64(3). https://doi.org/10.14430/arctic4121
- Moore, S. E., & Stabeno, P. J. (2015). Synthesis of Arctic Research (SOAR) in marine ecosystems of the Pacific Arctic. Progress in Oceanography, 136, 1–11. https://doi.org/10.1016/j.pocean.2015.05.017
- Blackwell, S. B., Richardson, W. J., Greene, Jr., C. R., & Streever, B. (2009). Bowhead whale (Balaena mysticetus) migration and calling behaviour in the Alaskan Beaufort Sea, autumn 2001–04: An acoustic localization study. Arctic, 60(3). https://doi.org/10.14430/arctic218
- Castellote, M., Small, R. J., Lammers, M. O., Jenniges, J. J., Mondragon, J., & Atkinson, S. (2016). Dual instrument passive acoustic monitoring of belugas in Cook Inlet, Alaska. The Journal of the Acoustical Society of America, 139(5), 2697–2707. https://doi.org/10.1121/1.4947427
- Clark, C. W., Berchok, C. L., Blackwell, S. B., Hannay, D. E., Jones, J., Ponirakis, D., & Stafford, K. M. (2015). A year in the acoustic world of bowhead whales in the Bering, Chukchi and Beaufort seas. Progress in Oceanography, 136, 223–240. https://doi.org/10.1016/j.pocean.2015.05.007
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- Laidre, K. L., Stirling, I., Lowry, L. F., Wiig, Ø., Heide-Jørgensen, M. P., & Ferguson, S. H. (2008). Quantifying the sensitivity of Arctic marine mammals to climate-induced habitat change. Ecological Applications, 18(sp2), S97–S125. https://doi.org/10.1890/06-0546.1
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- MacIntyre, K. Q., Stafford, K. M., Conn, P. B., Laidre, K. L., & Boveng, P. L. (2015). The relationship between sea ice concentration and the spatio-temporal distribution of vocalizing bearded seals (Erignathus barbatus) in the Bering, Chukchi, and Beaufort Seas from 2008 to 2011. Progress in Oceanography, 136, 241–249. https://doi.org/10.1016/j.pocean.2015.05.008
- Mikhalevsky, P. N., Sagen, H., Worcester, P. F., Baggeroer, A. B., Orcutt, J., Moore, S. E., … Yuen, M. Y. (2015). Multipurpose acoustic networks in the integrated Arctic Ocean observing system. Arctic, 68(5), 11. https://doi.org/10.14430/arctic4449
- Moore, S. E., Stafford, K. M., Mellinger, D. K., & Hildebrand, J. A. (2006). Listening for large whales in the offshore waters of Alaska. BioScience, 56(1), 49. https://doi.org/10.1641/0006-3568(2006)056[0049:LFLWIT]2.0.CO;2
- Moore, S. E., & Huntington, H. P. (2008). Arctic marine mammals and climate change: Impacts and resilience. Ecological Applications, 18(sp2), S157–S165. https://doi.org/10.1890/06-0571.1
- Moore, S. E., Stafford, K. M., & Munger, L. M. (2010). Acoustic and visual surveys for bowhead whales in the western Beaufort and far northeastern Chukchi seas. Deep Sea Research Part II: Topical Studies in Oceanography, 57(1–2), 153–157. https://doi.org/10.1016/j.dsr2.2009.08.013
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