In the North Pacific, underwater noise has doubled in intensity every decade for the past 60 years.
Noise from shipping, seismic exploration, and military sonar contribute to underwater noise and may impact the ability of cetaceans (whales, dolphins and porpoises) to conduct critical life processes such as foraging, finding mates, and navigating through their underwater environment. Click the drop down menus below to learn more about how underwater noise impacts cetacean species found in British Columbia.
Killer Whales
Killer whales depend on echolocation and acoustic communication to forage, socialize, and find mates. The sophisticated echolocation system of killer whales is likely their primary sensory mode, and allows them to navigate and find prey in turbid, dark waters2. Communication is also key to foraging success for resident killer whales. Southern and northern resident killer whales are highly social animals that live out their entire lives in family groups. Resident (fish-eating) killer whales travel together in matrilines, maintaining contact through a series of distinct underwater dialects that are unique to the group3. While foraging, members of a group can spread out over several kilometres, maintaining contact and coordinating movements through the frequent exchange of loud vocalizations2. When an individual captures a prey item, it is often shared among members of its matriline4. Bigg’s (transient) killer whales, in contrast, often forage in silence2. They depend on passive listening to hunt other marine mammal prey, since vocalizing could increase the chance of their prey detecting them.
Vessel noise can interrupt critical life processes for killer whales. In areas of high vessel traffic, killer whale echolocation and communication can be almost completely masked by boat noise5, and can interrupt important behaviours such as foraging, group cohesion, resting, and mating6. Studies have shown that southern resident killer whales increase the duration of their calls when boats are present, likely as an adaptation to the masking effects caused by increased noise levels5. Vessel noise can also increase a whale’s stress level and cause them to avoid certain areas5,6. Avoidance of key foraging areas due to acoustic disturbance places additional stress on the endangered southern resident killer whale population, whose survival is already threatened by a reduction in prey availability and environmental contamination6.
Vessel speed reduction may help decrease underwater noise. In order to determine how vessel noise impacts killer whale foraging behaviour, the Port of Vancouver’s ECHO (Enhancing Cetacean Habitat and Observation) Program conducted a research trial to slow down vessels through Haro Strait. Haro Strait is known to be a key foraging area for southern resident killer whales during the summer months7. It is also geographically constrained area with a busy shipping lane, which creates the potential for loss of foraging as a result of vessel noise. The trial requested piloted commercial vessels to voluntarily slow down to 11 knots while transiting Haro Strait from August 7th to October 16th, 2017. Previous studies have indicated that slower ships are quieter; a one knot reduction in vessel speed may result in one decibel reduction in vessel noise8. The trial aims to better understand the relationship between vessel speed and sound, the effects of reduced speed on the total underwater ambient noise in critical killer whale habitat, and the potential benefit that reduced speed might have on killer whale foraging behaviour. To analyze the potential noise benefits achieved by slower speeds for different vessel classes, two hydrophones were deployed in the shipping lanes in Haro Strait to directly measure the acoustic signature of passing vessels and compare noise levels before, during and after the trial. Monitoring of total ambient underwater noise was conducted at the Lime Kiln hydrophone off San Juan Island, which serves as an indicator of potential received noise levels by killer whales in this important foraging area. Comparison between trial and non-trial months will identify important factors affecting ambient noise levels. Visual observations and acoustic detection will be used in conjunction with a computer model, developed by JASCO Applied Sciences, in order to analyze the relative change in southern resident killer whale behavioural response. Preliminary results of the trial suggest that speed reduction is an effective method for reducing vessel noise. Approximately 60% of piloted vessels participated in the slow down trial. On average, vessels reduced their mean speed by 2.2 to 5.8 knots, resulting in a 4.9dB to 9.3dB reduction in vessel noise. Slowing speed by 40% reduced noise emissions by approximately 10dB. During the trial, there was a 44% reduction in ambient noise levels when a vessel was within acoustic detection range (6km) of the Lime Kiln hydrophone. These initial findings support speed reduction as a promising mitigation measure to help reduce underwater noise in the Salish Sea. The next steps will include a fine scale analysis of changes in ambient noise levels and behavioural modelling of killer whale response. Read more about the Port of Vancouver’s ECHO program here!
Baleen Whales
Low frequency ambient noise from human activity can mask the calls of baleen whales. Hearing is as important to cetaceans as vision is to humans. In response to the limited visibility of most ocean environments, cetaceans have adapted to take advantage of the physics of sound underwater. Sound travels approximately 4.5 times faster and 100 times further in salt water than in air2. Low frequency sound experiences little attenuation, making it particularly effective for underwater communication over great distances1; Baleen whales rely on these low frequency calls primarily for social communication, and their vocalizations can be heard by other individuals for hundreds of kilometres9. Increasing levels of low frequency ambient noise from shipping, seismic exploration, and military sonar have been identified as a major threat to the recovery of blue, fin, and humpback whales in B.C. waters, as it may mask their vocalizations and displace them from their critical habitat9,10.
Harbour Porpoise
Offshore Species
Noise pollution is impacting cetacean populations worldwide
Dr. Valeria Vergara, a Researcher at Ocean Wise, is investigating how underwater noise impacts beluga communication. Read more in the drop down below.
Belugas
In 2018, The BC Cetacean Sightings Network launched the WhaleReport Alert System, an alert system that broadcasts pertinent details of whale presence to large commercial vessels. Information on whale presence is obtained from real-time observations reported to the B.C. Cetacean Sightings Network via the WhaleReport app. These alerts inform shipmasters and pilots of cetacean occurrence in their vicinity. This awareness will better enable vessels to undertake adaptive mitigation measures, such as slowing down or altering course in the presence of cetaceans, to reduce the risk of collision and disturbance.
Vessels aren’t the only source of underwater noise

The marine soundscape is made up of all sources that contribute sound to the environment. Soundscapes include sounds made by humans (anthropogenic; orange sound waves), the environment (natural sounds; green sound waves), and by biological sources (animals: marine mammals, fish, and invertebrates; blue sound waves). Credit: NOAA. Read more.
What can you do to help?
Vessel traffic, both commercial and recreational, has increased significantly along the British Columbia Coast. This rise in vessl traffic has caused an increase in physical and acoustic disturbance in cetacean habitat.
Follow the Be Whale Wise Guidelines
Report Marine Mammal Harassment and Violations
Watch Whales from Shore
Tools for Commercial Mariners
References
- Hildebrand, J. (2009). Anthropogenic and natural sources of ambient noise in the ocean. Marine Ecological Progress Series, 395, 5-20.
- Ford, J.K.B. Marine Mammals of British Columbia. (2014). Royal BC Museum. Victoria, Canada.
- Fisheries and Oceans Canada (2017). Action Plan for the Northern and Southern Resident Killer Whale (Orcinus orca) in Canada. Species at Risk Act Action Plan Series. Fisheries and Oceans Canada, Ottawa. v + 33pp.
- Wright, B.M., Stredulinsky, E.H., Ellis, G.M., & Ford, J.K.B. (2016). Kin-directed food sharing promotes lifetime natal philopatry of both sexes in a population of fish-eating killer whales, Orcinus orca. Animal Behaviour, 115, 81-95.
- Erbe, C. (2002). Underwater noise of whale-watching boats and potential effects on killer whales (Orcinus orca), based on an acoustic impact model. Marine Mammal Science, 18, 394-418.
- Williams, R., Lusseau, D., & Hammond, P. (2006). Estimating relative energetic costs of human disturbance to killer whales (Orcinus orca). Biological Conservation, 133(3), 301-311.
- Fisheries and Oceans Canada (2011). Recovery Strategy for the Northern and Southern Resident Killer Whales (Orcinus orca) in Canada. Species at Risk Act Recovery Strategy Series, Fisheries and Oceans Canada, Ottawa. ix + 80pp.
- International Maritime Organization (2014). Guidelines for the reduction of underwater noise from commercial shipping to address adverse impacts on marine life, MEPC.1/Circ.833. London, U.K: IMO Publishing. 8pp.
- Gregr, E.J., Calambokidis, L., Convey, L., Ford, J.K.B. Perry, R.I., Spaven, L. & Zacharias, M. (2006). Recovery Strategy for the Blue, Fin, and Sei Whales (Balaenoptera musculus, B. physalus, and B. borealis) in Pacific Canadian Waters. Species at Risk Act Recovery Strategy Series. Fisheries and Oceans Canada, Vancouver. Vii + 53pp.
- Fisheries and Oceans Canada. (2013). Recovery Strategy for the North Pacific Humpback Whale (Megaptera noavengliae) in Canada. Species at Risk Act Recovery Strategy Series. Fisheries and Oceans Canada, Ottawa. x + 67 pp.
- Fisheries and Oceans Canada. (2009). Management Plan for the Pacific Harbour Porpoise (Phocoena phocoena) in Canada. Species at Risk Act Management Plan Series. Fisheries and Oceans Canada, Ottawa. v + 49pp.
- Fahlman, A., Tyack, P.L. Miller, P.J.O., & Kvadsheim, P.H. (2004). How man-made interferences might cause gas bubble emboli in deep diving whales. Frontiers in Physiology, 5(13).
- Fisheries and Oceans Canada. (2012). Recovery strategy for the beluga whale (Delphinapterus leucas) St. Lawrence Estuary population in Canada. Species at Risk Act Recovery Strategy series. Fisheries and Oceans Canada, Ottawa. 88pp + X pp.
- Vergara, V., Michaud, R., & Barrett-Lennard, L. (2010). What can captive whales tell us about their wild counterparts? Identification, usage, and ontogeny of contact calls in belugas (Delphinapterus leucas). International Journal of Comparitive Psychology, 23 (3)
- Vergara, V. & Barrett-Lennard, L. (2008). Vocal development in a beluga calf (Delphinapterus leucas). Aquatic Mammals, 34 (1), 123-143.
- Fisheries and Oceans Canada (2017). St. Lawrence Estuary Beluga: A science based review of recovery actions for three at-risk whale populations. 64pp. http://www.dfo-mpo.gc.ca/species-especes/whalereview-revuebaleine/review-revue/beluga/index-eng.html