Abstract

ESR Endangered Species Research Contact the journal Facebook Twitter RSS Mailing List Subscribe to our mailing list via Mailchimp HomeLatest VolumeAbout the JournalEditorsSpecials ESR 34:397-415 (2017) - DOI: https://doi.org/10.3354/esr00857 Theme Section: 21st century paradigms for measuring and managing the effects of anthropogenic ocean noise Predicting the acoustic exposure of humpback whales from cruise and tour vessel noise in Glacier Bay, Alaska, under different management strategies Adam S. Frankel1,2,*, Christine M. Gabriele3 1Marine Acoustics, Incorporated, 4350 N Fairfax Drive, Suite 600, Arlington, VA 22203, USA 2Hawai‘i Marine Mammal Consortium, PO Box 6107, Kamuela, HI 96743, USA 3National Park Service, Glacier Bay National Park & Preserve, PO Box 140, Gustavus, AK 99826, USA *Corresponding author: adam.frankel@marineacoustics.com ABSTRACT: Vessel traffic management regimes intended to protect baleen whales can have unexpected consequences on whale exposure to underwater noise. Using the Acoustic Integration Model, we simulated whale and vessel movements in Glacier Bay National Park (GBNP). We estimated vessel noise exposures to humpback whales Megaptera novaeangliae while varying the number, speed (13 vs. 20 knots [kn]), and timing of cruise ships, and keeping a constant number, speed, and timing of smaller tour vessels. Using calibrated noise signatures for each vessel and the known sound velocity profile and bathymetry of Glacier Bay, we estimated received sound levels for each simulated whale every 15 s in a 24 h period. Simulations with fast ships produced the highest maximal sound pressure level (MSPL) and cumulative sound exposure levels (CSEL). Ships travelling at 13 kn produced CSEL levels 3 times lower than those traveling at 20 kn. We demonstrated that even in cases where a ship is only a few dB quieter at a slower speed, CSEL is lower, but the ship’s transit may take substantially longer. Synchronizing ship arrival times had little effect on CSEL or MSPL but appreciably decreased cumulative sound exposure time (CSET). Overall, our results suggest that the most effective way to reduce humpback whale acoustic exposure in GBNP is to reduce the numbers of cruise ships or their speed, although adjusting ship schedules may also be beneficial. Marine protected area managers may find these results illustrative or adapt these methods to better understand the acoustic effects of specific vessel management circumstances. KEY WORDS: Acoustic propagation · Vessel noise · Chronic exposure · Management · Cumulative effects · Marine Protected Area Full text in pdf format PreviousNextCite this article as: Frankel AS, Gabriele CM (2017) Predicting the acoustic exposure of humpback whales from cruise and tour vessel noise in Glacier Bay, Alaska, under different management strategies. Endang Species Res 34:397-415. https://doi.org/10.3354/esr00857 Export citation RSS - Facebook - Tweet - linkedIn Cited by Published in ESR Vol. 34. Online publication date: November 30, 2017 Print ISSN: 1863-5407; Online ISSN: 1613-4796 Copyright © 2017 Inter-Research.

Highlights

  • The effect of vessel noise on marine mammals is an increasing concern worldwide

  • This study focused on the acoustic effects of different numbers of cruise ships and different ship operational factors to help inform management decisions on the number, location, density, and speed of ships allowed in Glacier Bay National Park (GBNP)

  • The maximal maximal sound pressure level (MSPL) and cumulative sound exposure levels (CSEL) values always occurred in simulations with fast cruise ships

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Summary

Introduction

The effect of vessel noise on marine mammals is an increasing concern worldwide. Quantifying the effects and how they might change under alternative vessel management actions, is a substantial challenge. The US Coast Guard, in collaboration with the Channel Islands National Marine Sanctuary, implemented a voluntary 10 kn speed limit within 20 nautical miles (nmi) of the entrances to the ports of Los Angeles and Long Beach in response to a number of ship strike deaths of blue whales Balaenoptera musculus in waters off southern California. These measures seem to have had limited success due to poor compliance (McKenna et al 2012)

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