PASSIVE ACOUSTIC MONITORING

ARU
Autonomous Recording Unit (ARU) developed by Cornell University's Bioacoustics Research Program and used to monitor underwater sound in the SBNMS.
 

People and marine animals use sound in the sea to accomplish many tasks. Since light travels relatively short distances in the ocean, sound is often used for such basic activities as finding food or a mate, navigating, and communicating. For that reason, the oceans are filled with sound generated by a variety of human-related sources, including not biotic sources (e.g. marine life) but abiotic sources such as breaking waves, earthquakes, wind and rain. Underwater sound is also generated by a variety of anthropogenic sources, such as vessels, military sonars, oil and gas drilling, and some oceanographic research technologies.

The background "omnipresent" sound in the ocean is called ambient noise. The primary sources of ambient noise vary with the frequency. For example, ambient noise between 20-500 Hz is primarily generated by vessels whereas ambient noise between 500-100,000 Hz is mostly due to spray and bubbles associated with breaking waves.

Current knowledge about the effects of sound on marine animals relies heavily on experimentation with small numbers of individuals in captivity and/or post-hoc evaluation of mortality events in the wild, in which cause and effect is often impossible to determine. Due to their charismatic nature, protected status and their use of sound for communication, marine mammals have been the focus of increasing levels of attention and controversy possible adverse effects of noise in the marine environment. Marine mammals have been shown to manifest behavioral changes in the presence of certain types of noise. In addition, exposure to anthropogenic noise can impact cetaceans by masking biologically important sounds (e.g. intraspecific communication and localization of prey resources), provoking avoidance or attraction, causing temporary or permanent hearing damage and, in extreme cases, death.

In its 2003 report (one of three devoted to sound sources and marine mammals), the US National Research Council of the National Academies' (NRC's) Committee on the Potential Impacts of Ambient Noise in the Ocean on Marine Mammals concluded that concern surrounding anthropogenic sound and marine mammals was warranted, given the endangered status of many marine mammals, the identified importance of sound in the lives of marine mammals, the potential for harm from excessive noise and the paucity of data with regards to the amount of sound introduced into the oceans by human activity and its potential impact on marine mammals.

The NRC's report recommended the establishment of "noise budgets", defined as the sum of the relative contributions made by identified sound sources to the total sound field. The report further recommended that "noise budget" determinations for various parts of the ocean should include representations of seasonal and spatial/temporal differences. Finally, the NRC specifically identified the need to define the sound contribution of different vessel types within the major category of shipping. While the report's focus was global, many of its insights and recommendations can be used at the sanctuary level to provide a local understanding of the issue. Insights achieved at the local level can then be used to inform the larger issue at national and international levels.

Numerous anthropogenic sources of underwater sound produced both within and in the waters surrounding SBNMS contribute to the sanctuary's ambient noise budget. Commercial, recreational, military, and research vessels all contribute to ambient underwater noise in the sanctuary, whether directly through their marine operations (e.g., engines, props and electronics) or indirectly through the activities they perform (e.g. towing and dredging). Whales are known to aggregate in and near the existing traffic separation scheme (i.e., shipping lanes to and from the Port of Boston) and their long-term acoustic exposure to vessel traffic may represent a source of chronic impact.

The operations of fishing vessels regularly overlap the distribution of cetaceans in the sanctuary and may be an additional source of repeated acoustic disturbance. In addition, some vessels, such as commercial and private whale watching boats, preferentially expose large whales to noise as a byproduct of routine and frequent close approaches, creating another opportunity for chronic exposure. Finally, because low-frequency sounds can retain their intensities over large distances, industrial and commercial activities taking place or proposed within the Gulf of Maine, can or will contribute to low frequency sound in the sanctuary.

To begin characterizing the acoustic environment and health of SBNMS, a collaborative group of researchers from the SBNMS, NOAA Fisheries (Northeast Science Center and Regional Offices) and Cornell University's Bioacoustics Research Program has installed an array of nine autonomous recording units (ARUs) to monitor underwater sounds between 0 and 1000Hz throughout sanctuary waters for one calendar year.

ARU data will be used to compare sanctuary sound levels with (1) baleen whale audiogram models to estimate the potential for hearing loss and (2) the sounds produced by baleen whales in the sanctuary to determine the potential for masking. To calculate the "noise budget" of SBNMS, the contributions and frequency characteristics of noise from biological, meteorological, and anthropogenic sources will be identified. Modeling will determine, for a specific location and its acoustic environment, the range at which a sound of a given frequency could be received from that location and how that range would change daily, seasonally, and yearly, as a result of changes in the acoustic environment.

ARU data will be used to localize vocalizing whales (identified by the species-specific characteristics of their vocalizations) and calculate distributions and acoustic densities for different species in sanctuary waters throughout the year. These data will aid the sanctuary's ongoing monitoring of whale densities relative to vessel traffic. Due to their critically endangered status, locating vocalizing right whales within the sanctuary will remain a priority for ARU data analysis.
The same data can be analyzed to determine the number of vessels traversing the acoustic monitoring area, the acoustic characteristics of individual vessel types, and the received characteristics of the vessel as a function of such factors as distance, bathymetry, and water temperature.

Financial support for this research is provided by the National Marine Sanctuary Program, NOAA Fisheries Northeast Science Center and Northeast Regional Office, the National Marine Sanctuary Foundation, the International Fund for Animal Welfare and the Massachusetts Environmental Trust

ARU's

Autonomous Recording Units (ARUs) in their packing cases onboard the deploying vessel.

ARU array

Research design for ARU array affording approximately 85% acoustic reception coverage with the SBNMS' boundaries.

Spectogram

24 Hour Spectrogram of sound within a portion of the SBNMS resulting from 2004 pilot study. Note chronic loud sound in the <1000 Hz bandwidth used by baleen whales. Figure credit: Ingrid Biedron, Bioacoustics Research Program, Cornell University.

PRESENTATIONS
Hatch, L. T., and Wiley, D. 2006. The Gerry E. Studds Stellwagen Bank National Marine Sanctuary as a model for integrating platforms to characterize the marine acoustic environment. NOAA Passive Acoustics Workshop, Woods Hole, Massachusetts; April 12-14.

Hatch, L. T., Gontz, A. M, Clark, C. W., and Wiley, D. 2006. The Gerry E. Studds Stellwagen Bank National Marine Sanctuary as a regional case study for integrating protected species and protected area management tools to study and mitigate impacts of anthropogenic noise sources on marine mammals. SC/58/E2. Presented to Environmental Concerns Working Group's Pre-Meeting to Review the Potential Impacts of Seismic Surveys on Cetaceans; 58th Annual Meeting, Scientific Committee of the International Whaling Commission, St. Kitts, West Indies; May 24-25.

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Revised May 18, 2006 by Stellwagen Bank National Marine Sanctuary Web Group
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