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Composite Training Unit Exercises and Joint Task ... - Govsupport.us

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CD-086-06, Navy <strong>Training</strong> <strong>Exercises</strong>Southern CaliforniaPage 27of two studies <strong>and</strong> one after-the-fact investigation wherein the naturalbehavior patterns of marine mammals exposed to levels of tactical midfrequencysonar, or sounds similar to mid-frequency sonar, lower thanthose thought to induce TTS were disrupted to the point where it wasab<strong>and</strong>oned or significantly altered:(1) Finneran <strong>and</strong> Schlundt (2004) analyzed behavioral observationsfrom related TTS studies (Schlundt et al., 2000; Finneran et al., 2001;2003) to calculate cetacean behavioral reactions as a function of knownnoise exposure. During the TTS experiments, four dolphins <strong>and</strong> two whitewhales were exposed during a total of 224 sessions to 1-s pulsesbetween 160 <strong>and</strong> 204 dB re 1 mPa (root-mean-square sound pressure level(SPL)), at 0.4, 3, 10, 20, <strong>and</strong> 75 kHz. Finneran <strong>and</strong> Schlundt (2004)evaluated the behavioral observations in each session <strong>and</strong> determinedwhether a ``behavioral alteration'' (ranging from modifications ofresponse behavior during hearing sessions to attacking the experimentalequipment) occurred. For each frequency, the percentage of sessions inwhich behavioral alterations occurred was calculated as a function ofreceived noise SPL. By pooling data across individuals <strong>and</strong> testfrequencies, respective SPL levels coincident with responses by 25, 50,<strong>and</strong> 75 percent behavioral alteration were documented. 190 dB re 1 mPa(SPL) is the point at which 50 percent of the animals exposed to 3, 10,<strong>and</strong> 20 kHz tones were deemed to respond with some behavioralalteration, <strong>and</strong> the threshold that the Navy originally proposed forsub-TTS behavioral disturbance.(2) Nowacek et al. (2004) conducted controlled exposure experimentson North Atlantic right whales <strong>us</strong>ing ship noise, social sounds of conspecifics,<strong>and</strong> an alerting stimul<strong>us</strong> (frequency modulated tonal signalsbetween 500 Hz <strong>and</strong> 4.5 kHz). Animals were tagged with aco<strong>us</strong>tic sensors(D-tags) that simultaneo<strong>us</strong>ly measured movement in three dimensions.Whales reacted strongly to alert signals at received levels of 133-148dB SPL, mildly to conspecific signals, <strong>and</strong> not at all to ship sounds oractual vessels. The alert stimul<strong>us</strong> ca<strong>us</strong>ed whales to immediately ceaseforaging behavior <strong>and</strong> swim rapidly to the surface. Although SEL valueswere not directly reported, based on received exposure durations,approximate received values were on the order of 160 dB re: 1 mPa\2\-s.(3) NMFS (2005) evaluated the aco<strong>us</strong>tic exposures <strong>and</strong> coincidentbehavioral reactions of killer whales in the presence of tactical midfrequencysonar. In this case, none of the animals were directly fittedwith aco<strong>us</strong>tic dosimeters. However, based on a Naval Research Laboratory(NRL) analysis that took advantage of the fact that calibrated

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