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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 23equipment) 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 calibratedmeasurements of the sonar signals were made in situ <strong>and</strong> <strong>us</strong>ing advancedmodeling to bound likely received exposures, estimates of receivedsonar signals by the killer whales were possible. Received SPL valuesranged from 121 to 175 dB re: 1 mPa. The most probable SEL values were169.1 to 187.4 dB re: 1 mPa\2\-s; worst-case estimates ranged from177.7 to 195.8 dB re: 1 mPa\2\-s. Researchers observing the animalsduring the course of sonar exposure reported un<strong>us</strong>ual alterations inswimming, breathing, <strong>and</strong> diving behavior.For more detailed information regarding how marine mammals mayrespond to sound, see the Navy's IHA application, the Navy's associatedEA, Richardson's Marine Mammals <strong>and</strong> Noise (1995), or the referencescited on NMFS' Ocean Aco<strong>us</strong>tic Program website (see ADDRESSES)

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