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Analysis and Ranking of the Acoustic Disturbance Potential of ...

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Report No. 6945<br />

BBN Systems <strong>and</strong> Technologies Corporation<br />

whales, which occurred in <strong>the</strong> 24-29 April time period. On 1 May <strong>the</strong> visual<br />

count was 20 whalesoduring a 7 hour period. The count during <strong>the</strong> time <strong>of</strong><br />

maximum passage had averaged 43 animals per day over a 3-day period. Some<br />

fluctuations in count were clearly due to poor visual conditions (fog, wind,<br />

rain), but <strong>the</strong>se numbers indicate <strong>the</strong> trend in <strong>the</strong> whale count. On 2 May at<br />

164300 toward <strong>the</strong> end <strong>of</strong> <strong>the</strong> oQservation period, seismic energy arrived from a<br />

M = 6.7 earthquake in Coalinga, California--144 km away. During <strong>the</strong> following<br />

24 hours a series <strong>of</strong> 15<br />

,<br />

aftershocks in <strong>the</strong> M = 3.5 - 5.1 range were reported<br />

by seismic stations, on 4 May six shocks <strong>of</strong> M 3.4 were reported, with<br />

nine events <strong>of</strong> M 2 3.4 reported for <strong>the</strong> 5th <strong>of</strong> May. On 3 May only a single ,<br />

mo<strong>the</strong>r/calf pair was seen from <strong>the</strong> shore observation site (late in <strong>the</strong><br />

afternoon), <strong>and</strong> three pairs each day were seen on 5/4 <strong>and</strong> 5/5. Observation<br />

conditions were good to fair on 5/2, excellent 5/3-5/4 <strong>and</strong> good to very good<br />

on 5/5 when <strong>the</strong> observation work was terminated.<br />

The sound measurement system used by BBN was overloaded by <strong>the</strong> main shock<br />

on 5/2 <strong>and</strong> was not operating at <strong>the</strong> time <strong>of</strong> calculated aftershock arrival,<br />

hence we do not have sound pressure level data available for comparison with<br />

spectra in Fig. 3.2 or with predictions given in Fig. 3.8. Based on <strong>the</strong> known<br />

overload limit <strong>of</strong> <strong>the</strong> hydrophone preamplifier, a received sound pressure level<br />

<strong>of</strong> 176 dB will cause signal distortion; saturation should occur at a higher<br />

level <strong>of</strong> about 186 dB. The overall received sound pressure level from <strong>the</strong><br />

main shock was expected to be about 195 - 206 dB (Fig. 3.8) .<br />

Obviously, we do not know whe<strong>the</strong>r <strong>the</strong> underwater sound (fluctuating<br />

compressional wave energy) f~om <strong>the</strong> main shock <strong>and</strong> from subsequent aftershocks<br />

caused <strong>the</strong> gray whales to move fur<strong>the</strong>r from shore (beyond visual observation<br />

capability). Even though it is tempting to draw that conclusion, we may have<br />

been observing a natural rapid cessation <strong>of</strong> <strong>the</strong> migration pulse. Never<strong>the</strong>less,<br />

it is conceivable that marine mammals will change behavior temporarily<br />

during <strong>the</strong> onset <strong>of</strong> earthquake short term events. There have been many<br />

anecdotal observations <strong>of</strong> animal behavioral anomalies before <strong>and</strong> during<br />

seismic disturbances (see, for instance Lee et al., 1976 <strong>and</strong> Stierman, 1980).<br />

3.2.6 Ice noise<br />

There are several dynamic processes associated with ice in arctic <strong>and</strong><br />

near-arctic regions which can contribute in a significant way to <strong>the</strong> natural<br />

underwater background noise. Under-ice noise studies, notably by Milne<br />

(1960), Milne <strong>and</strong> Ganton (1964), Greene <strong>and</strong> Buck ( 1964), <strong>and</strong> Buck <strong>and</strong> Wilson<br />

(1986), <strong>and</strong> summaries (e.g., Urick, 1983) have demonstrated <strong>the</strong> high<br />

variability <strong>of</strong> ambient noise levels in relation to such parameters as wind<br />

speed <strong>and</strong> changes in temperature <strong>and</strong> pressure ridge activity. During calm<br />

wind conditions <strong>and</strong> stable temperature, sound levels under a continuous ice<br />

sheet are frequently below those measured in <strong>the</strong> open ocean under sea state=O<br />

conditions. Environmental changes such as a decrease in temperature (causing<br />

ice cracking) or an increase in wind speed can result in an increase in <strong>the</strong><br />

background noise by as much as 40 dB. Rising temperatures tend to stabilize<br />

<strong>the</strong> ice <strong>and</strong> background noise levels drop. Wind-related effects have relatively<br />

little influence on under-ice noise when <strong>the</strong>re is solid ice cover, but<br />

<strong>the</strong>y become quite important when <strong>the</strong>re are fractures in <strong>the</strong> ice with leads <strong>and</strong><br />

floes <strong>and</strong> sharp ice/water discontinuities at <strong>the</strong> edge <strong>of</strong> <strong>the</strong> ice pack or ice

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