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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 />

seemed to be ignored. However, whales that had been exposed repeatedly to<br />

whale-watching vessels sometimes approached those vessels. On <strong>the</strong> o<strong>the</strong>r h<strong>and</strong>,<br />

whales <strong>of</strong>ten moved,away in response to strong or rapidly-changing vessel<br />

noise. Avoidance reactions were especially strong when a boat was directly<br />

approaching (Watkins 1986). All <strong>of</strong> <strong>the</strong>se phenomena have also been documented<br />

by o<strong>the</strong>r workers studying various species <strong>of</strong> baleen whales.<br />

Reactions <strong>of</strong> gray whales to vessels have been described by several<br />

workers, but very- little information has been reported (even indirectly) about<br />

<strong>the</strong> sound levels to which <strong>the</strong>y do <strong>and</strong> do not react. Migrating gray whales<br />

have been reported to begin to exhibit avoidance when vessels approach within<br />

200-300 m (Wyrick 1954). Summering gray whales may avoid ships that approach<br />

within 350-550 m (Bogoslovskaya et al. 1981). Jones <strong>and</strong> Swartz (1986) found<br />

that wintering gray whales tend to become less sensitive to boats as <strong>the</strong><br />

winter progresses, presumably reflecting a habituation process. They <strong>and</strong><br />

o<strong>the</strong>r workers also have documented an increasing tendency for gray whales to<br />

approach ra<strong>the</strong>r than flee from vessels in recent years. On <strong>the</strong> o<strong>the</strong>r h<strong>and</strong>,<br />

gray whales ceassd using one wintering lagoon for a number <strong>of</strong> years when ship<br />

traffic was especially intense <strong>the</strong>re, <strong>and</strong> returned in later years after ship<br />

traffic had abated (Bryant et al. 1984).<br />

Humpback whales summering in waters <strong>of</strong> sou<strong>the</strong>ast Alaska <strong>of</strong>ten swim away<br />

when vessels approach within 2-4 km, <strong>and</strong> tend to dive when vessels are within<br />

2 km (Baker et al. 1983). Sound levels received by <strong>the</strong> whales during those<br />

observations were determined by Malme et al. (1982) <strong>and</strong> Miles <strong>and</strong> Malme<br />

(1983). Dean et al. (1985) also found evidence that avoidance <strong>and</strong> o<strong>the</strong>r<br />

behavioral changes were common when vessels were underway within several<br />

kilometers <strong>of</strong> summering humpbacks. However, humpbacks sometimes show little<br />

or no obvious reaction even when vessels are much closer than <strong>the</strong> typical<br />

reaction distances reported by Baker et al. <strong>and</strong> Dean et al. Humpbacks are<br />

less likely to react overtly when actively feeding than when resting or<br />

engaged in o<strong>the</strong>r activities (Krieger <strong>and</strong> Wing 1986). Thus, no single<br />

"response thresholdI1 can be defined that will apply to all humpbacks <strong>of</strong>f<br />

sou<strong>the</strong>ast Alaska. Reactions <strong>of</strong> humpbacks wintering in Hawaiian waters to<br />

boats have been studied (e.g. Bauer <strong>and</strong> Herman 1986), but little information<br />

is available about <strong>the</strong> reaction distances or <strong>the</strong> sound levels that cause<br />

reactions in winter.<br />

Reactions <strong>of</strong> bowhead whales to boats have been determined by experiments<br />

as well as opportunistic observations (Richardson et al. 1985a,b; Koski <strong>and</strong>c .<br />

Johnson 1987). Bowheads occasionally occur within a few hundred meters <strong>of</strong> oil<br />

industry <strong>and</strong> o<strong>the</strong>r vessels. However, exper.iments have shown that bowheads<br />

normally begin to swim rapidly away when vessels approach within 2-4 km.<br />

Reactions at even greater distances apparently occur in some situations (Koski<br />

<strong>and</strong> Johnson 1987). In one disturbance test where noise levels were measured<br />

directly, <strong>the</strong> noise level 4 km away from <strong>the</strong> vessel, <strong>the</strong> approximate distance<br />

at which bowheads began reacting, was only 84 dB re 1 uPa in <strong>the</strong> 1/3-octave<br />

b<strong>and</strong> <strong>of</strong> strongest noise; that level was only 6 dB above <strong>the</strong> background ambient<br />

level in that b<strong>and</strong> (Miles et al. 1987, p 225-231). However, bowheads tolerate<br />

higher vessel noise levels in some situations (Koski <strong>and</strong> Johnson 1987).. They

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