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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 />

Figure 2.25. Underwater Audiograms <strong>of</strong> Several Odontocetes: (A) Uhite Whale<br />

(Uhite et al. 1978; Awbrey et al. 1988); Killer Whale (Hall <strong>and</strong><br />

Johnson 1972); Harbor Porpoise (Andersen 1970); (B) Bottlenose<br />

Dolphin (Johnson 1968a; Ljungblad et al. 1982~); Amazon River<br />

Dolphin or Boutu (Jacobs <strong>and</strong> Hall 1972); False Killer Whale<br />

. (Thomas et a1 . 1978).<br />

For each species <strong>the</strong>re is a range <strong>of</strong> frequencies where hearing thresholds<br />

are low. Below <strong>and</strong> above this range <strong>the</strong> hearing thresholds increase with<br />

decreasing or increasing frequency. The increase in thresholds is ra<strong>the</strong>r<br />

gradual at low frequencies. It is possible that estimated auditory thresholds<br />

for many species are too high for frequencies below 1-10 kHz, since <strong>the</strong> small<br />

tanks in which most audition tests have been done may have many echoes,<br />

st<strong>and</strong>ing waves <strong>and</strong> o<strong>the</strong>rwise elevated noise levels. This problem was<br />

suspected in <strong>the</strong> studies by Hall <strong>and</strong> Johnson (1972), Jacobs <strong>and</strong> Hall (1972)<br />

<strong>and</strong> Ljungblad et al. (1982). The limited <strong>and</strong> questionable data on sensitivity<br />

at low frequencies (

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