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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 />

Section 2'.1.3 for each potential source - specie$ encounter situation. Thus<br />

ratings are obtained for both <strong>the</strong> encounter sensitivity for a single animal<br />

<strong>and</strong> <strong>the</strong> specific potential for acoustic impact for <strong>the</strong> population within an<br />

area. The SER values obtained from <strong>the</strong> analysis are shown in bar graph format.<br />

to supplement <strong>the</strong> data presented in <strong>the</strong> tables.<br />

The SER Model is designed to show which species are potentially most<br />

influenced by a given noise source by developing high values when compared to<br />

<strong>the</strong> input SNCl value. If <strong>the</strong> SER value is comparable to, or less than <strong>the</strong><br />

SNC1 value, <strong>the</strong> species is likely to be minimaly influenced as a result <strong>of</strong> a<br />

mismatch between <strong>the</strong> source noise spectrum <strong>and</strong> <strong>the</strong> species hearing sensitivity<br />

<strong>and</strong>/or a low species population density in <strong>the</strong> area being considered. A<br />

procedure was devised for summarizing <strong>the</strong> results <strong>of</strong> <strong>the</strong> SER analysis using<br />

three general ratings <strong>of</strong> low, medium <strong>and</strong> high. These ratings were established<br />

by statistically analyzing <strong>the</strong> output <strong>of</strong> <strong>the</strong> SER Model for all <strong>of</strong> <strong>the</strong> source<br />

species encounters examined in <strong>the</strong> 4 planning areas. The average <strong>and</strong> <strong>the</strong><br />

st<strong>and</strong>ard deviation <strong>of</strong> <strong>the</strong> area SER values were determined for a total <strong>of</strong> 75<br />

data points. The values ranged between 111 <strong>and</strong> 207 dB with a mean value <strong>of</strong><br />

159 dB. The st<strong>and</strong>ard deviation was 20 dB. With <strong>the</strong>se results as a guide <strong>the</strong><br />

general ratings were defined as<br />

Low - SER values 140 dB <strong>and</strong> lower<br />

Medium - SER values between 141 <strong>and</strong> 179 dB<br />

High - SER values 180 dB <strong>and</strong> higher.<br />

These values are designed to provide a broad ranking <strong>of</strong> source audibility<br />

for <strong>the</strong> various source - species encounters considered under st<strong>and</strong>ardized<br />

conditions. These SER ratings are not based on behavioral observations <strong>and</strong><br />

are intended only as a means <strong>of</strong> ranking encounter situations where potential<br />

behavioral responses may occur.<br />

Only a limited number <strong>of</strong> behavioral studies are available to provide a<br />

means <strong>of</strong> calibrating this ranking scheme. Averaged results from gray whale<br />

disturbance studies using playback <strong>of</strong> several types <strong>of</strong> continuous noise from<br />

industrial sources (Malme et al. 1984) showed that 50% <strong>of</strong> <strong>the</strong> whales migrating<br />

through <strong>the</strong> test area avoided areas where sound levels were about 120 dB.<br />

Over 90% <strong>of</strong> <strong>the</strong> whales avoided <strong>the</strong> region near <strong>the</strong> source where sound levels<br />

were higher than 130 dB. Reviewing <strong>the</strong> results <strong>of</strong> <strong>the</strong> SER analysis for those<br />

areas where continuous source - gray whale encounters were considered provided<br />

<strong>the</strong> following results which show a comparison <strong>of</strong> <strong>the</strong> mean SER ratings with <strong>the</strong><br />

mean <strong>of</strong> <strong>the</strong> received levels at <strong>the</strong> reference range <strong>of</strong> 300 m for <strong>the</strong> various<br />

sources considered (<strong>the</strong> number <strong>of</strong> samples <strong>and</strong> <strong>the</strong> st<strong>and</strong>ard deviation are also<br />

shown) :<br />

SER Rank N Mean SER(~B) SD Mean Lrl(dB) SD<br />

High 2 18 1 - 138 -<br />

Medium 8 167 - 8 125 ' 7<br />

These results suggest that <strong>the</strong> SER ranking scheme is consistent with<br />

behavioral observations for at least one species. However, more acoustic

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