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Effects of Airgun Sounds on Bowhead Whale Calling Rates: Evidence for Two Behavioral Thresholds

机译:气枪声音对弓头鲸鸣叫率的影响:两个行为阈值的证据。

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摘要

In proximity to seismic operations, bowhead whales (Balaena mysticetus) decrease their calling rates. Here, we investigate the transition from normal calling behavior to decreased calling and identify two threshold levels of received sound from airgun pulses at which calling behavior changes. Data were collected in August–October 2007–2010, during the westward autumn migration in the Alaskan Beaufort Sea. Up to 40 directional acoustic recorders (DASARs) were deployed at five sites offshore of the Alaskan North Slope. Using triangulation, whale calls localized within 2 km of each DASAR were identified and tallied every 10 minutes each season, so that the detected call rate could be interpreted as the actual call production rate. Moreover, airgun pulses were identified on each DASAR, analyzed, and a cumulative sound exposure level was computed for each 10-min period each season (CSEL10-min). A Poisson regression model was used to examine the relationship between the received CSEL10-min from airguns and the number of detected bowhead calls. Calling rates increased as soon as airgun pulses were detectable, compared to calling rates in the absence of airgun pulses. After the initial increase, calling rates leveled off at a received CSEL10-min of ~94 dB re 1 μPa2-s (the lower threshold). In contrast, once CSEL10-min exceeded ~127 dB re 1 μPa2-s (the upper threshold), whale calling rates began decreasing, and when CSEL10-min values were above ~160 dB re 1 μPa2-s, the whales were virtually silent.
机译:在地震作业附近,弓头鲸(Balaena mysticetus)会降低鸣叫率。在这里,我们研究了从正常的通话行为到降低的通话行为的转变,并从气枪脉冲中识别出两个阈值水平的呼气行为发生变化的气枪脉冲。数据是在2007年8月至10月于阿拉斯加博福特海向西秋季迁移期间收集的。在阿拉斯加北坡近海的五个地点部署了多达40个定向声波记录器(DASAR)。使用三角测量法,每个季节每10分钟识别并定位在每个DASAR 2公里以内的鲸鱼鸣叫次数,以便将检测到的鸣叫率解释为实际鸣叫率。此外,在每个DASAR上识别气枪脉冲,进行分析,并计算每个季节的每10分钟(CSEL10分钟)的累积声暴露水平。使用Poisson回归模型来检查从气枪接收到的CSEL10分钟与检测到的弓头鸣叫次数之间的关系。与没有气枪脉冲时的呼叫率相比,一旦检测到气枪脉冲,呼叫率就会增加。初始增加后,呼叫速率在接收到的CSEL10分钟(〜94 dB,1μPa 2 -s)(较低的阈值)处趋于平稳。相反,一旦CSEL10-min超过〜127 dB re 1μPa 2 -s(上限阈值),鲸鱼的鸣叫率就会开始下降,当CSEL10-min值大于〜160 dB re 1μPa时就开始下降。 2 -s,鲸鱼几乎没有声音。

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