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The Ecology, Sonic Environment, and Acoustic Occurrence of Subarctic Baleen Whales in the Bering Strait over a Decade of Change

机译:十年来白令海峡亚北极须鲸的生态学、声波环境和声学分布

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摘要

The southern Chukchi Sea is a productive, shallow continental shelf ecosystem that is undergoing rapid change due to climate warming. Annual sea ice cover has declined significantly, potentially allowing for more temperate species to move further north into the Arctic and stay for longer periods. Monitoring the presence and occupation patterns of top predators, such as baleen whales, is important for detecting shifts in species assemblages and distributions in response to climate change. This dissertation examines the acoustic occurrence of three subarctic baleen whales in the Chukchi Sea—fin whales (Balaenoptera physalus), humpback whales (Megaptera novaeangliae), and gray whales (Eschrichtius robustus)—and seeks to uncover patterns in their presence, the environmental drivers that draw them into the Arctic, and how ships affect the acoustic habitat of the region during the open-water season. In Chapter 2, I use acoustic recordings from three moored hydrophones in the Bering Strait region from 2009–2015 to identify fin whale calls during the open-water season (July–November) and investigate the potential influence of local environmental conditions on fin whale presence. The results show significant interannual variability in the acoustic presence of fin whales with the greatest detections of calls in years with contrasting environmental conditions (2012 and 2015). Colder temperatures, lower salinities, slower water velocities, and weak southward winds prevailed in 2012 while warmer temperatures, higher salinities, faster water velocities, and moderate southward winds prevailed in 2015. Most detections (96%) were recorded at the mooring site, Site A3, nearest the confluence of the nutrient-rich Anadyr and Bering Shelf water masses, ~ 35 km north of Bering Strait, indicating that productive water masses may influence the occurrence of fin whales.In Chapter 3, I expanded my efforts to include humpback and gray whales and added two years of acoustic and environment data, 2017 and 2018, to the dataset from Chapter 2. Using recordings and in situ environmental data from Site A3 collected from 2009 to 2018, I identified fin, humpback, and gray whale calls during the open-water season (May–December), and examined the timing of migration as well as investigated potential environmental drivers of whale presence. The acoustic presence of humpback and fin whales varied across the years with the highest occurrence of humpback calls in 2009, 2017, and 2018 and the highest occurrence of fin whale calls in 2015, 2017, and 2018. The years 2013 and 2015 had the highest proportion of recordings with gray whale calls. Fin whales had significantly later departure dates during the study period (~ 3 days yr-1, p = 0.02), likely on account of warmer temperatures in the Chukchi Sea in the later years of the study (2017 and 2018). Individual models for the three species identified day of the year, sea-surface temperatures, near-bottom temperatures, and the presence of a thermal front the previous month as drivers of fin, humpback, and gray whale presence.In Chapter 4, I characterized ship activity in the Bering Strait during the open-water season (July?November) for 2013?2015 and quantified the impact of ship noise on third-octave frequency bands used by baleen whales (25?1000 Hz). Peak ship activity occurred in July?September with the greatest overlap in ship noise and whale vocalizations observed in October. Ships elevated sound levels by ~ 4 dB on average for all third-octave frequency bands combined, and sound levels exceeding 100 dB re 1 μPa for the 250-Hz third-octave frequency band were recorded from two large vessels over 11 km away from the hydrophones. The results show that ship noise has the potential to impact baleen whales in the Bering Strait and serve as a baseline for measuring future impacts of ship activity in the region.Overall, the results presented within this dissertation provide a snapshot of the presence of subarctic baleen wh
机译:楚科奇海南部是一个多产的浅层大陆架生态系统,由于气候变暖,它正在经历快速变化。年度海冰覆盖率已显著下降,这可能使更多的温带物种能够进一步向北移动到北极并停留更长的时间。监测须鲸等顶级捕食者的存在和占领模式,对于检测响应气候变化的物种组合和分布变化非常重要。本论文研究了楚科奇海三种亚北极须鲸的声学分布——长须鲸 (Balaenoptera physalus)、座头鲸 (Megaptera novaeangliae) 和灰鲸 (Eschrichtius robustus),并试图揭示它们存在的模式、将它们吸引到北极的环境驱动因素,以及船只在开阔水域季节如何影响该地区的声学栖息地。在第 2 章中,我使用了 2009 年至 2015 年白令海峡地区三个系泊水听器的声学记录来识别开阔水域(7 月至 11 月)期间长须鲸的叫声,并调查当地环境条件对长须鲸存在的潜在影响。结果显示,长须鲸的声学存在显着的年际变化,在环境条件对比鲜明的年份(2012 年和 2015 年)中检测到的叫声最多。2012 年气温较低、盐度较低、水速较慢和南风较弱,而 2015 年气温较高、盐度较高、水速较快和适度南风盛行。大多数探测到 (96%) 是在系泊地点 A3 记录的,该地点最靠近营养丰富的 Anadyr 和 Bering Shelf 水团的交汇处,位于白令海峡以北 ~ 35 公里处,这表明生产性水团可能会影响长须鲸的出现。在第 3 章中,我扩大了工作范围,将座头鲸和灰鲸纳入其中,并在第 2 章的数据集中添加了 2017 年和 2018 年的两年声学和环境数据。使用 2009 年至 2018 年从 Site A3 收集的录音和原位环境数据,我确定了开阔水域季节(5 月至 12 月)的鳍鲸、座头鲸和灰鲸的叫声,并检查了迁徙的时间以及调查了鲸鱼存在的潜在环境驱动因素。座头鲸和长须鲸的声学存在多年来各不相同,2009 年、2017 年和 2018 年座头鲸叫声的发生率最高,2015 年、2017 年和 2018 年长须鲸叫声的发生率最高。2013 年和 2015 年灰鲸叫声的录音比例最高。长须鲸在研究期间的出发日期明显较晚(~ 3 天 yr-1,p = 0.02),这可能是由于研究后期(2017 年和 2018 年)楚科奇海的温度较高。这三个物种的单个模型确定了一年中的日期、海面温度、近海底温度以及上个月热锋的存在,这些都是长鳍鲸、座头鲸和灰鲸存在的驱动因素。在第 4 章中,我描述了开阔水域季节(7 月?November) 进行 2013-2015 年,并量化了船舶噪声对须鲸使用的第三倍频程频段 (25?1000 Hz) 的影响。船舶活动高峰发生在 7 月?9 月,10 月观察到的船舶噪音和鲸鱼发声重叠最大。船舶将所有第三倍频程频段的声级平均提高了 ~ 4 dB,并且在距离水听器超过 11 公里的两艘大型船只上记录到的 250 Hz 第三倍频程频段的声级超过 100 dB re 1 μPa。结果表明,船舶噪音有可能影响白令海峡的须鲸,并作为衡量该地区船舶活动未来影响的基线。总体而言,本论文中介绍的结果提供了亚北极须 wh 存在的快照

著录项

  • 作者

    Escajeda, Erica Danielle.;

  • 作者单位

    University of Washington.;

    University of Washington.;

    University of Washington.;

  • 授予单位 University of Washington.;University of Washington.;University of Washington.;
  • 学科 Ecology.;Acoustics.;Zoology.;Aquatic sciences.
  • 学位
  • 年度 2023
  • 页码 226
  • 总页数 226
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    Ecology.; Acoustics.; Zoology.; Aquatic sciences.;

    机译:生态学。;声学。;动物学。;水生科学。;
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