Christopher D. H. Thompson, Jessica J. Meeuwig, Alan M. Friedlander, Enric Sala
{"title":"Remote seamounts are key conservation priorities for pelagic wildlife","authors":"Christopher D. H. Thompson, Jessica J. Meeuwig, Alan M. Friedlander, Enric Sala","doi":"10.1111/conl.12993","DOIUrl":null,"url":null,"abstract":"<p>The pelagic ocean is Earth's largest habitat, constituting 99% of the global biosphere by volume, directly or indirectly supporting most marine life, and supplying the majority of fish consumed by humans (Game et al., <span>2009</span>; Pauly et al., <span>2002</span>). However, the world's pelagic fauna is globally declining largely as a result of unsustainable fishing (Pauly & Zeller, <span>2016</span>). Industrial fishing has reduced the populations of tunas and their relatives by 60% and of oceanic sharks and rays by 71% over the past half century (Juan-Jordá et al., <span>2011</span>; Pacoureau et al., <span>2021</span>). Declines in pelagic wildlife weaken ecosystem functioning, drive biodiversity loss, and undermine food security and economic stability for many of the world's people.</p><p>Remote regions of the ocean that remain less impacted by humans are refuges for mobile and heavily targeted species. These regions harbor wildlife assemblages with higher diversity, greater abundance, larger size, and increased biomass, and can yield valuable insights into ecological processes (Campbell et al., <span>2020</span>; Juhel et al., <span>2019</span>; Thompson & Meeuwig, <span>2022</span>). Remote regions offer a glimpse of what the ocean was like prior to large-scale anthropogenic impact, a source from which the rest of the ocean can be regenerated, and a benchmark for marine protected areas (MPAs) and fisheries management. However, with human impacts now extending across the global ocean (Halpern et al., <span>2008</span>; Tickler et al., <span>2018</span>), remote areas are increasingly threatened. Urgent attention is required to ensure that remote regions avoid mirroring the degradation seen in areas more proximate to humans.</p><p>Our knowledge of the pelagic ocean remains limited relative to shallow coastal habitats, making prioritizing conservation efforts difficult. This is especially the case in remote regions where scientific information is even more scarce. We do know, however, that pelagic species associate strongly with bathymetric features such as seamounts, undersea canyons, and oceanic islands (Bouchet, <span>2015</span>; Morato et al., <span>2010</span>; Thompson et al., <span>2021</span>). Both physical and biological drivers make these features important locations for foraging, reproduction, navigation, and other essential functions of pelagic wildlife (Garrigue et al., <span>2015</span>; Maguire et al., <span>2023</span>; Rogers, <span>2018</span>). Seamounts are particularly important to large pelagic animals and often hold relatively high densities of threatened and commercially important species such as sharks, tunas, and billfishes, some of which are generally highly mobile but show high residency at these features (Morato et al., <span>2008</span>; Wright et al., <span>2021</span>). However, the high economic value and conservative life histories of these species mean fishing can quickly decimate seamount communities. As such, seamount communities proximate to humans often become degraded first (Clark, <span>1999</span>).</p><p>There are an estimated 37,889 seamounts in the global ocean, yet less than 4% have been surveyed (Yesson et al., <span>2021</span>; Figure 1). Moreover, less than 6% are located in fully and highly protected MPAs (mpatlas.org; Grorud-Colvert et al., <span>2021</span>). The protection of seamounts thus represents a significant conservation opportunity. Importantly, different bathymetric structures support distinct assemblages (Thompson et al., <span>2021</span>) and thus a range of remote structures should be included to ensure representative protection. The protection of subsurface features will benefit pelagic biodiversity, as well as providing significant benefits in the conservation of important demersal fish assemblages (Galbraith et al., <span>2021</span>) and many vulnerable benthic marine ecosystems such as deep reef communities given their higher concentration at these features (Rogers, <span>2018</span>). Many seamounts, including those proximate to human populations, have significant biodiversity conservation value (Morato et al., <span>2010</span>). However, we argue that remote seamounts where degradation has been limited to date are priorities for protection given the high abundance of targeted species present and the disproportionate contribution that such places make to biodiversity and our understanding of how human impact is transforming our oceans.</p><p>Well-designed and well-managed highly protected MPAs demonstrably halt and reverse declines in ocean wildlife, increase fisheries yields in adjacent waters, and enhance resilience to climate change (Edgar et al., <span>2014</span>; Roberts et al., <span>2017</span>; Sala & Giakoumi, <span>2018</span>). The combination of remoteness and large-scale protection is particularly effective in biodiversity conservation (Juhel et al., <span>2018</span>) and large fully and highly protected MPAs contribute significantly to seamount protection within EEZs. There is ample scientific evidence of the need to protect at least 30% of land and sea by 2030 (Dinerstein et al., <span>2019</span>; O'Leary et al., <span>2016</span>), a commitment now made in the Kunming–Montreal Global Biodiversity Framework, ratified in December 2022. The United Nations General Assembly has also recently established a treaty to facilitate conservation and sustainable use of marine biodiversity in areas beyond national jurisdiction (ABNJs; Stokstad, <span>2023</span>; United Nations General Assembly, <span>2023</span>). This instrument provides a legal framework for the implementation of MPAs in ABNJs. With 58% of seamounts located in ABNJs, and less than 1% of these in highly protected MPAs, remote seamounts are a prime target to deliver on biodiversity conservation commitments. Moreover, recent multinational treaties have recognized the importance of these features and are collaborating to protect areas both across national and international waters. For example, the Eastern Tropical Pacific Marine Corridor (CMAR) initiative extends across islands, coasts, and seamount chains in the Exclusive Economic Zones (EEZs) of Costa Rica, Panamá, Colombia, and Ecuador. Perú and Chile are also working together to protect the Nazca and Salas y Gómez Ridge system, which stretches across their EEZs and the international waters between them (Wagner et al., <span>2021</span>). These progressive steps provide a clear and positive example of how collaboration among countries is possible and can protect valuable marine habitats.</p><p>Increasing threats and growing recognition of the importance of the natural world have strengthened and necessitated the demand for protection of natural environments globally. The high density of life and residency of, generally highly mobile, pelagic fauna at remote seamounts make these locations prone to anthropogenic destruction but also ideal targets for conservation (Morato et al., <span>2010</span>; Wright et al., <span>2021</span>). Given the body of evidence on the importance of remote seamounts, their protection is a critical step in sustaining pelagic wildlife populations and will benefit the many species that utilize them, including ourselves.</p>","PeriodicalId":157,"journal":{"name":"Conservation Letters","volume":"17 1","pages":""},"PeriodicalIF":7.7000,"publicationDate":"2023-11-20","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://onlinelibrary.wiley.com/doi/epdf/10.1111/conl.12993","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Conservation Letters","FirstCategoryId":"93","ListUrlMain":"https://onlinelibrary.wiley.com/doi/10.1111/conl.12993","RegionNum":1,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"BIODIVERSITY CONSERVATION","Score":null,"Total":0}
引用次数: 0
Abstract
The pelagic ocean is Earth's largest habitat, constituting 99% of the global biosphere by volume, directly or indirectly supporting most marine life, and supplying the majority of fish consumed by humans (Game et al., 2009; Pauly et al., 2002). However, the world's pelagic fauna is globally declining largely as a result of unsustainable fishing (Pauly & Zeller, 2016). Industrial fishing has reduced the populations of tunas and their relatives by 60% and of oceanic sharks and rays by 71% over the past half century (Juan-Jordá et al., 2011; Pacoureau et al., 2021). Declines in pelagic wildlife weaken ecosystem functioning, drive biodiversity loss, and undermine food security and economic stability for many of the world's people.
Remote regions of the ocean that remain less impacted by humans are refuges for mobile and heavily targeted species. These regions harbor wildlife assemblages with higher diversity, greater abundance, larger size, and increased biomass, and can yield valuable insights into ecological processes (Campbell et al., 2020; Juhel et al., 2019; Thompson & Meeuwig, 2022). Remote regions offer a glimpse of what the ocean was like prior to large-scale anthropogenic impact, a source from which the rest of the ocean can be regenerated, and a benchmark for marine protected areas (MPAs) and fisheries management. However, with human impacts now extending across the global ocean (Halpern et al., 2008; Tickler et al., 2018), remote areas are increasingly threatened. Urgent attention is required to ensure that remote regions avoid mirroring the degradation seen in areas more proximate to humans.
Our knowledge of the pelagic ocean remains limited relative to shallow coastal habitats, making prioritizing conservation efforts difficult. This is especially the case in remote regions where scientific information is even more scarce. We do know, however, that pelagic species associate strongly with bathymetric features such as seamounts, undersea canyons, and oceanic islands (Bouchet, 2015; Morato et al., 2010; Thompson et al., 2021). Both physical and biological drivers make these features important locations for foraging, reproduction, navigation, and other essential functions of pelagic wildlife (Garrigue et al., 2015; Maguire et al., 2023; Rogers, 2018). Seamounts are particularly important to large pelagic animals and often hold relatively high densities of threatened and commercially important species such as sharks, tunas, and billfishes, some of which are generally highly mobile but show high residency at these features (Morato et al., 2008; Wright et al., 2021). However, the high economic value and conservative life histories of these species mean fishing can quickly decimate seamount communities. As such, seamount communities proximate to humans often become degraded first (Clark, 1999).
There are an estimated 37,889 seamounts in the global ocean, yet less than 4% have been surveyed (Yesson et al., 2021; Figure 1). Moreover, less than 6% are located in fully and highly protected MPAs (mpatlas.org; Grorud-Colvert et al., 2021). The protection of seamounts thus represents a significant conservation opportunity. Importantly, different bathymetric structures support distinct assemblages (Thompson et al., 2021) and thus a range of remote structures should be included to ensure representative protection. The protection of subsurface features will benefit pelagic biodiversity, as well as providing significant benefits in the conservation of important demersal fish assemblages (Galbraith et al., 2021) and many vulnerable benthic marine ecosystems such as deep reef communities given their higher concentration at these features (Rogers, 2018). Many seamounts, including those proximate to human populations, have significant biodiversity conservation value (Morato et al., 2010). However, we argue that remote seamounts where degradation has been limited to date are priorities for protection given the high abundance of targeted species present and the disproportionate contribution that such places make to biodiversity and our understanding of how human impact is transforming our oceans.
Well-designed and well-managed highly protected MPAs demonstrably halt and reverse declines in ocean wildlife, increase fisheries yields in adjacent waters, and enhance resilience to climate change (Edgar et al., 2014; Roberts et al., 2017; Sala & Giakoumi, 2018). The combination of remoteness and large-scale protection is particularly effective in biodiversity conservation (Juhel et al., 2018) and large fully and highly protected MPAs contribute significantly to seamount protection within EEZs. There is ample scientific evidence of the need to protect at least 30% of land and sea by 2030 (Dinerstein et al., 2019; O'Leary et al., 2016), a commitment now made in the Kunming–Montreal Global Biodiversity Framework, ratified in December 2022. The United Nations General Assembly has also recently established a treaty to facilitate conservation and sustainable use of marine biodiversity in areas beyond national jurisdiction (ABNJs; Stokstad, 2023; United Nations General Assembly, 2023). This instrument provides a legal framework for the implementation of MPAs in ABNJs. With 58% of seamounts located in ABNJs, and less than 1% of these in highly protected MPAs, remote seamounts are a prime target to deliver on biodiversity conservation commitments. Moreover, recent multinational treaties have recognized the importance of these features and are collaborating to protect areas both across national and international waters. For example, the Eastern Tropical Pacific Marine Corridor (CMAR) initiative extends across islands, coasts, and seamount chains in the Exclusive Economic Zones (EEZs) of Costa Rica, Panamá, Colombia, and Ecuador. Perú and Chile are also working together to protect the Nazca and Salas y Gómez Ridge system, which stretches across their EEZs and the international waters between them (Wagner et al., 2021). These progressive steps provide a clear and positive example of how collaboration among countries is possible and can protect valuable marine habitats.
Increasing threats and growing recognition of the importance of the natural world have strengthened and necessitated the demand for protection of natural environments globally. The high density of life and residency of, generally highly mobile, pelagic fauna at remote seamounts make these locations prone to anthropogenic destruction but also ideal targets for conservation (Morato et al., 2010; Wright et al., 2021). Given the body of evidence on the importance of remote seamounts, their protection is a critical step in sustaining pelagic wildlife populations and will benefit the many species that utilize them, including ourselves.
中上层海洋是地球上最大的栖息地,占全球生物圈总量的99%,直接或间接支持大多数海洋生物,并供应人类消费的大部分鱼类(Game et al., 2009;Pauly et al., 2002)。然而,由于不可持续的捕捞,世界上的远洋动物在全球范围内正在减少(Pauly &泽勒,2016)。在过去的半个世纪里,工业化捕鱼使金枪鱼及其近亲的数量减少了60%,海洋鲨鱼和鳐鱼的数量减少了71% (juan - jord<e:1>等人,2011;Pacoureau et al., 2021)。远洋野生动物的减少削弱了生态系统功能,导致生物多样性丧失,并破坏了世界上许多人的粮食安全和经济稳定。受人类影响较小的海洋偏远地区是流动和重点目标物种的避难所。这些地区拥有多样性更高、丰度更高、规模更大、生物量更高的野生动物群落,可以对生态过程产生有价值的见解(Campbell et al., 2020;Juhel et al., 2019;汤普森,Meeuwig, 2022)。偏远地区让人们得以一窥大规模人为影响之前的海洋面貌,是海洋其他部分得以再生的来源,也是海洋保护区和渔业管理的基准。然而,随着人类影响现在扩展到全球海洋(Halpern et al., 2008;Tickler等人,2018),偏远地区受到的威胁越来越大。需要紧急注意,以确保偏远地区避免出现与人类更接近的地区出现的退化现象。相对于浅海栖息地,我们对远洋海洋的了解仍然有限,这使得优先保护工作变得困难。在科学信息更加匮乏的偏远地区尤其如此。然而,我们确实知道,远洋物种与海底山、海底峡谷和海洋岛屿等深海特征密切相关(Bouchet, 2015;Morato et al., 2010;Thompson et al., 2021)。物理和生物驱动因素使这些特征成为觅食、繁殖、导航和其他重要功能的重要场所(Garrigue et al., 2015;Maguire et al., 2023;罗杰斯,2018)。海底山对大型远洋动物尤其重要,通常拥有相对高密度的受威胁和商业上重要的物种,如鲨鱼、金枪鱼和长嘴鱼,其中一些通常是高流动性的,但在这些特征上显示出很高的居住率(Morato等人,2008;Wright et al., 2021)。然而,这些物种的高经济价值和保守的生活史意味着捕捞会迅速摧毁海底山群落。因此,靠近人类的海底山群落往往首先退化(Clark, 1999)。据估计,全球海洋中有37,889个海山,但只有不到4%被调查过(Yesson et al., 2021;此外,不到6%位于完全和高度保护的海洋保护区(mpatlas.org;groud - colvert et al., 2021)。因此,海底山的保护是一个重要的保护机会。重要的是,不同的水深结构支持不同的组合(Thompson等,2021),因此应该包括一系列远程结构,以确保代表性保护。对地下特征的保护将有利于远洋生物多样性,并为保护重要的底栖鱼类群落(Galbraith et al., 2021)和许多脆弱的底栖海洋生态系统(如深礁群落)提供重大好处,因为它们在这些特征上的浓度更高(Rogers, 2018)。许多海山,包括靠近人类种群的海山,具有重要的生物多样性保护价值(Morato et al., 2010)。然而,我们认为,考虑到目标物种的高丰度,以及这些地方对生物多样性的不成比例的贡献,以及我们对人类影响如何改变海洋的理解,迄今为止退化有限的偏远海山是保护的重点。图1打开图形查看器powerpoint全球海洋保护区(浅绿色;unep - wcmc,IUCN, 2022)与Yesson等人(2020)定义的海底山(蓝色三角形)的全球分布重叠。这种分布显示了沿构造边界和海底地质活跃部分的集中。设计良好、管理良好、受到高度保护的海洋保护区可以明显阻止和扭转海洋野生动物数量的下降,增加邻近水域的渔业产量,并增强对气候变化的适应能力(Edgar et al., 2014;Roberts et al., 2017;萨拉,Giakoumi, 2018)。偏远和大规模保护的结合在生物多样性保护中特别有效(Juhel et al., 2018),大型全面和高度保护的海洋保护区对专属经济区内的海底山保护做出了重大贡献。 有充分的科学证据表明,到2030年需要保护至少30%的陆地和海洋(Dinerstein等人,2019;O’leary et al., 2016),这一承诺现已在2022年12月批准的《昆明-蒙特利尔全球生物多样性框架》中作出。联合国大会最近还制定了一项条约,以促进国家管辖范围以外地区海洋生物多样性的养护和可持续利用(ABNJs;Stokstad, 2023;联合国大会,2023年)。该文书为在非洲国家保护区实施海洋保护区提供了法律框架。由于58%的海底山位于ABNJs,其中不到1%位于高度保护的海洋保护区,偏远的海底山是实现生物多样性保护承诺的主要目标。此外,最近的多国条约已经认识到这些特征的重要性,并正在合作保护国家和国际水域的区域。例如,东热带太平洋海洋走廊(CMAR)倡议横跨哥斯达黎加、巴拿马、哥伦比亚和厄瓜多尔专属经济区(eez)的岛屿、海岸和海山链。Perú和智利还共同努力保护纳斯卡和萨拉斯Gómez海脊系统,该系统横跨两国的专属经济区及其之间的国际水域(Wagner et al., 2021)。这些渐进的步骤提供了一个明确和积极的例子,说明国家之间的合作是可能的,并且可以保护宝贵的海洋栖息地。日益增加的威胁和对自然世界重要性的日益认识,加强了对全球自然环境保护的要求,并使之成为必要。在偏远的海底山,高密度的生物和通常高度流动的远洋动物的居住使这些地点容易受到人为破坏,但也是理想的保护目标(Morato等人,2010;Wright et al., 2021)。鉴于有关偏远海底山重要性的大量证据,对它们的保护是维持远洋野生动物种群的关键一步,并将使利用它们的许多物种受益,包括我们自己。
期刊介绍:
Conservation Letters is a reputable scientific journal that is devoted to the publication of both empirical and theoretical research that has important implications for the conservation of biological diversity. The journal warmly invites submissions from various disciplines within the biological and social sciences, with a particular interest in interdisciplinary work. The primary aim is to advance both pragmatic conservation objectives and scientific knowledge. Manuscripts are subject to a rapid communication schedule, therefore they should address current and relevant topics. Research articles should effectively communicate the significance of their findings in relation to conservation policy and practice.