Muyang Wang, Yingying Zhuo, Alice C. Hughes, Weikang Yang
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However, it is increasingly evident that a more nuanced, ecologically based approach is necessary (Lucas et al. <span>2025</span>). In newly published research in <i>Global Change Biology</i>, Osmolovsky et al. (<span>2025</span>) investigate the longstanding proposition that species will move upslope or away from the equator under climate change, or rather, when and why this is not always the case. However, mounting evidence shows that this is frequently not the case, with over a third of species examined (20%–37%) showing “counterintuitive” responses (Rubenstein et al. <span>2023</span>). This challenges the longstanding view of the need to track climatic niches and undermines the ability of models to perform accurately. Understanding why this might occur is clearly crucial for grasping the impacts of climate change, including where and why this might occur, especially given differing responses across species, even within a single locality (Gibson-Reinemer and Rahel <span>2015</span>). Importantly, understanding that these responses are not merely “an exception” is crucial, not only because they represent a large proportion of all known responses, but because the mechanistic elements provide insights into how and why species respond differently.</p><p>Osmolovsky et al. highlight the potential role of biotic interactions as a mediating factor to explain these unanticipated shifts, proposing the ‘Interaction Opportunists Hypothesis’. This hypothesis highlights that counterintuitive shifts to climate change may reflect changes in biotic interactions at the warmer edge of species' distributions. Further, these changing interactions may manifest through a number of different mechanisms. Principally the study explores three forms of interaction: reduced antagonistic interactions, increased positive interactions, and changes in equilibrium due to shifts in competitive dynamics between species. Ultimately these changes would either increase the suitability of previously marginal habitats on the warmer edge of the range (i.e., increasing the abundance of key resources) or reduce pressures that previously prevented species from occupying these spaces (such as predation pressure).</p><p>The “stress trade-off hypothesis”, anticipates that the cooler edge of species ranges will be delimited by climate, whilst the warmer edge of the range will be determined by biotic interaction. As such, agonistic (negative) interactions, such as competition, or predation could potentially decrease on the warmer edge of the range, potentially as predators are more likely to be larger-bodied and therefore sensitive to climate change. In addition, warming climate may actively reverse generally antagonistic relationships to help increase the potential survival of the host under stress (as a harmful parasite or pathogen kills its host). However, only a limited number of studies have shown support for this. Furthermore, lags in responses may allow temporary persistence of a species in some of these spaces, further altering the interactions present; and further complicating patterns of response, and our ability to understand them.</p><p>Yet interpreting the drivers of range shift may be challenging. For example, most species have their realised niche truncated, either due to land-boundaries (and other physical barriers) or the loss of lower elevations of the range due to development, or other forms of use. Recovery of habitats in the lower elevations of the range can allow recolonisation of former range i.e., Himalayan plants following the cessation of grazing, or the downhill shift of the squirrel <i>Tamiasciurus hudsonicus</i> following the recovery of spruce forests (Morelli et al. <span>2025</span>). Basic analysis could suggest a counter-intuitive range shift in these cases, yet it is important to understand that range limits may be bounded by an array of factors, rather than climate, and alleviation of other threats may enable recolonisation or range expansion. This has fundamental implications for analysing the effects of climate change on species distributions, as even if species may track climate change, models based on truncated data will over-estimate the impacts of those changes.</p><p>Additionally, other characteristics and traits of species also likely need to be considered. For example, studies have shown that in anurans, climate extremes favor medium body sizes, selecting against very large or very small species (Feijó et al. <span>2023</span>), and this trend is present over temporal, spatial, and elevational gradients. For other taxa, a suite of traits has been shown to play a role in predicting responses (MacLean and Beissinger <span>2017</span>). Thus, ignoring key traits, as well as biotic interactions, will likely undermine our ability to predict responses to a changing climate. Furthermore, the mean elevation of occurrence is also likely related to key traits that play significant roles in determining species' responses (Mamantov et al. <span>2021</span>), though it should be noted that how traits may interact and their contribution in determining species range shifts remains an area that requires further work. Other important dimensions that need to be considered are changes in precipitation (which may not follow the same patterns as temperature) as well as changes in climate extremes and extreme events, which may lead to changes in distributional changes that do not correlate with mean changes in temperature (Latimer and Zuckerberg <span>2019</span>).</p><p>This myriad of different responses across space, time, and taxa highlights a number of key points. Firstly, simple correlative models are insufficient for understanding the impacts of climate change, highlighting the urgent need to re-examine our approaches to predicting the impact of climate change and, especially, to avoid over-reliance on models. Secondly, this reminds us of the need to better reflect species ecology in models, for example, better reproducing non-linear responses to changing climates and how the impacts manifest differently depending on when these changes occur (based on lifecycle) as well as how climate extremes impact distribution. Building on this, while experiments may be needed to better model thermal niches and changes in tolerance—especially in novel climates (Kearney and Porter <span>2020</span>)—further work will be necessary to translate these findings into natural environments, considering species interactions (Osmolovsky et al. <span>2025</span>). This is likely especially true in montane ecosystems. Furthermore, it should be noted that when climate change occurs and how it impacts other elements of the ecosystem (e.g., species phenology) has the potential to cause trophic cascades due to reliance on different cues to trigger phenological events, causing mismatches. How these interactions and shifts manifest on climate gradients is particularly complex, and more work will be needed to understand these interactions and their sensitivity to change.</p><p>Further work is clearly needed to build on these theories, and better understand how species interactions contribute to species' abilities not only to potentially withstand a changing climate, but also to potentially expand their ranges. Until we better understand what is limiting species ranges, and how species interactions play a part in this, predicting species future responses to changes in climate will likely continue to have high rates of error. Better understanding the role of biotic interactions is critical for improving forecasts of species' responses and vulnerabilities to changing climates, and thus apportioning resources to best meet species needs. The framework provided by Osmolovsky et al. (<span>2025</span>) is a solid step toward untangling yet another piece of the complex puzzle of understanding and predicting how species may respond to a changing climate, further refining our ability to understand, predict, and conserve species in a changing world.</p><p><b>Muyang Wang:</b> conceptualization, funding acquisition, project administration, supervision, writing – original draft, writing – review and editing. <b>Yingying Zhuo:</b> writing – original draft. <b>Alice C. Hughes:</b> writing – original draft, writing – review and editing. <b>Weikang Yang:</b> funding acquisition, writing – review and editing.</p><p>The authors declare no conflicts of interest.</p><p>This article is a Invited Commentary on Inna Osmolovsky et al. https://doi.org/10.1111/gcb.70332.</p>","PeriodicalId":175,"journal":{"name":"Global Change Biology","volume":"31 9","pages":""},"PeriodicalIF":12.0000,"publicationDate":"2025-09-04","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://onlinelibrary.wiley.com/doi/epdf/10.1111/gcb.70470","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Global Change Biology","FirstCategoryId":"93","ListUrlMain":"https://onlinelibrary.wiley.com/doi/10.1111/gcb.70470","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
Climate change poses one of the greatest threats to species survival in the 21st century. However, predicting species responses, identifying the most vulnerable species and locations, and determining effective conservation interventions remain significant challenges. Many studies employ correlative approaches to understand how species climate niches might be expected to shift under a changing climate by “tracking climate” and maintaining their climate niche. Species distribution models (SDMs) remain the primary tool for anticipating responses to climate change, yet most models are built on a straightforward correlation between current distribution points and prevailing environmental conditions. However, it is increasingly evident that a more nuanced, ecologically based approach is necessary (Lucas et al. 2025). In newly published research in Global Change Biology, Osmolovsky et al. (2025) investigate the longstanding proposition that species will move upslope or away from the equator under climate change, or rather, when and why this is not always the case. However, mounting evidence shows that this is frequently not the case, with over a third of species examined (20%–37%) showing “counterintuitive” responses (Rubenstein et al. 2023). This challenges the longstanding view of the need to track climatic niches and undermines the ability of models to perform accurately. Understanding why this might occur is clearly crucial for grasping the impacts of climate change, including where and why this might occur, especially given differing responses across species, even within a single locality (Gibson-Reinemer and Rahel 2015). Importantly, understanding that these responses are not merely “an exception” is crucial, not only because they represent a large proportion of all known responses, but because the mechanistic elements provide insights into how and why species respond differently.
Osmolovsky et al. highlight the potential role of biotic interactions as a mediating factor to explain these unanticipated shifts, proposing the ‘Interaction Opportunists Hypothesis’. This hypothesis highlights that counterintuitive shifts to climate change may reflect changes in biotic interactions at the warmer edge of species' distributions. Further, these changing interactions may manifest through a number of different mechanisms. Principally the study explores three forms of interaction: reduced antagonistic interactions, increased positive interactions, and changes in equilibrium due to shifts in competitive dynamics between species. Ultimately these changes would either increase the suitability of previously marginal habitats on the warmer edge of the range (i.e., increasing the abundance of key resources) or reduce pressures that previously prevented species from occupying these spaces (such as predation pressure).
The “stress trade-off hypothesis”, anticipates that the cooler edge of species ranges will be delimited by climate, whilst the warmer edge of the range will be determined by biotic interaction. As such, agonistic (negative) interactions, such as competition, or predation could potentially decrease on the warmer edge of the range, potentially as predators are more likely to be larger-bodied and therefore sensitive to climate change. In addition, warming climate may actively reverse generally antagonistic relationships to help increase the potential survival of the host under stress (as a harmful parasite or pathogen kills its host). However, only a limited number of studies have shown support for this. Furthermore, lags in responses may allow temporary persistence of a species in some of these spaces, further altering the interactions present; and further complicating patterns of response, and our ability to understand them.
Yet interpreting the drivers of range shift may be challenging. For example, most species have their realised niche truncated, either due to land-boundaries (and other physical barriers) or the loss of lower elevations of the range due to development, or other forms of use. Recovery of habitats in the lower elevations of the range can allow recolonisation of former range i.e., Himalayan plants following the cessation of grazing, or the downhill shift of the squirrel Tamiasciurus hudsonicus following the recovery of spruce forests (Morelli et al. 2025). Basic analysis could suggest a counter-intuitive range shift in these cases, yet it is important to understand that range limits may be bounded by an array of factors, rather than climate, and alleviation of other threats may enable recolonisation or range expansion. This has fundamental implications for analysing the effects of climate change on species distributions, as even if species may track climate change, models based on truncated data will over-estimate the impacts of those changes.
Additionally, other characteristics and traits of species also likely need to be considered. For example, studies have shown that in anurans, climate extremes favor medium body sizes, selecting against very large or very small species (Feijó et al. 2023), and this trend is present over temporal, spatial, and elevational gradients. For other taxa, a suite of traits has been shown to play a role in predicting responses (MacLean and Beissinger 2017). Thus, ignoring key traits, as well as biotic interactions, will likely undermine our ability to predict responses to a changing climate. Furthermore, the mean elevation of occurrence is also likely related to key traits that play significant roles in determining species' responses (Mamantov et al. 2021), though it should be noted that how traits may interact and their contribution in determining species range shifts remains an area that requires further work. Other important dimensions that need to be considered are changes in precipitation (which may not follow the same patterns as temperature) as well as changes in climate extremes and extreme events, which may lead to changes in distributional changes that do not correlate with mean changes in temperature (Latimer and Zuckerberg 2019).
This myriad of different responses across space, time, and taxa highlights a number of key points. Firstly, simple correlative models are insufficient for understanding the impacts of climate change, highlighting the urgent need to re-examine our approaches to predicting the impact of climate change and, especially, to avoid over-reliance on models. Secondly, this reminds us of the need to better reflect species ecology in models, for example, better reproducing non-linear responses to changing climates and how the impacts manifest differently depending on when these changes occur (based on lifecycle) as well as how climate extremes impact distribution. Building on this, while experiments may be needed to better model thermal niches and changes in tolerance—especially in novel climates (Kearney and Porter 2020)—further work will be necessary to translate these findings into natural environments, considering species interactions (Osmolovsky et al. 2025). This is likely especially true in montane ecosystems. Furthermore, it should be noted that when climate change occurs and how it impacts other elements of the ecosystem (e.g., species phenology) has the potential to cause trophic cascades due to reliance on different cues to trigger phenological events, causing mismatches. How these interactions and shifts manifest on climate gradients is particularly complex, and more work will be needed to understand these interactions and their sensitivity to change.
Further work is clearly needed to build on these theories, and better understand how species interactions contribute to species' abilities not only to potentially withstand a changing climate, but also to potentially expand their ranges. Until we better understand what is limiting species ranges, and how species interactions play a part in this, predicting species future responses to changes in climate will likely continue to have high rates of error. Better understanding the role of biotic interactions is critical for improving forecasts of species' responses and vulnerabilities to changing climates, and thus apportioning resources to best meet species needs. The framework provided by Osmolovsky et al. (2025) is a solid step toward untangling yet another piece of the complex puzzle of understanding and predicting how species may respond to a changing climate, further refining our ability to understand, predict, and conserve species in a changing world.
Muyang Wang: conceptualization, funding acquisition, project administration, supervision, writing – original draft, writing – review and editing. Yingying Zhuo: writing – original draft. Alice C. Hughes: writing – original draft, writing – review and editing. Weikang Yang: funding acquisition, writing – review and editing.
The authors declare no conflicts of interest.
This article is a Invited Commentary on Inna Osmolovsky et al. https://doi.org/10.1111/gcb.70332.
气候变化是21世纪物种生存面临的最大威胁之一。然而,预测物种的反应,确定最脆弱的物种和地点,以及确定有效的保护措施仍然是重大的挑战。许多研究采用相关的方法,通过“跟踪气候”和维持物种的气候生态位来了解物种气候生态位在气候变化下的变化。物种分布模型(SDMs)仍然是预测气候变化响应的主要工具,然而大多数模型都是建立在当前分布点与当时环境条件之间的直接相关性上的。然而,越来越明显的是,一种更细微的、基于生态的方法是必要的(Lucas et al. 2025)。在最近发表在《全球变化生物学》上的研究中,Osmolovsky等人(2025)调查了一个长期存在的命题,即在气候变化下,物种将向上坡或远离赤道移动,或者更确切地说,何时以及为什么情况并非总是如此。然而,越来越多的证据表明,情况往往并非如此,超过三分之一的被调查物种(20%-37%)表现出“违反直觉”的反应(Rubenstein et al. 2023)。这挑战了长期以来关于需要跟踪气候生态位的观点,并破坏了模型准确执行的能力。理解为什么会发生这种情况显然对掌握气候变化的影响至关重要,包括在哪里以及为什么会发生这种情况,特别是考虑到物种之间的不同反应,甚至在一个地方(Gibson-Reinemer和Rahel 2015)。重要的是,理解这些反应不仅仅是“例外”是至关重要的,不仅因为它们代表了所有已知反应的很大一部分,而且因为机械因素提供了对物种如何以及为什么会有不同反应的见解。Osmolovsky等人强调了生物相互作用作为解释这些意外变化的中介因素的潜在作用,提出了“相互作用机会主义者假说”。这一假设强调,气候变化的反直觉转变可能反映了物种分布较温暖边缘的生物相互作用的变化。此外,这些变化的相互作用可能通过许多不同的机制表现出来。该研究主要探讨了三种形式的相互作用:减少拮抗相互作用,增加积极相互作用,以及由于物种之间竞争动态的变化而导致的平衡变化。最终,这些变化要么会增加以前边缘栖息地在温暖边缘的适宜性(即增加关键资源的丰度),要么会减少以前阻止物种占据这些空间的压力(如捕食压力)。“压力权衡假说”预测,物种范围较冷的边缘将由气候划定,而范围较暖的边缘将由生物相互作用决定。因此,竞争或捕食等竞争(消极)相互作用可能会在更温暖的边缘地区减少,因为捕食者更有可能体型更大,因此对气候变化敏感。此外,气候变暖可能积极地逆转一般的拮抗关系,以帮助增加宿主在压力下的潜在存活率(如有害的寄生虫或病原体杀死其宿主)。然而,只有有限数量的研究支持这一观点。此外,响应的滞后可能允许一个物种在某些空间中暂时存在,进一步改变现有的相互作用;以及更复杂的反应模式,以及我们理解它们的能力。然而,解释范围转换的驱动因素可能具有挑战性。例如,由于陆地边界(和其他物理障碍)或由于开发或其他形式的利用而使范围的较低海拔丧失,大多数物种的已实现生态位被截断。低海拔地区栖息地的恢复可以让以前的栖息地重新定居,例如,停止放牧后的喜马拉雅植物,或者在云杉林恢复后,松鼠Tamiasciurus hudsonicus的下坡迁移(Morelli et al. 2025)。基本分析可能表明,在这些情况下,与直觉相反的范围转移,但重要的是要理解,范围限制可能受到一系列因素的限制,而不是气候,减轻其他威胁可能会使重新殖民或范围扩大。这对于分析气候变化对物种分布的影响具有根本性的意义,因为即使物种可以跟踪气候变化,基于截断数据的模型也会高估这些变化的影响。此外,物种的其他特征和特征也可能需要考虑。 例如,研究表明,在无尾动物中,极端气候倾向于中等体型,而不是非常大或非常小的物种(Feijó等,2023),这种趋势在时间、空间和海拔梯度上都存在。对于其他分类群,一系列特征已被证明在预测反应中发挥作用(MacLean和Beissinger 2017)。因此,忽略关键特征以及生物相互作用,可能会破坏我们预测对气候变化的反应的能力。此外,发生的平均海拔也可能与在决定物种反应中发挥重要作用的关键性状有关(Mamantov et al. 2021),尽管应该注意的是,性状如何相互作用及其在决定物种范围变化中的贡献仍然是一个需要进一步研究的领域。需要考虑的其他重要方面是降水的变化(可能与温度的模式不同)以及极端气候和极端事件的变化,这可能导致与平均温度变化无关的分布变化的变化(Latimer和Zuckerberg 2019)。这种跨越空间、时间和分类群的无数不同的反应突出了一些关键点。首先,简单的相关模型不足以理解气候变化的影响,迫切需要重新审视我们预测气候变化影响的方法,特别是避免过度依赖模型。其次,这提醒我们需要在模型中更好地反映物种生态学,例如,更好地再现对气候变化的非线性响应,以及这些影响如何根据这些变化发生的时间(基于生命周期)表现不同,以及极端气候如何影响分布。在此基础上,虽然可能需要实验来更好地模拟热生态位和耐受性的变化-特别是在新的气候条件下(Kearney和Porter 2020) -将这些发现转化为自然环境将需要进一步的工作,考虑到物种的相互作用(Osmolovsky et al. 2025)。在山地生态系统中尤其如此。此外,应该指出的是,当气候变化发生时,以及它如何影响生态系统的其他要素(例如物种物候学),由于依赖不同的线索触发物候事件,导致不匹配,有可能导致营养级联。这些相互作用和变化如何表现在气候梯度上是特别复杂的,需要更多的工作来了解这些相互作用及其对变化的敏感性。显然需要进一步的工作来建立这些理论,并更好地了解物种之间的相互作用如何不仅有助于物种抵御气候变化的能力,而且还有助于扩大它们的范围。在我们更好地了解是什么限制了物种的范围,以及物种之间的相互作用如何在其中发挥作用之前,预测物种未来对气候变化的反应可能会继续有很高的错误率。更好地理解生物相互作用的作用对于改善物种对气候变化的反应和脆弱性的预测,从而分配资源以最好地满足物种需求至关重要。Osmolovsky等人(2025)提供的框架是解开理解和预测物种如何应对气候变化这一复杂难题的又一个坚实步骤,进一步提高了我们在不断变化的世界中理解、预测和保护物种的能力。王牧阳:项目构思、资金获取、项目管理、监督、撰写-原稿、撰写-审稿、编辑。卓莹颖:写作-原稿。Alice C. Hughes:写作-原稿,写作-评论和编辑。杨维康:资金筹措、撰写、评审、编辑。作者声明无利益冲突。这篇文章是Inna Osmolovsky等人https://doi.org/10.1111/gcb.70332的特邀评论。
期刊介绍:
Global Change Biology is an environmental change journal committed to shaping the future and addressing the world's most pressing challenges, including sustainability, climate change, environmental protection, food and water safety, and global health.
Dedicated to fostering a profound understanding of the impacts of global change on biological systems and offering innovative solutions, the journal publishes a diverse range of content, including primary research articles, technical advances, research reviews, reports, opinions, perspectives, commentaries, and letters. Starting with the 2024 volume, Global Change Biology will transition to an online-only format, enhancing accessibility and contributing to the evolution of scholarly communication.