Radomski Tom
Tyson Research Center, Washington University in Saint Louis, 6750 Tyson Valley Road, Eureka, MO, 63025, USA.
Biol Rev Camb Philos Soc. 2025 Aug 28. doi: 10.1111/brv.70070.
Identifying processes underlying species' geographic range limits is currently at the forefront of ecological research, in part due to increasing attention to climate change effects on the distributions of organisms. Our understanding of range limits has benefitted from a rich body of theory, but several influential reviews have insisted that we know little about causes of range limits in nature because there is scant empirical work relative to theoretical. More recent syntheses show mounting support for different hypotheses, although they are not always able to separate different ecological processes. In this review, I recommend a shift in how researchers think about range limits: (i) identifying a first-principles hypothesis of range limits which should structure range limit studies; and (ii) reconsidering the processes that limit geographic distributions, which are relatively few and redundant. First, I argue that estimating the scenopoetic niche (habitat requirements that exclude biotic interactions) allows a first-principles approach to understanding geographic distributions and limits. Some general empirical support for the scenopoetic niche as a primary range-limiting factor has accumulated. Estimates of the scenopoetic niche will structure subsequent tests of range-limiting processes based on how it underpredicts or overpredicts species' distributions. I discuss observational and empirical ways of testing whether the scenopoetic niche is actively limiting species' distributions. Second, I review various theoretical models of geographic range limits; theoretical ecological models only vary a few key parameters, so our understanding of what limits species' geographic distributions might be much better than previously asserted. For instance, predation, competition, and parasitism are all distinct biotic relationships, but they are all antagonistic biotic interactions that can influence range limits in similar ways by reducing the set of conditions under which a species could persist. Several issues complicate causal inferences from static geographic patterns that have remained problematic in empirical work for decades. These issues are related to spatial autocorrelation and interpretation of range overlap. Theoretical metapopulation models have been developed to understand how range limits can form, although metapopulation processes are understood to be consequences of ecological dynamics that are formally modelled in non-metapopulation models (e.g. per capita effects of interspecific interactions, effects of the abiotic environment). I then discuss methods for empirical tests of various range limit hypotheses. Implementation of different methods will depend on tractability with geography and ecology - many researchers cannot survey remote areas, study demography of long-lived organisms, collect large sample sizes for rare species, or conduct field manipulations. However, at least some of the methods showcased will have applicability for any study system. Finally, I suggest a research agenda for improving our understanding of the ecology of geographic range limits: better teasing apart of ecological causes of range limits (e.g. scenopoetic niche versus various biotic interactions) and incorporating spatiotemporal variability. Hopefully some of the ideas highlighted here will support more conservative interpretations of data, stimulate tests of multiple hypotheses, and produce better predictions of changes in geographic distributions under environmental change.
确定物种地理分布范围限制背后的过程是当前生态研究的前沿领域,部分原因是人们越来越关注气候变化对生物分布的影响。我们对分布范围限制的理解受益于丰富的理论体系,但一些有影响力的综述坚持认为,我们对自然界中分布范围限制的原因了解甚少,因为相对于理论而言,实证研究很少。最近的综合研究表明,对不同假设的支持越来越多,尽管它们并不总是能够区分不同的生态过程。在这篇综述中,我建议研究人员改变对分布范围限制的思考方式:(i)确定一个分布范围限制的第一性原理假设,该假设应构建分布范围限制研究;(ii)重新考虑限制地理分布的过程,这些过程相对较少且有冗余。首先,我认为估计景观生态位(排除生物相互作用的栖息地要求)允许采用第一性原理方法来理解地理分布和限制。作为主要分布范围限制因素的景观生态位已经积累了一些普遍的实证支持。景观生态位的估计将基于其对物种分布的预测不足或过度预测来构建后续对分布范围限制过程的测试。我讨论了检验景观生态位是否积极限制物种分布的观测和实证方法。其次,我回顾了各种地理分布范围限制的理论模型;理论生态模型只改变几个关键参数,因此我们对限制物种地理分布的因素的理解可能比以前声称的要好得多。例如,捕食、竞争和寄生都是不同的生物关系,但它们都是拮抗生物相互作用,通过减少物种能够生存的条件集,以相似的方式影响分布范围限制。有几个问题使从静态地理模式得出的因果推断变得复杂,这些问题在几十年的实证研究中一直存在问题。这些问题与空间自相关和分布范围重叠的解释有关。已经开发了理论集合种群模型来理解分布范围限制是如何形成的,尽管集合种群过程被认为是非集合种群模型中正式建模的生态动态的结果(例如种间相互作用的人均效应、非生物环境的效应)。然后我讨论了对各种分布范围限制假设进行实证检验的方法。不同方法的实施将取决于地理和生态的可处理性——许多研究人员无法调查偏远地区、研究长寿生物的种群统计学、为稀有物种收集大样本量或进行实地操作。然而至少这里展示的一些方法将适用于任何研究系统。最后,我提出了一个研究议程,以提高我们对地理分布范围限制生态学的理解:更好地区分分布范围限制的生态原因(例如景观生态位与各种生物相互作用)并纳入时空变异性。希望这里强调的一些想法将支持对数据更保守的解释,激发对多个假设的检验,并对环境变化下地理分布的变化做出更好的预测。