Ecological Uniqueness: New Measures to Reconcile Method With Concept

IF 6.5 1区 环境科学与生态学 Q1 ECOLOGY
Andrés Baselga, Carola Gómez-Rodríguez
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引用次数: 0

Abstract

Aim

Ecological uniqueness quantifies how different a community is relative to all other communities within the study. This broad-sense definition of uniqueness makes it dependent on the choice of the dissimilarity metric used to quantify differences between communities. Moreover, under a narrow-sense definition of the concept, a uniqueness metric should indicate the proportion of species in the community that are unique to that community, i.e., absent from other communities. Here we develop and assess the key properties of a reliable metric for the quantification of uniqueness and compare the behaviour of two widely used approaches: (i) average pairwise dissimilarity between the focal community and all others and (ii) Local Contribution to Beta Diversity (LCBD).

Innovation

We introduce two new metrics to compute ecological uniqueness using presence/absence (Urlb) and abundance data (Urlb.ab), based on asymmetric Ruggiero dissimilarity (βrlb) and a new abundance-based asymmetric dissimilarity index (βrlb.ab), respectively. We also identify two key properties for the quantification of uniqueness under a narrow definition of the concept: pairwise index asymmetry and independence from the number of non-focal sites included in the study. Pairwise asymmetry refers to the possibility that the dissimilarity between community A and B differs from the dissimilarity between B and A. To show this, we provide conceptual and simulated examples assessing the behaviour of uniqueness when quantified as LCBD (Hellinger and Sørensen), as average symmetric dissimilarity (Sørensen and Simpson) and as average asymmetric dissimilarity (Ruggiero) using presence/absence data. We also include a case study using real data on European longhorn beetles. We show that both approaches (average dissimilarity and LCBD) are conceptually and mathematically equivalent, but only average dissimilarity can be interpreted in absolute terms as it accounts for the overall beta diversity (i.e., community differentiation) within the region and does not depend on the number of non-focal communities.

Conclusion

Our results show that only average dissimilarity values based on an asymmetric index allow the quantification of uniqueness that is consistent with its ecological narrow-sense concept. Uniqueness thus emerges as an important ecological attribute that, if properly quantified, can be used to identify highly valuable communities, containing many species exclusive to them. Consequently, by focusing on uniqueness, conservation efforts can target large-scale conservation goals with a site-focused perspective.

生态独特性:方法与概念协调的新措施
目的生态独特性量化了一个群落相对于研究中所有其他群落的不同程度。这种广义的独特性定义使其依赖于用于量化社区之间差异的不相似性度量的选择。此外,在狭义的概念定义下,独特性度量指标应该表明该群落中特有的物种比例,即其他群落所没有的物种比例。在这里,我们开发并评估了一种量化独特性的可靠度量的关键属性,并比较了两种广泛使用的方法的行为:(i)焦点群落与所有其他群落之间的平均两两不相似性(ii)对Beta多样性的本地贡献(LCBD)。我们引入了两个新的指标来计算生态独特性,使用存在/缺失(U rlb)和丰度数据(U rlb)。ab),基于不对称Ruggiero不相似度(β rlb)和新的基于丰度的不对称不相似度指数(β rlb)。分别为Ab)。在狭义的概念定义下,我们还确定了量化独特性的两个关键属性:成对指数不对称和与研究中包含的非焦点站点数量的独立性。两两不对称是指群落A和B之间的不相似性不同于群落B和A之间的不相似性的可能性。为了证明这一点,我们提供了概念性和模拟的例子,评估了使用存在/不存在数据量化为LCBD (Hellinger和Sørensen)、平均对称不相似性(Sørensen和Simpson)和平均不对称不相似性(Ruggiero)时的独特性行为。我们还包括一个案例研究,使用欧洲长角甲虫的真实数据。研究表明,这两种方法(平均差异和LCBD)在概念上和数学上都是等效的,但只有平均差异可以用绝对术语解释,因为它解释了区域内的整体beta多样性(即群落分化),而不依赖于非焦点群落的数量。结论只有基于非对称指数的平均不相似度值才能量化其唯一性,这符合其生态学狭义概念。因此,独特性作为一种重要的生态属性出现,如果适当量化,可以用来识别具有高价值的群落,其中包含许多独有的物种。因此,通过关注独特性,保护工作可以从以地点为中心的角度来实现大规模的保护目标。
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来源期刊
Global Ecology and Biogeography
Global Ecology and Biogeography 环境科学-生态学
CiteScore
12.10
自引率
3.10%
发文量
170
审稿时长
3 months
期刊介绍: Global Ecology and Biogeography (GEB) welcomes papers that investigate broad-scale (in space, time and/or taxonomy), general patterns in the organization of ecological systems and assemblages, and the processes that underlie them. In particular, GEB welcomes studies that use macroecological methods, comparative analyses, meta-analyses, reviews, spatial analyses and modelling to arrive at general, conceptual conclusions. Studies in GEB need not be global in spatial extent, but the conclusions and implications of the study must be relevant to ecologists and biogeographers globally, rather than being limited to local areas, or specific taxa. Similarly, GEB is not limited to spatial studies; we are equally interested in the general patterns of nature through time, among taxa (e.g., body sizes, dispersal abilities), through the course of evolution, etc. Further, GEB welcomes papers that investigate general impacts of human activities on ecological systems in accordance with the above criteria.
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