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Abstract and Figures

The relationship between biodiversity and stability, or its inverse, temporal variability, is multidimensional and complex. Temporal variability in aggregate properties, like total biomass or abundance, is typically lower in communities with higher species diversity (i.e., the diversity–stability relationship [DSR]). At broader spatial extents, regional‐scale aggregate variability is also lower with higher regional diversity (in plant systems) and with lower spatial synchrony. However, focusing exclusively on aggregate properties of communities may overlook potentially destabilizing compositional shifts. It is not yet clear how diversity is related to different components of variability across spatial scales, nor whether regional DSRs emerge across a broad range of organisms and ecosystem types. To test these questions, we compiled a large collection of long‐term metacommunity data spanning a wide range of taxonomic groups (e.g., birds, fish, plants, invertebrates) and ecosystem types (e.g., deserts, forests, oceans). We applied a newly developed quantitative framework for jointly analyzing aggregate and compositional variability across scales. We quantified DSRs for composition and aggregate variability in local communities and metacommunities. At the local scale, more diverse communities were less variable, but this effect was stronger for aggregate than compositional properties. We found no stabilizing effect of γ‐diversity on metacommunity variability, but β‐diversity played a strong role in reducing compositional spatial synchrony, which reduced regional variability. Spatial synchrony differed among taxa, suggesting differences in stabilization by spatial processes. However, metacommunity variability was more strongly driven by local variability than by spatial synchrony. Across a broader range of taxa, our results suggest that high γ‐diversity does not consistently stabilize aggregate properties at regional scales without sufficient spatial β‐diversity to reduce spatial synchrony.
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ARTICLE
Diversitystability relationships across organism
groups and ecosystem types become decoupled across
spatial scales
Nathan I. Wisnoski
1,2,3
| Riley Andrade
4,5
| Max C. N. Castorani
6
|
Christopher P. Catano
7
| Aldo Compagnoni
8,9
| Thomas Lamy
10,11
|
Nina K. Lany
12
| Luca Marazzi
13,14
| Sydne Record
15,16
|
Annie C. Smith
17,18,19,20
| Christopher M. Swan
21
|
Jonathan D. Tonkin
22,23,24
| Nicole M. Voelker
21
|
Phoebe L. Zarnetske
18,19
| Eric R. Sokol
25,26
1
Department of Biological Sciences, Mississippi State University, Mississippi State, Mississippi, USA
2
Wyoming Geographic Information Science Center, University of Wyoming, Laramie, Wyoming, USA
3
Department of Biology, Indiana University, Bloomington, Indiana, USA
4
Department of Natural Resources and Environmental Sciences, University of Illinois at Urbana-Champaign, Urbana,
Illinois, USA
5
Department of Wildlife Ecology and Conservation, University of Florida, Gainesville, Florida, USA
6
Department of Environmental Sciences, University of Virginia, Charlottesville, Virginia, USA
7
Department of Plant Biology, Michigan State University, East Lansing, Michigan, USA
8
Martin Luther University Halle-Wittenberg, Halle (Saale), Germany
9
German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig, Leipzig, Germany
10
Marine Science Institute, University of California, Santa Barbara, Santa Barbara, California, USA
11
MARBEC, University of Montpellier, CNRS, Ifremer, IRD, Montpellier, France
12
Northern Research Station, Forest Service, US Department of Agriculture (USDA), Durham, New Hampshire, USA
13
Institute of Environment, Florida International University, Miami, Florida, USA
14
Thames21, London, UK
15
Department of Biology, Bryn Mawr College, Bryn Mawr, Pennsylvania, USA
16
Department of Wildlife, Fisheries, and Conservation Biology, University of Maine, Orono, Maine, USA
17
Department of Forestry, Michigan State University, East Lansing, Michigan, USA
18
Ecology, Evolution, and Behavior Program, Michigan State University, East Lansing, Michigan, USA
19
Department of Integrative Biology, Michigan State University, East Lansing, Michigan, USA
20
Washington State Department of Natural Resources, Olympia, Washington, USA
21
Department of Geography and Environmental Systems, University of Maryland, Baltimore, Maryland, USA
22
School of Biological Sciences, University of Canterbury, Christchurch, New Zealand
23
Te P
unaha Matatini Centre of Research Excellence, University of Canterbury, Christchurch, New Zealand
24
Bioprotection Aotearoa Centre of Research Excellence, University of Canterbury, Christchurch, New Zealand
25
National Ecological Observatory Network (NEON), Boulder, Colorado, USA
26
Institute of Arctic and Alpine Research (INSTAAR), University of Colorado, Boulder, Colorado, USA
Received: 5 October 2022 Revised: 9 June 2023 Accepted: 15 June 2023
DOI: 10.1002/ecy.4136
Ecology. 2023;104:e4136. https://onlinelibrary.wiley.com/r/ecy © 2023 The Ecological Society of America. 1of17
https://doi.org/10.1002/ecy.4136
... Much of the empirical support for a positive relationship between species diversity and community stability comes from biodiversity experiments that manipulate plant species number (Tilman, Reich, and Knops 2006;Craven et al. 2018;Zhao et al. 2022), while studies using observational data and encompassing numerous taxonomic groups are relatively rare (but see Jarzyna et al. 2022, Wisnoski et al. 2023). Moreover, current literature mainly focuses on exploring the effect of taxonomic diversity on stability (Liang et al. 2022, Wisnoski et al. 2023, while studies incorporating other facets of diversity (e.g., functional diversity) tend to focus on a single species group (Craven et al. 2018;Li et al. 2021). ...
... Much of the empirical support for a positive relationship between species diversity and community stability comes from biodiversity experiments that manipulate plant species number (Tilman, Reich, and Knops 2006;Craven et al. 2018;Zhao et al. 2022), while studies using observational data and encompassing numerous taxonomic groups are relatively rare (but see Jarzyna et al. 2022, Wisnoski et al. 2023). Moreover, current literature mainly focuses on exploring the effect of taxonomic diversity on stability (Liang et al. 2022, Wisnoski et al. 2023, while studies incorporating other facets of diversity (e.g., functional diversity) tend to focus on a single species group (Craven et al. 2018;Li et al. 2021). Thus, while the importance of functional traits on community assembly and functioning is increasingly recognised (Gross et al. 2017), it remains unknown how ubiquitous the biodiversity-stability relationship is across variable taxa in natural communities and how functional trait diversity contributes to this relationship in the wild (Qiao et al. 2023). ...
... Grace, Loreau, and Schmid 2022), but with taxon-dependent underpinnings. By using long-term species' monitoring data across a large spatial extent, our findings support previous studies (see e.g., Downing, Brown, and Leibold 2014, Craven et al. 2018, Zhao et al. 2022, but see e.g., Evans et al. 2022, Wisnoski et al. 2023 for natural communities). However, our approach enables us to identify how the pathways differ among taxa. ...
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Anthropogenic environmental change is altering biodiversity at unprecedented rates, threatening the stability of ecosystem services on which humans depend. However, most of what is known about biodiversity–stability relationships comes from experimental studies making extrapolation to real ecosystems difficult. Here, we ask whether the shape and underlying mechanisms of the biodiversity–stability relationship vary among taxa in real‐world communities. Our study harnesses the power of six terrestrial and aquatic long‐term monitoring datasets, encompassing entire assemblages at hundreds of georeferenced sites providing 20 years long community measurements, covering a 1200 km latitudinal gradient across Finland. In general, we detect a positive relationship between species richness and stability. Structural equation modelling reveals that this relationship is modified by functional trait community composition, with specific mechanisms varying among the taxa. Our study is among the first to highlight the importance of functional traits in elucidating both general and taxon‐specific impacts of biodiversity on community stability.
... In contrast to experiments, investigations of DSRs along natural diversity gradients have yielded less consistent outcomes (Houlahan et al. 2018; van der Plas 2019; Valencia et al. 2020;Wisnoski et al. 2023). While positive DSRs are common, naturally assembled communities often exhibit non-significant DSRs (Houlahan et al. 2018; van der Plas 2019), and a noteworthy minority of DSRs may be inverted (Houlahan et al. 2018;Wisnoski et al. 2023). ...
... In contrast to experiments, investigations of DSRs along natural diversity gradients have yielded less consistent outcomes (Houlahan et al. 2018; van der Plas 2019; Valencia et al. 2020;Wisnoski et al. 2023). While positive DSRs are common, naturally assembled communities often exhibit non-significant DSRs (Houlahan et al. 2018; van der Plas 2019), and a noteworthy minority of DSRs may be inverted (Houlahan et al. 2018;Wisnoski et al. 2023). Evidence for positive DSRs along natural richness gradients is particularly sparse for marine systems. ...
... The remaining two produced divergent results; one reported a positive DSR (Lamy et al. 2020), and the other a negative DSR (Valdivia and Molis 2009). Within marine systems, studies often concentrate on the mesoscale (~ hundreds of km 2 or less; see, e.g., datasets in Wisnoski et al. 2023). For larger-scale studies, researchers have tended to focus on stability in species composition, or short-term proxies for stability in community abundance (Mellin et al. 2016(Mellin et al. , 2019Yan et al. 2023;Yeager, Gouhier, and Hughes 2020), rather than stability of community abundance itself. ...
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The stabilising effect of biodiversity on aggregate community properties is well‐established experimentally, but its importance in naturally assembled communities at larger scales requires considering its covariation with other biotic and abiotic factors. Here, we examine the diversity–stability relationship in a 27‐year coral reef fish time series at 39 reefs spanning 10° latitude on Australia's Great Barrier Reef. We find that an apparent relationship between species richness and synchrony of population fluctuations is driven by these two variables' covariation with proximity to coastal influences. Additionally, coral cover volatility destabilises fish assemblages by increasing average population variability but not synchrony, an effect mediated by changes in the intensity of density regulation in the fish community. Our findings indicate that these two environmental factors, both of which are strongly influenced by anthropogenic activity, impact community stability more than diversity does, but by distinct pathways reflecting different underlying community‐dynamic processes.
... The second mechanism is known as species stability within communities, which can be defined as the ability of some species to tolerate environmental fluctuations and to maintain relatively constant abundance or performance through time (Box 1, Panel A, figure 1c; Hector et al., 2010;Loreau & de Mazancourt, 2013). Recently there has been an increasing awareness about the importance of investigating mechanisms that connect diversity and stability across spatial scales (e.g., Liang et al., 2022;Qiao et al., 2022;Wang & Loreau, 2014, 2016Wilcox et al., 2017;Wisnoski et al., 2023). ...
... To date, most empirical studies report a positive stabilizing effect of β-diversity (e.g., Catano et al., 2020;Liang et al., 2022;Qiao et al., 2022), although non-significant effects have also been reported (Wilcox et al., 2017;Zhang et al., 2019). Whereas some studies have found a higher contribution of local stability than spatial asynchrony to regional stability (e.g., Wilcox et al., 2017;Wisnoski et al., 2023), others have found the opposite pattern (e.g., Catano et al., 2020;Qiao et al., 2022;Qiao, Lamy, et al., 2023). In general, the larger the spatial extent covered by a given study, the larger the environmental heterogeneity and the spatial β-diversity, which enhances the relative contribution of spatial asynchrony to regional stability (e.g., Catano et al., 2020;Qiao et al., 2022;Qiao, Lamy, et al., 2023). ...
... Our study shows that spatial asynchrony consistently contributes more to the regional stability of IRs compared to PRs. Such contribution results in spatial decoupling of diversity-stability relationships across spatial scales (Wisnoski et al., 2023), indicating that regional stabilization is reached despite local communities being individually highly variable through time. ...
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Climate change is increasing the proportion of river networks experiencing flow intermittence, which in turn reduces local diversity (i.e., α‐diversity) but enhances variation in species composition among sites (i.e., β‐diversity), with potential consequences on ecosystem stability. Indeed, the multiscale theory of stability proposes that regional stability can be attained not only by local processes but also by spatial asynchrony among sites. However, it is still unknown whether and how scale‐dependent changes in biodiversity associated with river flow intermittence influence stability across spatial scales. To elucidate this, we here focus on multiple metacommunities of French rivers experiencing contrasting levels of flow intermittence. We clearly show that the relative contribution of spatial asynchrony to regional stability was higher for metacommunities of intermittent than perennial rivers. Surprisingly, spatial asynchrony was mainly linked to asynchronous population dynamics among sites, but not to β‐diversity. This finding was robust for both truly aquatic macroinvertebrates and for taxa that disperse aerially during their adult stages, implying the need to conserve multiple sites across the landscape to attain regional stability in intermittent rivers. By contrast, metacommunities of truly aquatic macroinvertebrates inhabiting perennial rivers were mainly stabilized by local processes. Our study provides novel evidence that metacommunities of perennial and intermittent rivers are stabilized by contrasting processes operating at different spatial scales. We demonstrate that flow intermittence enhances spatial asynchrony among sites, thus resulting in a regional stabilizing effect on intermittent river networks. Considering that climate change is increasing the proportion of intermittent rivers worldwide, our results suggest that managers need to focus on the spatial dynamics of metacommunities more than on local‐scale processes to monitor, restore, and conserve freshwater biodiversity.
... Such that the species richness of plant community remains relatively constant and is not sensitive to the invasion of alien species [2][3][4][5][6]. However, the corresponding research results have shown that there is no correlation between species diversity and ecological stability, and even negative correlations [7][8][9]. Accompanied by the continuation of different research results, the maintenance of environmental stability is the result of multidimensional and multiple maintenance mechanisms [10,11]. Such as, diversity insurance hypothesis [12], moderate interference hypothesis [13], resource limitation hypothesis [14], complex food web hypothesis [15][16][17], and dominant population hypothesis [18,19], etc. ...
... It is a generally accepted approach to measure the functional stability of plant community by using above-ground net primary productivity or standing crops [1]. Researchers have emphasized the significance of species diversity in this process, but they have weakened or ignored the influence of species composition ratio and interactions among plant species [4,9,14]. It is well known that the proportion of species is a fundamental structural property of plant community [21,22]. ...
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Background Assessing the relationships between spatial and temporal structures and functions of plant communities is an effective way to understand the changing dynamics of plant communities in specific environments. In this study, we investigated the response of structural and functional stabilities of plant communities to stocking rate in the desert steppe over a 16-year grazing period as the research background. Methods We used classical statistical methods to investigate the quantitative characteristics of plant communities over time (2014–2019) and space (2017–2019) at four stocking rates (control, CK, 0 sheep·ha–1·month–1; light grazing, LG, 0.15 sheep·ha–1·month–1; moderate grazing, MG, 0.30 sheep·ha–1·month–1; heavy grazing, HG, 0.45 sheep·ha–1·month–1) in the Stipa breviflora desert steppe of Inner Mongolia. We then examined the relationship between structural and functional stability of plant communities. Results On the spatial scale, the structural stability of plant community was the highest in the LG treatment and the lowest in the MG treatment. The functional stability of plant community was the highest in the MG treatment and the lowest in the HG treatment. On the temporal scale, the structural stability of plant community was the highest in the MG treatment and the lowest in the LG treatment. The functional stability of plant community was the highest in the LG treatment and the lowest in the HG treatment. Affected by the stocking rate, the structural stability of plant community fluctuated more widely on the spatial scale and its functional stability varied more widely on the temporal scale. Nonetheless, the functional stability of the plant community is more responsive to the stocking rate. Conclusions Our findings suggest that influenced by the disturbance of stocking rate, the structural stability of plant community is more significant than the functional stability in the desert grassland ecosystem, which lays a solid foundation for the study of ecosystem stability.
... Empirical evidence from grassland ecosystems, such as the Loess Plateau and northern Tibetan Plateau, further validated this positive relationship [23,24]. However, contemporary research reveals complex non-linear relationships, with some studies reporting destabilization effects at high diversity levels [25][26][27][28] or context-dependent correlations [29,30]. Furthermore, certain studies have argued against a simple linear relationship between these two variables, proposing instead a multivariate interaction [31]. ...
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Grassland ecosystems play a crucial role in sustaining the stability of global ecosystem functions. However, the plant communities of grasslands exhibit spatially heterogeneous stability patterns such as vegetation patches influenced by human disturbances, herbivore activities, and climatic and topographic factors. This study investigated the vegetation dynamics in the Thymus mongolicus steppe in Bairin Right Banner, Inner Mongolia, analyzing the structural characteristics, species diversity, and community stability across six vegetation patches. Our findings revealed that patches dominated by grasses exhibited the highest values in coverage, height, density, and aboveground biomass. Besides, species diversity indices were highest in Achnatherum splendens patches and Festuca litvinovii patches, followed by Thymus mongolicus communities and Leymus chinensis patches, while the lowest diversity indices were observed in Artemisia frigida patches and Convolvulus ammannii patches. The order of community stability from high to low was Leymus chinensis patches, Festuca litvinovii patches, Achnatherum splendens patches, Convolvulus ammannii patches, Artemisia frigida patches, and Thymus mongolicus communities. Both the Patrick richness index and Margalef index showed a significant positive correlation with community stability (p < 0.05), indicating that plant communities with a higher species diversity tend to be more stable. These results emphasize the critical role of plant diversity in mediating community stability and contribute to the development of more effective grassland conservation and restoration strategies to maintain the health and sustainability of grassland ecosystems.
... In addition, environmental variability results in notable variations in population dynamics between various communities. Preventing regional homogenization will further increase the resilience of island ecosystems (Wisnoski et al. 2023). ...
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... Likewise, as comparative and synthetic (e.g. meta-analytic) approaches continue to gain in popularity, many studies explicitly compare stability across systems (Biggs et al., 2020;Hillebrand et al., 2018;Hillebrand & Kunze, 2020;Huang & Xia, 2019;Jones & Schmitz, 2009;Rip & McCann, 2011;Wisnoski et al., 2023;Xu et al., 2021). For example, variability tends to be lower and recovery is slower in terrestrial than in aquatic systems (Hillebrand & Kunze, 2020;Jones & Schmitz, 2009;Rip & McCann, 2011) and forested systems compared to grasslands and shrublands (Geng et al., 2019). ...
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Ecological stability is a vital component of natural ecosystems that can inform effective conservation and ecosystem management. Furthermore, there is increasing interest in making comparisons of stability values across sites, systems and taxonomic groups, often using comparative synthetic approaches, such as meta‐analysis. However, these synthetic approaches often compare/contrast systems where measures of stability mean very different things to the taxa involved. Here, we present results from theoretical models and empirical data to illustrate how differences in growth rates among taxa influence four widely used metrics of ecological stability of species abundances responding to pulse perturbations: resilience, recovery, resistance and temporal stability. We refer to these classic growth‐rate‐dependent metrics as ‘realised’ stability. We show that realised resilience and realised temporal stability vary as a function of organisms' growth rates; realised recovery depends on the relation between growth rate and sampling duration; and realised resistance depends on the relation between growth rate and sampling interval. To account for these influences, we introduce metrics intended to be more independent of growth rates, which we refer to as ‘intrinsic’ stability. Intrinsic stability can be used to summarise the overall effects of a disturbance, separately from internal recovery processes – thereby allowing more general comparisons of disturbances across organisms and contexts. We argue that joint consideration of both realised and intrinsic stability is important for future comparative studies.
... Our results indicate that local stability is the main driver of regional stability, suggesting that habitat protection and restoration might be important to increase both local and regional stability of butterflies. This agrees with studies that report a high contribution of local scale processes to the regional stability of multiple organisms (e.g., Wisnoski et al., 2023). ...
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... For example, it has been shown in Puzin et al. (2019) that the dispersal of soil macroorganisms is influenced by their individual density and habitat availability at different spatial scales. Markfeld et al. (2022) showed that the impact of patch connectivity on soil arthropod diversity in the agricultural ecosystem is spatially dependent and the stability of metacommunities in different taxonomic groups varies with the spatial scales (Wisnoski et al., 2023). However, it is still unclear how the metacommunities of soil organisms vary with different spatial scales. ...
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