Vincent Devictor’s research while affiliated with Center for Natural Resource Studies and other places

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Publications (169)


Figure 3: Temporal changes in network metrics of bird communities between 2001 and 2017 (note that only estimates for 2001 and 2017 of the linear model are presented for clarity). a) Temporal change in the number of species s, b) temporal change in the number of associations a (while controlling for the number of species), c) temporal change in connectance c (while controlling for the number of species), d) temporal change in modularity m (while controlling for connectance), e) temporal change in evenness of the degree distribution e (while controlling for connectance). Black dot is for all
Figure 4: Examples of observed networks illustrating the topological changes between 2001 and 2017
Rapid structural network changes in bird communities
  • Preprint
  • File available

February 2025

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81 Reads

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Vincent Devictor

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Vasilis Dakos

As biodiversity is declining, the dynamics of species interactions is a growing conservation concern. However, estimating and monitoring species interactions across large spatial and temporal scales remain challenging, and thus changes in species interactions and the subsequent networks of interactions remain relatively unexplored. Here, we assess changes in the network structure of common bird communities from France. We estimate associated species pairs using spatial and temporal information for 109 species monitored across 1,969 sites during 17 years. We validate the ecological significance of associated species pairs by testing the relationship between the propensity to be associated and species functional proximity or shared habitat preference. We reconstruct association networks for these intra-guild bird communities and track temporal changes in network layout in terms of size, density of links, modularity and degree distribution. We show that, beyond species change, birds' local association networks become smaller with a similar relative number of associations that becomes unevenly distributed. These structural changes vary among types of bird communities and may impact community functioning and how communities can cope with global change.

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Non‐linearity and Temporal Variability Are Overlooked Components of Global Vertebrate Population Dynamics

October 2024

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96 Reads

Aim Population dynamics are usually assessed through linear trend analysis, quantifying their general direction. However, linear trends may hide substantial variations in population dynamics that could reconcile apparent discrepancies when quantifying the extent of the biodiversity crisis. We seek to determine whether the use of non‐linear methods and the quantification of temporal variability can offer a more complete representation of changes in global population dynamics than commonly‐used linear approaches. Methods We analysed 6437 population time series from 1257 vertebrate species from the Living Planet Database over the period 1950–2020. We modelled populations through the use of second‐order polynomials and classified trajectories according to their direction and acceleration. We modelled and classified these same populations using a more classical linear trend analysis. We quantified temporal variability using the mean squared error of the fitted polynomials. We then used generalised linear mixed models to test potential sources of heterogeneity in non‐linear trajectories and temporal variability. Results In all, 44.8% of the analysed population time series were non‐linear. Across all populations, 30% were declining, 30% were increasing, and 40% were with no linear trend. Among the population showing no linear trend, half were concave or convex. Non‐linearity was expressed differently between taxonomic groups, with mammals showing higher prevalence of non‐linearity. Marine and freshwater populations were more variable than terrestrial populations, and fish were more variable than other vertebrates. Differences between geographical regions were detected in both non‐linearity and temporal variability, but no straightforward pattern emerged. There were no differences in both components between IUCN categories. Main Conclusions Non‐linearity and temporal variability reveal usually overlooked dramatic declines or recovery signals in global population dynamics. Thus, moving beyond linearity can improve our understanding of complex population dynamics and better inform conservation decisions. In particular, populations usually classified as ‘stable’ can hide informative changes in non‐linear and variability patterns that need to be considered in global biodiversity assessments.


Sources of confusion in global biodiversity trends

April 2024

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69 Reads

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5 Citations

Populations and ecological communities are changing worldwide, and empirical studies exhibit a mixture of either declining or mixed trends. Confusion in global biodiversity trends thus remains, while assessing such changes is of major social, political, and scientific importance. Part of this variability may arise from the difficulty to reliably assess global biodiversity trends. Here, we conducted a literature review of studies documenting the temporal dynamics of global biodiversity. We classified the differences among approaches, data, and methodology used by the reviewed papers to reveal common findings and sources of discrepancies. We show that reviews and meta‐analyses, along with the use of global indicators, are more likely to conclude that trends are declining. On the other hand, the longer the data are available, the more nuanced are the trends they generate. Our results also highlight the lack of studies providing information on the impact of synergistic pressures on a global scale, making it even more difficult to understand the driving factors of the observed changes and how to decide conservation plan accordingly. Finally, we stress the importance of taking into account the sources of confusion identified, as well as the complexity of biodiversity changes, in order to implement effective conservation strategies. In particular, biodiversity dynamics are almost systematically assumed to be linear, while non‐linear trends are largely neglected. Clarifying the sources of confusion in global biodiversity trends should strengthen large‐scale biodiversity monitoring and conservation.


Trajectory shapes (or classes) with associated properties (A) and trajectory classification step by step (B). Four models are fitted to the timeseries (including threshold regression, second order polynomial and linear models) for which corrected Akaike Information Criteria (AICc), AICc weights (wAICc), and normalized root mean square error (NRMSE) are computed (step 1, see main text for details). According to the best trajectory found in terms of AICc, the shape is validated either with another breakpoints detection method (step 2a) or by checking the significance of the coefficients (step 2b). To classify a timeseries as “abrupt”, break dates detected by both methods need to be congruent and not too close to the start or the end. For “abrupt” trajectories, an optional extra step aims at finding multiple breakpoints (step 2c). The reliability of the classification is then assessed by a leave-one-out procedure (LOO, step 3) that consists in repeating steps 1 and 2 on the original timeseries to which one timepoint is omitted sequentially. From these, the most influential points can be detected and the proportion of LOO trajectories the same shape as the full timeseries can be computed.
Examples of simulated timeseries covering the four different trajectory shapes, “no change” (A), “linear” (B), “quadratic” (C), and “abrupt” (D). The solid black line show examples of biomass timeseries with low demographic stochasticity (σr = 0.025) and the solid blue line in the small panels show timeseries of maximum mortality rate F driving the biomass trajectories.
Classification output in R with the example of a correctly classified “abrupt” simulated timeseries. Each of the four panels (A–D) describes the shape and trend of the trajectory: the same timeseries is shown (black line) with a different fit (solid blue line) and standard deviation (dashed lines for all panels except “abrupt” fit). In the “abrupt” panel D, the location of breakpoints is indicated by vertical dashed lines (in blue from chngpt – step 1, in red from asdetect – step 2a), the pink background corresponds to the uncertainty of asdetect breakpoints, and the distribution of breakpoint locations from Leave-One-Out (LOO) timeseries are represented by colour bars. Timepoints that if removed in the LOO process result in a specific shape are highlighted by orange dots in the corresponding panel. The panel with the best shape is highlighted in blue. Panel subtitles show AICc score, AICc weight (wAICc), LOO, and normalized root mean square error (NRMSE). Trajectoryspecific values are also displayed: the intercept of the “no change” model (6.6), the slope ( 4.2e-2) and associated p-value (<0.001) of the linear model, the second order coefficient ( 5.1e-5) and associated p-value (0.659) of the quadratic model, the location of breakpoints (in blue from chngpt at t = 49, in red from asdetect at t = 48) and abruptness (the standardized magnitude of the abrupt shift equal to 4.35 here).
Confusion matrices for simulated timeseries classified with step 1 – AICc only (A–C), or steps 1 and 2a – AICc + asdetect (D-F). For each row, the different matrices correspond to different timeseries length, 100 (A, D), 50 (B, E), or 20 (C, F) timepoints. Expected trajectory classes are in columns and predictions are in rows, numbers are the proportions by reference (expected) classes. For instance, in panel A for complete timeseries (100 points) classified with step 1 only, 53 % of the timeseries simulated to be “no change” were correctly classified, 1 % was misclassified as “linear”, 3 % as“quadratic”, and 43 % as “abrupt”. The diagonal in each matrix corresponds to the proportion of correctly classified timeseries.
Three empirical timeseries classified either as “abrupt”, “quadratic”, or “linear” following our classification approach, namely, (A) Atlantic bluefin tuna (Thunnus thynnus) catch in Eastern Atlantic (source: RAM Legacy Data Base), (B) Northern wheatear (Oenanthe oenanthe) abundance in Europe (source: EBCC/ BirdLife/RSPB/CSO), and (C) Red-eyed damselfly (Erythromma najas) occupancy in Britain (source: Termaat et al., 2019). The location of breakpoints is indicated by vertical dashed lines (in blue from chngpt, in red from asdetect), the pink background corresponds to the uncertainty of asdetect breakpoints, and the location of breakpoints from LOO timeseries are represented by colour bars. Timepoints highlighted by orange dots indicate that if removed in the LOO process the best trajectory would remain the same as the complete timeseries. Animal silhouettes come from https://www.phylopic.org/.
A systematic approach for detecting abrupt shifts in ecological timeseries

February 2024

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201 Reads

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6 Citations

Biological Conservation

Conservation efforts and sustainable use of natural populations often seek to reach or maintain viable abundance levels for a target population. Yet, this goal can be undermined by a number of events resulting from out-of-equilibrium dynamics, including large and sudden changes in abundance. The dynamical properties of such temporal changes are valuable indications about population's capacity to cope with environmental changes. Correctly identifying past or anticipating impending occurrences of temporal abrupt shifts in ecological systems is thus of major importance to adjust conservation and management strategies. Despite many available abrupt shift detection methods, few offer the possibility to compare and agree on the best model among linear, nonlinear, or abrupt models. By combining several existing methods, we develop an approach that classifies any timeseries to a trajectory type – no change, linear, nonlinear (quadratic), abrupt – and confirms the occurrence of potential abrupt shifts. We assessed the classification performances using a set of simulated data for which we had deterministic predictions for each type of trajectories. We used various levels of noise and perturbation events to make the simulations more realistic. This classification can be of particular interest when comparing dynamics of many populations across space or time. We show this by applying this classification approach to three different temporal datasets commonly used in conservation: catch tonnage, bird index, and insect occupancy timeseries. With this tool, we hope to promote conservation and management practices that explicitly take into account the likelihood of out-of-equilibrium trajectories and especially abrupt shifts in ecological systems.


Non-linearity and temporal variability are overlooked components of global population dynamics

January 2024

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42 Reads

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2 Citations

Aim. Population dynamics are usually assessed through linear trend analysis, quantifying their general direction. However, linear trends may hide substantial variations in population dynamics that could reconcile apparent discrepancies when quantifying the extent of the biodiversity crisis. We seek to determine whether the use of non-linear methods and the quantification of temporal variability can add value to the linear approach by offering a more complete representation of global population changes. In addition, we seek to determine how these components are distributed among biogeographical regions and taxonomic groups. Location.Global.Methods.We analysed 6,437 population time series from 1,257 species from the Living Planet Database over the period 1950-2020. We modeled populations through the use of second order polynomials and classified trajectories according to their direction and acceleration. We modeled and classified these same populations using a more common linear trend analysis. We quantified temporal variability using three metrics, the coefficient of variation, the mean squared error and the consecutive disparity index. We then used chi-squared tests and linear mixed-effects models to test potential sources of heterogeneity in non-linear trajectories and temporal variability.Results.Non-linear models were a better fit for 44.8 % of the analyzed time series, and temporal variability was higher among trajectories classified as linear. Linear models missed meaningful information by misclassifying recent declines or recovery signals. Marine populations were highly variable, and all taxonomic groups or IUCN categories exhibited variability in their degree of non-linearity and temporal variability.Main conclusions.Non-linearity and temporal variability reveal usually overlooked dramatic declines or recovery signals in global population dynamics. Thus, moving beyond linearity can help reduce the risk of misleading conclusions and better inform conservation decisions. In particular, population usually classified as « stable » can hide informative non-linear and variable changes to integrate in more advanced global biodiversity assessment.


Sources of confusion in global biodiversity trends

September 2023

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158 Reads

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2 Citations

Populations and ecological communities are changing worldwide, and empirical studies exhibit a mixture of either declining or mixed trends. Confusion in global biodiversity trends thus remains while being of major social, political, and scientific importance. Part of this variability may arise from the difficulty to reliably assess global biodiversity trends. Here, we conducted a literature review of studies documenting the temporal dynamics of global biodiversity. We classified the differences among approaches, data and methodology used by the reviewed papers to reveal common findings and sources of discrepancies. We show that reviews and meta-analyses, along with the use of global indicators, are more likely to conclude that trends are declining. On the other hand, the longer the data are available, the more nuanced are the trends they generate. Our results also highlight the lack of studies providing information on the impact of synergistic pressures on a global scale, making it even more difficult to understand the driving factors of the observed changes and how to decide conservation plan accordingly. Finally, we stress the importance of taking into account the sources of confusion identified, as well as the complexity of biodiversity changes, in order to implement effective conservation strategies. In particular, biodiversity dynamics are almost systematically assumed to be linear, while non-linear trends are largely neglected. Clarifying the sources of confusion in global biodiversity trends should strengthen large scale biodiversity monitoring and conservation.


Fig. 1. Temporal change in bird abundance in Europe between 1996 and 2016 for countries participating in the PanEuropean Common Bird Monitoring Scheme (PECBMS) (n = 28, non-PECBMS countries in gray). For each country, the color represents the slope (red for decline, blue for increase) and the black line corresponds to the time series of the multispecies index (MSI) between 1996 and 2016 (species lists by country in SI Appendix, Appendix 5). (A) Change in abundance of farmland species (MSI by country on 19 species) showing an overall sharp while decelerating decline. (B) Change in abundance of woodland species (MSI by country on 25 species) showing an overall linear decline. (C) Change in abundance of urban dwellers (MSI by country on 22 species) showing an overall stable trajectory. (D) Change in abundance of cold dwellers (light gray, MSI by country on 35 species) showing an overall linear decline. Change in abundance of hot dwellers (dark gray, MSI by country on 35 species) showing an overall stable trajectory. Color for hot dweller trends on the southern part of countries and color for cold dwellers on the northern part of countries.
Fig. 2. Anthropogenic pressures for countries participating in the PanEuropean Common Bird Monitoring Scheme (PECBMS) (n = 28, non-PECBMS countries and countries with no available data in gray). For each country and each pressure, the color represents the mean and the black line corresponds to the time series. (A) High-input farm cover (% of total cultivated area covered by high-input farms), period covered by data 2007 to 2016. (B) Forest cover (% of the country's surface), 1996 to 2016. (C) Urbanization (% of the country's surface), 2009 to 2016. (D) Temperature (°C), 1996 to 2016.
Fig. 3. Relationship between anthropogenic pressures and bird trends and time series. (A) Relative effects of high-input farm cover, forest cover, urbanization, and temperature and their trends on bird trends (1996 to 2016, 141 species) obtained by partial least square regression (PLS). Bias-corrected and accelerated CIs are displayed. (B) Distribution of the strength of the influence of pressures (scaled S-map coefficients) on bird time series. The number of species with negative and positive mean S-map coefficients is shown.
Fig. 4. Results of the partial least square regression between each pressure influence on species time series and species traits. Nonsignificant effects are shown in gray, negative effects are shown in light red, and positive effects are shown in blue. The magnitude of the effect is displayed by the line width, scaled for each pressure.
Farmland practices are driving bird population decline across Europe

May 2023

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2,278 Reads

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282 Citations

Proceedings of the National Academy of Sciences

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Vasilis Dakos

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[...]

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Vincent Devictor

Declines in European bird populations are reported for decades but the direct effect of major anthropogenic pressures on such declines remains unquantified. Causal relationships between pressures and bird population responses are difficult to identify as pressures interact at different spatial scales and responses vary among species. Here, we uncover direct relationships between population time-series of 170 common bird species, monitored at more than 20,000 sites in 28 European countries, over 37 y, and four widespread anthropogenic pressures: agricultural intensification, change in forest cover, urbanisation and temperature change over the last decades. We quantify the influence of each pressure on population time-series and its importance relative to other pressures, and we identify traits of most affected species. We find that agricultural intensification, in particular pesticides and fertiliser use, is the main pressure for most bird population declines, especially for invertebrate feeders. Responses to changes in forest cover, urbanisation and temperature are more species-specific. Specifically, forest cover is associated with a positive effect and growing urbanisation with a negative effect on population dynamics, while temperature change has an effect on the dynamics of a large number of bird populations, the magnitude and direction of which depend on species' thermal preferences. Our results not only confirm the pervasive and strong effects of anthropogenic pressures on common breeding birds, but quantify the relative strength of these effects stressing the urgent need for transformative changes in the way of inhabiting the world in European countries, if bird populations shall have a chance of recovering.


Do large‐scale associations in birds imply biotic interactions or environmental filtering?

November 2022

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198 Reads

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7 Citations

Aim There has been a wide interest in the effect of biotic interactions on species' occurrences and abundances at large spatial scales, coupled with a vast development of the statistical methods to study them. Still, evidence for whether the effects of within‐trophic‐level biotic interactions (e.g. competition and heterospecific attraction) are discernible beyond local scales remains inconsistent. Here, we present a novel hypothesis‐testing framework based on joint dynamic species distribution models and functional trait similarity to dissect between environmental filtering and biotic interactions. Location France and Finland. Taxon Birds. Methods We estimated species‐to‐species associations within a trophic level, independent of the main environmental variables (mean temperature and total precipitation) for common species at large spatial scale with joint dynamic species distribution (a multivariate spatiotemporal delta model) models. We created hypotheses based on species' functionality (morphological and/or diet dissimilarity) and habitat preferences about the sign and strength of the pairwise spatiotemporal associations to estimate the extent to which they result from biotic interactions (competition, heterospecific attraction) and/or environmental filtering. Results Spatiotemporal associations were mostly positive (80%), followed by random (15%), and only 5% were negative. Where detected, negative spatiotemporal associations in different communities were due to a few species. The relationship between spatiotemporal association and functional dissimilarity among species was negative, which fulfils the predictions of both environmental filtering and heterospecific attraction. Main conclusions We showed that processes leading to species aggregation (mixture between environmental filtering and heterospecific attraction) seem to dominate assembly rules, and we did not find evidence for competition. Altogether, our hypothesis‐testing framework based on joint dynamic species distribution models and functional trait similarity is beneficial in ecological interpretation of species‐to‐species associations from data covering several decades and biogeographical regions.


Frequency distribution of standardized titmouse abundance (given as biomass; g) in Finland (a). The relationship between log‐predicted density of forest birds (g/km²) and standardized titmouse abundance (given as biomass; g) in Finland in 2001 (i.e., first study year; β = 10.315, γ1 = 0.025; see Table 1 for definition of all symbols) (b). Circles are predicted forest bird densities for the sampling points and the fitted line with 95% confidence intervals derives from the spatial Gompertz model (see Section 2.3 for details) visualizing the linear relationship between predicted forest bird density and titmouse abundance. There was minor variance among years in the intercept (10.184 < β < 10.418), so the elevation of the line varies among years, but the slope remains the same. Frequency distribution of log‐predicted density of forest birds (g/km²) in Finland (c)
Frequency distribution of standardized titmouse abundance (given as biomass; g) in France (a). The relationship between log‐predicted density of forest birds (g/km²) and standardized titmouse abundance (given as biomass; g) in France in 2001 (i.e., first study year; β = 10.251, γ1 = 0.198, γ2 = −0.030; see Table 1 for definition of all symbols) (b). Circles are predicted forest bird densities for the sampling points and the fitted line with 95% confidence intervals derives from the spatial Gompertz model (see Section 2.3 for details) visualizing the quadratic relationship between predicted forest bird density and titmouse abundance. There was minor variance among years in the intercept (10.145 < β < 10.259), so the elevation of the line varies among years, but the curve remains the same. Frequency distribution of log‐predicted density of forest birds (g/km²) in France (c)
VAST estimates from the models that converged and had a significant parameter estimate (a: n = 158; b: n = 293) for the associations between abundance (given as biomass) of each randomly drawn control group and forest bird density (γ4) with error bars showing the 95% confidence intervals in Finland (a) and in France (b). Red filled circles represent those estimates that were statistically different from the titmouse estimate (γ1; a: n = 39; b: n = 235) and the black triangles depict those estimates that were not significantly different from the titmouse estimate (a: n = 119; b: n = 58) at 95% confidence level (see Section 2.4 for details). The estimate for the association between titmouse abundance (given as biomass) and forest bird density is shown with the blue dashed line (a: γ1 = 0.025; b: γ1 = 0.174), and the gray shaded area shows the 95% confidence intervals for the titmouse estimates
Titmice are a better indicator of bird density in Northern European than in Western European forests

February 2022

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212 Reads

Population sizes of many birds are declining alarmingly and methods for estimating fluctuations in species' abundances at a large spatial scale are needed. The possibility to derive indicators from the tendency of specific species to co-occur with others has been overlooked. Here, we tested whether the abundance of resident titmice can act as a general ecological indicator of forest bird density in European forests. Titmice species are easily identifiable and have a wide distribution, which makes them potentially useful ecological indicators. Migratory birds often use information on the density of resident birds, such as titmice, as a cue for habitat selection. Thus, the density of residents may potentially affect community dynamics. We examined spatio-temporal variation in titmouse abundance and total bird abundance, each measured as biomass, by using long-term citizen science data on breeding forest birds in Finland and France. We analyzed the variation in observed forest bird density (excluding titmice) in relation to titmouse abundance. In Finland, forest bird density linearly increased with titmouse abundance. In France, forest bird density nonlinearly increased with titmouse abundance, the association weakening toward high titmouse abundance. We then analyzed whether the abundance (measured as biomass) of random species sets could predict forest bird density better than titmouse abundance. Random species sets outperformed titmice as an indicator of forest bird density only in 4.4% and 24.2% of the random draws, in Finland and France, respectively. Overall, the results suggest that titmice could act as an indicator of bird density in Northern European forest bird communities, encouraging the use of titmice observations by even less-experienced observers in citizen science monitoring of general forest bird density.


Citations (65)


... However, best practice in the field is not fully established. Trend assessments undertaken using the same dataset can therefore reach different conclusions, generating significant debate in the literature (Seibold et al. 2019, Desquilbet et al. 2020, van Klink et al. 2020a, b, Daskalova et al. 2021, Jähnig et al. 2021, Gould et al. 2023, Boënnec et al. 2024, Johnson et al. 2024. This issue of reproducibility is echoed in a broad range of disciplines attempting to explain and predict complex phenomena through the synthesis of large datasets (Breznau et al. 2022). ...

Reference:

Revealing hidden sources of uncertainty in biodiversity trend assessments
Sources of confusion in global biodiversity trends
  • Citing Article
  • April 2024

... DRP is an approach that attempts to align the biomass objectives to the biological realities of stock productivity (Silvar-Viladomiu et al. 2021). DRP may change biomass reference points continuously or in regimes (alternative stable states) and deciding when and how to change reference points accordingly is critical (Pélissié et al. 2024). MSE seeks to find strategies to safely exploit a stock that is robust to uncertainties in the methods, data, biology and ecology of a stock, and the fisheries management process itself (Goethel et al. 2019). ...

A systematic approach for detecting abrupt shifts in ecological timeseries
  • Citing Article
  • February 2024

Biological Conservation

... In non-tropical soy and maize landscapes, both total abundance and biotic homogenization generally decrease, suggesting that abundance decreases in these landscapes are also driven by changes in the abundance of widespread species, this time decreases. Supporting evidence for this pattern comes from abundance decreases in common European birds 66 , often attributed to agricultural intensification 67 . There are two considerations that can help interpret these opposing responses of widespread species to yield increases. ...

Farmland practices are driving bird population decline across Europe

Proceedings of the National Academy of Sciences

... Interestingly, the local abundance of the Canary Island stonechat was positively and significantly associated with the abundance of two other more widespread insectivorous species that share coarse-grained habitat preferences: Berthelot's pipits and the spectacled warblers. This spatial coincidence could be interpreted as being due to shared ecological requirements, with these species preferring similar food availability, moderate shrub development, and limited anthropic disturbance, consistent with the generalised dominance of positive interactions in spatiotemporal associations among bird species, driven by environmental filtering and/or heterospecific attraction (Elo et al., 2023). Given the challenges of quantifying food availability for the Canary Islands stonechat on a regional scale in monitoring and ecological studies, the local abundance of this species and other small passerines sharing the same trophic niche could serve as an effective proxy for small-scale food Marginal relationships account for the partial effect of counts of each species, controlling for spatial and temporal variations in environmental variables (altitude, slope of terrain, sandy nature of the soil, rock and stone cover, herbaceous cover, therophyte cover, shrub cover, and average height of herbaceous plants and shrubs). ...

Do large‐scale associations in birds imply biotic interactions or environmental filtering?

... Obvious, in turn, is the trend towards faunal homogenisation . In birds, homogenised communities were found to exhibit lower temporal variability in community structure and dominance at a coarse annual resolution (Rigal et al., 2022). Our results indicate that long-term homogenisation and intra-annual compositional variability might not be directly linked. ...

Biotic homogenisation in bird communities leads to large‐scale changes in species associations

... The size-selective fishing scenario, through changes in fish community structure and abundance, shifts nutrient concentrations on the reef, affecting both corals and macroalgae. Fisheries can alter fish community size-structure (Graham et al. 2005, Bosch et al. 2022) and composition (D'agata et al. 2016, Loiseau et al. 2021 since they are often both species-and sizeselective. By targeting species at higher trophic levels or large herbivorous fishes (Graham et al. 2017, Edgar et al. 2018, size-selective fisheries shift fish populations towards smaller species and individuals, which generally have higher N:P ratio excretions due to their higher metabolic rates (Moody et al. 2015 ). ...

Maximizing regional biodiversity requires a mosaic of protection levels

... We included an offset of 0.05 to make CCI calculations possible when dark diversity was 0 and calculate the CCI for each coffee plantation under the different thresholds (i.e., the first, fifth, and tenth percentile). To ensure the robustness of our estimates, we averaged the three CCI estimates for each coffee plantation as per Gaüzère and Devictor (2021). Positive CCI values indicate that the communities are more complete, and that observed diversity is greater than dark diversity, while negative values indicate the opposite (Lewis et al., 2016b). ...

Mismatches between birds' spatial and temporal dynamics reflect their delayed response to global changes
  • Citing Article
  • May 2021

... G lobal science suffers from persistent geographical disparities that skew research toward affluent countries and regions, primarily in Europe and North America (Maas et al. 2021;Gomez et al. 2022). Despite increased awareness, efforts to foster inclusivity within scientific communities often perpetuate existing biases. ...

Women and Global South strikingly underrepresented among top‐publishing ecologists

... CTI accounts for the relative abundance of each species in the community. CTI can be used across different taxonomic groups (Benoit et al., 2021;Lehikoinen et al., 2021a;Löffler et al., 2019) as a proxy for climate change impacts on biodiversity. CTI reflects the balance between warm-and cold-dwelling species as it is derived from the Species Temperature Indices (STI, for detailed methods, see Appendix). ...

Wintering bird communities are tracking climate change faster than breeding communities

... Species' responses to climate changes also often have a time lag, which means that species may need decades or even centuries to adapt to the recent climate changes [35,36]. For example, changes in French breeding bird communities lag behind climate warming, resulting in a climate-driven extinction debt [37,38]. ...

Disentangling the latitudinal and altitudinal shifts in community composition induced by climate change: The case of riparian birds
  • Citing Article
  • October 2020