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Phenology varies with phylogeny but not by trophic level with climate change

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Abstract

Shifts in phenology with climate change can lead to asynchrony between interacting species, with cascading impacts on ecosystem services. Previous meta-analyses have produced conflicting results on whether asynchrony has increased in recent decades, but the underlying data have also varied—including in species composition, interaction types and whether studies compared data grouped by trophic level or compared shifts in known interacting species pairs. Here, using updated data from previous studies and a Bayesian phylogenetic model, we found that species have advanced an average of 3.1 days per decade across 1,279 time series across 29 taxonomic classes. We found no evidence that shifts vary by trophic level: shifts were similar when grouped by trophic level, and for species pairs when grouped by their type of interaction—either as paired species known to interact or as randomly paired species. Phenology varied with phylogeny (λ = 0.4), suggesting that uneven sampling of species may affect estimates of phenology and potentially phenological shifts. These results could aid forecasting for well-sampled groups but suggest that climate change has not yet led to widespread increases in phenological asynchrony across interacting species, although substantial biases in current data make forecasting for most groups difficult.

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Fig. 1: Estimating shifts in synchrony may—or may not—vary between known interacting species or randomly paired species (where data come from single-species time series that were often not collected originally for questions of synchrony).
Fig. 2: Time series analysis includes globally distributed and spanning the tree of life.
Fig. 3: Phenological shifts were similar across species trophic levels and functional groups.
Fig. 4: Changes in phenological synchrony were similar across known interacting pairs of species (shown in blue, with n given) and randomly paired species (shown in red) across different interaction types.
Fig. 5: Current estimated shifts in phenology, as represented by the solid lines, suggest most species have not been pushed beyond their pre-1980 variation in phenology (solid lines do not exceed their pre-existing variation, the 95% range of the quantile of which is represented by the coloured bands).

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Data availability

All data we scraped is available through the Knowledge Network for Biocomplexity (https://doi.org/10.5063/F12J69B2)56.

Code availability

Code developed for this analysis is available through the Knowledge Network for Biocomplexity (https://doi.org/10.5063/F12J69B2)56.

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Acknowledgements

We thank the many researchers, citizen scientists and organizations who contributed data, including S. Thackeray, J. Cohen, Rothamsted Insect Survey, UK Phenology Network, Woodland Trust and Centre for Ecology & Hydrology T. J. Davies provided comments that improved the manuscript. Funding was provided by a Natural Sciences and Engineering Research Council (NSERC) Canada Graduate Scholarship-Doctoral award to D.L. and Canada Research Chair award in Temporal Ecology and NSERC Discovery awards to E.M.W.

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Conceptualization: D.L. and E.M.W.; methodology: D.L., E.M.W., G.L., S.J. and M.B.; critical insights: D.L., E.M.W., G.L., S.J. and M.B.; writing—original draft: D.L. and E.M.W.; writing—review and editing: D.L., E.M.W., H.M.K., G.L., S.J. and M.B.

Corresponding author

Correspondence to Deirdre Loughnan.

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Nature Ecology & Evolution thanks Brian Inouye and the other, anonymous, reviewer(s) for their contribution to the peer review of this work.

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Extended data

Extended Data Fig. 1 Conceptual diagram of how phenological shifts by interacting species pairs effect species synchrony.

A conceptual diagram of how species within an interacting pair may differ in their phenological shifts and the resulting effects on species synchrony. a, Within an interacting pair, illustrated here using a consumer and resource species (shown in blue and red respectively) as an example (though our data includes five types of interactions), the resource species may shift at a greater, lesser, or equal rate than their consumer. b, This results in different synchrony responses, with negative asynchrony occurring when the consumers phenology shifts earlier (dotdash line), positive asynchrony occurring when the resources phenology shifts earlier relative to the consumer (dashed line), and no change when both species shift at the same rate (solid line).

Extended Data Fig. 2 The global distribution of our phenological time-series and lack of variation with latitudinal gradients.

Species time-series were observed across the globe, but with strong biases towards certain regions, a, with point colour representing the original source of the dataset and point size the number of species within a dataset. b, The observed trends in species phenological shifts do not vary with latitude despite spanning latitudinal gradients across temperate ecosystems (Table ED1), as shown using points coloured to depict the magnitude of species shift per decade.

Extended Data Fig. 3 Species pairs exhibiting variable shifts in phenology and the resulting changes in synchrony.

To assess how pairs of species differ in their phenological shifts and synchrony, we randomly sampled 1000 posterior estimates from both the high and low-level species within each interaction, as shown here for two sets of species pairs. a, Some pairs differ in their phenological shifts, as shown for the interaction between Parus major and it’s caterpillar prey, b, while others shift at similar rates, shown here for Accipiter nisus and Parus ater. c, Changes in synchrony are calculated as the differences between the high-level species, shown here as predators, and the low-level species, or prey.

Extended Data Fig. 4 Species phenological synchrony across suites of interactions when simulated for terrestrial and aquatic interactions separately.

Species phenological synchrony across a, pollination (n = 47), b, predation (n = 24), c, herbivory (n = 10), and d, competitive (n = 18) interactions amongst terrestrial species (ac), in comparison to e, predation (n = 13), f, herbivory (n = 10), and g, competitive (n = 54) interactions amongst aquatic species (eg), showed no differences in the distributions of posterior estimates of consumer or resource species phenological shifts for pairs of known interacting species (in blue) and randomly paired species (in red) for any of the four types of interactions. Plots are normalized by counts, with the x-axis spanning the total density distribution. Above the figures, the two lines depict the 90% uncertainty intervals (thinner line) and 50% interval (thicker line), and the point the median.

Extended Data Fig. 5 Estimated phenological shifts of the well-studied interaction between Parus major and caterpillars.

Our model replicates the strong asynchronies found in interactions of well studied species pairs. Illustrated here is the classic example of the estimated phenological shifts of Parus major and caterpillars, shown across each type of phenological event represented in our dataset.

Extended Data Fig. 6 Species phenological shifts across trophic levels, consumer types, habitats, and types of phenological events.

Shifts in species phenology are similar across several grouping factors, in- cluding: a, trophic levels, b, consumer types, and c, habitat types. d, We also observed similar shifts across phenological events, with the exception of juvenile bird first ap- pearance. Eye-plots of the posterior estimates from our full phylogeny model (including phylogenetic effects, Table ED1) include a gray distribution as the density of the posteri- ors, black circles for the median value, thick dark lines depict the 50% quantile interval, and thin black lines depict the 90% quantile interval. Letters denote groups of species — f = fish, mo = mollusc, a = arachnids, am = amphibians, b = birds, c = copeopod, d = diatom, f = fish, fu = fungi, i = insects, m = mammals, p = plants, plk = plankton, t = turtle.

Extended Data Fig. 7 Trophic level differences across our species phylogeny and well-studied evolutionary lineages.

a, Within our highly diverse and global dataset, species trophic level is highly confounded with phylogeny, limiting our ability to model trophic level directly. This is further illustrated for the four most well-sampled evolutionary lineages in our dataset, each of which map strongly to certain trophic levels, b, as all plants are primary producers, c, while most insects are primary consumers, c, the majority of birds (aves) secondary consumers, d, and all of amphibia are secondary consumers.

Extended Data Fig. 8 Species phenological shifts with temperature change across study sites.

Shifts in species phenology show no strong relationships to the rate of temperature change at each site of observation across a & e, North America (n = 42 sites), b & f, Europe (n = 109 sites), c & g, the United Kingdom (n = 98 sites), d & h, or independent studies in the United Kingdom, not including data from RIS or the Woodland trust (n sites = 14). Analyses were replicated for both the three month period around which an event occurred (ad) and for the annual monthly temperatures (eh). Gray bands represent the 50% quantile interval and crosses the 50%.

Extended Data Table 1 Summary of model outputs from our phylogenetic model, latitudinal model, and models of well-sample evolutionary lineages
Extended Data Table 2 Bibliographic information of recent studies added to the database for 2015 to 2020

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Loughnan, D., Joly, S., Legault, G. et al. Phenology varies with phylogeny but not by trophic level with climate change. Nat Ecol Evol 8, 1889–1896 (2024). https://doi.org/10.1038/s41559-024-02499-1

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