Abstract
Top predator declines are pervasive and often have dramatic effects on ecological communities via changes in food web dynamics, but their evolutionary consequences are virtually unknown. Tasmania’s top terrestrial predator, the Tasmanian devil, is declining due to a lethal transmissible cancer. Spotted-tailed quolls benefit via mesopredator release, and they alter their behaviour and resource use concomitant with devil declines and increased disease duration. Here, using a landscape community genomics framework to identify environmental drivers of population genomic structure and signatures of selection, we show that these biotic factors are consistently among the top variables explaining genomic structure of the quoll. Landscape resistance negatively correlates with devil density, suggesting that devil declines will increase quoll genetic subdivision over time, despite no change in quoll densities detected by camera trap studies. Devil density also contributes to signatures of selection in the quoll genome, including genes associated with muscle development and locomotion. Our results provide some of the first evidence of the evolutionary impacts of competition between a top predator and a mesopredator species in the context of a trophic cascade. As top predator declines are increasing globally, our framework can serve as a model for future studies of evolutionary impacts of altered ecological interactions.
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Data availability
Raw sequence data and sample metadata necessary for reproducing the study have been deposited at NCBI under BioProject PRJNA922561 and BioSamples SAMN32664143–32664814. Any other relevant data can be found within the article and its Supplementary Information.
Code availability
Scripts for running analyses underlying this study’s results are publicly available in a GitHub repository (https://github.com/marcabeer/stquoll_landscape_genomics).
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Acknowledgements
We thank M. F. Lawrance, R. A. Kane, B. McCulloch, S. L. Bartel and R. M. Rautsaw for constructive comments during project development. Funding was provided by the National Science Foundation Division of Environmental Biology through grant NSF DEB 2027446 (A.S., M.J.M., H.M., M.E.J.), the National Institute of General Medical Sciences under the National Institutes of Health under the US Department of Health and Human Services through grant R01-GM126563-01 (A.S., P.A.H., H.M. and M.E.J.), and the National Science Foundation Graduate Research Fellowship Program under Award 1842493 (M.A.B.). Sample collection was additionally funded by the Australian Research Council through Discovery and Linkage Program grants LP130100949 (M.E.J.), DP110103069 (M.E.J., H.M.), DP110102656 (M.E.J., H.M.), LP0989613 (M.E.J.) and LP0561120 (M.E.J., H.M.), and a Future Fellowship (FT100100031) to M.E.J.
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A.S., M.J.M., H.M. and M.E.J. devised the project. K.M.P., R.H., D.G.H. and C.P.B. contributed samples, and M.A.B., K.M.P. and C.P.K. carried out DNA extractions. A.V. completed RADseq DNA library preparations and, along with P.A.H., assisted genotyping. A.S. supervised the project and M.A.B. carried out all analyses. M.A.B. and A.S. drafted the paper, and all authors contributed to the final version.
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Extended data
Extended Data Fig. 1 Relative support for different values of K.
Optimal K was determined by a) maximum marginal likelihood in FastStructure and b) minimum BIC in DAPC. Error bars in A indicate standard error across replicates.
Extended Data Fig. 2 Population genomic structure across Tasmania.
a) FastStructure results for K = 3. b) DAPC results for K = 3. c, d) FastStructure results for K = 4-5. Each individual is represented by a pie chart reflecting the proportion of ancestry assigned to each genetic cluster.
Extended Data Fig. 3 EEMS plots of effective migration rates.
Effective migration rate surfaces were determined for a) 250-, b) 500-, and c) 1000-deme lattices. Color indicates regions where effective migration is higher (blue) or lower (orange) than expected under a model of isolation by distance.
Extended Data Fig. 4 All 100 linear mixed effects models with maximum likelihood population effects evaluating the contribution of abiotic and biotic variables to isolation-by-resistance.
a–c) Models ordered left-to-right by increasing (worsening) AICc. d–f) Models ordered left-to-right by decreasing (worsening) marginal R-squared left to right. A, D) Average AICc of models based on 10,000 bootstrap replicates. B, E) Average marginal R-squared of models. Marginal R-squared is the proportion of variance in pairwise individual genetic distances explained by a resistance surface representing the composite of the indicated variables. C, F) Matrix indicating inclusion of environmental variables in each model. Isothermality (IT), TS (temperature seasonality), mean annual temperature (MAT), annual precipitation (AP), devil density lagged by 20, 15, 10, and 5 quoll generations (for example, Gen20_devil), landcover classes (TASVEG) and temperature diurnal range (TDR) are abbreviated in the matrix.
Extended Data Fig. 5 Partitioning of model deviance in GDM.
a) Percentages of total model deviance attributable to different factors, with individual environmental factors collapsed into climate, landcover, and generations diseased (DFTD). b) Percentages of deviance explained attributable to individual environmental factors and geography. Percentages in parentheses indicate contributions to total model deviance. Some explained deviance cannot be attributed uniquely to geography versus the environment (Geog-Env confound) or can be attributed uniquely to the environment but not individual environmental factors (Env. Confound).
Extended Data Fig. 6 GDM splines relating pairwise genetic distance to pairwise environmental differences.
Environmental factors were centered and scaled by standard deviation to enable plotting on the same axes.
Extended Data Fig. 7 Pearson’s correlation coefficients for pairs of environmental factors.
Numbers indicate the value of Pearson’s correlation coefficient for a pair of environmental factors. Blue colours indicate positive values and red colours indicate negative values of Pearson’s correlation coefficient.
Supplementary information
Supplementary Table 1
SNPs and nearby genes identified as associated with indicated environmental factors using GEA analyses.
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Beer, M.A., Proft, K.M., Veillet, A. et al. Disease-driven top predator decline affects mesopredator population genomic structure. Nat Ecol Evol 8, 293–303 (2024). https://doi.org/10.1038/s41559-023-02265-9
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DOI: https://doi.org/10.1038/s41559-023-02265-9
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