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Numbers matter: how irruptive bark beetles initiate transition to self-sustaining behavior during landscape-altering outbreaks

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Abstract

Irruptive forest insects such as bark beetles undergo intermittent outbreaks that cause landscape-scale tree mortality. Despite their enormous economic and ecological impacts, we still have only limited understanding of the dynamics by which populations transition from normally stable endemic to irruptive densities. We investigated density-dependent changes in mountain pine beetle reliance on stressed hosts, host selection, spatial configuration of attacks, and the interaction of host selection and spatial configuration by performing a complete census of lodgepole pine across six stands and 6 years. In addition, we compared the dynamics of mountain pine beetle with those of other bark beetles. We found that as population size increased, reliance on stressed trees decreased and new attacks shifted to larger trees with thicker phloem and higher growth rates that can support higher offspring production. Moreover, the spatial configuration of beetle-attacked trees shifted from random to spatially aggregated. Further, we found evidence that beetle utilization of larger trees was related to aggregation behavior as the size of tree attacked was positively correlated at 10–25 m, within the effective distance of pheromone-mediated signaling. In contrast, non-irruptive bark beetle species did not exhibit such density-dependent spatial aggregation at the stand scale or switches in host selection behavior. These results identify how density-dependent linkages between spatial configuration and host utilization can converge to drive population transitions from endemic to irruptive phases. Specifically, a combination of stand-level spatial aggregation, behavioral shifts, and higher quality of attainable hosts defines a critical threshold beyond which continual population growth becomes self-driving.

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Acknowledgements

This investigation comprised a very large and complex multi-year field study that would not have been possible without invaluable contributions from Douglas Linton, Tony Ibaraki, Greg Smith, Andrew Copeland, Dion Manastyrski and Fred Davis. Funding was generously provided to ALC by Natural Resources Canada—Mountain Pine Beetle Initiative. Further support was provided by the University of Wisconsin–Madison College of Agricultural and Life Sciences, Graduate School and Vilas-Sorenson Professorship. We thank Anthony R. Ives, (UW-Madison) and Guillherme Ludwig (University of Campinas) for helpful conversations on analyzing point patterns.

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The authors have not disclosed any funding.

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Authors and Affiliations

Authors

Contributions

AC conceived, designed, and performed the experiment. MH analyzed the data. MH, KR, BA, CG and AC wrote the manuscript.

Corresponding author

Correspondence to Allan L. Carroll.

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Conflict of interest

We declare no conflicts of interest.

Additional information

Communicated by Amy Austin.

Supplementary Information

Below is the link to the electronic supplementary material.

442_2022_5129_MOESM1_ESM.png

Figure 1: Screeplots for principal components analysis, depicting A) the variability explained by each dimension; and the factors contributing to the B) 1st, C) 2nd, and D) 3rd dimensions (PNG 715 KB)

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Figure 2: Walkthrough of hypothesis testing process given a small (200 x 200 m) window from stand A in 2005. The example tests whether the distribution of trees attacked by mountain pine beetle is more (aggregation) or less (inhibition) spatially correlated than randomly distributed points (Poisson) based on the underlying joint density of beetle attacks. Point color denotes bark beetle guild for threshold limited (i.e., mountain pine beetle; black) and lower-stem (yellow) beetles. Gradient color denotes intensity of the joint density and is depicted on different scales for each null hypothesis. Scales are not shown because the relative intensity is more important than the realized values (PNG 470 KB)

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Figure 3: Alternative hypothesis testing for the spatial configuration of attacked trees based on A) a nearest-neighbor approach (Clark Evan’s Aggregation Index) and B) how our interpretations of observed L(r)-r functions compares. Colors denote bark beetle guild. Shapes in A correspond to significance assessed at the α=0.01 level where filled circles denote significant and open circles denote not significant. Shapes in B correspond to our interpretation of the observed L(r)-r functions, where filled circles denote significant aggregation, circles with crosses denote weak significant aggregation (i.e., the observed L(r)-r function barely exceeded the significance bands), open circles denote no significant aggregation, and X’s denote stand/year/guild combinations where there were fewer than 5 attacked trees. (PNG 186 KB)

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Supplemental Table 1: Criteria used to estimate the number of years since initial complete (A) or partial (B) attacks by bole-infesting bark beetles on lodgepole pine trees. Adopted from Carroll et al. (2006) (DOCX 20 KB)

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Supplemental Table 2: Distribution of prior stressors A) in each stand, and B) the number of trees with at least 0, 1, 2, 3, or 4 stressors (DOCX 17 KB)

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Supplemental Table 3: Observed L(r)-r functions for each guild/stand/year combination. Patterns not shown contained less than five attacked trees. Panels for each point pattern correspond to different null hypotheses of the underlying spatial distribution of available host trees. We provide our interpretation of whether each pattern exhibits significant aggregation or inhibition in the right-hand columns. (DOCX 6076 KB)

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Howe, M., Raffa, K.F., Aukema, B.H. et al. Numbers matter: how irruptive bark beetles initiate transition to self-sustaining behavior during landscape-altering outbreaks. Oecologia 198, 681–698 (2022). https://doi.org/10.1007/s00442-022-05129-4

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  • DOI: https://doi.org/10.1007/s00442-022-05129-4

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