Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2018 Nov 28;8(24):12425-12434.
doi: 10.1002/ece3.4563. eCollection 2018 Dec.

Predator-prey feedback in a gyrfalcon-ptarmigan system?

Affiliations

Predator-prey feedback in a gyrfalcon-ptarmigan system?

Frédéric Barraquand et al. Ecol Evol. .

Abstract

Specialist predators with oscillating dynamics are often strongly affected by the population dynamics of their prey, yet they are not always the cause of prey cycling. Only those that exert strong (delayed) regulation of their prey can be. Inferring predator-prey coupling from time series therefore requires contrasting models with top-down versus bottom-up predator-prey dynamics. We study here the joint dynamics of population densities of the Icelandic gyrfalcon Falco rusticolus, and its prey, the rock ptarmigan Lagopus muta. The dynamics of both species are likely not only linked to each other but also to stochastic weather variables acting as confounding factors. We infer the degree of coupling between populations, as well as forcing by abiotic variables, using multivariate autoregressive models MAR(p), with p = 1 and 2 time lags. MAR(2) models, allowing for species to cycle independently from each other, further suggest alternative scenarios where a cyclic prey influences its predator but not the other way around (i.e., bottom-up scenarios). The classical MAR(1) model predicts that the time series exhibit predator-prey feedback (i.e., reciprocal dynamic influence between prey and predator), and that weather effects are weak and only affecting the gyrfalcon population. Bottom-up MAR(2) models produced a better fit but less realistic cross-correlation patterns. Simulations of MAR(1) and MAR(2) models further demonstrate that the top-down MAR(1) models are more likely to be misidentified as bottom-up dynamics than vice versa. We therefore conclude that predator-prey feedback in the gyrfalcon-ptarmigan system is likely the main cause of observed oscillations, though bottom-up dynamics cannot yet be excluded with certainty. Overall, we showed how to make more out of ecological time series by using simulations to gauge the quality of model identification, and paved the way for more mechanistic modeling of this system by narrowing the set of important biotic and abiotic drivers.

Keywords: Falco rusticolus; Lagopus muta; MAR; VAR; consumer‐resource; population cycles.

PubMed Disclaimer

Figures

Figure 1
Figure 1
Time series of gyrfalcon (red) and rock ptarmigan (black) standardized log‐densities in NE Iceland, and their corresponding one step ahead predictions under the best‐fitted, full interaction matrix MAR(1) model. 100 model simulations one step ahead are plotted, for each year, as small points—red for predator and black for prey
Figure 2
Figure 2
Time series of predator (gyrfalcon) and prey (rock ptarmigan) log‐densities, simulated for 35 years from the same starting conditions as the data, for the full MAR(1) model (top panel, predator in red) and the MAR(2) “bottom‐up’’ model (bottom panel, predator in blue)
Figure 3
Figure 3
Cross‐correlation functions (CCFs) for the fitted models (A to F), defined as Cor(x 1,t+k, x 2,t) so that a maximum at k = −4 means that the predator time series x 2 peaks on average 4 years after the prey x 1. Each thin line corresponds to one simulation of the fitted model, within each panel. A and B show MAR(1) models, without and with interactions; while C to F show the CCFs of simulated MAR(2) models, without interactions (C), with only bottom‐up interactions (D), bottom‐up without delayed predator regulation (E), and (D) full MAR(2) model. The cross‐correlation for the real data is highlighted as a thick black line in all panels

References

    1. Andersson, M. , & Erlinge, S. (1977). Influence of predation on rodent populations. Oikos, 29, 591–597. 10.2307/3543597 - DOI
    1. Angelstam, P. , Lindström, E. , & Widén, P. (1984). Role of predation in short‐term population fluctuations of some birds and mammals in Fennoscandia. Oecologia, 62, 199–208. 10.1007/BF00379014 - DOI - PubMed
    1. Barraquand, F. , Høye, T. T. , Henden, J. A. , Yoccoz, N. G. , Gilg, O. , Schmidt, N. M. , … Ims, R. A. (2014). Demographic responses of a site‐faithful and territorial predator to its fluctuating prey: Long‐tailed skuas and arctic lemmings. Journal of Animal Ecology, 83, 375–387. 10.1111/1365-2656.12140 - DOI - PubMed
    1. Barraquand, F. , Louca, S. , Abbott, K. C. , Cobbold, C. A. , Cordoleani, F. , DeAngelis, D. L. , … Tyson, R. C. (2017). Moving forward in circles: Challenges and opportunities in modelling population cycles. Ecology Letters, 20, 1074–1092. 10.1111/ele.12789 - DOI - PubMed
    1. Barraquand, F. , New, L. F. , Redpath, S. , & Matthiopoulos, J. (2015). Indirect effects of primary prey population dynamics on alternative prey. Theoretical Population Biology, 103, 44–59. 10.1016/j.tpb.2015.04.002 - DOI - PubMed

LinkOut - more resources