the scale of years (also called environmental stochasticity). Existing work has shown that
alterations in climatic variability can have much greater and more immediate impacts on
ecosystems than changes in mean climatic conditions (Hastings et al., 2021; Petchey et al.,
1997; Yang et al., 2019).
Short-term variations in climate metrics (e.g. precipitation, temperature) can be quan-
tified by their standard deviation, a measure of the amplitude of deviations from the mean,
and their temporal autocorrelation, a measure of the typical frequencies present. One of
the major alterations possible under climate change is a shift in the typical frequencies of
climate variability. More specifically, if the variability in local climates is analysed to de-
termine the dominant frequencies present, climate change in many geographic locations is
expected to lead to a downshift of these frequencies, or an increase in the temporal auto-
correlation of the climatic variability. In other words, climatic variability has a particular
“colour” (a non-uniform frequency spectrum) in any given location on the globe, and these
frequency spectra are changing shape, on average tending to more “reddened” - or more
autocorrelated - climatic variability (Di Cecco and Gouhier, 2018; T. Lenton et al., 2017; C.
Boulton and T. M. Lenton, 2015). The amplitude component of climatic variability is also
expected to increase with global warming, leading to greater extremes in climate conditions.
Since extreme climate conditions tend to be detrimental or, at the very least, challenging
for ecosystems, these extremes correspond to a further decrease in productivity during low
productivity years. While local conditions can certainly follow different patterns of change,
most geographic regions are expected to experience an increase in both the autocorrelation
and the amplitude of climatic variability (Di Cecco and Gouhier, 2018). The combined ef-
fect of these two changes in variability is that poor conditions will last longer, and be more
detrimental, than would be typical under normal variability. This scenario is the focus of
this paper.
The effect of changes in climatic variability on population dynamics has become a matter
of deep concern for ecologists (Vasseur and Yodzis, 2004; Vasseur, 2007b; Vasseur, 2007a;
Petchey et al., 1997; Yang et al., 2019; Hastings et al., 2021). It has been well-established that
environmental stochasticity has a strong effect on population dynamics, and so it is critical
that we understand the effect of changes to this stochasticity. Whether these changes will be
beneficial or detrimental to a given ecosystem is a complex issue (Yang et al., 2019; Petchey
et al., 1997), often with no clear answer (Barraquand and Yoccoz, 2013).
Recent work has demonstrated that increased reddening of climatic variability signif-
icantly increases extinction risk in populations whose dynamics include two stable states
that are stationary, one with high population numbers and one with very low population
numbers (van der Bolt et al., 2018). Here we consider the much less-studied case of a cyclic
system of interacting populations with two stable states: A self-oscillating (or cyclic) coexis-
tence state and a stationary extinction state. Below we describe the importance of oscillatory
states in real ecosystems, and the challenges these states present under climate reddening.
High amplitude multi-annual oscillations around cyclic coexistence states are ubiquitous
in consumer-resource systems, including predator-prey populations (Boutin et al., 1995; Han-
ski and Korpimaki, 1995; B. Kendall et al., 1999). Cyclic predator-prey systems are common
in the Northern Hemisphere (B.E. Kendall et al., 1998), and it is generally accepted that
their oscillations are inherent in the interaction dynamics of the system, i.e., they are not
simply the result of some external environmental forcing (Turchin, 2003). That is, while
external environmental factors certainly influence predator-prey cycles, these cycles would
continue in the absence of such forcing.
Many climate systems also exhibit either periodic oscillations or typical frequencies
(Bathiany et al., 2018), which can have strong effects on demographic rates (births, deaths,
predation, etc) (Paniw et al., 2021; De Jager et al., 2020; Bastille-Rousseau et al., 2018;
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