Reply to Youngflesh and Lynch: Migration and population growth rate in animal black-swan events
Research Article
March 7, 2017
Letter
October 12, 2017
We thank Youngflesh and Lynch (1) for their thoughtful comments on our paper (2). As they note, we should have mentioned immigration and emigration alongside the intrinsic population properties (e.g., population birth rate, mortality, and age at maturity) and extrinsic causes of black-swan events (e.g., extreme climate, disease, predation, competition, exploitation, and habitat destruction). After all, immigration and observation error are the only possible explanations for sudden abundance increases above those possible from the maximum biological rate of increase.
Youngflesh and Lynch (1) use a simple approach to flag which time series have population increases (r) that are greater than the demographic maximum [Cole’s (3), ], and hence may be driven by migration. However, they estimate the greatest realized without accounting for observation error (uncertainty in measuring population abundance); consequently, there will be false-positive cases of apparent high (Fig. 1 A–C). If we calculate for the populations referenced by Youngflesh and Lynch (1) while accounting for moderate observation error [coefficient of variation (CV) = 0.2], only six populations remain with probability Pr( > ) and the 95% credible interval excludes in only two cases (Fig. 1D). These two populations include lesser spotted dogfish () in the North Sea, which may indeed be an example of immigration from the English Channel due to thermal habitat expansion (4). In contrast, 18 of 26 populations with high probability of black-swan events in our original analysis were robust to allowing observation error (CV = 0.2).
Fig. 1.

In our paper, we examined the root cause of black-swan events wherever possible (2). The population of red grouse () flagged by Youngflesh and Lynch (1) is one of three red grouse populations in the dataset and has been intensely studied. The parasitic nematode , not emigration, is known to cause periodic population crashes for these populations (5, 6), and sampling error due to the time series being based on hunting records, not immigration, may be responsible for the high apparent maximum rates of population increase (6).
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In addition, immigration and emigration should, on average, be equally likely, yet the observed black-swan events are nearly all downward. This either means that most such events are caused by population die-offs or that migration is surprisingly one-sided, involving rapid emigration from stable populations and large but slower immigration to restore populations. Naturally, emigration and population die-offs followed by immigration are not mutually exclusive: Die-offs can open excellent habitat that attracts individuals from other areas.
Migration is one of many possible causes of apparent black-swan events in animal populations. We agree that migration likely affects some of the populations in our analysis and agree with the need for caution when fitting models to data from open populations. On a case-by-case basis, modeling factors, such as migration and disease dynamics, yield more realistic predictions of population abundance and can explain events that would otherwise be considered black swans. However, we rarely, if ever, model all factors affecting a population, and we therefore maintain that allowing for heavy-tailed process error is an important step toward allowing for ecological surprises.
Code and data for these analyses can be found at https://github.com/seananderson/heavy-tails-response and Zenodo at https://doi.org/10.5281/zenodo.998224.
Acknowledgments
Funding was provided by a Simon Fraser University Graduate Fellowship and David H. Smith Conservation Research Fellowship (to S.C.A.), the Natural Sciences and Engineering Research Council of Canada (S.C.A., A.B.C., and N.K.D.), and the Canada Research Chairs Program (N.K.D.). T.A.B. was funded in part by the Richard C. and Lois M. Worthington Endowed Professor in Fisheries Management.
References
1
C Youngflesh, HJ Lynch, Black-swan events: Population crashes or temporary emigration? Proc Natl Acad Sci USA 114, E8953–E8954 (2017).
2
SC Anderson, TA Branch, AB Cooper, NK Dulvy, Black-swan events in animal populations. Proc Natl Acad Sci USA 114, 3252–3257 (2017).
3
LC Cole, The population consequences of life history phenomena. Q Rev Biol 29, 103–137 (1954).
4
C Sguotti, CP Lynam, B García-Carreras, JR Ellis, GH Engelhard, Distribution of skates and sharks in the North Sea: 112 years of change. Glob Change Biol 22, 2729–2743 (2016).
5
GR Potts, SC Tapper, PJ Hudson, Population fluctuations in red grouse: Analysis of bag records and a simulation model. J Anim Ecol 53, 21–36 (1984).
6
PJ Hudson, AP Dobson, D Newborn, Prevention of population cycles by parasite removal. Science 282, 2256–2258 (1998).
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© 2017. Published under the PNAS license.
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Published online: October 12, 2017
Published in issue: October 24, 2017
Acknowledgments
Funding was provided by a Simon Fraser University Graduate Fellowship and David H. Smith Conservation Research Fellowship (to S.C.A.), the Natural Sciences and Engineering Research Council of Canada (S.C.A., A.B.C., and N.K.D.), and the Canada Research Chairs Program (N.K.D.). T.A.B. was funded in part by the Richard C. and Lois M. Worthington Endowed Professor in Fisheries Management.
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The authors declare no conflict of interest.
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Reply to Youngflesh and Lynch: Migration and population growth rate in animal black-swan events, Proc. Natl. Acad. Sci. U.S.A.
114 (43) E8955-E8956,
https://doi.org/10.1073/pnas.1714157114
(2017).
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