Abstract

For species of conservation concern, an essential part of the recovery planning process is identifying discrete population units and their location with respect to one another. A common feature among geographically proximate populations is that the number of organisms tends to covary through time as a consequence of similar responses to exogenous influences. In turn, high covariation among populations can threaten the persistence of the larger metapopulation. Historically, explorations of the covariance in population size of species with many (>10) time series have been computationally difficult. Here, we illustrate how dynamic factor analysis (DFA) can be used to characterize diversity among time series of population abundances and the degree to which all populations can be represented by a few common signals. Our application focuses on anadromous Chinook salmon (Oncorhynchus tshawytscha), a species listed under the US Endangered Species Act, that is impacted by a variety of natural and anthropogenic factors. Specifically, we fit DFA models to 24 time series of population abundance and used model selection to identify the minimum number of latent variables that explained the most temporal variation after accounting for the effects of environmental covariates. We found support for grouping the time series according to 5 common latent variables. The top model included two covariates: the Pacific Decadal Oscillation in spring and summer. The assignment of populations to the latent variables matched the currently established population structure at a broad spatial scale. At a finer scale, there was more population grouping complexity. Some relatively distant populations were grouped together, and some relatively close populations – considered to be more aligned with each other – were more associated with populations further away. These coarse‐ and fine‐grained examinations of spatial structure are important because they reveal different structural patterns not evident in other analyses.

Highlights

  • Efforts to conserve at-risk species can be hampered by a lack of understanding of the spatial structure of population units and the collective contributions of the populations to long-term persistence and recovery (Hanski 1998; Rieman and Dunham 2000; Bowen and Karl 2007; Fullerton et al 2011; Feldheim et al 2014)

  • We focused on subsequent model fitting by including each of the environmental covariates individually to dynamic factor analysis (DFA) models with 4 to 7 latent variables

  • Covariates were added to models with 4 to 7 latent variables according to their rank in a forward stepwise procedure because computational constraints prevented an exhaustive model search

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Summary

Introduction

Efforts to conserve at-risk species can be hampered by a lack of understanding of the spatial structure of population units and the collective contributions of the populations to long-term persistence and recovery (Hanski 1998; Rieman and Dunham 2000; Bowen and Karl 2007; Fullerton et al 2011; Feldheim et al 2014). Diversity across populations and their habitats can result in a degree of asynchrony among populations. Ecology and Evolution published by John Wiley & Sons Ltd. Ecology and Evolution published by John Wiley & Sons Ltd

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