Choice of baseline affects historical population trends in hunted mammals of North America
Introduction
Species population declines and extinctions undermine the functioning and resilience of ecosystems on which humans and wildlife depend (Cardinale et al., 2012; Oliver et al., 2015). To monitor and respond to species losses, changes in population abundance are used as a sensitive metric of change (Collen et al., 2011; Shoemaker and Akçakaya, 2015) and have been incorporated into globally adopted biodiversity indicators such as the Living Planet Index, which tracks changes in vertebrate population abundance from 1970 (Collen et al., 2009). However, data on population abundance typically become scarcer beyond a few decades from the present, prior to the implementation of species monitoring programmes (Willis et al., 2005; Bonebrake et al., 2010).
Knowledge of historical populations acts as an antidote to ‘shifting baseline syndrome’; a phenomenon in which with each new human generation comes a lowered expectation of a species population norm (Pauly, 1995; Kahn and Friedman, 1995; Soga and Gaston, 2018). Historical population baselines have many practical policy implications, for example when defining population recovery and conservation legacy, deciding harvest quotas, and influencing the general public's perception of a species (Papworth et al., 2009; Davies et al., 2014; Roman et al., 2015; Akcakaya et al., 2018; see Fig. 1a). Additionally, estimating historical populations can help to differentiate between a population trend that is unidirectional or cyclical, such as the Atlantic Multidecadal Oscillation inducing bidirectional changes in fish abundance (Jackson et al., 2001; Willis et al., 2007; Sundby and Nakken, 2005; see Fig. 1b). Without long-term measurements, observers may misattribute downward phases of natural population cycles as human-caused population declines (Koslow and Couture, 2013). Finally, historical population data can help to identify historic drivers of population change (see Fig. 1c), which is important for quantifying the relative significance of each past and present threat in order to develop threat-specific management strategies and inform future scenario modelling (Baker and Clapham, 2004; Pinnegar and Engelhard, 2008).
Many techniques available to reconstruct historical population baselines emerged from the discipline of marine historical ecology (Lotze and Worm, 2009). Faced with the need to sustainably manage fish stocks, fisheries researchers have used recorded history (e.g. ‘local ecological knowledge’) (Sáenz-Arroyo et al., 2005; Turvey et al., 2010), archaeogenomic data (e.g. analysis of relative stable isotope concentrations) (Finney et al., 2002), and fish stock assessments from historical catch data (Myers and Worm, 2003; Baker and Clapham, 2004) to extrapolate population size over time and capture stock collapses that pre-date direct monitoring.
Recorded history has also provided us with historical population estimates for terrestrial species, although not as frequently as in the marine realm. These studies are extremely valuable in painting a picture of past population condition (Cole and Woinarski, 2000; Rowe and Terry, 2014), but with each historical data source comes its own unique set of limitations. For instance, museum and fossil records are often patchy and taxonomically biased, and local ecological knowledge generally only covers a couple of generations spanning <100 years (Miller, 2011). Here, we add to our growing knowledge on reconstructing population baselines by focussing on harvest data of terrestrial mammals as another data source which holds great potential in historical baseline reconstruction.
Reports from the Hudson's Bay Company (HBC), Canada, have been previously used to document lynx (Lynx canadensis) and muskrat (Ondatra zibethica) population cycles (Elton and Nicholson, 1942a; Elton and Nicholson, 1942b), predator-prey dynamics of lynx and snowshoe hare (Krebs et al., 1995), and the potential roles of climate, productivity and disease in these cycles (Gamarra and Solé, 2000; Yan et al., 2013; Row et al., 2014). Here, we (a) show the utility of these harvest data to reconstruct historic populations by applying a stochastic population model first developed for marine vertebrates (Christensen, 2006), (b) use these population reconstructions to demonstrate that baselines differ when using over 100 years of data compared to <50 years of data and (c) show that choice of different baseline years results in different interpretation of estimated population trends.
Section snippets
Reconstructing historical abundance trends
To reconstruct historical trends in terrestrial mammal abundance, we used a stochastic stock reduction analysis (SSRA) originally developed by Walters et al. (2006) to analyse trends in fish populations. This method uses a simple growth model, and can be applied to species for which we have limited knowledge of life history parameters and catch-per-unit-effort (Kimura et al., 1984). The model and method outlined below was described in detail by Christensen (2006) for establishing historical
Analysis of historical baselines
The median population change across the eight species for 1850–2009 was a 15% decrease (−0.1%/yr), whereas populations between 1970 and 2009 showed a 4% increase (0.1%/yr) (paired t-test: t = −3.036,1 d.f. = 7, p = 0.002, n = 8; Table 1, Fig. 3a). Choice of baseline year resulted in a switch from a downward population trend for the period 1850–2009 to an upward trend for 1970–2009 for four species (Arctic fox, bobcat, polar bear, beaver) (Fig. 3b; Table S8; Fig. S1). Six species exhibited a
Discussion
Our study demonstrates that for eight species of Canadian mammals, choice of baseline year greatly affects our understanding of historic population change. Collectively, using an 1850 baseline year rather than 1970 significantly altered the population trend. Analysis of individual species demonstrated that deriving population change from the 1850 baseline resulted in four species shifting from a population increase since 1970 to a population decrease of between 0 and −22% since 1850, and the
Conclusions
By failing to estimate historical baselines, we may miss the historical demise of populations which have been exploited by humans since at least the 18th century in Europe and North America (Deinet et al., 2013), and adversely influence our perception of what constitutes species population norms. This may affect how scientists, decision makers and the general public perceive the growth of a population as a result of conservation action and species protection. While in many northern hemisphere
CRediT authorship contribution statement
Amy C. Collins: Conceptualization, Methodology, Software, Formal analysis, Writing - original draft, Visualization. Monika Böhm: Resources, Writing - review & editing, Supervision. Ben Collen: Conceptualization, Validation, Writing - review & editing, Supervision.
Declaration of competing interest
The authors have no competing interests to declare.
Acknowledgements
Dedicated to the memory of Ben Collen, a truly inspiring mentor and friend.
The authors would like to thank Christensen (2006) for original R code to the SSRA model, and Louise McRae, John Mola and Kate Tiedeman for comments on the manuscript.
Funding sources
Funding for this project was awarded by the Vodafone Foundation World of Difference programme and a generous grant from the Rufford Foundation.
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2022, One EarthCitation Excerpt :It is important to note that comparisons between regions should be interpreted with care because of the vastly different environmental conditions around the world at the onset of our data in 1970; assessments can skew the state or trends in biodiversity without considering shifting baselines.47 The baseline year chosen can be important for assessing long-term trends,48 particularly in regions where high human impact has been prevalent over centuries. In the case of North America and Western Europe, the baseline of 1970 hides a historical decline in species abundance that occurred as land use was transformed after the industrial revolution;49 after 1970, trends may therefore show less decline as populations stabilize, but at lower numbers.
Extending temporal baseline increases understanding of biodiversity change in European boreal waterbird communities
2021, Biological ConservationCitation Excerpt :Nevertheless, if eutrophication has been the main driver of their breeding numbers since the 1850s, as previous authors have asserted, its effect has turned from positive to negative, probably at some point between 1951–1970 and 1996–2015. This finding further underlines the importance of properly defining the temporal baseline against which population and biodiversity changes are evaluated, to set biologically realistic goals for conservation and management decisions and measures (cf. Collins et al., 2020). Data on temporal trends in water chemistry variables indicating eutrophication (e.g. total phosphorous, or TP, total nitrogen, or TN; and chlorophyll a; Ekholm and Mitikka, 2006) are not available from our study lakes.
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In memory of Dr. Ben Collen.