Abstract
Invasion biology is a relatively young discipline which is important, interesting and currently in turmoil. Biological invaders can threaten native ecosystems and global biodiversity; they can incur massive economic costs and even introduce diseases. Invasion biologists generally agree that being able to predict when and where an invasion will occur is essential for progress in their field. However, successful predictions of this type remain elusive. This has caused a rift, as some researchers are pessimistic and believe that invasion biology has no future, whereas others are more optimistic and believe that the key to successful prediction is the creation of a general, unified theoretical framework which encompasses all invasion events. Although I agree that there is a future for invasion biology, extensive synthesis is not the way to better predictions. I argue that the causes of invasion phenomena are exceedingly complex and heterogeneous, hence it is impossible to make generalizations over particular events without sacrificing causal detail. However, this causal detail is just what is needed for the specific predictions which the scientists wish to produce. Instead, I show that a limited type of synthesis (integration of data and methods) is a more useful tool for generating successful predictions. An important implication of my view is that it points to a more pluralistic approach to invasion biology, where generalization and prediction are treated as important yet distinct research goals.
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Notes
According to the National Research Council, “[t]he aggregate figure for crop and timber losses and for the use of herbicides and pesticides to fight invasive species exceeds $100 billion per year”, in the USA (National Research Council 2002, p.15). This figure is restricted to crops and does not include the funds spent on managing invasions of natural ecosystems.
In recent years there have been a number of papers published by practicing invasion biologists, with titles such as “Another call for the end of invasion biology” (Valéry et al. 2013).
I use the term ‘specificity’ in this paper, because it captures the fact that invasion biologists must specify which organism will invade, which particular environment (ecosystem or community) it will invade, how far it will spread, how fast it will spread, and of course whether it will succeed. I should note that invasion biologists often use the term ‘precision’ to refer to the types of predictions they should aim for. While there is overlap between these two terms, ‘precision’ is a technical term which is used differently in various contexts, some of which are not applicable to invasion biology (see Matthewson and Weisberg 2009). Instead, the term ‘specificity’ is meant to be a more neutral term, which captures only these aspects of ‘precision’ (see also pp. 5–6).
A popular view that has emerged in philosophy of science is that laws do not have to be universal in order to count as true laws, (Colyvan and Ginzburg 2003). In other words, laws in biology (just like laws in physics or chemistry) can have exceptions. Therefore the generalizations and regularities that we find in ecology can count as laws (Colyvan and Ginzburg 2003; Cooper 1998). If we adopt this position, we may be able to find laws or at least regularities in invasion biology, which could prove to be useful for explaining invasions. Yet even if this is the case, this will not help in the case of predictions.
In fact, interspecific competition is considered to be one of the few unifying themes in ecology. Many of those who argue that ecology is lawless believe that the problem applies mainly to community ecology, while population ecology (especially competition and predation) fare much better (Lawton 1999; Roughgarden 2009). However, the approach to studying invasions as a type of competition was very popular in the 1960s and 1970s and became one of the two major conceptual frameworks of invasion biology. Yet despite important advances models and experiments of interspecific competition, predictions of invasions remained elusive (Davis 2011; Zenni and Nuñez 2013). A similar point can be made with respect to ‘macroecology’, which refers to the study of ecological interactions at large scales, in terms of both time and space. The idea here is that at these scales general patterns re-emerge. Again, while this approach became popular in invasion biology, in the study of biodiversity and resistance to invasion it did not yield any important predictions.
I should note that this is just one of many of calls for synthesis in recent invasion research. More examples can be found in: (Blackburn et al. 2011; Catford et al. 2009; Gundale et al. 2013; Kolar and Lodge 2001; Milbau et al. 2008; Moles et al. 2012; Perkins et al. 2011; Richardson and Pyšek 2006; Richardson and Ricciardi 2013; Romanuk et al. 2009; Sousa et al. 2011; Van Kleunen et al. 2010).
Of course, management of invasions is an important goal for invasion research, and it is quite well funded. However, management of invasions that have already occurred or have already started is very costly, whereas predictions could lead to the complete avoidance of invasions, greatly reducing economic and environmental costs.
I should note that data integration and methodological integration are the most prevalent types of integration in invasion biology. Other examples of data integration include meta-analyses, (see for example Davidson et al. 2011). Other examples of methodological integration include mathematical and computational models from a range of different ecological sub-disciplines, laboratory experiments, field experiments etc (such as Dunstan and Johnson 2007).
The new studies were published about a decade later, perhaps in response to the criticism the authors received from the community.
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Acknowledgments
Author would like to thank Michael Weisberg, Carlos Santana, Adrian Curry, Eric Desjardins, Dan Hicks, Maureen O' Malley, Kim Sterelny and two anonymous reviewers for helpful comments on earlier drafts of this paper.
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Elliott-Graves, A. The problem of prediction in invasion biology. Biol Philos 31, 373–393 (2016). https://doi.org/10.1007/s10539-015-9504-0
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DOI: https://doi.org/10.1007/s10539-015-9504-0