Abstract
Wildlife tracking is one of the most frequently employed approaches to monitor and study wildlife populations. To date, the application of tracking data to applied objectives has focused largely on the intensity of use by an animal in a location or the type of habitat. While this has provided valuable insights and advanced spatial wildlife management, such interpretation of tracking data does not capture the complexity of spatio-temporal processes inherent to animal behaviour and represented in the movement path. Here, we discuss current and emerging approaches to estimate the behavioural value of spatial locations using movement data, focusing on the nexus of conservation behaviour and movement ecology that can amplify the application of animal tracking research to contemporary conservation challenges. We highlight the importance of applying behavioural ecological approaches to the analysis of tracking data and discuss the utility of comparative approaches, optimization theory and economic valuation to gain understanding of movement strategies and gauge population-level processes. First, we discuss innovations in the most fundamental movement-based valuation of landscapes, the intensity of use of a location, namely dissecting temporal dynamics in and means by which to weight the intensity of use. We then expand our discussion to three less common currencies for behavioural valuation of landscapes, namely the assessment of the functional (i.e. what an individual is doing at a location), structural (i.e. how a location relates to use of the broader landscape) and fitness (i.e. the return from using a location) value of a location. Strengthening the behavioural theoretical underpinnings of movement ecology research promises to provide a deeper, mechanistic understanding of animal movement that can lead to unprecedented insights into the interaction between landscapes and animal behaviour and advance the application of movement research to conservation challenges.
This article is part of the theme issue ‘Linking behaviour to dynamics of populations and communities: application of novel approaches in behavioural ecology to conservation’.
Keywords: home range, migration, biologging, resource selection, optimization, landscape conservation
1. Introduction
Animal movement data, consisting of temporally explicit relocations of individuals in space, provide detailed insights into animal–environment interactions. Because all environments are spatially structured (heterogeneous with respect to the distribution of different biotic and abiotic elements), movement is the fundamental behaviour by which individuals access resources, avoid risks and interface with conspecifics [1]. As such, movements underpin variation in individual fitness and other ecological and evolutionary processes such as gene flow, community structure and species density and distribution [2,3]. The increasing ease of collecting movement data on animals holds immense promise for providing unique understanding of how and why animals move across space, driving a renaissance of research into spatial ecology [4,5]. Critically, a mechanistic understanding of drivers of the movement offers actionable information to address contemporary conservation challenges, with specific application to landscape planning, wildlife protection, mitigating human wildlife conflicts and managing invasive species [6–9].
Technological advances in biologging and other sensing approaches used for animal tracking [9,10] have enabled the collection of fine-scale, long-term relocation data on organisms, which provides new opportunities for both basic (e.g. ontological changes in strategies) and applied (e.g. a response to human-driven landscape changes) research. With these advances, the quality and complexity of movement data has increased exponentially [10]. Given that most data on movement are captured remotely, common constraints of observational studies can be avoided (i.e. partial observability, bias and observer influence). However, such data present different challenges related to the contextualization of animal relocation data, specifically the interpretation of why an animal uses a given location without having adequate information on the latent process of interest.
Approaches used to study animal behaviour provide a useful lens through which to view movement ecology research that can lead to a deeper understanding of movement processes. Building on the fundamental currency of ecological and evolutionary research on behaviour, a key direction in movement ecology is to develop links between spatio-temporal behavioural patterns and metrics of fitness (e.g. resource aggregation rates, survival or reproduction) to enhance understanding of the causes and consequences of movement behaviour [11]. Classically, behavioural studies of this nature focused on quantifying fitness payoffs (i.e. the value) of behaviours of interest and contrasting the returns from different strategies (i.e. optimality analysis). However, the accurate quantification of the collective costs and benefits of animal movements (i.e. derivation of remotely sensed metrics of fitness to relate to movement decisions) is challenging given they are influenced by highly variable intrinsic and extrinsic factors [12]. As a result, research has focused more commonly on the consequences of movement to population distribution [2] or the description of movement phenomena [13]. Recent applications of tracking-based monitoring have allowed the quantification of fitness parameters, allowing insights to the relation between fitness and movement tactics (e.g. reproductive rate [14] or mortality [15]) or lack thereof [16]. Developing and quantifying individual location-based metrics derived from movement that accurately capture mechanistic and functional aspects of key behaviours can offer a powerful direction to advance movement ecological research, connect it explicitly to its behavioural theoretical underpinnings and, thereby, enable direct application to conservation challenges.
Because movement data are inherently spatial and the behaviours they represent have direct links to fitness, one of the most exciting promises of movement ecology is the ability to interpret the value of landscapes to individuals. However, this concept has been underserved in the literature. Here, we aim to consolidate the current approaches used to value locations within landscapes from movement data. By providing a template for developing indices capturing different aspects of movement, we intend to facilitate understanding of the importance of a location to an individual. We aim for this compilation to serve as a framework by which to interpret movement through its fundamental behavioural underpinnings and, thereby, help consolidate the mechanistic and theoretical foundation of the discipline of movement ecology. To enable a behavioural ecological approach to movement analysis, we first highlight relevant topics at the interface of behavioural theory and movement ecology. We then outline and discuss four fundamental currencies for the economic valuation of landscapes using movement data (table 1). Initially, we review the classic movement ecological currency focused on valuing locations by quantifying the intensity of use, highlighting the importance of using approaches that explore heterogeneity (including temporal dynamics) in this process. We then discuss three additional approaches for valuing locations from movement data, each of which offers unique insights into an aspect of movement behaviour: interpretation of the function of movement, assessment of the structural properties of locations relative to the broader landscape and commodifying movement data in a fitness framework (figure 1). We highlight key areas where these approaches can be developed further that will provide greater insights into animal behaviour and locational importance. Finally, we discuss the implications for our analyses to conservation.
Table 1.
class | definition | metrics | methods |
---|---|---|---|
intensity | How much is a location used? | fix density, time density, weighted use, persistence velocity, dot product, time to return, first passage time, probability of occurrence | home range estimation, habitat preference, resource selection, recurrence |
functional | What is an individual doing at a location? | speed, movement states (based on turning angle and speed) | hidden Markov modelling, behavioural change point analysis, agent-based models |
structural | How does a location influence use of the broader landscape? | connectivity, proximity, neighbourhood statistics (degree, interspersion, isolation, dispersion), network metrics (weight, degree, centrality) | network theoretical approaches, circuit theory, Fragstats, least-cost path |
fitness | What is the payoff of a location? | caloric expenditure/return, reproduction, survival, risk (predation), fitness proxies | physiological modelling (basal metabolic rate), vaginal implant transmitters, mortality monitoring, overall dynamic body acceleration |
2. Behavioural underpinnings of movement data
The key approaches to research design common to behavioural ecological research are well suited to movement ecology and can provide useful direction to the analysis of movement data. Prominent advances in behavioural ecological theory have been derived from the use of a comparative approach, economic valuation of behaviours and assessment of optimality [17]. Movement data are ideal for such approaches given they provide repeated measures on an individual, which is the fundamental unit of data collection in behavioural ecology. Furthermore, the spatio-temporal nature of the data allows the resolution of fundamental units of behaviour with conservation relevance (e.g. time-spent, expenditure and relative use of locations).
While the preponderance of the movement ecology literature has focused on method development to account for the complex spatio-temporal structure inherent in the movement process, the basic tenets of movement ecology are underlain by fundamental ecological and behavioural theories. The behavioural theory with the most direct application to the study of animal movement and space use is optimal foraging theory (i.e. patch/diet selection, marginal value theorem (MVT), giving up densities and landscape of fear), given movement has served as a unit of valuation to assess foraging strategies [18]. For instance, the MVT [19] provides the framework for patch-occupancy dynamics, formulated in respect to the time spent in a location rather than the nuances of the movement in a location. Relatedly, the theory of ideal free distribution (IFD) largely underpins the interpretation of resource selection behaviour [20,21]. While these foundational theories have served as a critical springboard to understanding movement behaviour, their application to systems that lack the basic metrics upon which these theories are based (i.e. energetic gain in the case of MVT and population growth in the case of IFD) merits consideration. For example, while the IFD fundamentally underpins our interpretation of habitat selection (i.e. intensity of use reflects differences in available resource value), intraspecific competition can lead to opposite mechanisms driving the intensity of use (i.e. density of use may reflect refuge habitats from despots rather than the intrinsic fitness value of the landscape) [21]. Similarly, incorporation of perceived risk can fundamentally structure distributions and use of habitats [22,23], which again can lead to misinterpretation of the value of specific locations on the landscape based solely on the intensity of use behaviour. Despite wide recognition of these drivers of the underlying process structuring space use, the risk of misinterpreting the mechanism underlying the intensity of use can be minimized through study design or with supporting behavioural information.
Despite the dominant role of foraging theory in structuring the analyses and questions asked of movement data, integrating movement ecology with other behavioural theories promises to enhance a practical understanding of animal space use as well as advance the testing and development of behavioural theory across larger scales and a greater number of individuals than can be accomplished with traditional methods such as direct observation. We highlight several fundamental behavioural lines of inquiry that movement is uniquely suited to help resolve (table 2). With access to increasingly high-resolution data (both spatially and temporally), greater insights into drivers of differentiation in the intensity of use are being derived by applying approaches initially used to study behavioural and phenotypic plasticity. Specifically, quantifying reaction norms (i.e. the patterns of individual phenotypes or behaviours expressed across an environmental range [32], analogous to functional responses when assessed at the population level [33]) in respect to resource selection along gradients of landscape variables is a particularly powerful analytical framework to understand individual responses to and requirements of landscape features. This framework is particularly valuable for exploring behavioural expression related to changes in landscapes, as commonly induced by human activities [34].
Table 2.
behavioural category | example issue | example metric | reference |
---|---|---|---|
optimal foraging theory | search behaviour | patch occupancy | [24] |
trade-offs | dispersal decisions | net squared displacement | [25] |
competition | costs to subordinates | rank-based space use | [26] |
alternative strategies | male reproductive states | daily activity budget | [27] |
group living | group size constraints | daily movement distance | [28] |
parental investment | impact of maternal investment on survival | foraging trip length | [29] |
behavioural syndromes | factors influencing different movement tactics | resource selection | [30] |
plasticity | response to human activity | vagility | [8] |
seasonal response | influence of longitudinal changes in resources | behavioural change point analysis | [31] |
Theoretically underpinned behavioural metrics derived in a spatially explicit manner can be interpreted as the value of landscapes for those behaviours. Linking behaviour to spatial locations provides a relevant and tangible means by which to summarize behavioural responses to landscape features, which can provide an elemental insight for structuring conservation planning and actions spatially. From the fore-mentioned functional response analyses that help elucidate behavioural modification of space use across gradients of particular features [35] to the quantification of the spatial degree of feature avoidance that can be translated into estimates of habitat loss [36], better resolution of spatial behaviour relative to landscape features has direct applied relevance. Mechanistic underpinnings of the interpretation of a metric are particularly important for the application of movement ecology to conservation objectives. A further development of metrics with strong theoretical underpinnings are important to resolve the specific contexts in which such metrics are meaningful.
3. Dissecting heterogeneity in the intensity of use
The focus of many movement-based analyses centres on the intensity of use metrics to infer the value of locations within landscapes and the theoretical underpinnings of such procedures are well established. The analysis of time spent in given locations can provide insights into investment in those locations by animals, which is a critical component of fitness. However, the interpretation of time spent in a location can be complex, and assumptions risk misinterpreting the rationale for prolonged use of a location (e.g. territorial exclusion from preferred areas sensu predictions from ideal despotic distribution theory). Awareness of this challenge has driven efforts to restructure the analysis of the intensity of use metrics. While we discuss the value of differentiating the behaviours associated with recorded locations when analysing movement data below, here we highlight the importance of using approaches to investigate spatio-temporal heterogeneity in the intensity of use across and within individuals. Behavioural assessment at the individual level is critical to resolve underlying mechanisms of the intensity of use patterns. While still the norm, simple aggregation of movement data to determine the intensity of use underserves the rich spatio-temporal information being collected through GPS tracking on movement patterns of individuals [37]. Direct assessment of the temporal aspect of space use, as outlined by time geography (see below), offers insights into heterogeneity in space use by an individual. In addition, we discuss the value of focusing analyses at the unit of data collection, the individual, rather than aggregating across individuals to derive an average, population-level metric.
Time geography is an integrative framework focused on the analysis of both the spatial and temporal dimension of a process [38]. Temporal variation in use can serve to identify changes in landscape value driven by ecological dynamics (i.e. seasonality) or related to known ontogeny (i.e. life-history stages), serving to address questions focused on the underlying biological dynamics in a system (table 2). The intensity of use of a location can be assessed as a function of time, analogous to the classic functional response where the intake rate of a consumer is a function of food density [39]. Such an approach (i.e. plotting cumulative use as a function of time) can distinguish a consistent increase in use intensity (type 1) reflecting daily required use (e.g. water hole), from use that saturates at a point in time (type 2) as expected to result from resource denudation, or sporadic use of a location (type 3) associated with resource pulses. These patterns of use can then be plotted to offer insights into heterogeneity in behaviour (figure 2). While relatively infrequent in the literature, one of the most interesting aspects of temporal dynamics in movement are return rates or revisitation. Revisitation and directed interpatch movement coupled with short-term occupancy may indicate strikingly a different value of a location than an extended, non-repeated stay [40,41], but would be considered equally in most contemporary analysis of the intensity of use [42]. The analysis of recursion rates or time spent in a patch initially focused on herbivore–vegetation dynamics, with relevance to range management [43], which has provided new insights to herbivore ecology, migratory behaviours and interspecific interactions [42,44]. Building on this, recursion and directed movement are recognized as potentially key behaviours to facilitate the study of cognitive decision processes and spatial memory [45,46]. Longer-term repeated-use patterns, such as inter-annual [47] or inter-generational [48] migratory patterns, offer additional avenues to investigate responses to slower landscape dynamics (e.g. phenological shifts and land-use change). Contemporary work focused on refined definitions of spatial and temporal patterns of use can provide new insights into the behaviours underlying the movement process.
While recursion and other temporal patterns of use are an important type of heterogeneity in the intensity of use metrics, the heterogeneity of use between time periods by an individual (i.e. ontogeny) or across individuals is another critical facet that can serve to gain understanding of behavioural mechanisms. Movement studies frequently smooth over the heterogeneity among individuals, time period (e.g. years) or both, reducing the inference gained by analyses of movement data. Normative behaviours are commonly used to derive landscape-level assessments, either through the density of use metrics or weighted approaches such as resource selection functions, which take into account the relative availability of a location attributes when analysing its weight of use. However, assessing and representing heterogeneity across individuals is critical for accurate characterization of a locational value based on use intensity, particularly given that heterogeneity can be driven by variation in responses to features related to personality, different life-history strategies (i.e. behavioural tactics) or different experiences (e.g. learned knowledge base) [46]. Leveraging variation in individual spatial behaviour in a comparative analytical approach common to behavioural ecological studies can help resolve the underlying mechanisms of heterogeneity. Such an approach can lead to a refined understanding of differences in spatial behaviours (as manifested from different tactics) or requirements (e.g. clustering individual-level resource selection function (RSF) coefficients to define tactics in a population [30]). Furthermore, juxtaposing the intensity of use between conspecifics can provide deeper insights into a landscape value, as exemplified by studies of ecological traps that identify features serving as sinks [22].
4. Assessing the function of movements
Determining the function of movements (i.e. what animals are doing at a location) remains a fundamental focus of movement ecology, as it provides a critical lens by which to understand behaviour, interpret the intensity of use metrics and evaluate locations on the landscape behaviourally [1]. Broadly, functional identification of movement typically focuses on mechanic definition (i.e. properties or type) or phenomenological characterization (i.e. underlying motivation) of a movement segment. In the former, the movement path or locational use can be discretized into movement states (e.g. encamped [49]), while in the latter different behavioural phenomenon, often identified independently, can be used to stratify the movement path (e.g. periods of rest [50]; figure 3). Complicating such functional definition is the fact that characteristic movement properties can reflect multiple behavioural phenomena (i.e. encamped movement state may reflect resting, nesting or intensive foraging).
Common approaches to discern the function of movements using the mechanics of a path define structural transition points (i.e. changes in movement properties) that serve to categorize movement types/states from which its function can be discerned. The definition of movement properties along the path can be used for discretization, whereby modelling approaches are used to categorize observations (e.g. locations) into putative states (figure 3a). This approach provides insights into latent processes and has become more common in the movement ecology literature [31,51,52]. Resolving the type of movement represented at different locations and the frequency with which such movements occur provides critical insights into activity budgets, attractants and feature avoidance, which ultimately allow inference to movement function. Such approaches have the potential to identify when and where the motivation for movements shift. This inference can be gained directly by simple density functions of movement states [53] whereby types of movement are related to landscape features, by contrasting the timing and relationship between movement states and known features [45] or using relative approaches such as RSFs or step selection functions on each state independently or in combination [54]. Such approaches provide a means to resolve mechanistic drivers of spatial heterogeneity in occurrence and population distribution building on approaches highlighted above (see §3). Analyses of discretized movement paths have also provided rare insights into the function of memory in movement behaviour, one of the fundamental and enigmatic areas of movement ecology [46]. Despite the importance of determining its underlying function, and the valuable insight gained by doing this, relying on the movement path itself to define function, however, is challenging without contextual information [52].
Phenomenological determination of movement properties provides an alternative approach to investigate movement function. Typically, phenomenological characterization entails additional information paired with the movement data, including data from paired sensors (e.g. physiological biologgers) or observations (e.g. reproductive condition) that are then used to isolate movement segments relative to a behavioural phenomenon of interest (figure 3b). Structuring analyses in a comparative framework to contrast movement properties across known behaviours can provide insights into different space-use properties and degrees of investment associated with specific behaviours [26]. Coupled behavioural monitoring, via direct observation or sensors, with movement has the potential to provide some of the most powerful inference on the movement process and promises to be a primary means by which to resolve function, including the influence of social and reproductive behaviour, physiology, perception (e.g. risk aversion) and ecological drivers (e.g. insect, parasite/disease and climate) on movement [55,56]. Technological innovations allowing new sensors to be coupled with tracking have enabled a diversity of new approaches to define underlying phenomena and interpret movement function [57]. Most notably, accelerometery has served as a key instrument to resolve activity levels related to locational positions and, in some cases, provides insights into energetic balance [55]. Building from this, additional sensors that record or allow a direct observation of the state and behaviour of the individual (e.g. animal borne video, acoustic, magnetometers and physiological monitoring systems) as well as sense conditions experienced in the environment (e.g. temperature, salinity and humidity) are opening novel avenues to resolve the drivers and function of movement [58].
While analytical approaches in isolation or relative to landscape features have provided important insights, multiple functions can be reflected in the same or similar movement path characteristics (or sensor measurements) (figure 3b). For instance, when using movement to resolve foraging behaviour, different resource distributions can elicit strongly differentiated foraging movements (e.g. high-value clumped versus dispersed resources can result in encamped or meandering movement paths), limiting the efficacy of describing a foraging state directly from the movement path. Given these limitations, coupled sources of information can provide confidence in interpretation or facilitate the quantification of uncertainty in functional definitions [59].
Understanding the functional driver of movements is fundamental to developing understanding of species distributions. Such insights can be used to demarcate habitats critical for survival and reproduction (e.g. important foraging grounds) or the spatial requirements for certain life stages (e.g. nesting or denning sites), information critical for species-specific landscape planning. Classically, the intensity of use metrics have largely been interpreted functionally, but improved resolution of movement data collection coupled with sensor or observational data provides elemental insights into the actual function of movements at different locations. Such combined data threads enable an improved valuation of landscapes and thus targeted spatial conservation planning with fewer assumptions [60].
5. Understanding the structure of the landscape
Defining a location by its structural role in the larger landscape as defined by an individual's movement provides an intermediate approach to the classic Eulerian (focusing on emerging population patterns) and Lagrangian (focusing on individual's movement steps) paradigms for characterizing movement [4,61]. We term this category structural valuation, whereby locational importance emerges from the role or function it plays within overall movement trajectories across the landscape [62]. Structural valuation of landscapes is related to work focusing on landscape ecology and movement connectivity, increasingly involving network- (or graph-) theoretical approaches (figure 4) or least-cost path approaches [63]. When applied to movement, network theory discretizes animal space use into different locations or patches on the landscape (referred to as nodes) and the potential connections (edges or links) among these locations [62,64]. Network metrics can also serve to characterize the importance of locations on the landscape in terms of use, connectedness and centrality measures [65].
Movement data have improved the application of network theory to spatial ecology in three ways that formerly relied on expert opinion-based definitions: definition of patches, quantifying connectivity and characterizing movement cost. Focusing on patch definition (figure 4a), structural valuation of landscapes can provide parallel inference to that derived from metrics of the intensity of use [66]. This allows the quantitative definition of preferred landcover types [67] or specific locations of behaviours of interest (e.g. central-place foraging or reproductive sites) [50]. In addition, centrality measures (e.g. degree and betweenness) can identify important areas even if animals do not spend a disproportionate amount of time there (figure 4b), as can emerge when cognitive processes drive directed long-distance movement [46]. Despite the low intensity of the use of corridors connecting chosen locations, their importance can be high if their disappearance prevented animals from accessing a specific area [65]. By defining the movement landscape in terms of patches (nodes) and connectivity corridors (key edges), movement summarization using network theory provides a natural structure for investigating patch-occupancy dynamics and testing ecological theory (e.g. the IFD or marginal value theorem) or exploring alternative processes affecting connectivity [68].
Combining movement networks with spatial environmental data can facilitate patch and movement resistance characterization across broad landscapes (i.e. the suitability of the landscape to movement flow) (figure 4c). The definition of patches and resistant surfaces can then be used to estimate optimal linkages (corridors) among patches using least-cost path, circuit theory and ‘hybrid’ approaches such as randomized shortest path [69]. Pros and cons of the different algorithms and how to best use these approaches have been the subject of extensive discussion, including that such optimality approaches may be misleading given wildlife often traverse unsuitable habitat or avoid apparently suitable habitat for alternate reasons [68,70,71].
Validation of movement networks is rarely done but is important for ensuring usefulness for conservation [72,73], as there is a potential risk that areas identified as potential movement corridors or important patches from a connectivity point of view are not actually used by individuals [66,68]. As with all extrapolative modelling, this is particularly the case when predicting beyond the area where data were captured. The validation of network approaches usually requires out-of-sample testing or additional streams of data such as camera or mortality data [66,74].
Where movement data are available for a large fraction of a population, network theory can be applied directly to the tracking data without relying on assumptions regarding how spatial covariates influence space use, patch definition or resistance [62]. For instance, applying network theoretical approaches to a grid overlaid on the movement landscape allows empirical definition of patches and corridors based on emergent properties of the network directly (i.e. assumption-free definition). Most usefully, this can serve to identify indirect connectedness (e.g. circuitous connecting paths). Such an approach avoids misspecification that can occur where subjective means are used to differentiate patches from non-patches or optimality approaches are used to define corridors [62]. Given the reliance on empirical data, outputs from such approaches provide a robust estimation of the structural value of an area, from which unexpected features of the movement landscape can emerge. However, such empirically derived definitions are conditioned on the explicit sample analysed, meaning sample design is critical to the derivation of general conclusions.
6. Towards a fitness landscape
Equating individual behavioural strategies to their fitness payoff provides fundamental inference on ecological and evolutionary processes, but collecting the data required for such assessments is challenging in natural systems [75]. The current renaissance in movement ecology allows the simultaneous collection of behavioural data on many individuals over long times. These data often are collected conjointly with fitness proxies such as reproduction, condition or survival, providing a platform for investigation of the links between behaviour and fitness [14,15]. Although movement data have been used to infer links between broadly defined behaviour and fitness [12,76], quantifying the fitness landscape (i.e. spatially explicit predictions of fitness costs and benefits) is a tantalizing prospect that would allow unparalleled insights into the mechanisms underlying the spatial behaviour of animals and, theoretically, allow maximally effective spatial conservation strategies. The ingredients for deriving fitness landscapes seem to be present (i.e. spatial predictions of behavioural metrics that have theoretical links to fitness). However, a number of key challenges exist stemming from the fact that the remote capture of movement data limits inference on the nuances of the behaviours characterized from tracking data and their fitness effects. Developing the opportunities and addressing the limitations of tracking data to facilitate a greater understanding of the links between fitness and behaviour are critical if movement ecology is to provide robust information on ecological and evolutionary dynamics to inform conservation. Deriving a fitness value of the landscape from movement is the most challenging of the four metrics we describe, but also the metric which offers the deepest inference. Broadly, fitness valuation of movement can occur by assigning fitness contributions to specific spatio-temporal events along individual movement paths or the derivation of landscape-level estimates of key fitness components, which can then be related to the movement path (figure 5). Both provide a powerful framework for investigating movement mechanisms and valuable information for addressing conservation and management objectives.
Fundamentally, we rarely have true measures of the fitness of an animal, driving a practical focus on quantifying components of fitness, such as reproduction and survival, or proxies of fitness, such as energetics. At the landscape scale, the focus is often on quantifying features representative of more tangible costs and benefits, such as predation risk, energetic cost of movement and forage availability (e.g. [15]). Commonly, this is done by relating movements to the direct measurement of landscape properties that have fitness relevance such as vegetative or a soil-based nutritional value (e.g. from remotely sensed layers) [77], resistance surfaces (e.g. from topographic features or distance) and abiotic features (e.g. thermal exposure) [78]. Increasingly, model-based estimates of landscape-level fitness surfaces, estimated from movement data, are also being added to such assessments (e.g. the risk landscape); for instance, movement data identify times and locations of reproductive or mortality events, which can be related to environmental factors to derive landscape-level correlates of these key events [16,79,80]. At the individual path scale, high-fidelity activity sensor data (e.g. accelerometers) or physiological monitors integrated into collars are increasingly available. This information can be blended with knowledge on basal metabolic rates and estimates of the increased cost of movement to produce relatively accurate measures of energetic expenditure along the movement path [55]. While derivation of the energetic costs of movement from paired tracking and sensor data are being developed, accessing information on energetic gain or return is more difficult, due to the highly variable temporal dynamics, distribution and quality of different food items. Data on prey capture and consumption rates from individual paths [56] may provide the best opportunities for high-resolution inference on energetic gain. Combining these data with multiple measures of individual animal condition, taken over relatively short-time periods, and the intervening movement data can provide information on the actual gains or losses experienced by the animal [56]. However, this information is difficult to obtain in most systems. Finally, focused analyses of movements around critical events, such as reproduction and mortality events, can serve to derive path-specific valuations [79,81].
While methods for developing the fitness value of landscapes are becoming more accessible, studies doing so are rare and typically quantify a single fitness component and its relationship to coarse representations of movement (e.g. home ranges). Integrating spatial representations of several components or proxies of fitness into a single analysis is beginning to be achievable in some systems (figure 5) and will facilitate more accurate spatial representation (i.e. mapping) of movement relative to the totality of their costs (e.g. mortality) and benefits (e.g. reproductive outputs). Metrics derived from individual movement paths can be considered behavioural strategies, and overlaying these on mapped proxies of fitness can provide inference to the optimization of space-use strategies or trade-offs individuals face when balancing the requirements of multiple contrasting fitness components [82]. Devolving spatially explicit representations of fitness components associated with a given behaviour (i.e. contribution to survival and reproduction) will remain difficult where that fitness contribution is a function of integrated behaviours over space and time. For example, given knowledge on lifetime reproductive success and the lifetime track of an animal (something that is becoming a reality for some species), biometric monitoring or repeated recaptures will be needed to identify location-specific contributions to reproductive success. Regardless of these challenges, focus on accurately quantifying the fitness landscape will drive understanding of the mechanisms underlying movement, individual decisions and population distributions.
7. Integrating movement and behavioural ecology to advance applied understanding
Given the foundational role of movement to a diversity of behaviours that influence individual fitness as well as population distribution and community structure, movement ecology underlies numerous disciplines and is fundamental to applied animal conservation. The richness of contemporary movement data collection offers new avenues for individual-based analyses to build deeper insights into fundamental behavioural questions. Extracting informative patterns from the complex structure found in movement data to infer underlying motivations of movement is challenging and has driven a blossoming of analytical advances in the discipline of movement ecology [83]. However, practitioners of movement analyses are now faced with a daunting number of approaches, often to estimate a single process (e.g. home range estimation), with cursory integration with theoretical underpinnings. Despite burgeoning methodological development, the insights gained through such approaches are constrained, and understanding those constraints is critical to effectively explore the information captured through recording movement. Specifically, without the key link between movement patterns and their underlying drivers, the field risks limiting its impact on ecological and evolutionary understanding and its translation to applied objectives (e.g. [84]).
Behavioural valuation of landscapes can greatly enhance our ability to understand mechanisms driving movement patterns, providing insights into classic and emerging topics including cognitive decision-making, memory and the investigation of behavioural tactics manifested in movement. The integration of behavioural theory in movement ecology remains relatively rudimentary, particularly in applied movement ecology—the area where movement analysis is put to conservation needs and uses. This produces general insights but often limits understanding of mechanisms critical for targeted conservation and management action.
Strengthening the behavioural theoretical underpinnings of movement ecological analysis can serve to provide a stronger mechanistic interpretation of movement behaviour and the needs of animals. We conceptualize approaches that translate movement into representations of the behavioural value of locations on landscapes by tracked animals, organizing the broad approaches in movement ecology into four thematic categories of movement-derived metrics: intensity of use, functionality, structural importance and fitness value. We outline the theoretical underpinnings of these metrics to encourage their interpretation from such a foundation. Building from this perspective will ensure the application of each metric to current conservation challenges is mechanistically based. Such valuation enables inference at the local scale emerging from the animal's behaviour (i.e. perspective) that can allow more targeted and efficient management and conservation actions on the landscape. Explicit understanding of why animals use certain locations is critical to reserve design, land-use planning in multi-use landscapes, restoration efforts and determining the impact of natural and human-caused dynamics on species (e.g. climate change). In addition, highlighting the understanding of the movement behaviour itself can garner public and government interest that can be leveraged for conservation returns [85].
Conservation challenges facing natural landscapes are immense. Driven by global food demand, intensification of agriculture and projected increase of 2.3 billion humans [86], 10 million km2 are projected to be cleared for agriculture by 2050 [87]. It is imperative that a mechanistic understanding of animal spatial behaviour is leveraged to determine wildlife spatial requirements, and that this information is incorporated in land-use planning efforts. Mechanistic-based valuation of the landscape can provide detailed insights into wildlife needs, focusing conservation efforts at key locations and optimizing investment to critical areas.
Acknowledgements
We thank Jakob Bro-Jorgensen for helpful comments and managing this issue. We also thank Jennifer Gill, Rachel Buxton, Aung Chan, Nathan Hahn, Jenna Parker, Kristen Snyder and an anonymous reviewer for helpful feedback on the manuscript.
Data accessibility
This article has no additional data.
Authors' contributions
G.W. designed the study. G.W. led the writing of the manuscript with contributions from G.B.-R. and J.M.N. All authors have commented and approved the final version of the manuscript.
Competing interests
We declare we have no competing interests.
Funding
G.B.-R. was supported by the Natural Sciences and Engineering Research Council of Canada. G.W. was supported by the Warner College of Natural Resources and the Monfort professorship at Colorado State University.
References
- 1.Lima SL, Zollner PA. 1996. Towards a behavioral ecology of ecological landscapes. Trends Ecol. Evol. 11, 131–135. ( 10.1016/0169-5347(96)81094-9) [DOI] [PubMed] [Google Scholar]
- 2.Turchin P. 1991. Translating foraging movements in heterogeneous environments into the spatial distribution of foragers. Ecology 72, 1253–1266. ( 10.2307/1941099) [DOI] [Google Scholar]
- 3.Bowler DE, Benton TG. 2005. Causes and consequences of animal dispersal strategies: relating individual behaviour to spatial dynamics. Biol. Rev. Camb. Philos. Soc. 80, 205–225. ( 10.1017/S1464793104006645) [DOI] [PubMed] [Google Scholar]
- 4.Nathan R, Getz WM, Revilla E, Holyoak M, Kadmon R, Saltz D, Smouse PE. 2008. A movement ecology paradigm for unifying organismal movement research. Proc. Natl Acad. Sci. USA 105, 19 052–19 059. ( 10.1073/pnas.0800375105) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 5.Holyoak M, Casagrandi R, Nathan R, Revilla E, Spiegel O. 2008. Trends and missing parts in the study of movement ecology. Proc. Natl Acad. Sci. USA 105, 19 060–19 065. ( 10.1073/pnas.0800483105) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Wall J, Wittemyer G, Klinkenberg B, Douglas-Hamilton I. 2014. Novel opportunities for wildlife conservation and research with real-time monitoring. Ecol. Appl. 24, 593–601. ( 10.1890/13-1971.1) [DOI] [PubMed] [Google Scholar]
- 7.Bastille-Rousseau G, Wall J, Douglas-Hamilton I, Wittemyer G. 2018. Optimizing the positioning of wildlife crossing structures using GPS telemetry. J. Appl. Ecol. 55, 2055–2063. ( 10.1111/1365-2664.13117) [DOI] [Google Scholar]
- 8.Tucker MA, et al. 2018. Moving in the Anthropocene: global reductions in terrestrial mammalian movements. Science 359, 466–469. ( 10.1126/science.aam9712) [DOI] [PubMed] [Google Scholar]
- 9.Tamburello N, Ma BO, Côté IM. 2019. From individual movement behaviour to landscape-scale invasion dynamics and management: a case study of lionfish metapopulations. Phil. Trans. R. Soc. B 374, 20180057 ( 10.1098/rstb.2018.0057) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Kays R, Crofoot MC, Jetz W, Wikelski M. 2015. Terrestrial animal tracking as an eye on life and planet. Science 348, 2478 ( 10.1126/science.aaa2478) [DOI] [PubMed] [Google Scholar]
- 11.Johnson MDM. 2007. Measuring habitat quality: a review. Condor 109, 489–504. ( 10.1650/8347.1) [DOI] [Google Scholar]
- 12.Gaillard JM, Hebblewhite M, Loison A, Fuller M, Powell R, Basille M, Van Moorter B. 2010. Habitat-performance relationships: finding the right metric at a given spatial scale. Phil. Trans. R. Soc. B 365, 2255–2265. ( 10.1098/rstb.2010.0085) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 13.Couzin ID, Krause J. 2003. Self-organization and collective behavior in vertebrates. Adv. Study Behav. 32, 1–75. ( 10.1016/S0065-3454(03)01001-5) [DOI] [Google Scholar]
- 14.DeMars CA, Auger-Méthé M, Schlägel UE, Boutin S. 2013. Inferring parturition and neonate survival from movement patterns of female ungulates: a case study using woodland caribou. Ecol. Evol. 3, 4149–4160. ( 10.1002/ece3.785) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.McLoughlin PD, Dunford JS, Boutin S. 2005. Relating predation mortality to broad-scale habitat selection. J. Anim. Ecol. 74, 701–707. ( 10.1111/j.1365-2656.2005.00967.x) [DOI] [Google Scholar]
- 16.St. Clair CC, Backs J, Friesen A, Gangadharan A, Gilhooly P, Murray M, Pollock S. 2019. Animal learning may contribute to both problems and solutions for wildlife–train collisions. Phil. Trans. R. Soc. B 374, 20180050 ( 10.1098/rstb.2018.0050) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Krebs JR, Davies NB. 1992. Behavioural ecology: an evolutionary approach. London, UK: Wiley. [Google Scholar]
- 18.MacArthur RH, Pianka ER. 1966. On optimal use of a patchy environment. Am. Nat. 100, 603–609. ( 10.1017/CBO9781107415324.004) [DOI] [Google Scholar]
- 19.Charnov EL. 1976. Optimal foraging, the marginal value theorem. Theor. Popul. Biol. 9, 129–136. ( 10.1016/0040-5809(76)90040-X) [DOI] [PubMed] [Google Scholar]
- 20.McLoughlin PD, Morris DW, Fortin D, Vander Wal E, Contasti AL. 2010. Considering ecological dynamics in resource selection functions. J. Anim. Ecol. 79, 4–12. ( 10.1111/j.1365-2656.2009.01613.x) [DOI] [PubMed] [Google Scholar]
- 21.Fretwell SD, Lucas HLJ. 1969. On territorial behaviour and other factors influencing habitat distribution in birds. Acta Biotheor. 19, 45–52. ( 10.1007/BF01601953) [DOI] [Google Scholar]
- 22.Schlaepfer MA, Runge MC, Sherman PW. 2002. Ecological and evolutionary traps. Trends Ecol. Evol. 17, 474–480. ( 10.1016/S0169-5347(02)02580-6) [DOI] [Google Scholar]
- 23.Brown JS, Kotler BP. 2004. Hazardous duty pay and the foraging cost of predation. Ecol. Lett. 7, 999–1014. ( 10.1111/j.1461-0248.2004.00661.x) [DOI] [Google Scholar]
- 24.Fortin D, Fryxell JM, O'Brodovich L, Frandsen D. 2003. Foraging ecology of bison at the landscape and plant community levels: the applicability of energy maximization principles. Oecologia 134, 219–227. ( 10.1007/s00442-002-1112-4) [DOI] [PubMed] [Google Scholar]
- 25.Bunnefeld N, Börger L, Van Moorter B, Rolandsen CM, Dettki H, Solberg EJ, Ericsson G. 2011. A model-driven approach to quantify migration patterns: individual, regional and yearly differences. J. Anim. Ecol. 80, 466–476 ( 10.1111/j.1365-2656.2010.01776.x) [DOI] [PubMed] [Google Scholar]
- 26.Wittemyer G, Getz WM, Vollrath F, Douglas-Hamilton I. 2007. Social dominance, seasonal movements, and spatial segregation in African elephants: a contribution to conservation behavior. Behav. Ecol. Sociobiol. 61, 1919–1931. ( 10.1007/s00265-007-0432-0) [DOI] [Google Scholar]
- 27.Taylor LA, Vollrath F, Lambert B, Lunn D, Douglas-Hamilton I, Wittemyer G. 2019. Movement reveals reproductive tactics in male elephants. J. Anim. Ecol. 88 ( 10.1111/1365-2656.13035) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Creel S, Creel NM. 1995. Communal hunting and pack size in African wild dogs, Lycaon pictus. Anim. Behav. 50, 1325–1339. ( 10.1016/0003-3472(95)80048-4) [DOI] [Google Scholar]
- 29.Saraux C, et al. 2011. Reliability of flipper-banded penguins as indicators of climate change. Nature 469, 203 ( 10.1038/nature09630) [DOI] [PubMed] [Google Scholar]
- 30.Bastille-Rousseau G, Wittemyer G. 2019. A framework for defining individual movement tactics demonstrates individual drivers of African elephant population distribution. Ecol. Lett. 22, 13327 ( 10.1111/ele.13327) [DOI] [PubMed] [Google Scholar]
- 31.Gurarie E, Bracis C, Delgado M, Meckley TD, Kojola I, Wagner CM. 2016. What is the animal doing? Tools for exploring behavioural structure in animal movements. J. Anim. Ecol. 85, 69–84. ( 10.1111/1365-2656.12379) [DOI] [PubMed] [Google Scholar]
- 32.Nussey DH, Wilson AJ, Brommer JE. 2007. The evolutionary ecology of individual phenotypic plasticity in wild populations. J. Evol. Biol. 20, 831–844. ( 10.1111/j.1420-9101.2007.01300.x) [DOI] [PubMed] [Google Scholar]
- 33.Mysterud A, Ims RA. 1998. Functional responses in habitat use: availability influences relative use in trade-off situations. Ecology 79, 1435–1441. ( 10.1890/0012-9658(1998)079[1435:FRIHUA]2.0.CO;2) [DOI] [Google Scholar]
- 34.Spiegel O, Leu ST, Bull CM, Sih A. 2017. What's your move? Movement as a link between personality and spatial dynamics in animal populations. Ecol. Lett. 20, 3–18. ( 10.1111/ele.12708) [DOI] [PubMed] [Google Scholar]
- 35.Moreau G, Fortin D, Couturier S, Duchesne T. 2012. Multi-level functional responses for wildlife conservation: the case of threatened caribou in managed boreal forests. J. Appl. Ecol. 49, 611–620. ( 10.1111/j.1365-2664.2012.02134.x) [DOI] [Google Scholar]
- 36.Northrup JM, Anderson CR, Wittemyer G. 2015. Quantifying spatial habitat loss from hydrocarbon development through assessing habitat selection patterns of mule deer. Glob. Chang. Biol. 21, 3961–3970. ( 10.1111/gcb.13037) [DOI] [PubMed] [Google Scholar]
- 37.Wittemyer G, Polansky L, Douglas-Hamilton I, Getz WM. 2008. Disentangling the effects of forage, social rank, and risk on movement autocorrelation of elephants using Fourier and wavelet analyses. Proc. Natl Acad. Sci. USA 105, 19 108–19 113. ( 10.1073/pnas.0801744105) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 38.Miller H. 2005. A measurement theory for time geography. Geogr. Anal. 37, 17–45. ( 10.1111/j.1538-4632.2005.00575.x) [DOI] [Google Scholar]
- 39.Holling CS. 1959. Some characteristics of simple types of predation and parasitism. Can. Entomol. 91, 385–398. ( 10.4039/Ent91385-7) [DOI] [Google Scholar]
- 40.Lyons AJ, Turner WC, Getz WM. 2013. Home range plus: a space-time characterization of movement over real landscapes. Mov. Ecol. 1, 2 ( 10.1186/2051-3933-1-2) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41.Bracis C, Bildstein KL, Mueller T. 2018. Revisitation analysis uncovers spatio-temporal patterns in animal movement data. Ecography 41, 1801–1811. ( 10.1111/ecog.03618) [DOI] [Google Scholar]
- 42.Bastille-Rousseau G, Fortin D, Dussault C. 2010. Inference from habitat-selection analysis depends on foraging strategies. J. Anim. Ecol. 79, 1157–1163. ( 10.1111/j.1365-2656.2010.01737.x) [DOI] [PubMed] [Google Scholar]
- 43.Bailey DW, Gross JE, Laca EA, Rittenhouse LR, Coughenour MB, Swift DM, Sims PL. 1996. Mechanisms that result in large herbivore grazing distribution patterns. J. Range Manag. 49, 386–400. ( 10.2307/4002919) [DOI] [Google Scholar]
- 44.McNaughton SJ. 1985. Ecology of a grazing ecosystem: the Serengeti. Ecol. Monogr. 55, 259–294. ( 10.2307/1942578) [DOI] [Google Scholar]
- 45.Polansky L, Kilian W, Wittemyer G. 2015. Elucidating the significance of spatial memory on movement decisions by African savannah elephants using state–space models. Proc. R. Soc. B 282, 20143042 ( 10.1098/rspb.2014.3042) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 46.Fagan WF, et al. 2013. Spatial memory and animal movement. Ecol. Lett. 16, 1316–1329. ( 10.1111/ele.12165) [DOI] [PubMed] [Google Scholar]
- 47.Northrup JM, Anderson CR, Wittemyer G. 2016. Environmental dynamics and anthropogenic development alter philopatry and space-use in a North American cervid. Divers. Distrib. 22, 547–557. ( 10.1111/ddi.12417) [DOI] [Google Scholar]
- 48.Gill JA, Alves JA, Gunnarsson TG. 2019. Mechanisms driving phenological and range change in migratory species. Phil. Trans. R. Soc. B 374, 20180047 ( 10.1098/rstb.2018.0047) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 49.Morales JM, Haydon DT, Frair J, Holsiner KE, Fryxell JM. 2004. Extracting more out of relocation data: building movement models as mixtures of random walks. Ecology 85, 2436–2445. ( 10.1890/03-0269) [DOI] [Google Scholar]
- 50.Wittemyer G, Keating LM, Vollrath F, Douglas-Hamilton I. 2017. Graph theory illustrates spatial and temporal features that structure elephant rest locations and reflect risk perception. Ecography 40, 598–605. ( 10.1111/ecog.02379) [DOI] [Google Scholar]
- 51.Thiebault A, Dubroca L, Mullers RHE, Tremblay Y, Pistorius PA. 2018. ‘M2B’ package in R: deriving multiple variables from movement data to predict behavioural states with random forests. Methods Ecol. Evol. 9, 1548–1555. ( 10.1111/2041-210X.12989) [DOI] [Google Scholar]
- 52.Nams VO. 2014. Combining animal movements and behavioural data to detect behavioural states. Ecol. Lett. 17, 1228–1237. ( 10.1111/ele.12328) [DOI] [PubMed] [Google Scholar]
- 53.Beyer HL, Morales JM, Murray D, Fortin MJ. 2013. The effectiveness of Bayesian state-space models for estimating behavioural states from movement paths. Methods Ecol. Evol. 4, 433–441. ( 10.1111/2041-210X.12026) [DOI] [Google Scholar]
- 54.Nicosia A, Duchesne T, Rivest LP, Fortin D. 2017. A multi-state conditional logistic regression model for the analysis of animal movement. Ann. Appl. Stat. 11, 1537–1560. ( 10.1214/17-AOAS1045) [DOI] [Google Scholar]
- 55.Williams TM, Wolfe L, Davis T, Kendall T, Richter B, Wang Y, Bryce C, Elkaim GH, Wilmers CC. 2014. Instantaneous energetics of puma kills reveal advantage of felid sneak attacks. Science 346, 81–85. ( 10.1126/science.1254885) [DOI] [PubMed] [Google Scholar]
- 56.Pagano AM, Durner GM, Rode KD, Atwood TC, Atkinson SN, Peacock E, Costa DP, Owen MA, Williams TM. 2018. High-energy, high-fat lifestyle challenges an Arctic apex predator, the polar bear. Science 359, 568–572. ( 10.1126/science.aan8677) [DOI] [PubMed] [Google Scholar]
- 57.Wilmers CC, Nickel B, Bryce CM, Smith JA, Wheat RE, Yovovich V, Hebblewhite M. 2015. The golden age of bio-logging: how animal-borne sensors are advancing the frontiers of ecology. Ecology 96, 1741–1753. ( 10.1890/14-1401.1) [DOI] [PubMed] [Google Scholar]
- 58.Wilson RP, et al. 2014. Wild state secrets: ultra-sensitive measurement of micro-movement can reveal internal processes in animals. Front. Ecol. Environ. 12, 582–587. ( 10.1890/140068) [DOI] [Google Scholar]
- 59.Lynch E, Angeloni L, Fristrup K, Joyce D, Wittemyer G. 2013. The use of on-animal acoustical recording devices for studying animal behavior. Ecol. Evol. 3, 2030–2037. ( 10.1002/ece3.608) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 60.Fraser KC, Davies KTA, Davy CM, Ford AT, Flockhart DTT, Martins EG. 2018. Tracking the conservation promise of movement ecology. Front. Ecol. Evol. 6, 150 ( 10.3389/fevo.2018.00150) [DOI] [Google Scholar]
- 61.Turchin P. 1998. Quantitative analysis of movement: measuring and modeling population redistribution in animals and plants. Sunderland, MA: Sinauer Associates. [Google Scholar]
- 62.Bastille-Rousseau G, Douglas-Hamilton I, Blake S, Northrup JM, Wittemyer G. 2018. Applying network theory to animal movements to identify properties of landscape space use. Ecol. Appl. 28, 854–864. ( 10.1002/eap.1697) [DOI] [PubMed] [Google Scholar]
- 63.Adriaensen F, Chardon JP, De Blust G, Swinnen E, Villalba S, Gulinck H, Matthysen E. 2003. The application of ‘least-cost’ modelling as a functional landscape model. Landsc. Urban Plan. 64, 233–247. ( 10.1016/S0169-2046(02)00242-6) [DOI] [Google Scholar]
- 64.Fall A, Fortin MJ, Manseau M, O'Brien D. 2007. Spatial graphs: principles and applications for habitat connectivity. Ecosystems 10, 448–461. ( 10.1007/s10021-007-9038-7) [DOI] [Google Scholar]
- 65.Rayfield B, Fortin MJ, Fall A. 2011. Connectivity for conservation: a framework to classify network measures. Ecology 92, 847–858. ( 10.1890/09-2190.1) [DOI] [PubMed] [Google Scholar]
- 66.LaPoint S, Gallery P, Wikelski M, Kays R. 2013. Animal behavior, cost-based corridor models, and real corridors. Landsc. Ecol. 28, 1615–1630. ( 10.1007/s10980-013-9910-0) [DOI] [Google Scholar]
- 67.Squires JR, DeCesare NJ, Olson LE, Kolbe JA, Hebblewhite M, Parks SA. 2012. Combining resource selection and movement behavior to predict corridors for Canada lynx at their southern range periphery. Biol. Conserv. 157, 187–195. ( 10.1016/j.biocon.2012.07.018) [DOI] [Google Scholar]
- 68.Berger-Tal O, Saltz D. 2019. Invisible barriers: anthropogenic impacts on inter- and intra-specific interactions as drivers of landscape-independent fragmentation. Phil. Trans. R. Soc. B 374, 20180049 ( 10.1098/rstb.2018.0049) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 69.Panzacchi M, Van Moorter B, Strand O, Saerens M, Kivimäki I, St. Clair CC, Herfindal I, Boitani L. 2016. Predicting the continuum between corridors and barriers to animal movements using step selection functions and randomized shortest paths. J. Anim. Ecol. 85, 32–42. ( 10.1111/1365-2656.12386) [DOI] [PubMed] [Google Scholar]
- 70.Zeller KA, McGarigal K, Whiteley AR. 2012. Estimating landscape resistance to movement: a review. Landsc. Ecol. 27, 777–797. ( 10.1007/s10980-012-9737-0) [DOI] [Google Scholar]
- 71.Cushman SA, McRae B, Adriaensen F, Beier P, Shirley M, Zeller K. 2013. Biological corridors and connectivity. In Key topics in conservation biology (eds MacDonald DW, Willis KJ), pp. 384–404. Hoboken, NJ: Wiley-Blackwell. [Google Scholar]
- 72.Abrahms B, Sawyer SC, Jordan NR, McNutt JW, Wilson AM, Brashares JS. 2016. Does wildlife resource selection accurately inform corridor conservation? J. Appl. Ecol. 54, 412–422. ( 10.1111/1365-2664.12714) [DOI] [Google Scholar]
- 73.McClure ML, Hansen AJ, Inman RM. 2016. Connecting models to movements: testing connectivity model predictions against empirical migration and dispersal data. Landsc. Ecol. 31, 1419–1432. ( 10.1007/s10980-016-0347-0) [DOI] [Google Scholar]
- 74.Koen EL, Bowman J, Sadowski C, Walpole AA. 2014. Landscape connectivity for wildlife: development and validation of multispecies linkage maps. Methods Ecol. Evol. 5, 626–633. ( 10.1111/2041-210X.12197) [DOI] [Google Scholar]
- 75.Clutton-Brock T, Sheldon BC. 2010. Individuals and populations: the role of long-term, individual-based studies of animals in ecology and evolutionary biology. Trends Ecol. Evol. 25, 562–573. ( 10.1016/j.tree.2010.08.002) [DOI] [PubMed] [Google Scholar]
- 76.Nielsen SE, Stenhouse GB, Boyce MS. 2006. A habitat-based framework for grizzly bear conservation in Alberta. Biol. Conserv. 130, 217–229. ( 10.1016/j.biocon.2005.12.016) [DOI] [Google Scholar]
- 77.Merkle JA, Fortin D, Morales JM. 2014. A memory-based foraging tactic reveals an adaptive mechanism for restricted space use. Ecol. Lett. 17, 924–931. ( 10.1111/ele.12294) [DOI] [PubMed] [Google Scholar]
- 78.van Beest FM, Van Moorter B, Milner JM. 2012. Temperature-mediated habitat use and selection by a heat-sensitive northern ungulate. Anim. Behav. 84, 723–735. ( 10.1016/j.anbehav.2012.06.032) [DOI] [Google Scholar]
- 79.Johnson CJ, Boyce MS, Schwartz CC, Haroldson MA. 2004. Modeling survival: application of the Andersen-Gill model to Yellowstone grizzly bears. J. Wildl. Manage. 68, 966–978. ( 10.1143/JJAP.47.2606) [DOI] [Google Scholar]
- 80.Severud WJ, Del Giudice G, Obermoller TR, Enright TA, Wright RG, Forester JD. 2015. Using GPS collars to determine parturition and cause-specific mortality of moose calves. Wildl. Soc. Bull. 39, 616–625. ( 10.1002/wsb.558) [DOI] [Google Scholar]
- 81.Webb SL, Dzialak MR, Harju SM, Hayden-Wing LD, Winstead JB. 2011. Influence of land development on home range use dynamics of female elk. Wildl. Res. 28, 163–167. ( 10.1071/WR10101) [DOI] [Google Scholar]
- 82.Leclerc M, Vander Wal E, Zedrosser A, Swenson JE, Kindberg J, Pelletier F. 2016. Quantifying consistent individual differences in habitat selection. Oecologia 180, 697–705. ( 10.1007/s00442-015-3500-6) [DOI] [PubMed] [Google Scholar]
- 83.Hooten MB, Johnson DS, McClintock BT, Morales JM. 2017. Animal movement: statistical models for telemetry data. Boca Raton, FL: CRC Press. [Google Scholar]
- 84.Durant SM, et al. 2019. Bridging the divide between scientists and decision-makers: how behavioural ecologists can increase the conservation impact of their research? Phil. Trans. R. Soc. B 374, 20190011 ( 10.1098/rstb.2019.0011) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 85.Caro T, Berger J. 2019. Can behavioural ecologists help establish protected areas? Phil. Trans. R. Soc. B 374, 20180062 ( 10.1098/rstb.2018.0062) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 86.United Nations Department of Economic and Social Affairs Population Division. 2015. World population prospects: the 2015 revision, key findings and advance tables. Working Paper no. ESA/P/WP.241. https://esa.un.org/unpd/wpp/publications/files/key_findings_wpp_2015.pdf. [Google Scholar]
- 87.Tilman D, Balzer C, Hill J, Befort BL. 2011. Global food demand and the sustainable intensification of agriculture. Proc. Natl Acad. Sci. USA 108, 20 260–20 264. ( 10.1073/pnas.1116437108) [DOI] [PMC free article] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Availability Statement
This article has no additional data.