Abstract
Landscape connectivity, the extent to which a landscape facilitates the flow of ecological processes such as organism movement, has grown to become a central focus of applied ecology and conservation science. Several computational algorithms have been developed to understand and map connectivity, and many studies have validated their predictions using empirical data. Yet at present, there is no published comparative analysis which uses a comprehensive simulation framework to measure the accuracy and performance of the dominant methods in connectivity modelling. Given the widespread usage of such models in spatial ecology and conservation science, a thorough evaluation of their predictive abilities using simulation techniques is essential for guiding their appropriate and effective application across different contexts. In this paper, we address this by using the individual-based movement model Pathwalker to simulate different connectivity scenarios generated from a wide range of possible movement behaviours and spatial complexities. With this simulated data, we test the predictive abilities of three major connectivity models: factorial least-cost paths, resistant kernels, and Circuitscape. Our study shows the latter two of these three models to consistently perform most accurately in nearly all cases, with their abilities varying substantially in different contexts. For the majority of conservation applications, we infer resistant kernels to be the most appropriate model, except for when the movement is strongly directed towards a known location. We conclude this paper with a review and interdisciplinary discussion of the current limitations and possible future developments of connectivity modelling.
Subject terms: Conservation biology, Ecological modelling
Introduction
Your task is not to seek for love, but merely to seek and find all the barriers within yourself that you have built against it. - Jalaluddin Rumi
Landscape connectivity
Movement is fundamental to all ecological processes in our more-than-human world1–3. In conservation science, it is commonly studied in the context of gene flow, dispersal, population dynamics, and shifting habitats in response to changes in climate and human activity4–6. Here, animal movement is often understood in response to a range of biotic and abiotic environmental factors, constituting a complex relationship between individuals and the landscape that is fluid in space and time, and which manifests at different scales7–9. Understanding and predicting the pathways of organism movement thus forms a cornerstone of ecological science and its application to conservation practice. However, it is usually very challenging to model accurately due to the countless factors which can shape and affect movement patterns10.
‘Landscape connectivity’, commonly defined to be the extent to which a landscape facilitates organism movement, is an emergent and dynamic phenomenon based on the cumulative movement pathways of individuals across time and space11. Conceptually, it provides a tractable and powerful methodology for analysing and mapping organism movement patterns, and its widespread utility has been established across an enormous body of ecological work12,13. As such, the theory, modelling and prediction of landscape connectivity has grown to become a central focus of applied ecology and conservation science14.
Modelling connectivity
Resistance surfaces
Several techniques for modelling landscape connectivity have been developed in recent years15. The most prominent methods today use ‘resistance surfaces’, which are pixelated maps (in the form of geospatial image layers) that provide the spatially-explicit input data necessary for modern connectivity models16. Each pixel of the surface is assigned a numerical value which reflects the estimated ‘cost of movement’ through the region of the landscape corresponding to that pixel, giving a spatiotemporally static approximation to how landscape structure affects movement.
Using these resistance surfaces, connectivity models typically then evaluate landscape connectivity with an algorithm based on either cost-distance measurements, or electrical circuit theory from classical physics14. Despite its widespread usage as the basis for modern connectivity models, the framework of landscape resistance does have its limitations as a basis for modelling animal movement, which we will revisit in the discussion section.
Connectivity algorithms
The simplest cost-distance algorithm is the ‘least-cost path’, which identifies a path (or corridor) between two geographical locations on the resistance surface that minimises the accumulated cost of movement between those locations17. This was later extended by synoptic approaches like the factorial least-cost path algorithm, which computes the least-cost paths between any set of source points simultaneously18.
However, there are severe limitations to these least-cost path approaches in practice19. Centrally, there is little reason to assume that an animal knows (or even thinks in terms of) the route of the least-cost path. Moreover, the destination may not be known to the animal; even if this were so, obtaining the knowledge of their precise destination can be very difficult, especially with dispersing animals. To remedy this latter issue, the resistant kernels method was developed20. It is a cost-distance algorithm that estimates connectivity as a function of source locations, landscape resistance and dispersal thresholds, without requiring knowledge of destination points.
In contrast, based on electrical circuit theory, Circuitscape is a connectivity model which simulates electrical current flow across a resistance surface21. Source locations of movement are treated as nodes of a circuit, with resistance values as the strength of electrical resistors, and animals modelled as electrons ‘flowing through this circuit’. This algorithm produces a current density for each pixel on the resistance surface, with higher current values assumed to reflect higher degrees of connectivity. See Fig. 1 for an illustration of the outputs of Circuitscape, factorial least-cost paths and resistant kernels.
Using simulation to evaluate connectivity model performance
Simulated versus empirical data
Simulation experiments are essential for comparing the performance of these computational models. At present, there exist a wide range of studies using empirical data which evaluate the abilities of connectivity models to match observed movement patterns22–25. These analyses typically investigate model performance by measuring the degree of correlation between empirical movement data and the predictions from different connectivity algorithms. However, in an empirical analysis, the relationships driving the observed movement remain unknown. Moreover, the model predictions are dependent on several factors which are also not empirically known, such as: dispersal ability, spatial scale of movement choice, mortality risk, density and distribution of the studied population, and how landscape structure affects movement.
As a result, the degree to which a connectivity model prediction matches observed movement paths does not necessarily demonstrate the model’s accuracy relative to other methods. This is because the many uncontrolled factors in an empirical study mean that the relationships driving movement patterns need not be reflected in the data. Thus, although empirical connectivity analyses can give tremendous insight in many contexts, they are limited in their ability to comparatively evaluate the performance of different connectivity models. Working instead with suitably generated simulated data allows us to compare model predictions with a ‘known truth’ - namely, the connectivity maps generated by simulated movement paths resulting from a controlled set of known parameters - and thus enables a more definitive analysis of model performance.
The utility of simulation experiments
Simulation frameworks have been instrumental for testing key hypotheses in many branches of spatial ecology. For example, in landscape genetics, simulated data generated by models such as CDPOP have been utilised to study central questions in this field which cannot be addressed with empirical data alone26–29. Simulation techniques have also recently been used in species-specific landscape connectivity studies, such as with the Sunda clouded leopard30 and northern spotted owls31. Yet at present, there is no published comparative evaluation which utilises a simulation framework to measure the relative performance of the connectivity models themselves. Given the widespread usage of Circuitscape, resistant kernels and factorial least-cost paths across an enormous range of connectivity analyses in recent years, a rigorous evaluation of their predictive abilities using simulation techniques is essential for guiding the appropriate and effective application of these connectivity models in conservation science.
In this paper, we used simulated data from the movement model Pathwalker (described below, see also32) to address this fundamental question in the field of connectivity modelling. Namely, how accurate are (1) factorial least-cost paths, (2) resistant kernels, and (3) Circuitscape, in predicting landscape connectivity as we vary movement behaviour and spatial complexity over a wide range of parameters? Pathwalker is an individual- and process-based, spatially-explicit movement model which simulates organism movement on a resistance surface as a function of several parameters, including: energetic cost of movement, landscape resistance, mortality risk, autocorrelated movement, and bias towards a known destination, all at multiple spatial scales.
The flexibility and detail of Pathwalker enable us to test a variety of hypotheses concerning the patterns of landscape connectivity which result from differing movement choices, allowing for a comprehensive comparison of major connectivity models used in conservation science. This means that we are able to quantify the extent to which resistant kernels, Circuitscape and factorial least-cost paths can approximate connectivity pathways through a landscape, giving an in-depth picture of their relative abilities in a wide range of contexts. The simulated data from Pathwalker is generated by stochastic movement rules which reflect and extend the assumptions that these three connectivity algorithms use to model movement behaviour, making it a suitable framework with which to analyse their predictive abilities.. Furthermore, with its ability to simulate movement pathways as a function of ecological processes in much greater detail than other mainstream connectivity models, Pathwalker itself provides a powerful new tool for understanding and mapping landscape connectivity.
Methods
Creating the connectivity model predictions
We begin by simulating 7 resistance surfaces of 256x256 pixels, which increase in complexity from a simple uniform landscape with three barriers, to surfaces with more continuous and varied simulated landscape features (Fig. 2). We also randomly select 100 points in a 256x256 grid, which act as the starting locations for the movement on the resistance surface. Each of these 7 surfaces, together with the 100 source points, is then given to our three connectivity models: factorial least-cost paths, resistant kernels and Circuitscape. For each of the 7 resistance surfaces, we thus obtain three predictions for landscape connectivity, one from each model. In our analysis described below, we test which of these three models best matches the actual connectivity pathways generated from the movement data simulated by Pathwalker, across a wide variety of scenarios arising from different simulated movement behaviours. All analyses in this study are performed using Python version 3.8 (https://www.python.org) with the SciPy package33, except for the redundancy analysis and variance partitioning, which are performed using R version 3.6 (https://www.r-project.org) with the vegan package34.
Pathwalker
Pathwalker simulates individual organism movement from a source point on a resistance surface as a biased random walk, which is a function of three basic movement mechanisms - energy, attraction and risk. These mechanisms can be used individually, or together in pairwise or three-way combination. The energy mechanism simulates the dispersal and energetic capabilities of an organism, represented by the energetic cost of movement across the resistance surface, and produces an unbiased random walk which ends once the specified energetic cost threshold has been reached. The attraction mechanism produces a random walk in which the movement is biased towards pixels of lower resistance values, resulting in a spatially-determined movement choice. The risk mechanism simulates mortality risk during movement by producing an unbiased random walk on a ‘risk surface’ (which can be proportional to the resistance surface, or an entirely different surface); the walk can probabilistically end at each step, with a higher likelihood of ending on pixels with higher risk values.
The movement mechanisms are compatible with a multiple-scale response to the spatially heterogeneous resistance surface: the energy, resistance and risk values can be calculated using the mean, maximum or minimum value of a focal window of size n around each pixel. Additionally, there are two directionality parameters: an autocorrelation parameter C, which determines the likelihood of continuing in the current direction of movement; and a destination bias parameter D, which governs the extent to which the walk is biased towards a particular destination on the resistance surface. This is summarised by the schematic in Fig. 3, but see32 for more details on Pathwalker.
Creating the simulated connectivity maps
Pathwalker outputs individual movement paths generated by these parameter combinations. It can then aggregate these movement paths into a ‘density of movement’ surface, which provides the simulated connectivity surface to which we compare the three connectivity model outputs. Figure 4 shows an example density surface, produced by aggregating 100 paths run from a single source point on a resistance surface. In our analysis, for each parameter configuration (which represents one possible combination of movement behaviours), we run Pathwalker 100 times from each of the 100 randomly selected source points; we then aggregate these 10,000 movement paths to create a single connectivity surface which results from the movement choices of this particular set of behavioural parameters. The length of each path in the analysis is capped at 500 steps.
In order to provide a comprehensive comparison of factorial least-cost paths, resistant kernels and Circuitscape, we perform two in-depth analyses. First, we test their accuracy with each of the 7 resistance surfaces across 252 possible configurations of movement behaviour, sampling the full parameter space of movement mechanism, spatial scaling and degree of autocorrelation, but without including destination bias. Explicitly, on each of the 7 resistance surfaces, we run 7 different movement mechanisms, 4 degrees of spatial scale, 3 types of scale response, and 3 degrees of autocorrelation, giving a total of 1,764 simulated connectivity scenarios (Table 1).
Table 1.
First analysis | Second analysis | |
---|---|---|
Resistance surface | All 7 resistance surfaces | All 7 resistance surfaces |
Movement mechanism | All 7 movement combinations | All 7 movement combinations |
Spatial scale | , , , | |
Scaling function | All 3 scaling functions | Focal mean |
Autocorrelation | 0, 0.35, 0.75 | 0.2 |
Destination bias | 0 | 0.1, 0.3, 0.6 |
Total combinations | 1764 | 147 |
For a second analysis, we then test the effect of 3 degrees of destination bias on the model accuracies, by varying this parameter together with the 7 different movement mechanisms while keeping the spatial scale, scaling function and autocorrelation fixed, providing an additional 21 movement scenarios for each of the 7 resistance surfaces (Table 1). This gives a further 147 connectivity scenarios, resulting overall in 1,911 simulated connectivity surfaces with which to compare the predictive abilities of factorial least-cost paths, resistant kernels and Circuitscape.
Measuring the accuracy of the connectivity model predictions
To measure the accuracy of these connectivity models in each of the 1,911 scenarios, we use three statistics: (1) the root-mean-squared error between the true and predicted surface, (2) the Pearson linear correlation coefficient between the true and predicted surface, and (3) the degree of spatial overlap between the areas of 10% highest connectivity in the true and predicted surface. For (1), we divide the total error by the number of pixels on the resistance surface, in order to obtain a scaled value between 0 and 1.
We subsequently perform a variance partitioning and a set of canonical correspondence analyses (CCA) on these three statistics, supported by appropriate boxplots and an analysis of variance. We do this first for the 1,764 surfaces which do not include movement biased towards a destination, and then separately for the 147 surfaces which do incorporate destination bias. These multivariate analyses allow us to synthesise our results over the whole collection of different simulated movement behaviours, and thus provide a definitive conclusion to the model accuracies across these behavioural scenarios.
Summary of analysis methodology
To summarise, we first simulate 7 different resistance surfaces, together with 100 source locations on these surfaces. We run the three connectivity models - factorial least-cost paths, resistant kernels and Circuitscape - on these 7 surfaces, giving three different connectivity model predictions for each resistance surface.
For each resistance surface, we then stipulate a range of possible movement behaviours, which sample the full parameter space of mechanisms, spatial scales and degrees of autocorrelation; we use the Pathwalker software to simulate one connectivity map from each parameter configuration, giving us 1,764 simulated connectivity surfaces. Additionally, we test the effect of destination bias on model performance by varying this parameter together with the movement mechanisms for each resistance surface, while fixing the scaling and autocorrelation parameters, generating a further 147 connectivity surfaces.
We then measure how closely the three connectivity models compare with each of the 1,911 simulated connectivity maps, by calculating the average error, linear correlation and degree of spatial overlap between the true (simulated) and predicted surfaces in each case.
Finally, we synthesise these statistics using variance partitioning, canonical correspondence analyses and analysis of variance, supported by appropriate boxplots. From this we obtain a comprehensive picture for the accuracy of each of the three models across the possible movement behaviour parameters and resistance surfaces.
Results
Connectivity model performance without destination bias
Recall that for the first analysis, across each resistance surface, we simultaneously vary the movement mechanism, autocorrelation, spatial scale and scale response function, without the movement being biased towards a known destination. The variance partitioning in Fig. 5a shows that the dominant factor in the accuracy of predicting connectivity is the choice of model used. More specifically, Fig. 5b shows that predictions using Circuitscape result in the least root-mean-squared error between the predicted and simulated connectivity maps, whereas the factorial least-cost paths model is the least accurate in all three statistics. Resistant kernels are seen to be the most accurate method overall, based on the linear correlation and spatial overlap between the predicted and true connectivity maps. This is shown numerically in Table 2.
Table 2.
Method | Average error | Linear correlation | Spatial overlap |
---|---|---|---|
Factorial least-cost paths | 0.0095 | 0.3943 | 0.3897 |
Resistant kernels | 0.0071 | 0.6736 | 0.6070 |
Circuitscape | 0.0062 | 0.5876 | 0.4503 |
Figure 5c demonstrates that variation in landscape structure can have a substantial effect on model performance: on average, as spatial heterogeneity increases, the models display much higher error but also substantially higher overlap, with little effect seen on the degree of linear correlation. Moreover, the four-way analysis of variance (Supplementary Table S1) shows very strong interaction between model accuracy and the choice of resistance surface. The boxplots in Supplementary Figure S2 show that the difference in model performance is much greater at lower levels of spatial complexity. As the spatial heterogeneity becomes more complex, on average, all three models display higher error; simultaneously, the correlation and overlap of factorial least-cost paths and Circuitscape increases, while that of resistant kernels remains consistently high across the variation in spatial complexity.
Figure 5d shows that these connectivity models are overall much less accurate if the movement is influenced only by landscape resistance values (which is parameterised by the attraction mechanism), without any limit on dispersal capabilities or mortality risk. This is seen by the position of the attraction mechanism (m2). More detail on the effects of movement mechanism on model performance is illustrated by the boxplots in Supplementary Figure S3. Specifically, with the presence of energy or risk, resistant kernels has much higher correlation and overlap than Circuitscape, and similar levels of error; without any threshold for dispersal or mortality risk, Circuitscape has substantially lower error, and similar levels of correlation and overlap.
Comparatively, the variance partitioning suggests that the effects of spatial scaling and autocorrelation are not seen to be major factors affecting the accuracy of the three connectivity models, as shown in the additional CCA diagrams in Supplementary Figure S1.
Connectivity model performance with destination bias
In the second study, we measure model accuracy when the movement is biased to differing degrees towards a known destination, and we vary the mechanisms and resistance surfaces but keep fixed the autocorrelation, spatial scale and scale response function. For this analysis, the variance partitioning in Fig. 6a shows destination bias to be the main driver in variation of model accuracy across the different connectivity scenarios, approximately three times as influential as the choice of model used. Figure 6(b) illustrates a very clear trend in model accuracy: as the degree of destination bias increases, the error increases and the correlation and overlap decrease.
In Fig. 6c, we see factorial least-cost paths to still be the least accurate by all three metrics. And as before, resistant kernels display the highest spatial overlap, and Circuitscape the lowest average error. This trend is in fact consistent over all degrees of destination bias, as seen with the boxplot diagrams in Supplementary Figure S4(a) and S4(c). However, the boxplot diagram in Supplementary Figure S4(b) shows that, for higher levels of destination bias, the connectivity predictions by Circuitscape produce the strongest linear correlations with the simulated connectivity maps; this results in the overall higher correlation seen with Circuitscape in Table 3. And in comparison with the first study, the presence of destination bias results in a stronger link between higher spatial complexity and greater model accuracy, as inferred from Fig. 6d.
Table 3.
Method | Average error | Linear correlation | Spatial overlap |
---|---|---|---|
Factorial least-cost paths | 0.0150 | 0.3318 | 0.4160 |
Resistant kernels | 0.0139 | 0.4627 | 0.5675 |
Circuitscape | 0.0127 | 0.5276 | 0.4801 |
Discussion
The theory, modelling and prediction of landscape connectivity has grown to become a central focus of applied ecology and conservation science, with widespread application in practice and policy. This has led to the development of sophisticated computational algorithms to estimate and map connectivity, with Circuitscape, resistant kernels and factorial least-cost amongst the most widely used. Despite the influential usage of these three models, there is at present no published analysis which comprehensively evaluates their relative predictive abilities with simulated data. Although many studies to date have tested and validated their predictions using empirical data, such analyses are limited in their ability to comparatively evaluate the accuracy and performance of these connectivity models, due to the unknown variables and relationships driving the movement patterns in empirical data.
In this paper, we have used the spatially-explicit individual-based movement model Pathwalker to generate different connectivity scenarios from a broad range of simulated movement behaviours and spatial complexities, and then measured the extent to which the three models are able to predict these simulated patterns of landscape connectivity. We are thus able to provide a clear and comprehensive evaluation of the performance of three of the most popular connectivity models in conservation science, giving crucial information for their effective use and application across different contexts.
Analysis results
The results of our simulation analysis show particular patterns in model performance which remain constant across the various combinations of movement mechanism, spatial scaling, autocorrelation, destination bias and spatial complexity. Centrally, factorial least-cost paths proved the least accurate of the three models, being consistent in having the highest error and lowest correlation and spatial overlap. This demonstrates that, despite being a widely used approach to modelling connectivity, the precise least-cost path (or corridor) between two locations on a resistance surface may dramatically not reflect the actual pathways of animal movement.
We also find resistant kernels to consistently produce predictions which result in the greatest degree of spatial overlap with the simulated connectivity maps, substantially higher than both Circuitscape and factorial least-cost paths. In terms of the other two statistics measuring accuracy - root-mean-squared error and linear correlation - the comparative predictive abilities of resistant kernels and Circuitscape vary according to two factors: primarily, the degree to which movement is inclined towards a known destination; and to a lesser degree, the spatial complexity of the resistance surface. Other movement parameters in Pathwalker did not affect model performance to same the extent as destination bias and spatial heterogeneity.
Without destination bias, resistant kernels produced connectivity predictions which correlated and overlapped more strongly with the simulated connectivity scenarios than those given by Circuitscape, across all degrees of spatial complexity, suggesting resistant kernels to be the most robust model regarding variation in landscape structure. Moreover, between these two models, the outputs from resistant kernels resulted in a smaller error for lower degrees of spatial complexity, with the reverse being true for higher spatial complexity. However, when the movement was strongly biased towards a known destination on the resistance surface, the connectivity predictions of Circuitscape typically correlated more strongly than those of resistant kernels. Additionally, in this case the error from these two models roughly doubled, and the spatial overlap in the predictions from Circuitscape increased but still remained less than those from resistant kernels.
Importantly, we note here that in many applications of connectivity modelling, knowledge of the precise destination of movement is often very difficult to obtain, particularly with dispersing animals. This limits the effectiveness of models such as Circuitscape which require knowledge of a location, or region, towards which the movement is inclined. In contrast, this is a strength of resistant kernels modelling, which does not require the knowledge (or assumption) of a destination prior to movement.
Connectivity modelling: limitations and future developments
The widespread usage and influence of the three models analysed in this study reflects the importance and centrality given to connectivity modelling in modern conservation science. Although such methods have grown in sophistication since the first least-cost path algorithms used in ecology two decades ago, there remain significant limitations to methods such as Circuitscape, factorial least-cost paths and resistant kernels, in their ability to understand and predict the pathways central to animal movement. For example, these models do not account for autocorrelation, spatial scale of movement, or mortality risk, despite the well-established and fundamental importance these factors have in shaping movement patterns5,35–37. Furthermore, as noted in21, Circuitscape assumes a directional symmetry of resistance between adjacent pixels, despite movement from an area of higher to lower resistance being much more likely than the reverse.
Before the emergence of landscape resistance as a framework for mapping connectivity, some agent-based models did incorporate more detailed aspects of individual movement choice38,39, but the lack of spatial complexity in these earlier methods greatly limited their effective application to conservation science. Pathwalker, and other recent agent-based approaches like HexSim and RangeShifter40,41, combine the spatially-explicit approach of resistance-based algorithms with the detail and flexibility given to simulating movement behaviour enabled by agent-based modelling. Because landscape connectivity is a phenomenon which arises from the cumulative movement routes of individual organisms, these individual-based methods thus address some important drivers of connectivity which are missing in the simplistic assumptions used by Circuitscape, resistant kernels and factorial least-cost paths.
However, many fundamental drivers of movement are still left unaccounted for: resistance-based connectivity models assume landscape resistance and animal movement behaviour to remain unchanging as the animal moves through space and time, and thus they ignore spatiotemporal variation and other key contextual details. These factors often lie at the heart of shaping movement and connectivity. For example, seasonal variability in the landscape can substantially alter movement patterns42,43, and spatial variability in movement behaviour can result in radically different estimates of landscape resistance and connectivity44,45. Recent work in connectivity modelling, such as dynamic landscape connectivity46, has developed in response to these spatiotemporal limitations of resistance surfaces.
Moreover, the earth’s ecosystems are now increasingly shaped by anthropogenic presence. Since ecological processes in reality do not follow a neat distinction between ‘nature’ and ‘society’7,47,48, traditional movement models which ignore the complexities of human influence on animal behaviour for the sake of theoretical and algorithmic simplicity are growing increasingly unreliable49–51. Emerging studies empirically demonstrate the varied effects of human presence on movement patterns and their potentially substantial impact on connectivity predictions52–54. Similarly, the dynamic presence of other nonhuman animals can be a major force in shaping movement behaviour and the resulting connectivity pathways, particularly with dispersing individuals55.
All scientific models ostensibly require a degree of simplification of ecological dynamics. But many recent studies point towards the enormous effect that spatiotemporal variation and context dependence have on connectivity predictions, and the central importance for their inclusion into connectivity modelling. As demonstrated in the above literature, these key contextual details pose a particular challenge to the minimalist assumptions used in resistance surfaces and the major resistance-based connectivity models. Namely, the assumption that animals are automatons moving through a static landscape, according to a simplistic set of cost-benefit movement rules, reduces the rich dynamics of both animal and landscape to an extent that often renders such models ineffective for application to conservation practice and policy.
Despite the complexities involved in developing connectivity models which attend to spatiotemporal variation, interactions, and other important contextual details, emerging technologies and methodologies are making this integration increasingly possible15. For example, flexible spatially-explicit individual-based models like Pathwalker provide a powerful framework with which to explore new movement parameters and modelling techniques, using simulation to test a range of hypotheses concerning drivers of movement which may be difficult to investigate empirically. Moreover, since conservation science and landscape ecology are inherently interdisciplinary56, this is an excellent opportunity to draw upon adjacent developments in the conservation social sciences57. Doing so will likely enable the identification of new objectives and parameters for models to fit better with the realities of conservation practice58–63. Scientists and modellers who are willing to engage with this interdisciplinary literature may find themselves at the forefront of revolutionary advances in applied ecological research.
Conclusion
The results of our study show that the choice of connectivity model, along with the degree of destination bias in the movement and spatial complexity of the landscape, had the greatest impact on the accuracy of connectivity predictions. Comparatively, aspects of movement behaviour such as autocorrelation and the spatial scale of response to the landscape had relatively little overall effect. We found the factorial least-cost path algorithm to be substantially less accurate than Circuitscape and resistant kernels across nearly all scenarios. Of these latter two models, resistant kernels was overall more accurate when movement was not inclined towards a particular known destination, and Circuitscape generally more accurate when there was destination bias. In practice however, knowledge of precise destinations are usually very difficult to obtain; connectivity models such as resistant kernels are thus likely to be more appropriate in a wider range of contexts.
Despite their widespread usage in conservation science, all three models are limited in their effective application and predictive abilities by their simplistic assumptions of animal movement. Many fundamental drivers of connectivity, such as spatiotemporal variability and the effects of human and nonhuman presence, are absent in the framework of landscape resistance and these resistance-based models. As discussed above, this is an important moment in the development of connectivity modelling: emerging methods and technologies are enabling us to move beyond the reductionist framework of landscape resistance as the primary basis for mapping connectivity. Recent spatially-explicit individual-based models, such as Pathwalker, provide a rich set of tools with which to explore and test a wide range of hypotheses concerning central questions in the field of landscape connectivity. Adjacent developments in the conservation social sciences provide an excellent range of methodologies and techniques for identifying new objectives and parameters in connectivity modelling. We sense this to be a tremendous and exciting opportunity for cross-disciplinary thought and collaboration, to create and develop connectivity models which better reflect the lively patterns and complexities of animal movement in our more-than-human world.
Supplementary Information
Acknowledgements
Siddharth Unnithan Kumar would like to make the following acknowledgements. I bow deeply to my family, for their love and nourishment; to Binsey Lane and Port Meadow, Sam Cushman, Josephine Reynell, Theodore Leigh, Lindsey Thompson and Gonzalo Gonzalez De Diego, for their wild generosity and loving friendship; to Sandhya Patel and Philip Maini, for their compassionate support; to the cleaners and maintenance staff at the Mathematical Institute, especially Maria Nemţanu, in admiration and respect for their efforts; to Tara Brach, for her teachings on radical acceptance; to Katie Polkinghorne, for our nights spent together under the stars; to Hugo Shakeshaft and Allegra Wint, for their cosmic love and wisdom; to David Abram, Thich Nhat Hanh, and the Buddha, Dhamma and Sangha, and the landscapes of Turtle Island, for their profound inspiration and wonder; and to our more-than-human earth, which sustains us all.
Author contributions
S.U.K. led the writing of the manuscript, wrote the code for the Pathwalker model and the comparative analysis for this paper, and performed the majority of the analysis. S.C. conceptualised the analysis and performed the multivariate statistics in the analysis. Both authors discussed each stage of the study thoroughly and have approved the submitted manuscript.
Data availibility
Access to the datasets used in this study may be supplied by the corresponding author upon request.
Competing interests
The authors declare no competing interests.
Footnotes
Publisher's note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Supplementary Information
The online version contains supplementary material available at 10.1038/s41598-022-20370-w.
References
- 1.Abram, D. The spell of the sensuous: Perception and language in a more-than-human world. Vintage (2012).
- 2.Ingold T. Being alive: Essays on movement, knowledge and description. Routledge. 2011 doi: 10.4324/9780203818336. [DOI] [Google Scholar]
- 3.Kimmerer, R.W. Braiding sweetgrass: Indigenous wisdom, scientific knowledge and the teachings of plants (Milkweed editions, 2013).
- 4.Tucker MA, Böhning-Gaese K, Fagan WF, Fryxell JM, Moorter BV, Alberts SC, Ali AH, Allen AM, Attias N, Avgar T, et al. Moving in the Anthropocene: Global reductions in terrestrial mammalian movements. Science. 2018;359(6374):466–469. doi: 10.1126/science.aam9712. [DOI] [PubMed] [Google Scholar]
- 5.Gibbs, J.P. Amphibian movements in response to forest edges, roads, and streambeds in southern New England. in The Journal of Wildlife Management (1998), pp. 584–589. 10.2307/3802333.
- 6.Moller, H., Berkes, F., O’Brian Lyver, P., & Kislalioglu, M. Combining science and traditional ecological knowledge: Monitoring populations for co-management. in Ecology and society (2004).
- 7.Lorimer, J. Wildlife in the Anthropocene: conservation after nature. (U of Minnesota Press, 2015).
- 8.Wiens JA. Spatial scaling in ecology. Funct. Ecol. 1989;3(4):385–397. doi: 10.2307/2389612. [DOI] [Google Scholar]
- 9.Abram, D. Becoming animal: An earthly cosmology. Vintage (2010).
- 10.Nathan R, Getz WM, Revilla E, Holyoak M, Kadmon R, Saltz D, Smouse PE. A movement ecology paradigm for unifying organismal movement research. Proc. Natl. Acad. Sci. 2008;105(49):19052–19059. doi: 10.1073/pnas.0800375105. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Tischendorf L, Fahrig L. On the usage and measurement of landscape connectivity. Oikos. 2000;90(1):7–19. doi: 10.1034/j.1600-0706.2000.900102.x. [DOI] [Google Scholar]
- 12.Rudnick, D., Ryan, S.J., Beier, P., Cushman, S.A., Dieffenbach, F., Epps, C., Gerber, L.R., Hartter, J.N., Jenness, J.S., & Kintsch, J. et al. The role of landscape connectivity in planning and implementing conservation and restoration priorities. Issues in Ecology (2012).
- 13.Hilty, J.A., Lidicker, W.Z., & Merenlender, A.M. Corridor Ecology: The Science and Practice of Linking Landscapes for Biodiversity Conservation (Island Press, 2012).
- 14.Cushman, S.A., McRae, B.H., Adriaensen, F., Beier, P., Shirley, M., & Zeller, K. Biological corridors and connectivity [Chapter 21]. in Key Topics in Conservation Biology 2nd ed. (eds Macdonald, D.W., Willis, K.J.) pp. 384–404 (Hoboken, NJ: Wiley-Blackwell, 2013).
- 15.Unnithan Kumar, S., Turnbull, J., Hartman Davies, O., Hodgetts, T., & Cushman, S.A. Moving beyond landscape resistance: Considerations for the future of connectivity modelling and conservation science. in Landscape Ecology (2022).
- 16.Zeller KA, McGarigal K, Whiteley AR. Estimating landscape resistance to movement: a review. Landscape Ecol. 2012;27(6):777–797. doi: 10.1007/s10980-012-9737-0. [DOI] [Google Scholar]
- 17.Adriaensen F, Chardon JP, Blust GD, Swinnen E, Villalba S, Gulinck H, Matthysen E. The application of ‘least-cost’ modelling as a functional landscape model. Landsc. Urban Plan. 2003;64(4):233–247. doi: 10.1016/S0169-2046(02)00242-6. [DOI] [Google Scholar]
- 18.Cushman SA, McKelvey KS. Use of empirically derived source-destination models to map regional conservation corridors. Conserv. Biol. 2009;23(2):368–376. doi: 10.1111/j.1523-1739.2008.01111.x. [DOI] [PubMed] [Google Scholar]
- 19.Moilanen, A. On the limitations of graph-theoretic connectivity in spatial ecology and conservation. J. Appl. Ecol. pp. 1543–1547 (2011).
- 20.Compton BW, McGarigal K, Cushman SA, Gamble LR. A resistant kernel model of connectivity for amphibians that breed in vernal pools. Conserv. Biol. 2007;21(3):788–799. doi: 10.1111/j.1523-1739.2007.00674.x. [DOI] [PubMed] [Google Scholar]
- 21.McRae BH, Dickson BG, Keitt TH, Shah VB. Using circuit theory to model connectivity in ecology, evolution, and conservation. Ecology. 2008;89(10):2712–2724. doi: 10.1890/07-1861.1.. [DOI] [PubMed] [Google Scholar]
- 22.Zeller KA, Jennings MK, Vickers TW, Ernest HB, Cushman SA, Walter MB. Are all data types and connectivity models created equal? Validating common connectivity approaches with dispersal data. Divers. Distrib. 2018;24(7):868–879. doi: 10.1111/ddi.12742.. [DOI] [Google Scholar]
- 23.Pullinger MG, Johnson CJ. Maintaining or restoring connectivity of modified landscapes: evaluating the least-cost path model with multiple sources of ecological information. Landscape Ecol. 2010;25(10):1547–1560. doi: 10.1007/s10980-010-9526-6. [DOI] [Google Scholar]
- 24.Sawyer SC, Clinton WE, Brashares JS. Placing linkages among fragmented habitats: do least-cost models reflect how animals use landscapes? J. Appl. Ecol. 2011;48(3):668–678. doi: 10.1111/j.1365-2664.2011.01970.x. [DOI] [Google Scholar]
- 25.Laliberté J, St-Laurent M-H. Validation of functional connectivity modeling: The Achilles’ heel of landscape connectivity mapping. Landsc. Urban Plan. 2020;202:103878. doi: 10.1016/j.landurbplan.2020.103878. [DOI] [Google Scholar]
- 26.Landguth EL, Cushman SA. CDPOP: A spatially explicit cost distance popula tion genetics program. Mol. Ecol. Resour. 2010;10(1):156–161. doi: 10.1111/j.1755-0998.2009.02719.x.. [DOI] [PubMed] [Google Scholar]
- 27.Landguth EL, Cushman SA, Schwartz MK, McKelvey KS, Murphy M, Luikart G. Quantifying the lag time to detect barriers in landscape genetics. Mol. Ecol. 2010;19(19):4179–4191. doi: 10.1111/j.1365-294X.2010.04808.x. [DOI] [PubMed] [Google Scholar]
- 28.Cushman SA, Landguth EL. Scale dependent inference in landscape genetics. Landsc. Ecol. 2010;25(6):967–979. doi: 10.1007/s10980-010-9467-0. [DOI] [PubMed] [Google Scholar]
- 29.Cushman SA, Shirk AJ, Landguth EL. Separating the effects of habitat area, fragmentation and matrix resistance on genetic differentiation in complex landscapes. Landscape Ecol. 2012;27(3):369–380. doi: 10.1007/s10980-011-9693-0. [DOI] [Google Scholar]
- 30.Macdonald EA, Cushman SA, Landguth EL, Hearn AJ, Malhi Y, Macdonald DW. Simulating impacts of rapid forest loss on population size, connectivity and genetic diversity of Sunda clouded leopards (Neofelis diardi) in Borneo. PLoS ONE. 2018;13(9):e0196974. doi: 10.1371/journal.pone.0196974. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31.Schumaker NH, Brookes A, Dunk JR, Woodbridge B, Heinrichs JA, Lawler JJ, Carroll C, LaPlante D. Mapping sources, sinks, and connectivity using a simulation model of northern spotted owls. Landscape Ecol. 2014;29(4):579–592. doi: 10.1007/s10980-014-0004-4. [DOI] [Google Scholar]
- 32.Unnithan Kumar S, Kaszta Ż, Cushman SA. Pathwalker: A new individual-based movement model for conservation science and connectivity modelling. ISPRS Int. J. Geo Inf. 2022;11(6):329. doi: 10.3390/ijgi11060329. [DOI] [Google Scholar]
- 33.Virtanen P, Gommers R, Oliphant TE, et al. SciPy 1.0: Fundamental algorithms for scientific computing in Python. Nat. Methods. 2020;17(3):261–272. doi: 10.1038/s41592-019-0686-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34.Dixon P. VEGAN, a package of R functions for community ecology. J. Veg. Sci. 2003;14(6):927–930. doi: 10.1111/j.1654-1103.2003.tb02228.x. [DOI] [Google Scholar]
- 35.Dray S, Royer-Carenzi M, Calenge C. The exploratory analysis of autocorrelation in animal-movement studies. Ecol. Res. 2010;25(3):673–681. doi: 10.1007/s11284-010-0701-7. [DOI] [Google Scholar]
- 36.Cushman, S.A. Animal movement data: GPS telemetry, autocorrelation and the need for path-level analysis. in Spatial Complexity, Informatics, and Wildlife Conservation (Springer, 2010), pp. 131-149.
- 37.Zeller KA, McGarigal K, Beier P, Cushman SA, Vickers TW, Boyce WM. Sensitivity of landscape resistance estimates based on point selection functions to scale and behavioral state: pumas as a case study. Landscape Ecol. 2014;29(3):541–557. doi: 10.1007/s10980-014-9991-4. [DOI] [Google Scholar]
- 38.Kareiva PM, Shigesada N. Analyzing insect movement as a correlated random walk. Oecologia. 1983;56(2):234–238. doi: 10.1007/BF00379695. [DOI] [PubMed] [Google Scholar]
- 39.Schumaker, N.H. Using landscape indices to predict habitat connectivity. Ecology (1996), pp. 1210–1225.
- 40.Schumaker NH, Brookes A. HexSim: A modeling environment for ecology and conservation. Landscape Ecol. 2018;33(2):197–211. doi: 10.1007/s10980-017-0605-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41.Bocedi G, Palmer SCF, Malchow A-K, Zurell D, Watts K. RangeShifter 2.0: An extended and enhanced platform for modelling spatial eco-evolutionary dynamics and species’ responses to environmental changes. Ecography. 2021;44(10):1453–1462. doi: 10.1111/ecog.05687. [DOI] [Google Scholar]
- 42.Kaszta Ż, Cushman SA, Slotow R. Temporal non-stationarity of path- selection movement models and connectivity: An example of African elephants in Kruger national park. Front. Ecol. Evol. 2021;9:207. doi: 10.3389/fevo.2021.553263. [DOI] [Google Scholar]
- 43.Osipova L, Okello MM, Njumbi SJ, Ngene S, Western D, Hayward MW, Balkenhol N. Using step-selection functions to model landscape connectivity for African elephants: Accounting for variability across individuals and seasons. Anim. Conserv. 2019;22(1):35–48. doi: 10.1111/acv.12432. [DOI] [Google Scholar]
- 44.Vergara M, Cushman SA, Ruiz-González A. Ecological differences and limiting factors in different regional contexts: landscape genetics of the stone marten in the Iberian Peninsula. Landscape Ecol. 2017;32(6):1269–1283. doi: 10.1007/s10980-017-0512-0. [DOI] [Google Scholar]
- 45.Reddy PA, Puyravaud J-P, Cushman SA, Segu H. Spatial variation in the response of tiger gene ow to landscape features and limiting factors. Anim. Conserv. 2019;22(5):472–480. doi: 10.1111/acv.12488. [DOI] [Google Scholar]
- 46.Zeller KA, Lewsion R, Fletcher RJ, Tulbure MG, Jennings MK. Understanding the importance of dynamic landscape connectivity. Land. 2020;9(9):303. doi: 10.3390/land9090303. [DOI] [Google Scholar]
- 47.Cronon W. The trouble with wilderness: or, getting back to the wrong nature. Environ. Hist. 1996;1(1):7–28. doi: 10.2307/3985059. [DOI] [Google Scholar]
- 48.Ingold, T. The Perception of the Environment: Essays on Livelihood, Dwelling and Skill (Routledge, 2021).
- 49.Boettiger AN, Wittemyer G, Starfield R, Volrath F, Douglas-Hamilton I, Getz WM. Inferring ecological and behavioral drivers of African elephant movement using a linear filtering approach. Ecology. 2011;92(8):1648–1657. doi: 10.1890/10-0106.1. [DOI] [PubMed] [Google Scholar]
- 50.Pooley S, Barua M, Beinart W, Dickman A, Holmes G, Lorimer J, Loveridge AJ, Macdonald DW, et al. An interdisciplinary review of current and future approaches to improving human-predator relations. Conserv. Biol. 2017;31(3):513–523. doi: 10.1111/cobi.12859. [DOI] [PubMed] [Google Scholar]
- 51.Benson ES. Minimal animal: Surveillance, simulation, and stochasticity in wildlife biology. Antennae. 2014;30:39. [Google Scholar]
- 52.Kaszta Ż, Cushman SA, Hearn AJ, Burnham D, Macdonald EA, Goossens B, Nathan SKSS, Macdonald DW. Integrating Sunda clouded leopard (Neofelis diardi) conservation into development and restoration planning in Sabah (Borneo) Biol. Cons. 2019;235:63–76. doi: 10.1016/j.biocon.2019.04.001. [DOI] [Google Scholar]
- 53.Penjor U, Astaras C, Cushman SA, Kaszta Ż, Macdonald DW. Contrasting effects of human settlement on the interaction among sympatric apex carnivores. Proc. R. Soc. B. 2022;289(1973):20212681. doi: 10.1098/rspb.2021.2681. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 54.Barua M. Bio-geo-graphy: Landscape, dwelling, and the political ecology of human-elephant relations. Environ. Plann. D Soc. Space. 2014;32(5):915–934. doi: 10.1068/d4213. [DOI] [Google Scholar]
- 55.Elliot NB, Cushman SA, Macdonald DW, Loveridge AJ. The devil is in the dispersers: Predictions of landscape connectivity change with demography. J. Appl. Ecol. 2014;51(5):1169–1178. doi: 10.1111/1365-2664.12282. [DOI] [Google Scholar]
- 56.Kareiva P, Marvier M. What is conservation science? Bioscience. 2012;62(11):962–969. doi: 10.1525/bio.2012.62.11.5. [DOI] [Google Scholar]
- 57.Bennett NJ, Roth R, Klain SC, Chan K, Christie P, Clark DA, Cullman G, Curran D, Durbin TJ, Epstein G, et al. Conservation social science: Understanding and integrating human dimensions to improve conservation. Biol. Conserv. 2017;205:93–108. doi: 10.1016/j.biocon.2016.10.006. [DOI] [Google Scholar]
- 58.Bunnefeld, N., Nicholson, E., & Milner-Gulland, E.J. Decision-Making in Conservation and Natural Resource Management: Models for Interdisciplinary Approaches. (Vol. 22, Cambridge University Press, 2017).
- 59.Parathian HE, McLennan MR, Hill CM, Fraza o-Moreira A, Hockings KJ. Breaking through disciplinary barriers: Human-wildlife interactions and multispecies ethnography. Int. J. Primatol. 2018;39(5):749–775. doi: 10.1007/s10764-018-0027-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 60.Hodgetts T. Connectivity as a multiple: In with and as “nature”. Area. 2018;50(1):83–90. doi: 10.1111/area.12353. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 61.Berkes, F. Sacred ecology (Routledge, 2017). 10.4324/9781315114644.
- 62.Parrenas, J.S. Decolonizing Extinction: The Work of Care in Orangutan Rehabilitation (Duke University Press, 2018).
- 63.Bill Adams, W., & Mulligan, M. Decolonizing Nature: Strategies for Conservation in a Post-Colonial Era (Routledge, 2012).
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
Access to the datasets used in this study may be supplied by the corresponding author upon request.