 Methodology article
 Open Access
 Published:
Potential path volume (PPV): a geometric estimator for space use in 3D
Movement Ecology volume 7, Article number: 14 (2019)
Abstract
Background
Many animals move in three dimensions and many animal tracking studies collect the data on their movement in three physical dimensions. However, there is a lack of approaches that consider the vertical dimension when estimating animal space use, which is problematic, as this can lead to mistakes in quantification of spatial differentiation, level of interaction between individuals or species, and the use of resources at different vertical levels.
Methods
This paper introduces a new geometric estimator for space use in 3D, the Potential Path Volume (PPV). The concept is based on time geography and generalises the accessibility measure, the Potential Path Area (PPA) into three dimensions. We derive the PPV mathematically and present an algorithm for their calculation.
Results
We demonstrate the use of the PPV in a case study using an open data set of 3D bird tracking data. We also calculate the size of the PPV to see how this corresponds to trip type (specifically, we calculate PPV sizes for departure/return foraging trips from/to a colony) and evaluate the effect of the temporal sampling on the PPV size. PPV sizes increase with the increased temporal resolution, but we do not see the expected pattern than return PPV should be smaller than departure PPV. We further discuss the problem of different speeds in vertical and horizontal directions that are typical for animal movement and to address this rescale the PPV with the ratio of the two speeds.
Conclusions
The PPV method represents a new tool for space use analysis in movement ecology where object movement occurs in three dimensions, and one which can be extended to numerous different application areas.
Trial registration
N/A
Introduction & Background
Many animals move freely in all dimensions within the biome and so the most appropriate characterisation of their space use and the patterns in their movement should use all three physical dimensions [1]. Of these, the first two represent the surface of the Earth and are either represented as geographic coordinates (longitude, latitude) or projected in some type of projected coordinate system (x – northing, y – easting). The third coordinate differs depending on the animal species: it can be elevation for species moving in highly variable terrain, such as deer in the mountains [2], altitude above the surface of the Earth for flying species [3] and species with a habitat in the forest canopies [4] or depth for fish [5, 6] or fossorial species [7].
Regardless of tracking technology used, data on animal movement are often mathematically represented in the form of trajectories, that is, sequences of geographic locations sampled at regular or irregular times. Many current tracking technologies allow location sampling in three physical dimensions: for example, GPS trackers measure elevation as well as longitude and latitude (although with worse accuracy for elevation than for the two surface dimensions) [8] and many biologgers for marine species include depth sensors [9]. Threedimensional location can also be extracted from stereo video footage [6] or in recent studies sometimes using passive integrated transponder tracking [7].
Despite the increased availability of threedimensional location in animal tracking data, the majority of space use methods are still based on only two geographical dimensions. In some cases the third dimension is independently examined, but in general it is altogether ignored. One of the most important concepts in ecology is the ecological niche hypervolume, which is the area within a multidimensional resource space that supports a species to persist and reproduce [10]. The most important dimensions of the niche are the three physical spatial dimensions and spatial differentiation in this 3D space is one of the vital factors of preventing competition among species [11]. Other dimensions (e.g. food resources or time use) are complementary to space use and can overlap even if there is spatial differentiations of niches. This differentiation often occurs through differences in use of vertical space [1] and yet the predominant way to explore such differentiations is by reverting to the two geographic dimensions only. This is problematic, since twodimensional approaches overlook the vertical space use, which, for species with a strong vertical component in their movement means that estimates of typical characteristics, such as the size of the home ranges, the amount of spatial overlap and consequently the level of interaction between individuals, and the use of resources at different vertical ranges, are often incorrect [12].
The reasons for third dimension being widely ignored in ecology are not very clear, especially since multidimensional statistical methods have existed for some time [1]. One reason could be the historically relatively high inaccuracy of vertical measurements in GPS trackers, which are one of the main sources of 3D data in ecology. This problem may soon be resolved with the deployment of the European positioning system Galileo [13] and the Chinese system COMPASS/Beidou, both of which are expected to significantly improve the accuracy of elevation measurements [14]. The second reason applies to marine tracking, where the third dimension, i.e. the depth, is typically collected by a different tag than the two geographic dimensions due to difficulties of satellite localisation for animals that live in water. Depth is normally collected using one of the triple combination data loggers (e.g. ConductivityTemperatureDepth or a TimeTemperatureDepth), while the 2D location comes from GPS or ARGOS tags for animals that frequently surface, such as sea mammals or from various types of acoustic localisation for fish. Linking depth and localisation data therefore requires further processing, such as deadreckoning between 2D locations and temporal data linkage, which can be a complex process with a high uncertainty [15]. The third reason may be that including the third dimension into movement models results in more complex geometrical calculations and introduces both a higher computational cost and a potentially more difficult interpretation of results. However, threedimensional data analysis methods are common in other fields, including areas where using the full range of the three dimensions in data is inevitable, such as 3D information visualisation of volumetric medical data [16]. These methods frequently employ geometric tools to optimise the complexity of 3D methods [17].
Some recent 3D space use studies introduced variations of kernel density estimates (KDE) in three dimensions and compared them with their twodimensional equivalents [6, 7, 18]. Others also incorporated time into their KDE methods, through development of new spatiotemporal kernels [19] or through adaptation of existing methods, such as for example an extension of Brownian bridges [20] into four dimensions [21, 22]. Outside of ecology Zou et al. [23] present a 4D time density algorithm and demonstrate its use on airplane trajectories. However, all these methods come with a high computational cost and are therefore relatively underused.
In this paper we propose a new geometric method for 3D space use, which is computationally fast in comparison with probabilistic methods. To do this, we generalise two wellknown time geography concepts, i.e. the SpaceTime Prism and the Potential Path Area [24], into four dimensions (three geographic dimensions and time). Time geography was introduced by Hägerstrand [25] to represent movement of people in a conceptual space of a SpaceTime Cube (STC), which consists of two geographic dimensions and time on the third axis. In this conceptual space, the volume that can be reached by a moving object given its observed speed is defined as a SpaceTime Prism [24,25,26]. The projection of this volume to the two geographic dimensions is an accessibility ellipse, called the Potential Path Area (PPA). PPAs are relatively easy and quick to calculate from movement trajectories and were proposed as a geometric estimator of animal space use in two geographic dimensions [27, 28].
We extend the principle of PPA into Potential Path Volumes (PPV) and propose that they could be used as a 3D space use estimator for trajectories where location is measured in three dimensions [26]. We define PPVs mathematically, present an algorithm for their calculation and demonstrate how they work on simulated data. We further apply PPVs on a case study using real animal movement data, where we demonstrate the use of PPVs for visualisation of the uncertainty of movement and evaluate how the size of PPVs depends on temporal sampling resolution. In human mobility and transportation research, spacetime prisms and PPAs are a common approach for modelling accessibility and are represented in different ways. A volumetric representation of the 2D prism was proposed by Forer [29], while Miller [24] developed a formal analytical definition for ndimensional spacetime prisms. This paper contributes by introducing an algorithm for a volumetric representation of the PPV in the 4D space and an application in the movement ecology context, where this type of modelling hasn’t been known before.
Our method is primarily aimed to represent unconstrained movement in three dimensions and is suitable for animals which live in air or in water. It may be of some value for movement that is loosely bound to three dimensions (such as movement of monkeys in tree canopies [4]), but less appropriate for movement where species are physically bound to the surface, even if this surface is three dimensional and there is an elevation component to the movement. Examples of this are deer climbing mountains [2] or ants crawling within a threedimensional nest [30]. Deer movement poses a different problem in terms of three dimensionality and may be better suited to be modelled with 2D PPAs superimposed on the terrain and reshaped based on the energy needed to climb in a certain direction. Ant movement has been represented using a network of chambers in the nest [30], which could serve as the frame for a three dimensional flow network, to be analysed with flow methods from human geography, such as spatial interaction modelling [31] or community detection [32].
The rest of this paper is structured as follows: in the Methods section we mathematically define the PPVs, present an algorithm for their calculation and demonstrate its use on simulated 3D correlated random walks. We introduce the case study by describing the data used and the intended use of PPVs. This is followed by the results and we conclude with a discussion where we comment on the potential of further methodological developments for 3D space use, such as consideration of external environmental conditions that affect 3D movement in our model.
Methods
We generalise a twodimensional time geography concept, the Potential Path Area (PPA, [24]) into three geographic dimensions. PPA is an accessibility measure from transport geography [33] but has also been used as a geometric estimator of animal home ranges [27]. Mathematically, the PPA is the projection of a SpaceTime Prism (STP) onto the geographical plane of the SpaceTime Cube (STC) [24]. The STP represents an accessibility volume within the STC which contains all the possible paths between two observed positions, P_{i} and P_{i + 1} (Fig. 1a), and whose size and orientation depend on the speed of movement between the two observed positions. Its projection onto the two geographic dimensions is an ellipse, whose size and orientation also depend on the speed between the two observed locations  this ellipse is called the PPA. The union of all PPAs, one built around each segment of a given trajectory, was proposed as a geometric delineator of the home range in two geographic dimensions [27].
We generalise the PPA ellipse into an ellipsoid in the threedimensional geographic space, which we call the Potential Path Volume (PPV, Fig. 1b). This ellipsoid is the projection of the fourdimensional SpaceTime HyperPrism (the 4D accessibility volume between the two observed positions) onto the 3D base space of the SpaceTime HyperCube. We calculate PPVs for all segments of a 3D trajectory, that is, a trajectory where location is measured in three geographic dimensions. The union of PPVs for a trajectory is an accessibility volume in the threedimensional geographic space. That is, given the observed 3D trajectory data and speed on each trajectory segment, the moving object could not have reached any of the locations outside this volume. The volume can consequently be used to delineate the outer boundary of potential space use in three geographic dimensions.
In the rest of this section we provide the mathematical definition of the PPV and describe the algorithm for calculation of PPVs for a set of given trajectories. We further demonstrate how PPVs work on a set of simulated trajectories, generated as 3D correlated random walks.
Mathematical definition
To obtain the Potential Path Area (PPA) in a twodimensional movement space, an ellipse is created around a movement segment by placing the start and end points of the trajectory segment, P_{i} and P_{i + 1}, in the foci of the ellipse. The ellipse equation is then derived using the maximum possible speed of the object and the time difference between P_{i} and P_{i + 1}. Given this speed and the elapsed time between the two locations, we can calculate the length of the longest path that the object could have traversed. If we imagine this path as a string fixed in P_{i} and P_{i + 1}, then placing a pen into this string and tracing as far as possible around the two foci while the pen is constrained by the string creates the ellipse that covers all possible paths that the object could have passed between points P_{i} and P_{i + 1} (Fig. 1a). This ellipse is thinner if the actual speed between the two points is closer to the maximum speed, and wider if the actual speed is slower. Note that normally PPA calculation assumes that the actual speed between two points is constant, which can be considered as valid when working with data where locations have been sampled with a high temporal frequency.
To create the Potential Path Volume (PPV) around a segment in a threedimensional movement space, we generalise this process into 3D (Fig. 1b), where P_{i} and P_{i + 1} form the foci of an oblique ellipsoid. The longest possible path between P_{i} and P_{i + 1} is again calculated using the time difference between the two points and the maximum possible speed of the moving object in three dimensions. We can then create the PPV ellipsoid by first tracing the ellipse in any plane that is parallel to movement direction between P_{i} and P_{i + 1} and then rotate the ellipse around the axis represented by the movement direction. This creates a special type of an ellipsoid, a socalled prolate spheroid, where the two minor axes are identical (Fig. 1b). That is, the ellipsoid has three axes: a major axis a and two identical minor axes b. This model assumes isotropic movement, meaning that movement along the two axes perpendicular to the line P_{i} to P_{i + 1} is equally possible. In a more general case, where the resistance to movement in different directions away from the P_{i} to P_{i + 1} line varies anisotropically, the PPV model could use a triaxial scalene ellipsoid, where all three axes are different (i.e. an ellipsoid with a major axis a and two minor axes b and c, where b ≠ c). As with PPA, the assumption is that the actual speed between the two points is constant, which creates a thinner/wider ellipsoid depending on how close the actual speed is to the maximum speed.
A PPV around each trajectory segment can be generated by knowing the following quantities (Fig. 1b): d  the distance between the two foci P_{i} to P_{i + 1}, a – the length of the major axis, b – the length of the two minor axes, P_{c} – the origin point of the ellipsoid’s own coordinate system and the centre of the ellipsoid and the two rotation angles (α, ß), which transform the coordinate system of the data into the ellipsoid’s coordinate system (Fig. 2a). In the following we derive each of these quantities.
Given a trajectory segment with start and end points P_{i}(x_{i}, y_{i}, z_{i}) and P_{i + 1}(x_{i + 1}, y_{i + 1}, z_{i + 1}), the origin point P_{c} is the central point between the two end points and is given by:
We calculate the distance d between P_{i} and P_{i + 1} as Euclidean distance in a threedimensional space:
Knowing the distance d, the time difference Δt between P_{i} and P_{i + 1} and the maximum possible speed of the moving object v_{max}, we can calculate the major and minor axes of the ellipsoid, a and b. The value of v_{max} can be either the maximum measured speed in the data, however note that that creates a degenerate ellipsoid on the segment where this speed was observed. We therefore use a more robust model for the maximum speed [27] and calculate it as per this:
Here v_{m} is the maximum observed speed and v_{m1} is the next largest observed speed. Then, a and b are calculated using:
The final task is to find the equations of the transformation of the original coordinate system (x, y, z) onto the ellipsoid axes (x’, y’, z’) (Fig. 2b). This transformation is a combination of a translation of the coordinate origin onto the central point P_{c}, followed by two rotations. The first rotation is around the z axis for the angle α and the second one around the rotated yaxis for angle ß (Fig. 2a). In navigation, α and ß are the Tait–Bryan nautical angles of pitch and yaw respectively (because of the symmetry of movement around the axis P_{i} to P_{i + 1}, the third nautical angle, the roll, is not important in our case) and can be calculated as:
Once we know the angles and the central point, then the transformation into the new coordinates is defined as follows:
where R(α) and R(ß) are the two rotation matrices given as:
The order of rotations in Eq. (7) corresponds to the right to left order in the matrix product, i.e. α first, then ß. Any point (x,y,z) in the original coordinate system is then within the PPV ellipsoid when the transformed coordinates satisfy the following inequality:
Algorithm to calculate PPVs around a trajectory
So far our solution for PPVs was presented analytically, but for the actual implementation of this solution we discretize the 3D space into a volume (a 3D grid with voxels). The main reason for this is the simplicity of combining several PPVs into one in a necessary step when we expand the segmentbased calculations from the previous section into a trajectorybased PPV. While an analytical solution of a trajectorybased PPV is possible (as a polysurface consisting of a union of individual segment ellipsoids), such a description would be limited in terms of visualisation and the possibility of combining the result with other data. Discretising the PPV on the other hand allows for a simple pervoxel combination with other data (both in the algorithm when we calculate the union of PPVs for all segments on a specific trajectory or if PPVs are derived for several individuals and merged into a populationwide descriptor of the use of 3D space, as is commonly done in ecology in 2D). Further, using a volumetric representation, the visualisation of results can be done using standard volumetric visualisation software, such as Voxler or ParaView. Based on all this we have chosen to represent the PPV as a volume.
The PPV for a trajectory is calculated per segment. For each segment we first find the characteristic values of the PPV ellipsoid (Eqs. 1, 2, 3, 4, 5, 6). To transform the PPV equations into a useable shape we use a discretization process where we divide the study area into small 3D pixels, termed voxels. We then transform the coordinates of the centre of each voxel in the PPV volume into the ellipsoid coordinate system (Eq. 7, Eq. 8) and use Eq. 9 to determine if the voxel is inside or outside the ellipsoid. We assign value 1 to internal voxels and value 0 to external voxels to create a Boolean volumetric representation of the PPV ellipsoid around this particular segment (Fig. 3a). The PPV volume for the entire trajectory is then built as a union of PPV volumes for each segment (Fig. 3b). The resulting volume can be visualised using standard volumetric visualisation techniques, such as volumetric rendering, surface mesh, or isosurfaces [34].
The pseudocode for our algorithm is provided in the Additional file 1, while Additional file 2 presents an example of use. The method has been integrated in the wildlifeTG R package (available at https://github.com/jedalong/wildlifeTG) and the R code used to generate the PPVs is also available individually at: http://github.com/udemsar/PPV. The code returns a volumetric data set, i.e. a set of voxel coordinates with the value of the PPV in each voxel, which should ideally be visualised in a volumetric visualisation software. We used Voxler (a 3D geology visualisation software from Golden Software) for this purpose, but a similar Free and Open Source Software option is ParaView.
PPVs on simulated trajectories
To demonstrate how the algorithm works for movement data, we calculate PPVs around a simulated trajectory, created as a correlated random walk (CRW) in three dimensions. Correlated random walks are commonly used as animal movement models [35]. Steps in a twodimensional CRW follow similar directional orientations, since most animals tend to keep the general direction of movement at a short temporal scale (i.e. moving forward). This is mathematically described by a small change in the angular direction of movement in the 2D plane from one step in the walk to another. Similarly, we generate a threedimensional CRW by varying two angular components of movement: the horizontal turning angle that describes the change in direction in the 2D geographic plane and the vertical turning angle that describes change in the vertical direction. We generate the 3D CRW on a series of uniform time steps and different speeds of movement at each step, in order to create a trajectory useful for demonstrating the PPV calculation. Figure 4 shows an example 3D CRW with the respective PPV volume, shown with a surface mesh and volumetric rendering.
Case study
In this case study we calculate the PPVs on a set of real 3D bird trajectories to demonstrate the potential of the method and investigate the effect of temporal sampling frequency and trip type on PPV size. In the second part of the case study we consider the problem of unequal movement characteristics in horizontal and vertical dimensions and propose a PPV solution where we rescale the coordinates in z direction according to ratio of vertical and horizontal speeds.
Data
We used open 3D bird tracking data from a study on avian movement [3], freely available from the Movebank repository [36]. The data consisted of GPS trajectories of foraging trips of 75 individual Antarctic petrels, Thalassoica antartica, which were collected to investigate the effect of wind conditions on the avian movement. A full description of the data can be found in Tarroux et al. [3], but here we summarise the points that are relevant to our method. Tracked individuals were tagged in the Svarthamaren breeding colony (71°53′S, 5°10′E) in Dronning Maud Land in Antarctica. The colony is located at 1600 m a.s.l. and 184 km away from the nearest point of (potentially) open water, where petrels can forage, with virtually no opportunities for finding the food in the areas between the colony and the open ocean. Trips were collected during three breeding seasons between 2011 and 2014, where each individual was fitted with a GPS tag and recaptured after returning from one foraging trip. GPS trackers were programmed to capture location at different temporal frequencies: 5 min, 10 min, 30 min, 60 min and 90 min. The mean absolute altitudinal error for GPS data was 52 m [3]. Figure 5 shows the 75 trajectories used in our study, superimposed over a digital elevation model of Antarctica [37] in three dimensions with exaggerated vertical dimension. Data were projected using Polar Stereographic projection with the standard parallel at 70°S.
The effect of temporal sampling on calculation of PPVs
One of the hypotheses in the Tarroux et al. [3] study is that birds drift more in their departure trips from the colony to the foraging grounds and take a more direct course on their return trips, compensating more strongly for wind drift. While the original study uses GPS tracking data combined with environmental data (atmospheric wind models) to investigate this hypothesis, we explored how this expected pattern would look in a geometric accessibility estimator, such as the PPV. We expected that the larger uncertainty in departure trips vs. return trips would mean that return PPVs should be overall smaller in size than the departure PPVs. Further, the size of the PPVs was expected to increase with the temporal sampling resolution, as longer sampling times produce longer segments, which in turn generates larger ellipses, that reflect larger uncertainty in movement between two observed points.
To test the effect of temporal sampling resolution on the size of the PPV, we separated bird trajectories into three groups with resolution of 5, 10 and 30 min and within each group into departure and return trips. We excluded trajectories with 90 min sampling as well as those trajectories where there were gaps in data that were of more than three times the resolution. For example, if a trajectory sampled at 5 min had a 16 min gap we excluded this trajectory from consideration. Such gaps could have occurred for a number of reasons (for example the GPS could momentarily lose connection to a required number of satellites), with the consequence that the focal distances of the PPV ellipsoid covering these gaps became very large and the resulting ellipsoids encompass the rest of the PPV. The final data set consisted of 68 trajectories: 18 with 5 min resolution, 34 with 10 min resolution and 16 with 30 min resolution.
We set the upper limit of the volume extent to 4000 m as no bird flew higher than 3170 m and the lower limit to 100 m to account for the GPS error creating seemingly underwater points. We then calculated the sizes of the PPVs and tested the effect of trip type (departure/return) and temporal sampling resolution with a twoway ANOVA.
Results of the sampling effect study
Figure 6 shows trajectories and PPVs of return and departure trips for two example birds. The PPVs in this figure are calculated without vertical exaggeration and are cut at maximum and minimum volume extent as per above.
Table 1 shows average sizes of PPVs for different sampling resolutions and split between departure and return trips. As expected, PPV sizes increase with the increased temporal resolution, but we do not see the expected pattern than return PPVs should be smaller than departure PPVs. This is also not apparent from the scatterplot of departure vs. return trips in Fig. 7a. The results of the ANOVA show that there is a highly significant main effect of trip type (F = 33.482, p < 0.001), a highly significant main effect of temporal sampling resolution (F = 447.679, p < 0.001) and a highly significant effect of interaction between the two factors (F = 218.309, p < 0.001). Figure 7b shows the interaction between trip types and temporal resolution on mean PPV sizes.
Addressing the differences in vertical and horizontal movement
One of the most challenging aspects of estimating the PPV is the selection of an appropriate value for v_{max}. With 2D PPA methods, Long & Nelson [27, 28] suggest several approaches derived from the statistical distribution of the individual segment velocities (i.e., distance / time between points P_{i} and P_{i + 1}) which we have extended to threedimensions. The biggest challenge in the estimation of the 2D PPA is the effect of having large and/or varied temporal durations between fixes, which results in a geometric space that overestimates the potential area of movement opportunity. The same effect can occur in the PPV, but is compounded by the fact that in most wildlife applications horizontal movement (i.e., across x and y dimensions) is fundamentally different from vertical movement (i.e., in z dimension). We propose to consider different v_xy_{max} and v_z_{max} values for horizontal and vertical speeds, which reflect different movement abilities of individual species.
Practically, this can be achieved by rescaling the zdimension coordinates proportionally to the ratio of v_z_{max} / v_xy_{max}. If v_z_{max} < v_xy_{max} (as would be the case for many species, for example for a long migratory flight at an almost constant elevation) this would have the effect of offsetting the vertical flatness inherent for movement across large distances to make the PPVs effectively flatter or narrower in the vertical dimension. We demonstrate this in Fig. 8, which shows PPVs calculated from the same data as Fig. 6, but where z dimension has been scaled with the ratio of v_z_{max} / v_xy_{max.}
Discussion
One of the limitations of our algorithm is that it creates a volumetric representation of movement, which as all volumetric algorithms involves a relatively long processing time. In particular, the computational complexity of our algorithm is O(n x p x v), where n is the number of trajectories (i.e. the number of moving individuals), p the length (number of points) of the longest trajectory and v the number of voxels. With high resolution (fine temporal interval) tracking data and representations with fine spatial volumetric resolution (i.e. those where voxels are relatively small), this means that the computational time will be longer and may increase beyond the expectation of what is practical for each dataset. There are ways of getting around this, for example, the complexity could be decreased by at each step considering only voxels from the box that bounds the ellipsoid around every segment instead of the entire volume. Currently the algorithm searches through the entire volume to identify if each voxel is inside the PPV or not. Instead, we could create a precut set of boxes within the volume, which would include only voxels that are nearest to the trajectory, but which can still potentially fall into any of the segmentbased ellipsoids. Then the option of being within/out of the PPV could be checked for these voxels only, resulting in fewer calculations than for the whole volume. This kind of improvement for volumetric algorithms is common in computer graphics [17] and has in GIScience been used previously in the case of spacetime densities [34].
Conversely, since the PPV defines the maximum volume that the moving object can reach given its maximum speed, it itself could be used to decrease the computational time of other complex three dimensional algorithms for space use. For example, calculations of any of the 3D densities (e.g. [21,22,23]) could be limited to voxels inside the PPV only, thus reducing the overall time needed for calculation of these volumetric representations.
Another limitation of the proposed model is the isotropic nature of movement in our choice of the ellipsoid. Currently we use a prolate ellipsoid, where the two minor axes are identical, thus assuming the ease of movement being the same in the two directions that are perpendicular to heading. This however is a simplification and a more complex scalene ellipsoid (i.e. the two minor axes are not necessarily the same) would be required to represent anisotropic movement. The anisotropy is related to the energetics and power costs associated with the animals’ physiology, but also the medium which the animal moves through. For example, in the absence of wind or thermoclines a vertical move upwards requires more energy than a comparable one downwards owing to the force of gravity. Vertical movement upward therefore requires higher power costs than downward movement and this could be accounted for by the shape of the ellipsoid. The opposite effects may be found in marine applications where buoyancy forces exceed gravity or where physiological limitations, such as availability of oxygen on deeper dives, may affect movement in vertical direction [15]. Previous movement analytics studies have included kinematics to create physically realistic spacetime prisms [38, 39] and a similar approach could be developed to account for energetics and power consumption of animal movement in 3D.
The calculation of the PPV is relevant only in cases where animals exhibit substantial movement in the vertical dimension (as well as horizontal). In many species, even substantial vertical movements will be an order of magnitude less than in the horizontal dimension [15, 40] reflecting different movement physiology and motivations in the vertical direction. We have suggested an approach to rescaling vertical coordinates to account for this effect (e.g., when v_z_{max} < v_xy_{max}) in an effort to capture differing movement ability in the vertical dimension. However, the temporal resolution of movement in the vertical dimension must also be carefully considered. That is, a fix interval suitable for capturing movement behaviour in the horizontal dimension, may be inappropriate (and likely too coarse) for capturing finescale movement in the vertical dimension. Thus, when implementing 3D movement models such as the PPV, the temporal resolution of the data must be examined carefully and consider the scale of movement in both horizontal and vertical dimensions. Where temporal fix intervals are coarse relative to movement behaviour in the vertical dimension (which might be typical), the PPV may overestimate potential movement opportunity in the vertical dimension.
Further, our model does not take into account environmental conditions that may affect the movement. To do this, the ellipsoid could be deformed by modelling the forces exerted by the external situation, for example, the uncertainty volume around a bird flying in strong winds could start as an ellipsoid, but the surface of this ellipsoid could then be stretched, twisted and distorted according to the forces exerted by the wind during the time that elapsed between the two observations’ of the bird’s location. Incorporating environmental conditions into 2D time geography has been previously explored [41, 42]), but is yet to be adapted to three dimensional systems.
PPVs could be used for trajectory annotation with 3D environmental data to support contextaware movement analytics. In 2D, trajectory annotation is a common way to link movement data with environmental data: the value of the environmental variable is calculated for the same moment in space and time as a trajectory point and appended to the trajectory point, creating a socalled semantic trajectory [43]. The calculation is typically done using different interpolation methods, for example the nearest neighbour interpolation or the dynamic interpolation in space [44] or various temporal interpolation methods [45]. For 3D environmental data, such as measurements of wind or the geomagnetic field, we propose that given the uncertainty in the movement, instead of trying to interpolate the field values from the nearest locations, we could consider the uncertainty in 3D trajectory annotation itself. The idea is to use the PPV to delineate the accessibility volume in the environmental field observations, interpolate the environmental field values within the PPV volume and normalise the result with the PPV size as it has been done for other quantitative volumetric measures [46]. The result could then be used to annotate the segment between the two 3D points, to create a 3D semantic trajectory and these data could then be used for identification of movement behaviour through trajectory segmentation or data mining methods [47].
Conclusions
This paper introduced the Potential Path Volume (PPV) as a new geometric estimator of space use in three physical dimensions. We described its mathematical derivation and presented two examples of use: as a visualisation tool for exploring the uncertainty of movement and as an estimator of the size of the uncertainty volume and how that depends on the temporal sampling frequency. Finally, we demonstrate how the PPV method can be used to study targeted questions pertaining to wildlife movement and space use in 3D. The PPV method represents a new tool for space use analysis in movement ecology where object movement occurs in three dimensions, and one which can be extended to numerous different application areas.12
Abbreviations
 2D:

Two dimensional
 3D:

Three dimensional
 ANOVA:

Analysis of variance
 CRW:

Correlated random walk
 GPS:

Global positioning system
 PPA:

Potential Path Area
 PPV:

Potential Path Volume
 STC:

SpaceTime Cube
 STP:

SpaceTime Prism
References
 1.
Belant JL, Millspaugh JJ, Martin JA, Gitzen RA. Multidimensional space use: the final frontier. Front Ecol Environ. 2012. https://doi.org/10.1890/12.WB.003.
 2.
De Groeve J, Van de Weghe N, Ranc N, Neutens T, Ometto L, RotaStabelli O, et al. Extracting spatiotemporal patterns in animal trajectories: an ecological application of sequence analysis methods. Methods Ecol Evol. 2015;7:369–79.
 3.
Tarroux A, Weimerskirch H, Wang SH, Bromwich DH, Cherel Y, Kato A, et al. Flexible flight response to challenging wind conditions in a commuting Antarctic seabird: do you catch the drift? Anim Behaviour. 2016;113:99–112.
 4.
Makin DF, Payne HFP, Kerley GIH, Shrader AM. Foraging in a 3D world: how does predation risk affect space use of vervet monkeys? J Mammal. 2012;93(2):422–8.
 5.
Heupel MR, Lédée EJI, Simpendorfer C. Telemetry reveals spatial separation of cooccurring reef sharks. Mar Ecol Prog Ser. 2018;589:183–96.
 6.
Vivancos A, Closs G, Tentelier C. Are 2D spaceuse analyses adapted to animals living in 3D environments? A case study on a fish shoal. Behav Ecol. 2017;28(2):485–93.
 7.
Ousterhout BH, Burkhart JJ. Moving beyond the plane: measuring 3D home ranges of juvenile salamanders with passive integrated transponder (PIT) tags. Behav Ecol Sociobiol. 2017;71:59. https://doi.org/10.1007/s0026501722846.
 8.
Cagnacci F, Boitani L, Powell RA, Boyce MS. Animal ecology meets GPSbased radiotelemetry: a perfect storm of opportunities and challenges. Philos Trans R Soc B. 2010;365:2157–62.
 9.
Wilmers CC, Nickel B, Bryce CM, Smith JA, Wheat RE, Yovovich V. The golden age of biologging: how animalborne sensors are advancing the frontiers of ecology. Ecology. 2015;96(7):1741–53.
 10.
Hutchinson M. Concluding remarks. In: Cold spring harbour Symposia on quantitative biology: population studies: animal ecology and demography. New York: Cold Spring Harbor laboratory, cold Spring Harbor; 1957. p. 415–27.
 11.
Cunha AA, Vieira MV. Two bodies cannot occupy the same place at the same time, or the importance of space in the ecological niche. Bull Ecol Soc. 2004;116:25–6.
 12.
LópezLópez P. Individualbased tracking Systems in Ornithology: welcome to the era of big data. Ardeola. 2016;63(1):103–36.
 13.
ESA, Galileo begins serving the globe. 2016. Accessed on 27 Nov 2018. http://www.esa.int/Our_Activities/Navigation/Galileo_begins_serving_the_globe
 14.
Li X, Zhang X, Ren X, Fritsche M, Wickert J, Schuh H. Precise positioning with current multiconstellation global navigation satellite systems: GPS, GLONASS, Galileo and BeiDou. Nat Sci Rep. 2015;5:8328.
 15.
Bestley S, Jonsen ID, Hindel MA, Harcourt RG, Gales NJ. Taking animal tracking to new depths: synthesizing horizontalvertical movement relationships for four marine predators. Ecology. 2015;96(2):417–27.
 16.
Kehrer J, Hauser H. Visualization and visual analysis of multifaceted scientific data: a survey. IEEE Trans Vis Comput Graph. 2013;19(3):495–513.
 17.
Schneider P, Eberly DH. Geometric tools for computer graphics. Amsterdam: Morgan Kaufmann; 2002.
 18.
Simpendorfer CA, Olsen EM, Heupel MR, Moland E. Threedimensional kernel utilization distributions improve estimates of space use in aquatic animals. Can J Fish Aquat Sci. 2012;69:565–72.
 19.
Keating KA, Cherry S. Modeling utilization distributions in space and time. Ecology. 2009;90(7):1971–80.
 20.
Horne JS, Garton EO, Krone SM, Lewis JS. Analyzing animal movements using Brownian bridges. Ecology. 2007;88(9):2354–63.
 21.
Tracey JA, Sheppard JK, Zhu J, Wei F, Swaisgood RR, Fisher RN. Movementbased estimation and visualization of space use in 3D for wildlife ecology and conservation. PLoS One. 2014;9(7):e101205.
 22.
Tracey JA, Sheppard JK, Lockwood GK, Chourasia A, Tatineni M, Fisher RN, et al. Efficient 3D MovementBased Kernel Density Estimator and Application to Wildlife Ecology. In: Proceedings of the 2014 Annual Conference on Extreme Science and Engineering Discovery Environment XSEDE '14, Atlanta, GA, USA; 2014. https://doi.org/10.1145/2616498.2616522.
 23.
Zou Y, Chen Y, He J, Pang G, Zhang K. 4D time density of trajectories: discovering spatiotemporal patterns in movement data. ISPRS Int J GeoInfo. 2018;7:212. https://doi.org/10.3390/ijgi7060212.
 24.
Miller HJ. A measurement theory for time geography. Geogr Anal. 2005;37:17–45.
 25.
Hägerstrand T. What about people in regional science? Pap Reg Sci. 1970;24:7–21.
 26.
Demšar U, Long JA. Timegeography in four dimensions: potential path volumes around 3D trajectories. In: Proceedings of GIScience 2016. Montreal; 2016. p. 27–30.
 27.
Long JA, Nelson TA. Time geography and wildlife home range delineation. J Wildl Manag. 2012;76(2):407–13.
 28.
Long JA, Nelson TA. Home range and habitat analysis using dynamic time geography. J Wildl Manag. 2015;79(3):481–90.
 29.
Forer P. Geometric approaches to the Nexus of time, space and microprocess: implementing a practical model for mundane sociospatial systems. In: Egenhofer MJ, Golledge RG, editors. Spatial and temporal reasoning in geographic information systems. Oxford: Oxford University Press; 1998. p. 171–90.
 30.
Varoudis T, Swenson AG, Kirkton SD, Waters JS. Exploring nest structures of acorn dwelling ants with Xray microtomography and surfacebased threedimensional visibility graph analysis. Phil Trans R Soc B. 2018;373:20170237.
 31.
SiłaNowicka K, Fotheringham AS. Calibrating spatial interaction models from GPS tracking data: an example of retail behaviour. Comput Environ Urban Syst. 2019;74:136–50.
 32.
Sekulić S, Long JA, Demšar U. The effect of geographical distance on community detection in flow networks. In: Proceedings of the AGILE 2018 conference, Lund, Sweden; 2018. p. 12–5.
 33.
Patterson Z, Farber S. Potential path areas and activity spaces in application: a review. Transp Rev. 2015;35(6):679–700.
 34.
Demšar U, Virrantaus K. Spacetime density of trajectories: exploring spatiotemporal patterns in movement data. Int J Geogr Inf Sci. 2010;24(10):1527–42.
 35.
Codling EA, Plank MJ, Benhamou S. Random walk models in biology. J R Soc Interface. 2008;5:813–34.
 36.
Tarroux A, Weimerskirch H, Wang S, Bromwich DH, Cherel Y, Kato A, et al. Data from: flexible flight response to challenging wind conditions in a commuting Antarctic seabird: do you catch the drift? In: Movebank data repository; 2016. https://doi.org/10.5441/001/1.q206rm6b.
 37.
Di Marzio JP. GLAS/ICESat 500 m Laser Altimetry Digital Elevation Model of Antarctica, Version 1. [Subset used: long = (−2.99°, 9.04°), lat = (−72.41°,69.52°)]. NSIDC: National Snow and Ice Data Center, Boulder, Colorado USA. 2007; Date accessed: 1 Nov 2018. doi: https://doi.org/10.5067/K2IMI0L24BRJ.
 38.
Kuijpers B, Miller HJ, Othman W. Kinetic prisms: incorporating acceleration limits into space–time prisms. Int J Geogr Inf Sci. 2017;31(11):2164–94.
 39.
Long JA, Nelson TA, Nathoo FS. Toward a kineticbased probabilistic time geography. Int J Geogr Inf Sci. 2014;28(5):855–74.
 40.
Weimerskirch H, Bishop C, JeanniardduDot T, Prudor A, Sachs G. Frigate birds track atmospheric conditions over monthslong transoceanic flights. Science. 2016;353(6294):74–8.
 41.
Miller HJ, Bridwell SA. A fieldbased theory for time geography. Ann Assoc Am Geogr. 2009;99(1):49–75.
 42.
Long JA. Modeling movement probabilities within heterogeneous spatial fields. J Spatial Info Sci. 2018;(16):85–116.
 43.
Alvares LO, Bogorny V, Kuijpers B, de Macedo JAF, Moelans B, Vaisman A. A model for enriching trajectories with semantic geographical information. In: Proceedings of the 15^{th} Annual ACM International Symposium on Advances in Geographic Information Systems (GIS '07), 2007; 22:1–8. doi: https://doi.org/10.1145/1341012.1341041
 44.
Brum Bastos VS, Long JA and Demšar U. Dynamic trajectory annotation for integration of context into movement data. Visuallysupported computational movement analysis (VCMA2016) workshop at AGILE 2016 conference, Helsinki, 14 June 2016.
 45.
Dodge S, Bohrer G, Weinzierl R, Davidson SC, Kays R, Douglas D, et al. The environmentalDATA automated track annotation (EnvDATA) system: linking animal tracks with environmental data. Mov Ecol. 2013:1–3.
 46.
Demšar U, Çöltekin A. Quantifying gaze and mouse interactions on spatial visual interfaces with a new new movement analytics methodology. PLoS One. 2017;12(8):e0181818.
 47.
Brum Bastos VS, Long JA, Demšar U. Weather effects on human mobility: an analysis using MultiChannel sequence analysis. Comput Environ Urban Syst. 2018;71:131–52.
Acknowledgements
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Funding
Urška Demšar is supported by a Leverhulme Trust Research Project Grant (RPG2018258).
Availability of data and materials
The datasets used in the current study are available as per following: the Antarctic petrel tracking data set is in Movebank Repository, doi:https://doi.org/10.5441/001/1.q206rm6b [36] and the free GLAS/ICESat 500 m Laser Altimetry Digital Elevation Model of Antarctica is provided the by National Snow and Ice Data Center (NSIDC), doi:https://doi.org/10.5067/K2IMI0L24BRJ [37]. Code is available as part of wildlifeTG R package (https://github.com/jedalong/wildlifeTG) and separately (http://github.com/udemsar/PPV).
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UD conceived the study and developed and coded the PPV algorithm. JL developed the 3D CRW example and implemented the CRW and PPV algorithms as part of his R package. Both authors worked on the case study and contributed to writing the manuscript. Both authors read and approved the final manuscript.
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Correspondence to Urška Demšar.
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Additional files
Additional file 1:
Pseudocode of the PPV algorithm. (PDF 94 kb)
Additional file 2:
A worked example as R markdown. (RMD 3 kb)
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Demšar, U., Long, J.A. Potential path volume (PPV): a geometric estimator for space use in 3D. Mov Ecol 7, 14 (2019) doi:10.1186/s4046201901584
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Keywords
 Movement analytics
 Animal movement
 3D
 Time geography
 Space use
 Volumetric visualisation