Rigorous home range estimation with movement data: a new autocorrelated kernel density estimator
Corresponding Editor: E. G. Cooch.
Abstract
Quantifying animals' home ranges is a key problem in ecology and has important conservation and wildlife management applications. Kernel density estimation (KDE) is a workhorse technique for range delineation problems that is both statistically efficient and nonparametric. KDE assumes that the data are independent and identically distributed (IID). However, animal tracking data, which are routinely used as inputs to KDEs, are inherently autocorrelated and violate this key assumption. As we demonstrate, using realistically autocorrelated data in conventional KDEs results in grossly underestimated home ranges. We further show that the performance of conventional KDEs actually degrades as data quality improves, because autocorrelation strength increases as movement paths become more finely resolved. To remedy these flaws with the traditional KDE method, we derive an autocorrelated KDE (AKDE) from first principles to use autocorrelated data, making it perfectly suited for movement data sets. We illustrate the vastly improved performance of AKDE using analytical arguments, relocation data from Mongolian gazelles, and simulations based upon the gazelle's observed movement process. By yielding better minimum area estimates for threatened wildlife populations, we believe that future widespread use of AKDE will have significant impact on ecology and conservation biology.
Introduction
Home range estimation, a critical statistical challenge, applies to areas of ecology ranging from theoretical ecology to wildlife management. Whether quantifying space use or designing conservation strategies, ecologists need to know what habitats an animal uses in terms of both location and extent. Animal tracking data increasingly constitute the key inputs into home range estimation procedures. Conventional methods of home range estimation largely fall into two camps: geometric techniques, such as the minimum convex polygon (MCP; Bekoff and Mech 1984, Fieberg and Börger 2012), that lack an underlying probabilistic model, and statistical techniques that were not developed for use with animal tracking data, such as kernel density estimators (KDEs; Worton 1989). While KDEs are the most efficient nonparametric estimators of probability density functions (PDFs), they are derived under the assumption of independent and identically distributed (IID) data, an assumption violated by autocorrelation and nonstationarity (Silverman 1986). When faced with realistic, autocorrelated movement data, KDEs have been observed (Swihart and Slade 1985, Hansteen et al. 1997) and proven (Fleming et al. 2014a) to underestimate home range area, often dramatically (Fig. 1). Common suggestions for dealing with autocorrelated location data include coarsening the sampling rate (Swihart and Slade 1985) and stratification across individuals (Otis and White 1999), but these types of adjustments are generally inefficient.

(A) A simulation of location data points (red dots) drawn from a spatial point process that unrealistically lacks autocorrelation between points. (B) More realistic data drawn from a continuous, stochastic process fit to tracking data for Mongolian gazelle, Procapra gutturosa (Fleming et al. 2014a). The true home ranges (95% confidence regions) for the stochastic processes underlying the plots in (A) and (B) are identical (black circles) and in both cases there is an identical number of data points, but in (B) the observation period is only long enough to observe a few home range crossings. (C) The home range area of (B) is estimated using conventional kernel density estimation (KDE; dashed blue line) and our new autocorrelated KDE (AKDE; dotted aqua line). The conventional KDE approach draws tight boundaries around the observed data, while AKDE can project future space use from limited data. (D) The stochastic process from (B) is run 10 times further into the future, demonstrating that AKDE was correct and KDE was incorrect in (C), even though KDE might have seemed reasonable based on visual inspection.
Autocorrelation means that an individual's position, velocity, or acceleration measured at one point in time are statistically correlated with the same measurements in the past, and also implies that these correlations will carry on into the future. Autocorrelation is the rule, not the exception, in animal movement data. Autocorrelation can arise from diverse sources and may occur over multiple timescales in a single individual's movement path. First, and most fundamentally, autocorrelation is an ineluctable consequence of the fact that animal movement is a continuous process. Uncorrelated location data would lack any degree of continuity, whereas real animals trace continuous paths through the environment and have continuous velocity and acceleration. Second, autocorrelation arises when individuals continue a particular movement behavior for an extended period of time or repeat certain behaviors such as revisiting the same foraging areas, dens, or nesting sites. Typically, correlations diminish as observations grow farther apart in time, but autocorrelations in movement data often persist over long time periods, e.g., months or years (McNay et al. 1994, Rooney et al. 1998, Boyce et al. 2010, Fleming et al. 2014a, b).
The conceptual definition of home range given by Burt (1943) lacks an objective, mathematical description that can be statistically estimated from data. We view relocation data as a sample of a much longer, continuous trajectory that is only one of many possible movement‐path realizations of a continuous‐time stochastic process. In this formalism, movement‐path realizations that exhibit realistic behaviors and result in heavy use of the observed animal's core areas are assigned higher probabilities than those that stray off into little‐used regions. This definition thus operationalizes Burt's intuition that rare excursions should not be included in the home range by down‐weighting such excursions. We therefore define the home range area as a percent coverage region, usually taken to be 95%, of the probability distribution of all possible locations, as determined from the distribution of all possible paths (hereafter, range distribution). This is the same distribution that the conventional KDE approach estimates when its input data are independent. The range distribution addresses the lifetime space requirements of an animal and provides a metric that can be compared across individuals. Unfortunately, the range distribution is frequently conflated with the occurrence distribution, which does not quantify the home range but instead estimates where an animal was located during the observation period (see Appendix A for a detailed discussion of these two distributions, their differences, and their estimators). While both of these distributions are sometimes referred to as the utilization distribution, in what follows, we focus only on the range distribution, as it is closest to Burt's original definition.
Natural statistical intuitions often fail in the presence of autocorrelation. In a random sample of n independent observations from an individual's position distribution, on average, we expect 0.95 n observations to fall inside the estimated distribution's 95% contour and 5% to fall outside. However, this is not the case for autocorrelated data, which contain less positional information than an equivalently sized sample of independent data (Fig. 1). For autocorrelated data, the proportion of sampled points that falls within a given contour of the range distribution depends entirely on the timespan and the strength of the autocorrelation. Consequently, to match the position information contained in an independent sample of a particular size, a larger and longer‐term sample is needed for autocorrelated movement data. This explains why the conventional KDE will tend to yield underestimates on autocorrelated data and also why, when using such data, an individual's estimated home range area tends to initially increase with sampling duration even if their movement process remains stationary (Girard et al. 2002). In this latter scenario, the underlying range distribution being estimated, and thus the true home range, has not necessarily changed, but it becomes more completely sampled and thus better resolved as the observation time increases.
What then are ecologists to do when faced with autocorrelated movement data of short duration, for which conventional KDE always underestimates the animal's ultimate space use? Fortunately, the other side of the autocorrelation coin offers a solution. Autocorrelation implies relationships between past and future movements and can therefore be harnessed to make statistically rigorous predictions of future movement. Most current space‐use estimators discard this information, but an estimator purpose‐built for autocorrelated data could, in a mechanistic way, leverage the information to make better home range predictions (Börger et al. 2008). Previous home range estimators that account for autocorrelation have been extremely limited. Autocorrelated bivariate Gaussian density estimation (AGDE; Dunn and Gipson 1977, Fleming et al. 2014b) can incorporate realistic movement behaviors featuring strong, multiscale autocorrelations; however, AGDE typically estimates Gaussian range distributions, which will not work for many species. Mechanistic home range analysis (MHRA; Moorcroft and Lewis 2006, Moorcroft 2012, Potts and Lewis 2014) can provide more detailed range distributions, however current modeling efforts are limited to Markov processes (Appendix A: A.2), which cannot describe the continuous velocity motion revealed by modern ARGOS and GPS telemetry data (Johnson et al. 2008, Fleming et al. 2014a). Moreover, while Moorcroft and Barnett (2008) provide a fitting method that can account for Markovian autocorrelation, the traditional method of assuming independent observations remains in use (Bateman et al. 2014). Finally, while Brownian bridge density estimation (BBDE; Horne et al. 2007) is sometimes mistakenly employed as a home range estimator, its estimation target is actually the occurrence distribution, which does not quantify the home range (Appendix A: A.3).
We develop a new home range estimator that combines KDE's flexibility and efficiency with AGDE's ability to account for and leverage the information content of highly autocorrelated movement data. We formally re‐derive the KDE explicitly assuming the data represent a sample from a nonstationary, autocorrelated, continuous movement process. The resulting autocorrelated KDE (hereafter AKDE) incorporates movement effects through the autocorrelation function (ACF), which can either be derived from a fitted movement model (as in Fleming et al. 2014a) or directly estimated from the data (Appendix C). We illustrate AKDE's improved performance with both simulated data where the true home range area is known and an empirical example featuring Mongolian gazelles (Procapra gutturosa), which previous analyses have shown to exhibit highly autocorrelated movement. We outline the conditions under which the AKDE will outperform the classical KDE and show that our AKDE reduces to the standard KDE in the limit where autocorrelation vanishes and samples are truly independent. The AKDE is therefore a generalization of KDE.
Kernel density estimation
KDE proceeds by placing small kernels of smoothing bandwidth or covariance σB at each sampled location (Silverman 1986). The average of these kernels provides the estimate,
, of the PDF p. The kernel's shape matters little, but the bandwidth selection is paramount (Silverman 1986, Izenman 1991, Turlach 1993). The optimal bandwidth minimizes the mean integrated squared error (MISE) between p and its estimate
. The optimal σB will vary among data sets, but its calculation can be automated. KDE bandwidth optimization poses more problems than ordinary regression analysis. Several methods have been developed; plug‐in and cross‐validation approaches are the two most common (Silverman 1986, Turlach 1993). In general, plug‐in methods tend to over‐smooth the estimate, while cross‐validation methods tend to under‐smooth the estimate; adaptive‐bandwidth methods tend to produce more detail in areas of high frequency compared to fixed‐bandwidth methods (Silverman 1986, Izenman 1991, Turlach 1993).



Application
In Fig. 2, we plot KDEs for the ranging behavior of one Mongolian gazelle monitored over a 1‐yr period. We obtained a total of n = 866 relocations for this individual using an hourly sampling schedule with 5‐h gaps every 20 h and 11‐d gaps after every 5 d of sequential data. Fig. 2A uses the conventional bandwidth, which only applies to uncorrelated data, while Fig. 2B uses Eq. B.35 (in Appendix B), along with the ACF estimate calculated in Fleming et al. (2014b). The AKDE predicts a home range area of 50 000–94 000 km2, with confidence intervals calculated according to data in Appendix B: Eq. B.3, while the conventional KDE estimate is only 19 000–20 000 km2. Next, we restrict our analysis to the first half of the data to test how the two methods predict future space use, using conventional KDE in Fig. 2C and the AKDE in Fig. 2D. With half the data, AKDE predicts a home range area of 47 000–96 000 km2, which is consistent with its better estimate derived from the full data, though the confidence intervals are slightly wider. In contrast, conventional KDE predicts a home range area of 9000–10 000 km2, which differs substantially from its better estimate. Because of the quantity and resolution of the data, the range estimate using the conventional KDE approach falls tightly around the sampled data. Increasing the sampling frequency will further degrade the conventional estimate, causing the home range to split into numerous isolated areas of high utilization.

(A) KDE and (B) AKDE are compared against the distribution of locations (red dots) for a Mongolian gazelle, observed over a period of 361 d. In all cases, the density estimate is shown as blue shading, a black contour line delineates the point estimate of the 95% home range area, and two gray contour lines express the 95% confidence range of the home range area. For AKDE, there is significant uncertainty in delineating how much area the gazelle will use 95% of the time, which is estimated to fall between the two gray contours, while for conventional KDE, the estimated uncertainty is hardly visible. The wide confidence intervals of the AKDE are appropriate for this data set, as will be demonstrated in the final two panels, while KDE massively underestimates the real uncertainty associated with home range estimation. In panels (C) for KDE and (D) for AKDE, the data set is segmented into its first half (red dots) and second half (orange stars), and only the first half is used for both autocorrelation parameter estimation and kernel density estimation. This subsetting has a large effect on the home range predictions from the KDE method, but only a very minor change for the AKDE predictions, given that there is already enough information in the first half of the data to fully represent the movement behavior (but not necessarily the space use). The KDE method fails to anticipate the possibility of the long sojourns that the gazelle undertook during the second half of the monitoring period. This possibility was already accounted for by the AKDE method, which was well informed by the autocorrelation structure present in the first half of the data. Traditional leave‐one‐out cross‐validation assumes independence and does not cross‐validate the data in such a temporally meaningful way.
This behavior typifies the conventional KDE and leads some researchers (e.g., Swihart and Slade 1985) to advocate for nonstatistical measures (i.e., MCP) that at least appear visually reasonable. However, note that in both cases (Fig. 2A, C) the 95% home range area of the AKDE is much larger than the MCP would be. Mongolian gazelles are nomadic wanderers whose movements may involve gross displacements exceeding 1000 km/yr with little concordance among years (Olson et al. 2010, Mueller et al. 2011, Fleming et al. 2014b) Consequently, longer observation periods tend to show the gazelles using larger amounts of space, up to an asymptote set by the ACF's details (Fleming et al. 2014a). The AKDE captures this important behavior, whereas conventional space‐use estimates will miss it because they discard the information encoded in the ACF on the movement process' long‐run behavior.
Visually, AKDE estimates often look too large because they contain substantial areas where the focal individual was not directly observed (e.g., Figs. 1 and 2; Appendix B: Eq. B.3). However, as previously mentioned, statistical intuition derived from experience with independent data often fails to transfer to situations where data are autocorrelated. In particular, as we have demonstrated with simulation (Fig. 1; Appendix B: B.3) and shown mathematically (Appendix B: Eq. B.35), the home range area cannot be determined from the locations alone, so the intuitive expectation that a home range area should conform closely to the observed locations is often inappropriate. Instead, accurately characterizing the individual's long‐term space use requires leveraging the information that exists in the transitions between spatial locations (i.e., in the ACF). Because the data points are linked together by the animal's movements, it is the time dependence in the data that ultimately provides insight into space usage.
Discussion
We have introduced AKDE, a new kernel density estimator that properly takes autocorrelation into account so that it accurately estimates home ranges from animal movement data. Among KDE techniques, only our estimator is asymptotically consistent, with an asymptotically optimal order of error, when data are autocorrelated. As we have shown, the conventional KDE only provides a lower bound for the estimate of home range area (Appendix B: B.2.1), and it is only valid when the relocation data are sampled so coarsely that they appear uncorrelated in time and the data are recorded for a far longer time than the timescale over which autocorrelations persist. When the sampling interval is much shorter than the autocorrelation timescales, which is inevitably the case for finely sampled (e.g., hourly) movement data in ungulates and other large animals, then the conventional KDE of home range area is too small. What is worse, using KDE with more continuously sampled locations will more severely underestimate an animals' area requirements (see Appendix B: B.4 and Fleming et al. 2014a), which runs counter to the intuition that more tracking data will reveal more space‐use detail. Moreover, if autocorrelations persist over timescales comparable to the observation period, then all conventional methods will underestimate space use.
Because of the aforementioned limits on easy visual assessment of autocorrelated movement data, ordinary intuitions are significantly biased when applied to animal tracking data, and, unfortunately, these biases only increase with increasing sampling frequency. In the limit of continuously sampled data, the conventional KDE home range area vanishes, while the AKDE asymptotes to a well‐defined estimate (Appendix B: B.4). Unless the sampling interval is much larger than the autocorrelation timescales, an increase in the sampling rate does not result in a proportional increase in the effective sample size (i.e., the information content). Importantly, the period of data needs to be at least as long as the home range crossing time, if not many times longer, for any home range estimation (Appendix C).
Conventional estimates of an individual's home range size often increase as the observation period increases (Girard et al. 2002). In this case, the underlying range distribution can be the same, but some of the bias inherent in conventional home range estimates decreases as the observation period increases. Conventional estimators assume that locations are sampled independently from the animal's range distribution; however, it can take a significant amount of time for an animal to journey through its home range, and a brief observation window will not yield a representative sample. Moreover, in the conventional perspective it can be difficult to ascertain if the home range has stopped increasing, as there are no reliable confidence intervals to compare growth with, and the home range estimates themselves are temporally autocorrelated, making trends difficult to distinguish from errors. Bootstrap and cross‐validation techniques may seem useful for this purpose, but they also generally assume a lack of autocorrelation in the data. Because our approach is rigorously built from first principles to account for autocorrelation, it provides accurate confidence intervals that can diagnose situations where the data are insufficient to provide a reasonable home range estimate. For our gazelle example with short observation periods (Fig. 2), instead of yielding a grossly underestimated home range with deceptively narrow confidence intervals, the AKDE returns a reasonable estimate with wide confidence intervals that appropriately reflect the estimate's limited precision.
In contrast with Swihart and Slade (1985) and Hansteen et al. (1997), several simulation studies have demonstrated situations where autocorrelation is not problematic for conventional KDE (De Solla et al. 1999 and references in Fieberg 2007). In particular, De Solla et al. (1999) simulated a situation in which velocities were discontinuous and even the shortest sampling interval was comparable to the home range crossing time. As a result, De Solla et al. (1999) drew the premature conclusion that including more autocorrelated data was generally better than coarsening the data to avoid autocorrelation. However, real movement data sampled with modern GPS technology will tend to feature much stronger and possibly much longer‐lasting autocorrelations, as well as much finer sampling relative to the home range crossing time. Under these conditions autocorrelation's negative effects on conventional home range estimates must be considered (McNay et al. 1994, Hansteen et al. 1997, Rooney et al. 1998, Boyce et al. 2010, Fleming et al. 2014a, b). Our results demonstrate how badly the conventional KDE will fail for different movement processes and different sampling schedules. Importantly, AKDE obviates the need for brute‐force strategies to avoid autocorrelation, such as thinning the data or sampling in an intentionally coarse way. There is no need to try and separate home range problems into situations that need AKDE and those for which a standard KDE is appropriate, because when there is no autocorrelation, AKDE returns the same result as KDE.
As animal tracking technology improves and relocation data sets continue to increase in sampling frequency, both the highly autocorrelated nature of movement data and the need for techniques that can leverage autocorrelation will become more apparent. While our AKDE is asymptotically consistent and has an asymptotically optimal order of error as a nonparametric estimator, there is a vast program of conventional KDE research focused on important statistical goals such as reducing the proportionality constant of the asymptotic error's leading‐order term, reducing bias (Silverman 1986, Izenman 1991, Turlach 1993) and correcting for hard boundaries (Silverman 1986). Undoubtedly, some of these techniques could be translated to AKDE. Even in its current form, however, AKDE provides a rigorous and flexible solution for estimating animal space use from autocorrelated movement data. Finally, future parametric estimators derived from consideration of the biological mechanisms governing space use, such as MHRA (Appendix A: A.2), but developed for autocorrelated data have the potential for even more statistical efficiency. The advantage of nonparametric estimators like AKDE lies in their broader applicability and lack of requirement for a detailed understanding of the focal species.
Acknowledgments
The project was funded by the U.S. National Science Foundation ABI 1062411. T. Mueller was funded by the Robert Bosch Foundation. C. H. Fleming was funded by a Smithsonian Institution postdoctoral fellowship.
Appendix
Ecological Archives
Appendices A–C are available online: http://dx.doi.org/10.1890/14‐2010.1.sm
Literature Cited
Citing Literature
Number of times cited according to CrossRef: 88
- Sam Khosravifard, Andrew K. Skidmore, Babak Naimi, Valentijn Venus, Antonio R. Muñoz, Albertus G. Toxopeus, Identifying Birds' Collision Risk with Wind Turbines Using a Multidimensional Utilization Distribution Method, Wildlife Society Bulletin, 10.1002/wsb.1056, 44, 1, (191-199), (2020).
- Vincent N. Naude, Guy A. Balme, Justin O'Riain, Luke T.B. Hunter, Julien Fattebert, Tristan Dickerson, Jacqueline M. Bishop, Unsustainable anthropogenic mortality disrupts natal dispersal and promotes inbreeding in leopards, Ecology and Evolution, 10.1002/ece3.6089, 10, 8, (3605-3619), (2020).
- A Schlaff, P Menéndez, M Hall, M Heupel, T Armstrong, C Motti, Acoustic tracking of a large predatory marine gastropod, Charonia tritonis, on the Great Barrier Reef, Marine Ecology Progress Series, 10.3354/meps13291, 642, (147-161), (2020).
- Ricardo Martinez-Garcia, Christen H. Fleming, Ralf Seppelt, William F. Fagan, Justin M. Calabrese, How range residency and long-range perception change encounter rates, Journal of Theoretical Biology, 10.1016/j.jtbi.2020.110267, (110267), (2020).
- Albert Peris, Francesc Closa, Ignasi Marco, Pelayo Acevedo, Jose A Barasona, Encarna Casas-Díaz, Towards the comparison of home range estimators obtained from contrasting tracking regimes: the wild boar as a case study, European Journal of Wildlife Research, 10.1007/s10344-020-1370-7, 66, 2, (2020).
- Natalie V. Klinard, Jordan K. Matley, Edmund A. Halfyard, Michael Connerton, Timothy B. Johnson, Aaron T. Fisk, Post‐stocking movement and survival of hatchery‐reared bloater (Coregonus hoyi) reintroduced to Lake Ontario, Freshwater Biology, 10.1111/fwb.13491, 65, 6, (1073-1085), (2020).
- OE Osborne, PD O’Hara, S Whelan, P Zandbergen, SA Hatch, KH Elliott, Breeding seabirds increase foraging range in response to an extreme marine heatwave, Marine Ecology Progress Series, 10.3354/meps13392, 646, (161-173), (2020).
- Edwin J. PARKER, Russell A. HILL, Andrew T. L. ALLAN, Caroline HOWLETT, Nicola F. KOYAMA, Influence of food availability, plant productivity, and indigenous forest use on ranging behavior of the endangered samango monkey (Cercopithecus albogularis schwarzi), in the Soutpansberg Mountains, South Africa, Integrative Zoology, 10.1111/1749-4877.12438, 15, 5, (385-400), (2020).
- Michael J. Noonan, Christen H. Fleming, Marlee A. Tucker, Roland Kays, Autumn‐Lynn Harrison, Margaret C. Crofoot, Briana Abrahms, Susan C. Alberts, Abdullahi H. Ali, Jeanne Altmann, Pamela Castro Antunes, Nina Attias, Jerrold L. Belant, Dean E. Beyer, Laura R. Bidner, Niels Blaum, Randall B. Boone, Damien Caillaud, Rogerio Cunha Paula, J. Antonio la Torre, Jasja Dekker, Christopher S. DePerno, Mohammad Farhadinia, Julian Fennessy, Claudia Fichtel, Christina Fischer, Adam Ford, Jacob R. Goheen, Rasmus W. Havmøller, Ben T. Hirsch, Cindy Hurtado, Lynne A. Isbell, René Janssen, Florian Jeltsch, Petra Kaczensky, Yayoi Kaneko, Peter Kappeler, Anjan Katna, Matthew Kauffman, Flavia Koch, Abhijeet Kulkarni, Scott LaPoint, Peter Leimgruber, David W. Macdonald, A. Catherine Markham, Laura McMahon, Katherine Mertes, Christopher E. Moorman, Ronaldo G. Morato, Alexander M. Moßbrucker, Guilherme Mourão, David O'Connor, Luiz Gustavo R. Oliveira‐Santos, Jennifer Pastorini, Bruce D. Patterson, Janet Rachlow, Dustin H. Ranglack, Neil Reid, David M. Scantlebury, Dawn M. Scott, Nuria Selva, Agnieszka Sergiel, Melissa Songer, Nucharin Songsasen, Jared A. Stabach, Jenna Stacy‐Dawes, Morgan B. Swingen, Jeffrey J. Thompson, Wiebke Ullmann, Abi Tamim Vanak, Maria Thaker, John W. Wilson, Koji Yamazaki, Richard W. Yarnell, Filip Zieba, Tomasz Zwijacz‐Kozica, William F. Fagan, Thomas Mueller, Justin M. Calabrese, Effects of body size on estimation of mammalian area requirements, Conservation Biology, 10.1111/cobi.13495, 34, 4, (1017-1028), (2020).
- Dilek Tezel, Saban Inam, Sultan Kocaman, GIS-Based Assessment of Habitat Networks for Conservation Planning in Kas-Kekova Protected Area (Turkey), ISPRS International Journal of Geo-Information, 10.3390/ijgi9020091, 9, 2, (91), (2020).
- Lucía L. Tórrez-Herrera, Grace H. Davis, Margaret C. Crofoot, Do Monkeys Avoid Areas of Home Range Overlap Because They Are Dangerous? A Test of the Risk Hypothesis in White-Faced Capuchin Monkeys (Cebus capucinus), International Journal of Primatology, 10.1007/s10764-019-00110-0, (2020).
- David C. McNitt, Robert S. Alonso, Michael J. Cherry, Michael L. Fies, Marcella J. Kelly, Sex-specific effects of reproductive season on bobcat space use, movement, and resource selection in the Appalachian Mountains of Virginia, PLOS ONE, 10.1371/journal.pone.0225355, 15, 8, (e0225355), (2020).
- Cindy M. Hurtado, Harald Beck, Paporn Thebpanya, Mariana Altrichter, Spatial patterns of the first groups of collared peccaries (Pecari tajacu) reintroduced in South America, Tropical Ecology, 10.1007/s42965-020-00099-1, (2020).
- Gary J. Roloff, Bradford R. Silet, Steven M. Gray, John M. Humphreys, Eric M. Clark, Resource use by marten at fine spatial extents, Mammal Research, 10.1007/s13364-020-00525-8, (2020).
- Machawe I Maphalala, Ara Monadjem, Keith L Bildstein, Shane McPherson, Ben Hoffman, Colleen T Downs, Ranging behaviour of Long-crested Eagles Lophaetus occipitalis in human-modified landscapes of KwaZulu-Natal, South Africa , Ostrich, 10.2989/00306525.2020.1770888, (1-7), (2020).
- A. Baíllo, J. E. Chacón, A new selection criterion for statistical home range estimation, Journal of Applied Statistics, 10.1080/02664763.2020.1822302, (1-16), (2020).
- James Grogan, Andrew Plumptre, Joshua Mabonga, Simon Nampindo, Mustapha Nsubuga, Andrew Balmford, Ranging behaviour of Uganda’s elephants, African Journal of Ecology, 10.1111/aje.12643, 58, 1, (2-13), (2019).
- Mohammad S. Farhadinia, David R. Heit, Robert A. Montgomery, Paul J. Johnson, Kaveh Hobeali, Luke T. B. Hunter, David W. Macdonald, Vertical relief facilitates spatial segregation of a high density large carnivore population, Oikos, 10.1111/oik.06724, 129, 3, (346-355), (2019).
- Rocío Joo, Matthew E. Boone, Thomas A. Clay, Samantha C. Patrick, Susana Clusella‐Trullas, Mathieu Basille, Navigating through the r packages for movement, Journal of Animal Ecology, 10.1111/1365-2656.13116, 89, 1, (248-267), (2019).
- Jannis Gottwald, Ralf Zeidler, Nicolas Friess, Marvin Ludwig, Christoph Reudenbach, Thomas Nauss, Introduction of an automatic and open‐source radio‐tracking system for small animals, Methods in Ecology and Evolution, 10.1111/2041-210X.13294, 10, 12, (2163-2172), (2019).
- Josse Rühmann, Manuel Soler, Tomás Pérez-Contreras, Juan Diego Ibáñez-Álamo, Territoriality and variation in home range size through the entire annual range of migratory great spotted cuckoos (Clamator glandarius), Scientific Reports, 10.1038/s41598-019-41943-2, 9, 1, (2019).
- Andrea Campos‐Candela, Miquel Palmer, Salvador Balle, Josep Alós, Response to Abolaffio et al. (2019): Avoiding misleading messages, Journal of Animal Ecology, 10.1111/1365-2656.13084, 88, 12, (2017-2021), (2019).
- Ulrike E. Schlägel, Johannes Signer, Antje Herde, Sophie Eden, Florian Jeltsch, Jana A. Eccard, Melanie Dammhahn, Estimating interactions between individuals from concurrent animal movements, Methods in Ecology and Evolution, 10.1111/2041-210X.13235, 10, 8, (1234-1245), (2019).
- Théo Michelot, Pierre Gloaguen, Paul G. Blackwell, Marie‐Pierre Étienne, The Langevin diffusion as a continuous‐time model of animal movement and habitat selection, Methods in Ecology and Evolution, 10.1111/2041-210X.13275, 10, 11, (1894-1907), (2019).
- Guillaume Péron, The time frame of home‐range studies: from function to utilization, Biological Reviews, 10.1111/brv.12545, 94, 6, (1974-1982), (2019).
- Aimee L. Hoover, Dong Liang, Joanna Alfaro‐Shigueto, Jeffrey C. Mangel, Peter I. Miller, Stephen J. Morreale, Helen Bailey, George L. Shillinger, Predicting residence time using a continuous‐time discrete‐space model of leatherback turtle satellite telemetry data, Ecosphere, 10.1002/ecs2.2644, 10, 3, (2019).
- Michael J. Noonan, Marlee A. Tucker, Christen H. Fleming, Thomas S. Akre, Susan C. Alberts, Abdullahi H. Ali, Jeanne Altmann, Pamela Castro Antunes, Jerrold L. Belant, Dean Beyer, Niels Blaum, Katrin Böhning‐Gaese, Laury Cullen, Rogerio Cunha Paula, Jasja Dekker, Jonathan Drescher‐Lehman, Nina Farwig, Claudia Fichtel, Christina Fischer, Adam T. Ford, Jacob R. Goheen, René Janssen, Florian Jeltsch, Matthew Kauffman, Peter M. Kappeler, Flávia Koch, Scott LaPoint, A. Catherine Markham, Emilia Patricia Medici, Ronaldo G. Morato, Ran Nathan, Luiz Gustavo R. Oliveira‐Santos, Kirk A. Olson, Bruce D. Patterson, Agustin Paviolo, Emiliano Esterci Ramalho, Sascha Rösner, Dana G. Schabo, Nuria Selva, Agnieszka Sergiel, Marina Xavier da Silva, Orr Spiegel, Peter Thompson, Wiebke Ullmann, Filip Zięba, Tomasz Zwijacz‐Kozica, William F. Fagan, Thomas Mueller, Justin M. Calabrese, A comprehensive analysis of autocorrelation and bias in home range estimation, Ecological Monographs, 10.1002/ecm.1344, 89, 2, (2019).
- Jonathan M. Keith, Daniel Spring, Tom Kompas, Delimiting a species’ geographic range using posterior sampling and computational geometry, Scientific Reports, 10.1038/s41598-019-45318-5, 9, 1, (2019).
- Guillaume Péron, Modified home range kernel density estimators that take environmental interactions into account, Movement Ecology, 10.1186/s40462-019-0161-9, 7, 1, (2019).
- Ninon F. V. Meyer, Ricardo Moreno, Miguel Angel Martínez-Morales, Rafael Reyna-Hurtado, Spatial Ecology of a Large and Endangered Tropical Mammal: The White-Lipped Peccary in Darién, Panama, Movement Ecology of Neotropical Forest Mammals, 10.1007/978-3-030-03463-4, (77-93), (2019).
- Cécile Richard-Hansen, Rachel Berzins, Matthis Petit, Ondine Rux, Bertrand Goguillon, Luc Clément, Movements of White-Lipped Peccary in French Guiana, Movement Ecology of Neotropical Forest Mammals, 10.1007/978-3-030-03463-4, (57-75), (2019).
- José Fernando Moreira-Ramírez, Rafael Reyna-Hurtado, Mircea Hidalgo-Mihart, Eduardo J. Naranjo, Milton C. Ribeiro, Rony García-Anleu, Roan McNab, Jeremy Radachowsky, Melvin Mérida, Marcos Briceño-Méndez, Gabriela Ponce-Santizo, White-Lipped Peccary Home-Range Size in the Maya Forest of Guatemala and México, Movement Ecology of Neotropical Forest Mammals, 10.1007/978-3-030-03463-4, (21-37), (2019).
- Melissa Songer, Wildlife Ecology, Encyclopedia of Ecology, 10.1016/B978-0-12-409548-9.11177-7, (509-516), (2019).
- Wade A. Ryberg, Timothy B. Garrett, Connor S. Adams, Tyler A. Campbell, Danielle K. Walkup, Timothy E. Johnson, Toby J. Hibbitts, Life in the thornscrub: movement, home range, and territoriality of the reticulate collared lizard ( Crotaphytus reticulatus ) , Journal of Natural History, 10.1080/00222933.2019.1668491, 53, 27-28, (1707-1719), (2019).
- Jonathan R. Potts, Mark A. Lewis, Spatial Memory and Taxis-Driven Pattern Formation in Model Ecosystems, Bulletin of Mathematical Biology, 10.1007/s11538-019-00626-9, 81, 7, (2725-2747), (2019).
- Indrani Sasmal, Nicholas P. Gould, Krysten L. Schuler, Yung-Fu Chang, Anil Thachil, Jennifer Strules, Colleen Olfenbuttel, Shubham Datta, Christopher S. DePerno, LEPTOSPIROSIS IN URBAN AND SUBURBAN AMERICAN BLACK BEARS ( URSUS AMERICANUS ) IN WESTERN NORTH CAROLINA, USA , Journal of Wildlife Diseases, 10.7589/2017-10-263, 55, 1, (74-83), (2019).
- P. Palencia, J. Vicente, P. Barroso, J.Á. Barasona, R. C. Soriguer, P. Acevedo, Estimating day range from camera‐trap data: the animals’ behaviour as a key parameter, Journal of Zoology, 10.1111/jzo.12710, 309, 3, (182-190), (2019).
- Fabiola Iannarilli, Todd W. Arnold, John Erb, John R. Fieberg, Using lorelograms to measure and model correlation in binary data: Applications to ecological studies, Methods in Ecology and Evolution, 10.1111/2041-210X.13308, 10, 12, (2153-2162), (2019).
- LP Griffin, JT Finn, C Diez, AJ Danylchuk, Movements, connectivity, and space use of immature green turtles within coastal habitats of the Culebra Archipelago, Puerto Rico: implications for conservation, Endangered Species Research, 10.3354/esr00976, 40, (75-90), (2019).
- Hiroaki Ishii, Koji Yamazaki, Michael J. Noonan, Christina D. Buesching, Chris Newman, Yayoi Kaneko, Testing cellular phone-enhanced GPS tracking technology for urban carnivores, Animal Biotelemetry, 10.1186/s40317-019-0180-8, 7, 1, (2019).
- H. N. Abernathy, D. A. Crawford, E. P. Garrison, R. B. Chandler, M. L. Conner, K. V. Miller, M. J. Cherry, Deer movement and resource selection during Hurricane Irma: implications for extreme climatic events and wildlife, Proceedings of the Royal Society B: Biological Sciences, 10.1098/rspb.2019.2230, 286, 1916, (20192230), (2019).
- J. K. Matley, S. Eanes, R. S. Nemeth, P. D. Jobsis, Vulnerability of sea turtles and fishes in response to two catastrophic Caribbean hurricanes, Irma and Maria, Scientific Reports, 10.1038/s41598-019-50523-3, 9, 1, (2019).
- undefined Guo, undefined Du, undefined Ma, undefined Huo, undefined Peng, A Model for Animal Home Range Estimation Based on the Active Learning Method, ISPRS International Journal of Geo-Information, 10.3390/ijgi8110490, 8, 11, (490), (2019).
- Katherine Mertes, Jared A. Stabach, Melissa Songer, Tim Wacher, John Newby, Justin Chuven, Shaikha Al Dhaheri, Peter Leimgruber, Steven Monfort, Management Background and Release Conditions Structure Post-release Movements in Reintroduced Ungulates, Frontiers in Ecology and Evolution, 10.3389/fevo.2019.00470, 7, (2019).
- A L J Desbiez, D Kluyber, G F Massocato, L G R Oliveira-Santos, N Attias, Spatial ecology of the giant armadillo Priodontes maximus in Midwestern Brazil, Journal of Mammalogy, 10.1093/jmammal/gyz172, (2019).
- Lucy J. Mitchell, Piran C. L. White, Kathryn E. Arnold, The trade-off between fix rate and tracking duration on estimates of home range size and habitat selection for small vertebrates, PLOS ONE, 10.1371/journal.pone.0219357, 14, 7, (e0219357), (2019).
- Roy T. McBride, Jeffrey J. Thompson, Spatial ecology of Paraguay’s last remaining Atlantic forest Jaguars ( Panthera onca ): implications for their long-term survival , Biodiversity, 10.1080/14888386.2019.1590237, (1-7), (2019).
- Jehyeok Rew, Sungwoo Park, Yongjang Cho, Seungwon Jung, Eenjun Hwang, Animal Movement Prediction Based on Predictive Recurrent Neural Network, Sensors, 10.3390/s19204411, 19, 20, (4411), (2019).
- Jed A. Long, Estimating wildlife utilization distributions using randomized shortest paths, Landscape Ecology, 10.1007/s10980-019-00883-y, (2019).
- WILLIAM GOULDING, PATRICK T. MOSS, CLIVE A. MCALPINE, An assessment of the Tagula Honeyeater Microptilotis vicina, a Data Deficient bird species in a Melanesian endemic hotspot, Bird Conservation International, 10.1017/S095927091900025X, (1-20), (2019).
- Farid Cheraghi, Mahmoud Reza Delavar, Farshad Amiraslani, Kazem Alavipanah, Eliezer Gurarie, Houman Jowkar, Luke Hunter, Stephane Ostrowski, William F. Fagan, Inter-dependent movements of Asiatic Cheetahs Acinonyx jubatus venaticus and a Persian Leopard Panthera pardus saxicolor in a desert environment in Iran (Mammalia: Felidae) , Zoology in the Middle East, 10.1080/09397140.2019.1632538, (1-10), (2019).
- Gretchen H. Roffler, David P. Gregovich, Wolf space use during denning season on Prince of Wales Island, Alaska, Wildlife Biology, 10.2981/wlb.00468, 2018, 1, (wlb.00468), (2018).
- Kevin Winner, Michael J. Noonan, Christen H. Fleming, Kirk A. Olson, Thomas Mueller, Daniel Sheldon, Justin M. Calabrese, Statistical inference for home range overlap, Methods in Ecology and Evolution, 10.1111/2041-210X.13027, 9, 7, (1679-1691), (2018).
- C. H. Fleming, D. Sheldon, W. F. Fagan, P. Leimgruber, T. Mueller, D. Nandintsetseg, M. J. Noonan, K. A. Olson, E. Setyawan, A. Sianipar, J. M. Calabrese, Correcting for missing and irregular data in home‐range estimation, Ecological Applications, 10.1002/eap.1704, 28, 4, (1003-1010), (2018).
- Michael E. Byrne, Sarah C. Webster, Stacey L. Lance, Cara N. Love, Thomas G. Hinton, Dmitry Shamovich, James C. Beasley, Evidence of long-distance dispersal of a gray wolf from the Chernobyl Exclusion Zone, European Journal of Wildlife Research, 10.1007/s10344-018-1201-2, 64, 4, (2018).
- Lauri Liukkonen, Daniel Ayllón, Mervi Kunnasranta, Marja Niemi, Jacob Nabe-Nielsen, Volker Grimm, Anna-Maija Nyman, Modelling movements of Saimaa ringed seals using an individual-based approach, Ecological Modelling, 10.1016/j.ecolmodel.2017.12.002, 368, (321-335), (2018).
- Roy T. McBride, Jeffrey J. Thompson, Space use and movement of jaguar (Panthera onca) in western Paraguay, Mammalia, 10.1515/mammalia-2017-0040, 82, 6, (540-549), (2018).
- R.G. Morato, G.M. Connette, J.A. Stabach, R.C. De Paula, K.M.P.M. Ferraz, D.L.Z. Kantek, S.S. Miyazaki, T.D.C. Pereira, L.C. Silva, A. Paviolo, C. De Angelo, M.S. Di Bitetti, P. Cruz, F. Lima, L. Cullen, D.A. Sana, E.E. Ramalho, M.M. Carvalho, M.X. da Silva, M.D.F. Moraes, A. Vogliotti, J.A. May, M. Haberfeld, L. Rampim, L. Sartorello, G.R. Araujo, G. Wittemyer, M.C. Ribeiro, P. Leimgruber, Resource selection in an apex predator and variation in response to local landscape characteristics, Biological Conservation, 10.1016/j.biocon.2018.10.022, 228, (233-240), (2018).
- Samukelisiwe P. Ngcobo, Amy-Leigh Wilson, Colleen T. Downs, Home ranges of Cape porcupines on farmlands, peri-urban and suburban areas in KwaZulu-Natal, South Africa, Mammalian Biology, 10.1016/j.mambio.2018.10.006, (2018).
- MV Winton, G Fay, HL Haas, M Arendt, S Barco, MC James, C Sasso, R Smolowitz, Estimating the distribution and relative density of satellite-tagged loggerhead sea turtles using geostatistical mixed effects models, Marine Ecology Progress Series, 10.3354/meps12396, 586, (217-232), (2018).
- Jiachen Yang, Jiabao Wen, Bin Jiang, Zhihan Lv, Arun Kumar Sangaiah, Marine depth mapping algorithm based on the edge computing in Internet of things, Journal of Parallel and Distributed Computing, 10.1016/j.jpdc.2017.12.016, 114, (95-103), (2018).
- Orr Spiegel, Shay O’Farrell, Spatial Orientation and Time: Methods, Reference Module in Life Sciences, 10.1016/B978-0-12-809633-8.90090-6, (2018).
- Anne K. Scharf, Jerrold L. Belant, Dean E. Beyer, Martin Wikelski, Kamran Safi, Habitat suitability does not capture the essence of animal-defined corridors, Movement Ecology, 10.1186/s40462-018-0136-2, 6, 1, (2018).
- Shifra Z. Goldenberg, Iain Douglas-Hamilton, George Wittemyer, Inter-generational change in African elephant range use is associated with poaching risk, primary productivity and adult mortality, Proceedings of the Royal Society B: Biological Sciences, 10.1098/rspb.2018.0286, 285, 1879, (20180286), (2018).
- Robert E. Kenward, Eduardo M. Arraut, Peter A. Robertson, Sean S. Walls, Nicholas M. Casey, Nicholas J. Aebischer, Resource-Area-Dependence Analysis: Inferring animal resource needs from home-range and mapping data, PLOS ONE, 10.1371/journal.pone.0206354, 13, 10, (e0206354), (2018).
- Samantha M. Binion-Rock, Brian J. Reich, Jeffrey A. Buckel, A spatial kernel density method to estimate the diet composition of fish, Canadian Journal of Fisheries and Aquatic Sciences, 10.1139/cjfas-2017-0306, (1-19), (2018).
- Inês Silva, Matthew Crane, Pongthep Suwanwaree, Colin Strine, Matt Goode, Using dynamic Brownian Bridge Movement Models to identify home range size and movement patterns in king cobras, PLOS ONE, 10.1371/journal.pone.0203449, 13, 9, (e0203449), (2018).
- Mohammad S. Farhadinia, Paul J. Johnson, David W. Macdonald, Luke T. B. Hunter, Anchoring and adjusting amidst humans: Ranging behavior of Persian leopards along the Iran-Turkmenistan borderland, PLOS ONE, 10.1371/journal.pone.0196602, 13, 5, (e0196602), (2018).
- Oswald J. Schmitz, Jennifer R. B. Miller, Anne M. Trainor, Briana Abrahms, Toward a community ecology of landscapes: predicting multiple predator–prey interactions across geographic space, Ecology, 10.1002/ecy.1916, 98, 9, (2281-2292), (2017).
- Guillaume Péron, Christen H. Fleming, Rogerio C. Paula, Numi Mitchell, Michael Strohbach, Peter Leimgruber, Justin M. Calabrese, Periodic continuous‐time movement models uncover behavioral changes of wild canids along anthropization gradients, Ecological Monographs, 10.1002/ecm.1260, 87, 3, (442-456), (2017).
- Eric R. Dougherty, Colin J. Carlson, Jason K. Blackburn, Wayne M. Getz, A cross-validation-based approach for delimiting reliable home range estimates, Movement Ecology, 10.1186/s40462-017-0110-4, 5, 1, (2017).
- Katie M. Moriarty, Mark A. Linnell, Brandon E. Chasco, Clinton W. Epps, William J. Zielinski, Using high-resolution short-term location data to describe territoriality in Pacific martens, Journal of Mammalogy, 10.1093/jmammal/gyx014, 98, 3, (679-689), (2017).
- Shannon L. Kay, Justin W. Fischer, Andrew J. Monaghan, James C. Beasley, Raoul Boughton, Tyler A. Campbell, Susan M. Cooper, Stephen S. Ditchkoff, Steve B. Hartley, John C. Kilgo, Samantha M. Wisely, A. Christy Wyckoff, Kurt C. VerCauteren, Kim M. Pepin, Quantifying drivers of wild pig movement across multiple spatial and temporal scales, Movement Ecology, 10.1186/s40462-017-0105-1, 5, 1, (2017).
- Mevin B. Hooten, Devin S. Johnson, Brett T. McClintock, Juan M. Morales, References, Animal Movement, 10.1201/9781315117744, (273-290), (2017).
- Christen H. Fleming, Daniel Sheldon, Eliezer Gurarie, William F. Fagan, Scott LaPoint, Justin M. Calabrese, Kálmán filters for continuous-time movement models, Ecological Informatics, 10.1016/j.ecoinf.2017.04.008, 40, (8-21), (2017).
- Johannes Signer, John Fieberg, Tal Avgar, Estimating utilization distributions from fitted step‐selection functions, Ecosphere, 10.1002/ecs2.1771, 8, 4, (2017).
- Christen H. Fleming, Justin M. Calabrese, A new kernel density estimator for accurate home‐range and species‐range area estimation, Methods in Ecology and Evolution, 10.1111/2041-210X.12673, 8, 5, (571-579), (2016).
- Bart Kranstauber, Marco Smolla, Kamran Safi, Similarity in spatial utilization distributions measured by the earth mover's distance, Methods in Ecology and Evolution, 10.1111/2041-210X.12649, 8, 2, (155-160), (2016).
- Dominic A. W. Henry, Judith M. Ament, Graeme S. Cumming, Exploring the environmental drivers of waterfowl movement in arid landscapes using first-passage time analysis, Movement Ecology, 10.1186/s40462-016-0073-x, 4, 1, (2016).
- Guillaume Péron, Chris H. Fleming, Rogerio C. de Paula, Justin M. Calabrese, Uncovering periodic patterns of space use in animal tracking data with periodograms, including a new algorithm for the Lomb-Scargle periodogram and improved randomization tests, Movement Ecology, 10.1186/s40462-016-0084-7, 4, 1, (2016).
- Guillaume Bastille-Rousseau, Jonathan R. Potts, Charles B. Yackulic, Jacqueline L. Frair, E. Hance Ellington, Stephen Blake, Flexible characterization of animal movement pattern using net squared displacement and a latent state model, Movement Ecology, 10.1186/s40462-016-0080-y, 4, 1, (2016).
- Justin M. Calabrese, Chris H. Fleming, Eliezer Gurarie, ctmm: an r package for analyzing animal relocation data as a continuous‐time stochastic process, Methods in Ecology and Evolution, 10.1111/2041-210X.12559, 7, 9, (1124-1132), (2016).
- C. H. Fleming, W. F. Fagan, T. Mueller, K. A. Olson, P. Leimgruber, J. M. Calabrese, Estimating where and how animals travel: an optimal framework for path reconstruction from autocorrelated tracking data, Ecology, 10.1890/15-1607.1, 97, 3, (576-582), (2016).
- Andrew M. Allen, Navinder J. Singh, Linking Movement Ecology with Wildlife Management and Conservation, Frontiers in Ecology and Evolution, 10.3389/fevo.2015.00155, 3, (2016).
- Ronaldo G. Morato, Jared A. Stabach, Chris H. Fleming, Justin M. Calabrese, Rogério C. De Paula, Kátia M. P. M. Ferraz, Daniel L. Z. Kantek, Selma S. Miyazaki, Thadeu D. C. Pereira, Gediendson R. Araujo, Agustin Paviolo, Carlos De Angelo, Mario S. Di Bitetti, Paula Cruz, Fernando Lima, Laury Cullen, Denis A. Sana, Emiliano E. Ramalho, Marina M. Carvalho, Fábio H. S. Soares, Barbara Zimbres, Marina X. Silva, Marcela D. F. Moraes, Alexandre Vogliotti, Joares A. May, Mario Haberfeld, Lilian Rampim, Leonardo Sartorello, Milton C. Ribeiro, Peter Leimgruber, Space Use and Movement of a Neotropical Top Predator: The Endangered Jaguar, PLOS ONE, 10.1371/journal.pone.0168176, 11, 12, (e0168176), (2016).
- Javan M. Bauder, David R. Breininger, M. Rebecca Bolt, Michael L. Legare, Christopher L. Jenkins, Kevin McGarigal, The role of the bandwidth matrix in influencing kernel home range estimates for snakes using VHF telemetry data, Wildlife Research, 10.1071/WR14233, 42, 5, (437), (2015).
- Sarah E. Gutowsky, Marty L. Leonard, Melinda G. Conners, Scott A. Shaffer, Ian D. Jonsen, Individual-level Variation and Higher-level Interpretations of Space Use in Wide-ranging Species: An Albatross Case Study of Sampling Effects, Frontiers in Marine Science, 10.3389/fmars.2015.00093, 2, (2015).
- Natasha Ellison, Ben J. Hatchwell, Sarah J. Biddiscombe, Clare J. Napper, Jonathan R. Potts, Mechanistic home range analysis reveals drivers of space use patterns for a non‐territorial passerine, Journal of Animal Ecology, 10.1111/1365-2656.13292, 0, 0, (undefined).





