Recently developed low-cost Global Positioning System (GPS) data loggers are promising tools for wildlife research because of their affordability for low-budget projects and ability to simultaneously track a greater number of individuals compared with expensive built-in wildlife GPS. However, the reliability of these devices must be carefully examined because they were not developed to track wildlife. This study aimed to assess the performance and accuracy of commercially available GPS data loggers for the first time using the same methods applied to test built-in wildlife GPS. The effects of antenna position, fix interval and habitat on the fix-success rate (FSR) and location error (LE) of CatLog data loggers were investigated in stationary tests, whereas the effects of animal movements on these errors were investigated in motion tests. The units operated well and presented consistent performance and accuracy over time in stationary tests, and the FSR was good for all antenna positions and fix intervals. However, the LE was affected by the GPS antenna and fix interval. Furthermore, completely or partially obstructed habitats reduced the FSR by up to 80% in households and increased the LE. Movement across habitats had no effect on the FSR, whereas forest habitat influenced the LE. Finally, the mean FSR (0.90 ± 0.26) and LE (15.4 ± 10.1 m) values from low-cost GPS data loggers were comparable to those of built-in wildlife GPS collars (71.6% of fixes with LE < 10 m for motion tests), thus confirming their suitability for use in wildlife studies.
Citation: Forin-Wiart M-A, Hubert P, Sirguey P, Poulle M-L (2015) Performance and Accuracy of Lightweight and Low-Cost GPS Data Loggers According to Antenna Positions, Fix Intervals, Habitats and Animal Movements. PLoS ONE 10(6): e0129271. https://doi.org/10.1371/journal.pone.0129271
Academic Editor: Cédric Sueur, Institut Pluridisciplinaire Hubert Curien, FRANCE
Received: September 17, 2014; Accepted: May 6, 2015; Published: June 18, 2015
Copyright: © 2015 Forin-Wiart et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited
Data Availability: All of the data are available from the Dryad repository (doi:10.5061/dryad.7nm7b).
Funding: This work was supported by an operating grant from the Région Champagne-Ardenne. MAFW was funded by a PhD grant from the Conseil Régional de Champagne-Ardenne (grant number D201011937, https://www.cr-champagne-ardenne.fr/) and the Conseil Général des Ardennes (www.cg08.fr/). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Global positioning system (GPS) devices have improved the availability and accuracy of animal-relocation field studies and greatly enhanced wildlife research [1,2]. GPS provides large amounts of animal location data over short sampling intervals and large spatial scales, and the data are available day and night for various weather and terrain conditions [3,4,5]. Because of recent technological advances, GPS devices are now deployed to track large animals, such as the African elephant Loxodonta africana , fur seal Callorhinus ursinus  and white-tailed deer Odocoileus virginianus , and medium- and small-sized vertebrates, such as the European badger Meles meles , domestic cat Felis catus [10,11,12,13], common brushtail possum Trichosurus vulpecula , otter Lutra lutra , European hedgehog Erinaceus europaeus  and feral pigeon Columbia livia .
However, several constraints are associated with the use of built-in wildlife GPS receivers to monitor animals , particularly the financial costs of receivers (US $1000–2000 per unit), which limits their use and ability to provide conclusive inferences on population processes and behaviors [19,20]. However, to meet consumers increasing demand concerning location-aware technologies, GPS devices have now been adapted for everyday use, such as travel, sports or domestic pet tracking . These lightweight, commercially available GPS tracking devices rely on similar hardware to those used for built-in wildlife tracking with the advantage of being more affordable (e.g., US $50 for data loggers, such as Catnip GPS CatLog or Mobile Action i-gotU GT-120, and US $300 for a data transmitter, such as Garmin Astro 320 Dog Tracking GPS). However, the performance and accuracy of these low-cost GPS data loggers must be carefully assessed because these devices were not specifically developed to track wildlife and may be inappropriate for such use or less reliable than built-in wildlife GPS.
The accuracy of large or lightweight GPS built-in wildlife tracking systems is generally considered to range from less than 5 m to 30 m [21,22], and positions can be determined repeatedly across a broader range of sampling intervals [3,5]. However, location failures over a pre-defined time schedule and/or abnormally high measurement errors of up to several kilometers can occur with contemporary GPS receivers [4,23,24]. A low fix-success rate (FSR) and high location errors (LEs) can lead to habitat misclassifications in studies on resource selection because differential rates of data loss among habitats could bias the identification of habitats and their importance in fulfilling life-history requirements [20,25]. These errors can also bias estimates of movement paths , and imprecise location information can influence estimates of home-range size and shape . Assessing the effects of various factors on the performance and accuracy of wildlife GPS telemetry systems is essential for understanding the causes of GPS errors, which might be collar-brand dependent [28,29,30], and selecting the appropriate solution to correct errors and ensure that the GPS performance and accuracy meet the study's objectives [16,27]. Various solutions have been proposed for correcting bias produced by missing and/or imprecise locations in ecological analyses (review in , [31,32]). However, all of these solutions require assessments of the performance and accuracy of wildlife GPS under stationary tests [14,30,33,34] and controlled mobile tests [33,35,36] and/or to some extent by using returns from GPS devices mounted on free-ranging animals (i.e., data obtained by device retrieval or through remote transmission) [9,37,38].
Low-cost GPS data loggers have been deployed to study the post-release of hand-reared Irish hare Lepus timidus hibernicus , map sea behaviors of pelagic seabirds  and ranging behaviors of domestic cats F. catus in an urban environment , or quantify fine-scale movements of goats, sheep and dogs . Two studies have evaluated GPS data logger spatial accuracy for tracking human movements by estimating point and line errors in an urban environment [43,44]. Another study used returns from GPS devices mounted on free-ranging Mountain brushtail possum Trichosurus cunninghami to consider GPS data logger performance . However, the factors that can affect the performance and accuracy of low-cost and lightweight GPS data loggers for wildlife telemetry survey have not been assessed to date using stationary and motion controlled tests, and the same methods employed to test built-in wildlife GPS.
In stationary and motion controlled tests, GPS data logger errors are evaluated using indices that reflect the i) device performance in terms of the FSR according to the proportion of successful GPS scheduled attempts that resulted in successful location acquisition and ii) device accuracy in terms of the LE according to the Euclidean distance between GPS-estimated locations and “true positions”. Such errors are more likely to be obtained under specific environmental conditions and related to certain animal-related behaviors and technological factors that can spatially and temporally disturb signal transmission from satellites to receivers.
Typically, a greater number of satellite signals results in higher GPS receiver positioning performance and accuracy. However, the number of satellites available at any given time can be affected by physical obstructions between the receiver and satellites. The FSR and LE are largely influenced by environmental factors such as canopy closure [22,24,25,46] and topography [28,33,36], which can be approximated by sky availability and measures the quantity of visible sky from a given point. Furthermore, antenna positions < 45° from horizontal also affect the FSR [23,47] and LE [23,36] of GPS receivers, and technological factors such as the fix interval (i.e., frequency at which locations are collected) may also influence the FSR because of possible changes in satellite configurations over data acquisition intervals. Short fix intervals are generally associated with high FSR values without affecting the LE . In addition, an increase in the fix interval affects the receiver's ability to determine locations in a timely manner (e.g., a 60-min interval requires a longer fix acquisition time than a 10-min interval) . Furthermore, the duration of deployment may affect the FSR and LE values, although reference data on battery power are not presently available.
Aside from two studies that investigated lightweight built-in wildlife GPS collar performance and accuracy within urban  and suburban  environments, most of the research on GPS receivers has been performed in natural environments [8,25,34,38,48,49], which limits the ability to perform inferences on human-impacted landscapes used by medium-sized wild terrestrial species, such as the urban coyote Canis latrans , red fox Vulpes vulpes , raccoon Procyon lotor , ground squirrel Spermophilus citellus , and hedgehog E. europaeus .
The aim of this study was to investigate the performance and accuracy of lightweight and low-cost GPS data loggers in a rural environment to evaluate their suitability for wildlife research projects. Our objectives were therefore to 1) evaluate the consistency of same-brand commercially available GPS data loggers according to their duration of deployment; 2) characterize the influence of antenna position, fix interval and habitat on the rate of successful location acquisition and measurement accuracy using a stationary experimental arrangement; and 3) assess the effects on GPS performance and accuracy of motion across habitats by fitting medium-sized leashed mammals with GPS data loggers.
Material and Methods
This research was performed in a rural landscape in northeastern France. The study area was centered on two small villages (less than 200 inhabitants): Boult-aux-Bois (49°25’52”N, 4°50’33”E), which is characterized by a relatively flat topography (166–238 m), and Briquenay (49°24’19”N, 4°52’41”E), which is characterized by a more marked topography (130–258 m). The steepest terrain was located in a 3300-ha forested area (national forest of La Croix-aux-Bois) at the southeast border of the study area, whereas a low-relief landscape was found in the agricultural matrix composed of a mosaic of pastures, cultures, meadows, and groves (12%).
GPS data logger
This study was performed with 40 commercially available GPS CatLog data loggers (22 g, Catnip Technologies Ltd, Hong Kong) suitable for tracking mammals weighing more than 800 g. These USB-rechargeable units consist of a GPS chipset (SiRF III), battery pack (380 mAh) and built-in patch antenna configured to search for satellites from < 38 sec in warm-start conditions (i.e., the receiver remembers its last calculated position but not the satellites that were in view because of changes in the satellite constellation) to < 60 sec in cold-start conditions (i.e., the receiver dumps all of the information because of fix intervals that are too long). The GPS data loggers function from -10°C to +50°C, and the units can store up to 64,000 fixes and can be programmed using an interactive interface with two different GPS sampling programs, including a continuous sampling interval from 1 sec to 60 min or scheduled sampling interval depending on the date and time. A successfully acquired location provides the date and time (Greenwich Mean Time, GMT) of the positional data, latitude, and longitude (based on the World Geodetic System 84). Additional information, including the altitude (m), speed (m/h), and distance from the last fix (m), is also recorded. When the GPS receiver cannot acquire a successful fix, the device does not record data. The data stored in GPS data loggers cannot be broadcast, and the unit must be recovered to retrieve the data via USB. The batteries of the 40 CatLog units were fully charged via USB before their deployment.
Stationary unit tests
A stationary experimental arrangement of GPS units was designed to test the effects of antenna position and fix interval on the fix-success rate (FSR) and location error (LE). Twenty-four GPS data loggers were individually placed on the necks of 1.5-L plastic bottles (S1a Fig) and simultaneously deployed. The bottles were placed on small crossbars 15 cm above the ground and filled with a saline solution to mimic the ground plane of a medium-sized animal body . The GPS bottles were spaced 1.5 m apart in a two-row by three-column grid network, with a grid cell containing four GPS bottles (S1b Fig). This test pattern was placed in an open habitat without topographical or vegetation obstructions to ensure favorable satellite views. Each GPS bottle was placed at a known benchmark with available geodesic coordinates.
The effects of the antenna at up and down positions (± 90° from horizontal) and three fix intervals (5-min interval, program A; 15-min interval, program B; and 1-h interval, program C) on the FSR and LE were simultaneously tested by deploying four GPS bottles for each configuration (S1b Fig). The GPS units remained at each benchmark for a minimum of 145 fix attempts to ensure that program A covered at least one full GPS satellite constellation cycle (approximately 12 h). The four GPS bottles with upward antennas and program B (S1b Fig) were also used to test the FSR and LE consistency of GPS data loggers over time. These four units recorded positions over 40 full cycles.
The influence of habitat on the FSR and LE was tested with 16 GPS bottles, which were simultaneously deployed with open habitat conditions. Four of the GPS bottles were placed in a dense stand closed conifer forest, four were placed in a barn, four were placed in a household, and four were placed just outside of a barn (1 m from a wall) (S1c Fig). Concrete walls and small sky views characterized the household habitat, whereas the barn presented a permeable corrugated roof. These GPS data loggers were deployed with fixed conditions (antenna up and program B) during two complete cycles (i.e., 97 expected fixes). Each GPS bottle was placed at known benchmarks in four habitats with available geodesic coordinates.
Motion controlled tests
Two small dogs (6 kg and 8 kg) each carried one GPS data logger (Fig 1). The receivers were fixed to their collars, and the fix interval of the units was set to one minute. A research participant walked the dogs on a leash along the village streets and forest, meadow and edge paths. Two different routes (path one and two) were walked in similar weather conditions (clear skies and relative humidity of approximately 50%) in and around both villages leading to four trips (trip 1 = path 1, 1st walk, trip 2 = path 2, 1st walk, trip 3 = path 2, 2nd walk, and trip 4 = path 1, 2nd walk). The length of paths varied from 5.2 to 9.6 km with walking durations of 85 to 153 min. The reference paths were simultaneously recorded using a GPS Garmin Map 62s (root mean square (RMS) accuracy = ± 3–5 m) that collected positions at intervals of approximately 7 sec (range = 1–22 sec). This control device was held 1.5 m above the ground by the participant and remained at a constant distance from the dog equipped with the GPS data logger. Trajectories from the Garmin GPS control device were rediscretized in time to the second using linear interpolation to calculate the LE as the Euclidian distance between a CatLog-measured location and Garmin control location collected at the same time (Fig 1).
Locations recorded by the Garmin control device (small dark dot) and two CatLog data loggers (large green and blue dots) with a fix interval set to 1 min along the path centered on Briquenay. Red points represent starting and ending points.
Variations in the accuracy of the position estimates among collars were assessed by the horizontal and vertical errors of the 40 units deployed during the stationary unit tests. The FSR was obtained by dividing the number of successfully acquired locations by the number of scheduled attempts. The mean time of the fix acquisition (μTAF) was calculated by grouping units from each test configuration to understand the GPS performance. The LE was calculated for each positional fix as the Euclidean distance between each of the GPS-measured locations and corresponding ‘true’ reference positions defined as (i) the geodesic coordinates obtained from the Institut National de l’information Géographique et forestière (IGN) or (ii) fixes from a GPS Garmin Map 62s. The LE was determined as follows: where Δx and Δy are the differences between the GPS-measured location and x and y reference positions, respectively.
The RMS of the LE (LERMS), which measured the average location error of a GPS device extracted from a population of n positional fixes, was also calculated for each test configuration and habitat during stationary tests and for each trip and habitat during the motion tests. This measure assists in the selection of buffer sizes around GPS locations when performing habitat-related spatial analyses on free-ranging animals . The LERMS was computed as follows: The arithmetic mean (μLE) and median (mLE) of the location error of n fixes were also calculated for comparisons with previous studies for each test configuration and habitat during the stationary tests and for each trip and habitat during the motion tests. The interquartile range (LEIQR) was computed as an additional measure of LE dispersion (i.e., the precision of each configuration) for each test configuration in open habitat. The outlier LE values that occurred with all of the GPS devices  were identified as data that do not fall within three standard deviations of the mean LE value. The number of outlier values and LERMS values without outliers were also computed for each collar deployed during the stationary unit tests and for each habitat traversed during the motion tests.
Sky availability (Vd) was also computed as a topographic factor. Vd measures the quantity of visible sky from a given point and is computed based on a 25-m digital elevation model (DEM) by determining the horizon angle H(φ) in 64 discrete azimuth angles φ. Vd is then defined as the ratio between the solid angle subtended by the horizon lines and that of the entire upper hemisphere (Ω = 2π, visibility = 1, ). Therefore, sky availability was computed as follows: This measure can be considered a factor for the quality of the fix by quantifying the probability of the presence of a sufficient number of satellites under an appropriate geometry. Vd ranges from 0 for totally obscured sky conditions, such as the bottom of an incised valley, to 1 for an unobstructed horizontal surface. To exclusively assess the effect of the behavioral, technical, and environmental factors on GPS performance and accuracy, the units were deployed at locations that exhibited high sky availability (0.87–1.00) during the stationary unit tests .
The coordinates were projected from both the GPS CatLog devices and Garmin Map 62s to Universal Transverse Mercator (UTM) for analysis. The geographical analyses were performed using ArcGIS 10 (ESRI, Redlands, CA, USA). The model selection approach was based on the Information Theoretic Approach and performed with the Akaike Information Criterion (AIC) following the protocol described by Zuur et al. . The best model was validated by graphic inspection [56,57]. All of the statistical analyses and modeling were performed in the statistical software program R 3.1 , and a value of alpha = 0.05 was used for all tests.
The consistency of GPS data-logger performances was initially assessed by the FSR differences between the collars from the upward antenna and program B test configuration. Significant differences between those units (fUnit) (Table 1) relative to the log-transformed LE values from two full cycles (i.e., 97 possible fixes) were then tested using a one-way analysis of variance (ANOVA). Finally, the proportion of outliers (Nout) and median of the LE values (mLE) from the antenna-up receivers and program B logging over 40 full cycles (fTime, Table 1) were tested using linear and non-linear regressions to determine the consistency of the GPS data loggers over time and assess the potential effect of battery power.
The tendency of the estimated position accuracy to fluctuate among GPS data loggers according to the configuration (Fig 2a) and habitat (Fig 2b) during the stationary unit tests was investigated by descriptive statistics (Fig 2). The FSR was computed for each unit involved in the stationary unit tests (Table 2) and for each track and habitat crossed during controlled motion tests (Tables 3 and 4). For each stationary unit test configuration and successful location fix, we calculated the LE, LERMS with and without outlier values, and proportion of fixes with LE < 10 m (Table 2). These variables were also calculated for each trip walked and habitat crossed during the controlled motion tests (Tables 3 and 4).
Location errors from 39 GPS CatLog data loggers relative to the National Geodetic Survey coordinates obtained of (a) 700–2300 fixes per unit under antenna positions (up or down) and fix intervals (program A, program B or program C) in an open habitat and (b) 250–2300 fixes per unit under different habitats with fixed conditions. Ellipses represent 95% confidence areas and centroids represent the average location error.
When testing antenna positions and fix intervals, all of the measurements were calculated for one complete cycle for program A, three cycles for program B and 12 cycles for program C to attempt 145 fixes. When testing the influence of habitat types, all of the measurements were calculated for two cycles to attempt a minimum of 97 fixes. To manage variations in the logging rates, the FSR accounts for the actual maximum number of fix attempts rather than the anticipated value for each test configuration.
The effects of antenna position (fAntenna) and fix interval (fFix) (Table 1) on the FSR were initially assessed between each test configuration. The influence of the same explanatory variables and interaction between fAntenna and fFix on LE was then modeled through a linear mixed-effects model (LMM, nlme package). The response variable included all of the log-transformed LE values of the fixes for the 24 benchmarks and up to 145 fixes per unit. The variable GPS (fUnit, Table 1) was used as a random term to consider non-independence among the fixes collected by each GPS receiver [14,33]. Thus, five possible models (alternative hypotheses and a constant null model) were compiled (S1 Table). Finally, the effects of the same explanatory variables on the log-transformed LEIQR values were tested using a two-way ANOVA with permutation tests (lmPerm package), and post-hoc tests were performed for pairwise comparisons.
The probability of a fix attempt succeeding in a habitat type (fHabitat, Table 1) was modeled using a fixed-effect logistic regression. The fits of the full and reduced models were compared using a deviance test (G²) as an alternative to an individual parameter-based approach. Odds ratios with 95% confidence intervals were calculated for significant levels of the categorical predictor variable. Moreover, the influence of the same explanatory variable on the log-transformed LE values using a nested ANOVA (lme procedure) was investigated. GPS data loggers used within each habitat type (fUnit, Table 1) were treated as random terms.
The effects of habitat crossed (fHabCross), Vd, day of the path walked (fDay) and receiver (fUnit) (Table 1) on the LE were modeled through a Gaussian generalized-linear model (GLM). Following the method of Zuur et al. , data were screened using a multiple correspondence analysis (MCA, ade4 package) prior modeling to avoid correlated explanatory variables within the identical model. The response variable included all of the log-transformed LE values of the fixes from each GPS unit. Because the Vd values ranged between 0.84 and 1.00, the explanatory variable was centered on zero in all models. Eleven possible alternative—hypothesis models and a constant null model were considered (S2 Table).
Stationary unit tests were conducted with permission from private landowners and National Forestry Office by placing a stationary experimental arrangement of GPS units on private properties and in the national forest of La Croix-aux-Bois.
Motion tests were performed with two small dogs carrying GPS units on their collars to imitate the size and movement of a medium-sized terrestrial mammal and record the potential GPS unit antenna movement, variable speed and trajectory. In addition to collaring the dogs with GPS units in accordance with the manufacturer’s directions, the dogs were not handled or transported in an unfamiliar environment, and they did not perform unusual activities because they were used to wearing a collar and walking on a leash in various habitats. The tests were conducted under the supervision of an experienced behavioral biologist with the permission and in the presence of the dog owners, and they complied with the International Guiding Principles for Biomedical Research Involving Animals guidelines. Additionally, the municipalities of Boult-aux-Bois and Briquenay and National Forestry Office approved the paths into the villages and surrounding environments.
Stationary unit tests
The four units located in the upward antenna and program B test configuration (S1b Fig) had an FSR > 1. This result indicates that all of the expected positional fixes and additional fixes were obtained in open habitat because GPS data loggers presented a variation in logging rate (e.g., μFAT of 13 min 43 sec compared with the expected 15 min, Table 2). Similar variations in the logging rate against the fix interval scheduled (i.e., a μFAT lower than the programmed fix interval for the cycle) have previously been observed with commercially available GPS data loggers deployed during stationary tests .
After re-calculating the FSR to account for the actual maximum number of fixes attempts rather than the anticipated number (i.e., 106 versus 97 scheduled attempts), the FSR values remained high (FSR = 1.01 ± 0.08). The LE values between the units tended to differ significantly when simultaneously deployed (F3,420 = 2.28, p = 0.08), with LE values ranging between 0.2 and 163.2 m (median = 3.0 m). The frequency of outlier values was not linearly related to the number of full cycles the units were deployed (R2 = 0.02, p = 0.42). The median of the LE values also was not significantly explained by a cubic regression (R2 = 0.56, p = 0.89, S2 Fig).
The GPS data loggers provided coordinate errors of 3.3 m east and 3.6 m north on average compared with the 24 national geodetic survey (NGS) benchmarks involved in the stationary deployment in various configurations (Fig 2a). One of the GPS data loggers produced a mean location north of all other units, and the precision of the position estimates varied among the GPS units. In different habitats, the GPS data loggers provided coordinates that showed similar biases (2.9 m north and 5.1 m east in open habitat, 4.9 m north and 2.5 m east in forest, 5.5 m north and 6.2 m west near buildings, and 9.9 m north and 5.3 m east in barn habitat; Fig 2b). An exception was in the household habitat, which presented coordinates that showed north-south and east-west deviations depending on the units. Overall, the biases varied among the GPS units within each habitat.
Effect of antenna position and fix interval.
FSR values > 1 were obtained for all of the tested configurations once the actual maximum number of fix attempts (rather than the anticipated number of 145 possible fixes) was accounted for in the calculations (Table 2). The LERMS values ranged from 10.3 m to 65.4 m and increased when the unit’s antenna was down and over short fix intervals (Table 2). Filtering outliers from each unit improved the LERMS values ranging from 5.8 m to 19.9 m (Table 2) depending on tested configurations. Thus, the size of the dispersion buffers significantly decreased when filtering the outliers. The relative share of fixes with LE < 10 m was higher for each program when the antenna was up (> 90%, Table 2) and lower when the antenna was down, particularly for program A (Table 2). This result indicates that > 90% of the locations acquired can be accurate enough for fine-scale analyses in open habitats when the GPS data logger antenna is up.
The likelihood ratio test applied to the model selected for LE indicated that the model with random effects was significantly better than the model without random effects (L = 28.22, df = 1, p < 0.001). The top-ranked model included fAntenna and fFix, and the interaction between these two variables (R2 = 0.21, S1 Table). The antenna position had the strongest effect on LE, with LE values that were—1.14 ± 0.10 SE lower (on the logarithm-transformed scale) when the GPS unit’s antenna was up than when the antenna was directed downward (p < 0.001). The fix interval also influenced the LE, with lower values obtained for programs B and C compared with that of program A (coefficient = -0.44, SE = 0.10, p < 0.001 and coefficient = -0.39, SE = 0.10, p < 0.001 for programs B and C, respectively). Regardless of the antenna position, the LE values obtained with programs B and C were lower than those obtained with program A, and this difference persisted when the GPS receiver’s antenna was up (coefficient = 0.35, SE = 0.14, p < 0.05 and coefficient = 0.39, SE = 0.14, p < 0.05 for antenna up and program B, and antenna up and program C, respectively). Therefore, once a position was acquired, its accuracy was higher when the antenna was directed upward with fix intervals of 15 min and 1 h than with a fix interval of 5 min.
A two-factor ANOVA using permutation tests showed that antenna position had the strongest effect on the LEIQR values (F1,20 = 5.9, p < 0.001), with LEIQR values increasing (i.e., increased dispersion of locations caused decreased precision) when the GPS unit’s antenna was down. The fix interval also influenced the LEIQR values (F2,20 = 0.4, p < 0.05), with program A increasing the dispersion of positional fixes (p < 0.05) compared with that of program C, whereas program B only presented a tendency to increase the dispersion of positional fixes (p = 0.07) compared with that of program C.
Effect of habitats.
The LERMS values between habitats ranged from 12.4 to 68.9 m (Table 2). When filtering outliers, the highest LERMS value was observed in the household habitat (Table 2). Following outlier removal, LERMS values remained relatively high compared with that of LE filtering performed for the GPS units deployed in an open habitat except for that of units deployed near buildings (Table 2). Moreover, fixes with LE < 10 m were scarce for all tested habitats compared with the open habitat condition (Table 2).
The FSRs presented significant differences according to fHabitat (G² = 1183.3, df = 4, p < 0.001, R2 = 0.52). The odds of a fix attempt succeeding for units located in the barn were equivalent to those for units located in the forest and open habitats (Table 2). However, the odds of obtaining successful locations when the units were in a household and at proximity from a wall were 72 and 6 times lower (household: FSR = 0.20, OR = 0.01, 95% IC: 0.01–0.02; proximity from a wall: FSR = 0.75, OR = 0.17, 95% IC: 0.11–0.27), respectively, than those for units located in a barn (Table 2). In the household habitat, three of the four units successfully logged at least one location (i.e., one collar never collected positions).
A likelihood ratio test applied to the model selected for LE indicated that the model with the random effects was significantly better than the model without random effects (L = 30.43, df = 1, p < 0.001, R2 = 0.47). The LE values for the GPS units located in open habitat and at proximity from a wall were -2.09 ± 0.15 SE (p < 0.001) and -0.36 ± 0.16 SE lower (p < 0.05), respectively, than the LE values computed with GPS units deployed in a barn (on the logarithm-transformed scale). LE values produced by units located in the forest habitat and households did not differ from those produced from GPS located in a barn. Therefore, the GPS data loggers located in an open habitat and at proximity from a wall produced more accurate positional fixes than units located in human settlements (households and barns) and in forest habitat.
The trips yielded high FSR values that ranged from 0.97 to 1.12 with μFAT values < 1 min (Table 3). The LERMS values ranged from 13.2 m to 24.9 m with outliers and from 10.5 to 14.7 m without outliers. The highest LERMS values without outliers corresponded to trip 2 and trip 3 performed in and around Briquenay village, which is characterized by a more marked topography than Boult-aux-Bois. Outlier values occurred for each trip and were exclusively located in the forest. Removing these outliers reduced the LERMS values, particularly for the shortest path (Table 3). The highest LERMS value according to habitat was obtained for the forest habitat (16.8 m, associated with a large range of LE values) and then the edge habitat, whereas the village and open habitat had similar LERMS values (Table 4). An average of 69 ± 5% recorded fixes had an LE < 10 m. The proportion of fixes with an LE < 10 m was higher in the edge, open and village habitats compared with the forest habitat (Table 4).
The top-ranked model only included fHabCross (R2 = 0.17, S2 Table). During motion tests, GPS CatLog appeared to produce LE values that were 0.68 ± 0.11 SE higher (p < 0.001) when the fixes were acquired in the forest habitat than when the fixes were acquired in the edge habitat (on a log-transformed scale). The LE values were equivalent when the fixes were acquired in the open habitat, village and edge habitats. Therefore, the LE values significantly increased with increasing canopy cover.
This is the first study to investigate the performance and accuracy of low-cost GPS data loggers using the same testing methods employed to test expensive built-in wildlife GPS devices. The CatLog data logger fix-success rate (FSR) appears to be consistent among units, whereas location errors (LEs) have a tendency to vary among units. A similar finding was reported in a recent study that performed stationary tests on lightweight commercially available Sirtrack collars . Thus, testing individual GPS data loggers before deployment on animals is recommended. The GPS data loggers tested here were also temporally reliable during the entire battery lifespan. A recent study successfully increased the GPS data logger lifespan by increasing the battery pack . Our findings suggest that similar modifications could be performed on CatLog data loggers without affecting their performance and accuracy when tracking animals over a longer period.
During the stationary tests, the GPS units provided coordinates that deviated by 4 m on average in both the east-west and north-south directions relative to the NGS benchmarks. These results fell within the ranges of results recently reported for commercially available built-in wildlife GPS collars (e.g., Lotek large GPS collars with 4 m west and 10 m south mean deviations  and lightweight (105-g) Sirtrack collars with 5.4 m east and 6.0 m north mean deviations ). These systematic error ranges may not be detrimental depending on the study objectives (e.g., they must be considered when studying the fine-scale selection of habitat patches or redrawing precise animal paths) and animals surveyed (e.g., dimensions of habitat patches used by animals and their movement patterns).
All but one commercially available GPS data logger deployed during the stationary unit tests operated normally. The single unit that failed to fix positions in the household habitat did not undergo a technical failure and was found to function properly; thus, we believe that it did not receive sufficient satellite signals to compute the fixes. Based on all of the antenna positions and fix intervals, the average stationary FSR obtained for low-cost GPS data loggers was relatively high compared with the results reported in similar studies that have performed stationary tests with larger GPS collars (e.g., ATS collars, 1.00–0.76 ; G2000 ATS collars, 0–1.00 ; 3580 Telonics collars, 0.92–1.00 ). The results of the stationary tests did not identify an antenna oriented at < 45° from horizontal or different fix intervals as potential sources of FSR variation, which is inconsistent with previously reported results in the literature (Table 5). Thus, throughout this study, the movements of the CatLog GPS data loggers that were deployed on free-ranging animals and mimicked here by the antenna positions had no effect on the GPS data logger performance.
The reported values are the range of mean values reported across the studies indicated.
Moreover, except for the household habitat and proximity to buildings, the FSR values from the units deployed in the different habitats were comparable to those reported by the commercially available Lotek 3300 L GPS collars  and were larger than those reported by stationary studies performed with built-in lightweight GPS collars (e.g., 0.91 in a suburban environment ; 0.92 in New Zealand farmland habitat  and 0.89 in a natural habitat ) or with larger collars (0.96 ). Thus, the performance of low-cost GPS data loggers appears to be as good as commercially built-in GPS collars.
Modeling the FSR according to habitat emphasized that complete or partial sky obstruction influenced data acquisition because the FSR decreased as the amount of open sky decreased. For example, positioning the GPS data logger in a household can result in an 80% reduction in the FSR, whereas positioning it near buildings can result in a 25% reduction because of poor satellite view. These results confirm those of Adams et al. , who showed that particular suburban habitat types influenced the FSR because of variations in vegetation complexity and distance to buildings. Although all of the benchmarks were in locations with high sky availability, the GPS units in obstructed environments behaved identically to those deployed in steep terrain . In our study, the FSR was not dependent on canopy cover, which is inconsistent with the results of numerous studies (review in ). However, a recent study also reported that the FSR was not related to canopy cover (0.98–1.00 ). This difference may have occurred because the coniferous forest where the GPS units were deployed was not as closed-in as native forests  (Table 5).
Filtering out the outlier values led to a decrease in LERMS values from only 2 m to up to 45 m. Such variations may be associated with the number of satellites available to the receiver at a given time because the decrease in LERMS values followed a trend from non-obstructed habitats (open habitat) to partially obstructed (proximity to buildings) and obstructed habitats (forest, barn and household areas). Similar results were observed by Recio et al. , who located GPS collars under mature pine and native forests. The number of outliers that were documented in our stationary tests was similar to that in previously reported results using built-in wildlife GPS collars. In this study, 13 locations had errors of > 300 m (three fixes with downward antennas and 10 fixes in various obstructed habitats) out of 5046 successfully acquired locations. Other studies presented results that contained 2 outliers with errors > 300 m out of 6359 locations obtained with ATS collars  and 27 outliers with errors > 300 m out of 3441 locations obtained with Lotek 3300 L GPS collars . Moreover, the range of the average and/or median LE values for the positional fixes obtained during the stationary tests were comparable to those reported by studies performed in natural environments [28,33,36] and an urban environment (μLE = 30.1 m)  with built-in wildlife GPS collars.
Our LERMS values were larger than those obtained with similar commercially available GPS data loggers (LERMS = 4.4 m) under open sky conditions . A comparison of the different fix intervals and test durations used in our stationary unit tests and in tests performed with built-in wildlife GPS collars (e.g., 15 min to 13 h ) with those achieved by Vazquez-Prokopec et al.  may help to explain the inconsistency in the results. Vazquez-Prokopec et al.'s study used a 2-sec interval for 2-min tests, thus allowing the GPS data loggers to achieve positions under ‘hot-start’ conditions, which perform fast positional fixes because the GPS device remembers its final calculated position and visible satellites attempt to collect new positional data; however, the fix intervals used in this study only achieved fixes under ‘warm-start’ (5 min and 15 min) or ‘cold-start’ (1 h) conditions. For these conditions, the GPS device might remember its last calculated position but not the satellites that were visible because of a change in the satellite constellation (i.e., warm start). Alternatively, the device might dump all the information because of an extended fix interval (i.e., cold start). Consequently, the changes in the satellite constellation  and start conditions  had considerable influence on the GPS devices’ performance and accuracy.
If the antenna position did not influence the FSR, then it was shown to greatly influence the GPS accuracy, which was supported by the LEIQR values and proportion of fixes with LE < 10 m. These results were consistent with those from studies performed with built-in wildlife GPS collars that tested collar orientation [23,36] (Table 5). Our findings stressed that the position of the GPS data logger antenna had an important effect on GPS accuracy because it reduced the optimal antenna orientation related to specific behaviors of collared animals (i.e., scratching the GPS collar, climbing trees, and lying on side or resting).
In general, the shorter the fix interval, the higher the accuracy because the satellites are continuously tracked at short time lags (i.e., ‘warm-start’) [28,36]. Contrary to previous studies, our results indicate that the fix interval negatively influenced the measurement error, to a lesser extent when the antenna is directed upward (e.g., mLE = 3.2 m for 5 min against 2.7 m and 3.0 m for 15 min and 1 h, respectively), but markedly when associated with a collar orientation of—90° from the horizontal and a 5-min fix interval. Given our findings, one possible explanation is that short fix intervals might imply more temporally autocorrelated positional fixes (i.e., the accuracy of the fix acquired at time t + 1 depends on the accuracy of the fix acquired at time t by the GPS data logger). Therefore, when the number of satellites available to acquire a positional fix is low or when the GPS signal is reflected on the ground, the measurement error increased (e.g., 50.3% of fixes with LE < 10 m). However, longer fix intervals with positional fixes that were less correlated (15 min) or not temporally auto-correlated (1 h), this effect could be diluted (e.g., 72.4% and 71.4% for 15 min and 1 h, respectively). To the best of our knowledge, this represents the first time that this interaction has been tested, especially using such short fix intervals. Further research is needed to characterize better the effect of a ‘warm-start’ and antenna position on measurement error. Additionally, similar to previous studies performed in natural environments [29,35], the LE obtained with low-cost GPS data loggers was dependent on the habitat because the fixes performed in open habitats and near buildings were more accurate than those obtained inside buildings and under a closed coniferous cover (Table 5). However, even if the habitat did not include high-rise buildings, close proximity with human settlements significantly affected the satellite signals and GPS data-logger accuracy (e.g., 24.2% of fixes with LE < 10 m) despite presenting LE values that were similar to those previously reported in suburban environments (e.g., mLE = 30 m ).
The results from the controlled motion tests [33,35,36] and GPS devices mounted on free-ranging animals [24,28,30] generally indicated a reduction in GPS collar performance from stationary unit tests to motion tests (e.g., from 76% to 43% for stationary tests and collars deployed on the black bear Ursus americanus , respectively). We did not observe a similar reduction in accuracy, and our findings suggest that the FSR values between stationary and motion tests were similar. Our results were consistent with those reported by a recent study performed with low-cost GPS devices that reported higher FSR values with devices mounted on free-ranging otters compared to those tested in stationary conditions .
On average, our motion LERMS and FSR values were better than those from studies performed with a sled-like device that simulates domestic cat motion under various habitats  or devices attached to cars moving in open and forested areas  (Table 5). However, our FSR and fixes with LE < 10 m were similar to those reported in free-ranging animal returns  with a similar GPS data logger (I-gotU GT-120, Table 5). In addition, our LERMS and average LE values were comparable to those from motion tests performed for human epidemiology purposes [43,44] with the I-got-U GT-100 GPS data logger (Table 5). Similar to the results of the stationary unit tests, the LE increase was linked to a decrease in sky availability and traversal of forest habitat. We mimicked real data-collection conditions by testing the performance of mobile GPS data loggers carried by leashed dogs whose movements appeared to reduce the LE compared with stationary tests in forest habitat (LERMS = 40.9 m and 16.8 m in stationary and motion tests, respectively). However, the results should be interpreted cautiously because of our small sample size (two GPS data loggers on two dogs and four trips). Previous studies that performed stationary and motion tests concluded to a more realistic evaluation of performance for GPS collars based on the results derived from motion tests related to frequent changes in GPS position and direction or multipath crossings [33,35]. However, accurate motion tests are difficult to conduct because the accuracy of the reference position is reduced, the collar orientation is not controlled (i.e., low FSR associated with animal activity ) and various fix intervals are not used. In all of the motion tests conducted here, we ensured that the reference tracks were on the designed paths crossing habitats, although inherent error can be associated with the reference GPS. Additionally, the shortest fix interval was used to ensure a ‘hot-start’ of the reference GPS, the reference points were interpolated in time, and both units were synchronized.
By evaluating the performance and accuracy of the GPS CatLog data logger near the ground and by incorporating the effects of antenna positions, fix intervals, habitats and movements, we adopted a conservative approach to determining the fix rate reduction and measurement error for medium-sized terrestrial mammals. Additionally, because we developed error estimates for habitats in rural environments, our results may be comparable to those of other research conducted in both natural and human-impacted flat landscapes.
Although the GPS devices were placed near the ground, our results emphasized that antenna movements that mimic medium-sized species behaviors, proximity to human settlements and canopy cover did not generate missing value biases. Thus, the performance in terms of FSR of the CatLog GPS data loggers appears to be efficient for tracking a wide range of terrestrial species, from urban-adapter to forest-specialized species. Additionally, while unsuccessful fix attempts may be the result of device failure (i.e., simple software malfunctioning, [9,15]), the impressive reduction in the FSR in human settlements can also be indicative of resting sites (i.e., failure caused by temporary blockage to satellites, ), and provide useful information on recursions and the importance of building use by certain terrestrial mammals. Indeed, blocks of unsuccessful fixes can represent time periods that a species spends in locations with poor satellite reception due to a dense forest canopy  or other physical cover (e.g., tree hollow for possums , subterranean dens for African leopards Panthera pardus , nesting habitats for European hedgehogs , etc.). Further research is needed to identify the type of failure responsible for consecutive unsuccessful fixes.
Our findings also illustrated that CatLog GPS data loggers often presented the same accuracy as layered habitat maps created by GIS software (50–70% of the LE values < 10 m, see also ) and were as accurate as large and lightweight built-in wildlife GPS units tested in both natural and anthropogenic landscapes. However, large LE values (LERMS > 40 m) can be associated with down antennas, short-fix intervals and sky obstructions (human settlements and forested areas). Compared with built-in wildlife GPS collars, CatLog GPS data loggers do not provide information on the number of available satellites for a given positional fix (i.e., fixes quality). These technological limitations suggest that when using CatLog GPS data loggers, the risk of acquiring fixes with reduced accuracy must be considered because a lower number of satellites may be available, which occurs when the GPS data logger antenna is downward with a 5-min fix interval or when the GPS data logger is in human settlements.
The influence of LE values depends on the total amount of movement and is associated with research focus and types of tracked species. For instance, studying migration dynamics (e.g., birds, buffalos and marine mammals moving from nesting to foraging habitats) can accommodate conclusive inferences with large LE values, and estimating home range sizes and shapes may require less accuracy. However, studying the fine-scale dynamics of movements of animals requires more precise measurements of the dimensions of habitat patches and movement patterns of the species of interest. For instance, studying the dynamics of cat movements within a household and in human settlements requires high accuracy that cannot be produced by CatLog data loggers. However, these data loggers appear to be suitable for studying medium-size terrestrial mammal fine-scale movements in open habitats, such as pastures and meadows. To accommodate research outcomes with inherent measurement errors, GPS tags can be associated with tri-axial accelerometer data loggers to identify location errors that could not be directly associated with animal movements.
S1 Fig. Stationary unit tests.
The stationary experimental arrangement conducted with 40 GPS CatLog data loggers (● = one GPS) (a) mounted on a plastic bottle, (b) arranged on a 1.5-m grid to test the effects of two collar orientations (-90° from horizontal, antenna down; +90° from horizontal, antenna up) and three fix intervals (5 min, program A; 15 min, program B; and 1 h, program C) in an open habitat and (c) arranged to test the influence of various habitats.
S2 Fig. GPS data logger consistency.
The cubic graphic illustrating the relationship of the median location error (m) according to the deployment time (h).
S1 Table. Models explaining the location error (LE) of low-cost, lightweight GPS data loggers tested in stationary conditions (n = 24) with different antenna positions and fix intervals.
We thank the building owners for their authorization to test the GPS data loggers, Gilles Le Pape and Jean-François Gerard for statistical advice, and Thomas Quintaine and Julie Simon for their assistance with the statistical modeling. Special thanks to Philippe Ziegelmeyer, Steve Giglio and the dog owners for providing support during the motion tests. The authors are also grateful for the valuable comments from the reviewers.
Conceived and designed the experiments: MAFW PH. Performed the experiments: MAFW PH. Analyzed the data: MAFW. Contributed reagents/materials/analysis tools: MAFW PS. Wrote the paper: MAFW PH PS MLP.
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