Content uploaded by Jannis Gottwald
Author content
All content in this area was uploaded by Jannis Gottwald on Aug 17, 2020
Content may be subject to copyright.
Methods Ecol Evol. 2019;00:1–10. wileyonlinelibrary.com/journal/mee3
|
1
1 | INTRODUCTION
The analysis of animal movements based on tracking data enables
ecologists to investigate questions related to habitat and resource
utilization (Wyckof f, Sawyer, Albeke, Garman, & Kauffman, 2018),
migration and dispersal (Cagnacci, Boitani, Powell, & Boyce, 2010;
Walton, Samelius, Odden, & Willebrand, 2018) or to build predic-
tive models of animal behaviour (Browning et al., 2018). Recent im-
provement s in tracking technology have increased the number of
locations recorded per animal from a few dozen by manual radio te-
lemetr y to millions of movement steps from GPS tags and satellite
telemetry, leading Kays , Crofoot, Jetz, & Wikelski (2015) to proclaim
Received:15March2019
|
Accepted:28August2 019
DOI : 10.1111 /20 41-210X.13294
PRACTICAL TOOLS
Introduction of an automatic and open‐source radio‐tracking
system for small animals
Jannis Gottwald1 | Ralf Zeidler2 | Nicolas Friess1 | Marvin Ludwig1 |
Christoph Reudenbach1 | Thomas Nauss1
1Faculty of Geography, Philipps-University
Marburg, Marburg, Germany
2Freies Ins titut für Datenanalyse – Di pl.-
Phys. Ralf Zeidler, Freiburg, Germany
Correspondence
Ralf Zeidler
Email: ralf.zeidler@radio-tracking.eu
Funding information
Ministry of the Environment, Climate
Protection and the Energ y Sector Baden-
Württemberg, Germany; Hessen State
Ministry for Higher Educ ation, Researc h and
the Ar ts, Germany
Handling Editor: Chris Sutherland
Abstract
1. Movement ecology of small wild animals is often reliant on radio-tracking methods
due to the size and weight restrictions of available transmitters. In manual radio
telemetry, large errors in spatial position and infrequent relocations prevent the ef-
fective analysis of small-scale movement patterns and dynamic aspects of habitat
selection. Automatic radio-tracking systems present a potential solution for over-
coming these drawbacks. However, existing systems use customized electronics and
commercial software or exclusively record presence/absence data instead of trian-
gulating the position of tagged individuals.
2. We present a low-cost automatic radio-tracking system built from consumer elec-
tronic devices that can locate the position of radio transmitters under field condi-
tions. We provide information on the hardware components, describe mobile and
stationary set-up options, and offer open-source software solutions.
3. We describe the workflow from hardware setup and antenna calibration, to record-
ing and processing the data and present a proof of concept for forest-dwelling bats
using a mixed forest as study area. With an average bearing error of 6.8° and a
linear error of 21 m within a distance ranging from 65 m to 190 m, the accuracy of
our system exceeds that of both traditional methods as well as manual telemetry.
4. This affordable and easy-to-use automatic radio-tracking system complements
existing tools in movement ecology research by combining the advantages of
lightweight and cost-efficient radio telemetry with an automatic tracking set-up.
KEYWORDS
automatic radio-tracking, Marburg Open Forest, movement ecology, open-source, radio-
tracking, telemetry, triangulation
This is an op en access article under t he terms of the Creat ive Commons Attributio n License, which permits use, dist ribution and reproduc tion in any medium,
provide d the orig inal work is proper ly cited .
© 2019 The Authors. Methods in Ecology and Evolution published by John Wiley & Sons Ltd on behalf of British Ecological Society
2
|
Methods in Ecology and Evoluon
GOTT WALD eT AL.
a new golden age of animal tracking. To complement this more finely
resolved movement data, researchers have also developed a variety
of sophisticated analytical techniques such as path segmentation
analysis, step-selection functions and autocorrelated kernel meth-
ods (Fleming et al., 2015; Seidel, Dougherty, Carlson, & Getz, 2018).
Despite numerous advantages, both GPS tracking and satellite te-
lemetr y are still limited in their application to practical conservation
and ecological research. The cost of tags notwithstanding, size and
weight have limited their deployment in the past. New developments
have success fully reduced t he weight of such tag s to ~1 g (e.g. PinPoint
GPS tags, Lotek Wireless, Newmarket, CA). Nevertheless, bat tery
lifetime and recording frequency are inversely related to weight, so
the tags either record with low frequency or have short battery life-
times (e.g. 5 nights for a 4.2 g GPS tag with a 30 -s GPS-fixed sched-
ule; Roeleke, Teige, Hoffmeister, Klingler, & Voigt, 2016). Lightweight
GPS tags also need to be retrieved to access the data (Hallworth &
Marra, 2015), which either directly or indirectly increases most stud-
ies' expenditures in the form of lost material or data (Smith, Har t,
Mazzotti, Basille, & Romagosa, 2018; Tomkiewicz, Fuller, Kie, & Bates,
2010). These limitations aside, such tags are also too heav y for spe-
cies weighing less than 20 g, as their weight should not exceed 5% of
the individual's body mass to which it is attached (Brooks, Bonyongo,
& Harris, 2008). This leaves radio tags, with weights as low as 0.2 g,
as the single option for 5 0% of European passerines (Bau er, 2012) and
80% of European bats (Dietz, Nill, & Helversen, 2016).
Manual radio telemetry has disadvantages including labour in-
tensity, low temporal and spatial resolution (Montgomery, Roloff,
Ver Hoef, & Millspaugh, 2010; Thomas, Holland, & Minot, 2011),
infrequent and irregularly timed locations (Alexander & Maritz,
2015), small sample sizes (usually one frequency at a time; (Kays
et al., 2011)) and areal restrictions due to safet y concerns for field
workers (Smith et al., 2018). The qualit y of the resulting data also
precludes any advanced analytical techniques created for fine-scale
tracking data. Several working groups have designed automatic te-
lemetr y systems to overcome these drawbacks (Kays et al., 2011;
Řeřuchaetal.,2015;Weiseretal.,2016).Regardlessofequipment,
the key feature of modern automatic telemetr y systems is a contin-
uous signal record sent by radio tags using a st ationary automatic
receiver and a combination of either omnidirectional or directional
Yagi-Uda antennae. The former can detect presence and absence,
while the latter can detect the timing and direction of movement
(Crysler, Ronconi, & Taylor, 2016; Falconer, Mitchell, Taylor, &
Tozer, 2016). Existing systems use customized electronic devices
with proprietar y soft ware (Kays et al., 2011; Weiser et al., 2016)
BOX 1 Hardware overview
A Station with four antennae positioned in the cardinal directions and tuned to the regional frequency for wildlife telemetry (around
150.100 MHz in Germany)
B One RTL-SDR dongle per antenna (e.g. Nooelec NESDR SMart SDR, Nooelec, NY, USA) with a frequency range of 25–1,700 MHz and
a maximal sample rate of 2 MHz (quadrature sampling)
C Raspberry Pi 3B single-board computer (Farnell elements14, Leeds, UK) with the Raspbian operating system with a Docker-based
architecture
D High-capacity power supply with voltage regulation to work with the single-board computer, recommended for longer deployment
times. Battery time can be further increased through solar panels and a solar charge regulator.
E Power bank (20 Ah at 3.6 V ), able to supply a station for ~8 hr, recommended for mobile setups
F Mobile WiFi hot spot (Huawei E5330, Shenzhen, China), enables remote access within reach of the station's Raspberry Pi
|
3
Methods in Ecology and Evoluon
GOTT WALD eT AL.
or monitor presence and absence in large-scale movement studies,
but cannot triangulate the position of a tagged individual (Taylor et
al., 2017). Here, we describe an automatic radio-tracking system
for locating individuals Zeidler, R. (2017) that has a high temporal
and spatial resolution and works with inexpensive consumer elec-
tronics, flexible antenna designs and user-friendly, open-source
software. In addition to a field test of system accuracy, we present
a proof of concept based on forest-dwelling bats that illustrates the
general use of the system under field conditions.
2 | SYSTEM COMPONENTS AND
METHODS
2.1 | Core system
The low-cost, automatic radio-tracking system (Box 1, A, B, C) con-
sists of three basic elements: (a) a receiver chip, (b) antennae and
(c) a single-board computer (e.g. Raspberry Pi). Common DVB-T tel-
evision receivers with RTL2832U chips process the radio signal (e.g.
Nooelec NESDR SMArt SDR, NooElec, NY USA). Inexpensive soft-
ware-defined radios (RTL-SDRs, Laufer, 2015) allow multiple radio
signals to be simultaneously recorded. The RTL-SDRs connect the
single-board computer with the Yagi-Uda antennae.
To calculate the source direction of incoming signals, the antenna
pole at a given station requires an array of at least three directional
antennae (and an equal number of receivers) together with informa-
tion about their orientation. The number of receivers that one com-
puter can monitor depends on the number of available USB ports.
At least two antenna setups with known coordinates must be
available and within the range of the radio source to triangulate the
tag's position. Each station should be connected to the Internet
to guarantee synchronized system times with e.g. a mobile Wi-Fi
hotspot carrying a SIM card (Box 1, F). The Network Time Protocol
synchronizes the station times when they are first operational and
approximately every 5 min thereafter.
The stations are operated using custom software. Operational
hardware settings on the receiving units can be done by remote
access in a user-friendly web-interface. This includes the setting of the
monitored frequency band, activation of receivers as well as settings
to reduce the recording of interference. Once the receivers are acti-
vated, they digitize incoming signals. An algorithm based on liquidSDR
(Gaeddert, 2016) automatically detects peaks in the radio signals along
with timestamps, the frequency relative to a user-defined mid-fre-
quency (Hz), signal bandwidth (Hz), duration of the signal (s) and signal
streng th (dB; For additional information see www.radio-track ing.eu).
2.2 | Transmitter specifications
The system suppor ts any type of radio tag common in wildlife radio te-
lemetr y. Individual tags are identified by their specific frequency. The
number of tags that can be simultaneously monitored depends on the
tag feat ures and the possi ble width of the fre quency band, a s constrained
by the CPU per formance (e.g. 250 kHz for the Raspberry Pi 3 Model B,
1 MHz for the Model A+). With highly stable tag frequencies, tags can
have frequencies as small as 1 kHz apar t. Pulse timing is irrelevant for
signal detection, which enables tags that transfer additional information
(e.g. body temperature by varying time intervals between pulses) to be
deployed. Tags are attached to the animal's skin, fur or feathers using
skin glue that dissolves after a certain time. Alternatively, tags can be
attached by e.g. harnesses and collars. Depending on the size of the tag,
they can be operational between a few days and several months.
2.3 | Principle of bearing calculation and
triangulation
Signal amplification of a direc tional antenna depends on the angle
of the incoming electromagnetic wave. The relation between the
gain of a directional antenna and the angle of arrival can be approxi-
mated using a cosine func tion (Figure 1, Equation 1, Rabinovich &
Alexandrov, 2013), where g(ω) describes the gain or loss relative to
the angle ω in degrees compared to the gain of ω = 0°.
(1)
g(𝜔)=
cos
(
𝜋
90 ×𝜔
)
2
+
1
2
FIGURE 1 Radiation pattern of
directional antennae
4
|
Methods in Ecology and Evoluon
GOTT WALD eT AL.
In comparing two antennae of the same design, the absolute
gain in dB can be ignored because the values will be subtracted.
Assuming that the propagation path of the incoming electromag-
netic wave to the antenna is the same for both antennae (see also
calibration), the direction of arrival (ω) of the transmitter signal
is calculated by comparing the relative gains of two neighboring
antennae (Equations 2, 3, 4) with α describing the angle between
the antennae (Figure 2).
To calculate Δg in Equation 4, the dif ference in signal strength
between the two antennae (sl and sr) is normalized with the maxi-
mum signal strength difference Δm (Equation 5).
This can be derived by either simulating the gain pattern of the
antennae or a simple field experiment, in which the signal loss of the
antenna pointing directly at the tag (0°) is compared to the signal loss
of an antenna angled 90° relative to the tag.
Therefore, the direction of arrival is a function of the normal-
ized signal loss between the antennae and the angle bet ween those
antennae:
The tag's position is approximated by finding the point of inter-
section of two lines produced by bearing calculations at two sepa-
rate stations. If more than two stations simultaneously receive the
signal, the centroid of the resulting polygon is calculated.
2.4 | Calibration
Recorded signals may dif fer in strength due to varying sensitivities
of the components (e.g. antennae, cables, plugs, receivers). Since the
(2)
Δ
g(𝜔,𝛼)=
cos
(
𝜋
90 ×𝜔
)
2
−
cos
(
𝜋
90 ×(𝜔−𝛼)
)
2
(3)
Δ
g(𝜔)=cos
(
𝜋
90
×𝜔
)
with 𝛼=90
◦
(4)
𝜔
=
𝜋
90
×arcos (Δg)with 𝛼=90
◦
(5)
Δ
g=
(
sl−sr
)
Δm
(6)
𝜔
(Δg,𝛼)=
(
1−cos
(
−𝛼×𝜋
90 ))
×
(
1
𝛼
Δg+1
2)
FIGURE 2 Incoming signal (wavy line), angle ω in degrees
compared to ω = 0°, angle between antennae α
FIGURE 3 Calibration curves of
four HB9CV antennae arranged in an
array with 90° difference between
neighbouring antennae (Station 3–S3). A
radio tag was placed c. 115 m away and
the array was slowly turned on its vertical
axis
|
5
Methods in Ecology and Evoluon
GOTT WALD eT AL.
bearing calculation relies on an equal net gain at each receiving arm,
each arm must be calibrated. Calibration cur ves can be produced by
mounting a transmitter at a fixed distance to the station and rotating
the station around its vertical axis (Figure 3). Calculating the differ-
ence between each antenna's local maximum and the strongest local
maximum signal returns a correction value for each receiving arm.
Adding the correction value to the recorded signal strength adjusts
every antenna to the same maximum signal strength.
2.5 | Data processing
Different processing workflows were tested to identify relevant set-
tings and boundary conditions for obtaining optimal tracking results.
The bearing calculation requires that each receiving arm reliably
record the signal. An individual antenna may drop a signal when the
angle of the incoming electromagnetic wave strongly deviates from
the angle of possible maximum gain (ω = 0°). Furthermore, very small
or large intersection angles between bearings from two stations may
produce erroneous or no triangulations, if bearings run parallel.
We tested the effect of available antennae on the accuracy of
bearing calculations. The error of each bearing based on two, three
or four receiving antennae was assessed by the difference in the cal-
culated bearing and the angle between a station and the respective
test position.
To assess the influence of intersection angles between bear-
ings, we triangulated points and iteratively increased and decreased
the allowed minimum and maximum intersec tion angle by 10°,
respectively. For each set of triangulation points, we calculated the
position error, which is the mean dist ance bet ween the expected
and measured positions.
Data were processed using r version 3.6.0 (R Core Team, 2019).
The functions are publicly available as an r Shiny analysis tool (https
://github.com/radio track ingeu/ logger_app) or an r package (https ://
github.com/radio track ingeu/ radio track ingeu ).
2.6 | Accuracy study on an empty field
In Januar y 2019, we installed and tested this system on a bare field
free of vegetation to assess the its potential accuracy and evalu-
ate the data processing algorithm. The test setup comprised three
stations, each equipped with four directional antennae (HB9CV,
Telemetrie-Service Dessau) connected to RTL-SDR receivers
(Nooelec NESDR SMArt SDR, NooElec). The system was mounted
on 2.5 m tripods that were installed in an isosceles triangle forma-
tion with 200 m side length. The stations were calibrated against a
transmitter at a fixed distance of 115 m. After calibration, a sight-
ing compassed was used to position each station's antennae in the
cardinal directions. A regular, 50 m-wide test grid was constructed
between the stations and a 400 µW VHF radio-tag with a frequency
of 150.203 kHz and a pulse interval of 0.7 s mounted on a 2 m pole
was placed at each intersection of the test grid (Figure 4). The inter-
sections and the stations were localized with a dif ferential GPS. The
distance of the radio-tracking stations to the test positions ranged
from 65 m to 190 m.
FIGURE 4 Testing scheme. Radio-
tracking stations (S1–S3) were placed in
an isosceles triangle and a radio tag was
placed on each reference position for
2 min (M1–M6)
6
|
Methods in Ecology and Evoluon
GOTT WALD eT AL.
2.7 | Usability study of forest‐dwelling bats in a
mixed forest area
Results from an ongoing study that is part of the LOEWE priority pro-
gram Nature 4.0 – Sensing Biodiversity are briefly presented and dis-
cussed to demonstrate the system's capability under field conditions.
In 2019, 15 tracking stations were installed in the Marburg Open
Forest, the open research and education forest of the University of
Marburg, to track bats and songbirds over each breeding season until
2022. Each station is equipp ed with an array of four HB9CV antennae
mounted on 9 m aluminium poles. The stations record movement and
body temperature data of tagged bats, which belong to one of four
forest-dwelling species (Nyctalus leisleri, Myotis daubentonii, Myotis be‐
chsteinii, Barbastella barbastellus). The temperature sensitive tags (V3,
Telemetrie-Service Dessau, 0.35 g) vary the time interval between
consecutive signals based on the individual's skin temperature.
Exemplary results of bat ac tivit y are shown for 26 June 2019.
The optimal settings as identified in the accuracy test study were
used to triangulate individuals' positions. In order to handle and tag
the bats, a special license was granted by the Nature Conservancy
Department of Central Hessen (‘Obere Naturschutzbehörde
Mittelhessen, Regierungspräsidium Gießen’, v54-19c 2015 h01).
Tags were attached to the skin between the scapula with skin adhe-
sive (Manfred Sauer GmbH, Lobbach Germany) and the weight of the
attached tags was always <5% of the tagged individual's body mass.
3 | RESULTS
3.1 | Results of the accuracy study
Correction values obtained from local maxima in the calibration curves
ranged between 0.07 dB and 2.9 dB with the lowest and highest devia-
tions in maximum received signal s trength for st ations S3 and S2, resp ec-
tively ( Table 1). Thu s, calibrat ion had the stro ngest effec t on S2, improvin g
the bearing error from a median of 11.6° to 5.4° (Figure 5). Calibration
improved the median bearing accuracy by 2° across all stations.
Bearings calculated based on signals recorded by two antennae de-
viated from the real angle by 14.9° (median). Bearing error was reduced
to 6.8° when more than two antennae received a signal (Figure 6).
The position error decreased as the minimum and maximum
permissible intersection angles converged towards 90° (Figure 7).
Minimum and maximum angles of 40° and 140°, respectively, sub-
stantially improved results as well as sharply reducing the number
of triangulated point s. Placing additional limits on the intersection
angle steadily reduced the available data.
Positions were triangulated with calibrated signal strengths and a
minimum of three available antennae. Since a substantial number of
locations were lost due to restrictions to the intersection angle, we tri-
angulated positions with all intersection angles and with intersection
angles re stricted to 40 –140 °. Including a ll possible inters ection angles in
the tria ngulation process r esults in 673 locatio ns and a mean positio ning
error of 25 m. The triangulated points scatter in string-shaped patterns
TABLE 1 Correction values in dB based on calibration curves
obtained in the field
Station
Correction
[dB] 0°
Correction
[dB] 90°
Correction
[dB] 180°
Correction
[dB] 270°
S1 2.2 1.7 00.07
S2 0.26 1.7 02 .9
S3 0.8 00.9 0.98
FIGURE 5 Difference in angle error
before and after calibration. Calibration
substantially reduces the number of
points with a high bearing error (outliers in
the boxplot)
|
7
Methods in Ecology and Evoluon
GOTT WALD eT AL.
around the reference positions (Figure 8). Restricting the intersection
angles to a minimum of 40 ° and a maximum of 140° reduces this error
to 21 m. However, this results in a substantial loss of triangulated points
(292; Figure 8) with no points for position M5 (Figure 8).
3.2 | Results of the forest usability study
Tracking the movement of M. bechsteinii reveals different areas of
activity throughout the night (Figure 9, left). During 5-min intervals
that night (Figure 9, right), 301 positions were recorded within an
activity area of approximately 50 m2.
Body temperature patterns of four different bat species are
shown for nocturnal activity and resting in the day roost (Figure 10).
For the B. barbastellus as well as for the M. daubentonii, a clear drop
of the body temperature of approximately 7°C was recorded shor tly
before and after sunrise, respectively.
4 | DISCUSSION
The automatic radio-tracking system presented in this paper incorpo-
rates the advantages of lightweight and cost-efficient radio telemetry
into a continuous tracking setup. This enhances the number of tri-
angulated positions without manual telemetry and allows analytical
techniques previously reserved for fine-scale GPS tracks to be used.
These techniques enable researchers to glean important information
about dif ferent behaviour al states of an individual over lar ge trajecto-
ries. The exemplar y 5-min tracking interval, for example, shows a low
displacement in spatial units in relation to the time spent within the
area in question, which may be interpreted as an intensive area-re-
stricted search and, thus, foraging behaviour (Knell & Codling, 2012).
Overall, the accuracy of the radio-tracking system from the
field test compares well to reported manual bearing errors of ex-
perienced field workers (Bartolommei, Francucci, & Pezzo, 2013).
However, this strongly depends on the data processing techniques
used. Antenna calibration reduces the bearing error, confirming both
the underlying theoretic al assumption and the need for calibration
to obtain reasonable results. For more precise results, all bearings
calculated based on fewer than three available antennae should be
excluded from triangulated results. Reducing the intersection angle
improves results, yet also reduces the size of the dataset .
Since incorrect positioning in our field test appears systematic,
errors can be more accurately considered than in manual telemetry
and may be further reduced by, for example, field experiments that
are able to capture this regularity.
FIGURE 6 Absolute deviation of the bearings from the real
angle depending on the number of antennae available. The mean
absolute error is 7° with a standard deviation of 6.2°
FIGURE 7 Distance error and available
locations depending on the allowed
cutting angle
8
|
Methods in Ecology and Evoluon
GOTT WALD eT AL.
The low-cost solution for automatic radio-tracking presented
in this study enables researchers to apply automatic radio-track-
ing techniques in the field while the open-source hardware and
software components allows for active participation in future
development. As the principle of calculating bearing is based on
physical properties shared by most directional antennae, these
algorithms are suitable for triangulating positions with data
gathered by other systems such as SensorGnome (https ://senso
rgnome.org). Further relevant features, such as recording tagged
individuals' body temperature have also been implemented and
tested.
Continuously measuring animal positions and movement with a
long-term antenna setup can greatly contribute to research into animal
behaviour. The movement tracks it generates are comparable to those
generated by satellite and GPS tracking techniques, even below the
canopy in forested areas. This allows researchers to investigate ques-
tions related to small-scale habitat and resource utilization, choice of
breeding sites or migration and dispersal events in organism groups
FIGURE 8 Localization point s with all cutting angles bet ween two antennae allowed (lef t) and with cutting angles restricted to 40–140°
(right). Isolines represent point density increasing from the outside to the inside
FIGURE 9 Tracking data of a Bechstein's bat recorded on the night of 26 June 2019 (left). Yellow crosses indicate permanent radio-
tracking stations. The bounding box (black box) highlights the area of 5 min of relocations shown in detail in the right part of the figure
|
9
Methods in Ecology and Evoluon
GOTT WALD eT AL.
that movement ecologists cannot yet adequately study due to size re-
strictions. In this vein, this affordable and easy-to-use automatic radio-
tracking system adds a power ful tool to movement ecology research.
ACKNOWLEDGEMENTS
The first permanent setup of the system was implemented at
Marburg Open Forest – the open research and education forest
of Marburg University. The research is funded by the Hessen State
Ministr y for Higher Education, Research and the Arts, Germany,
as part of the LOEWE priority project Nature 4.0 – Sensing
Biodiversity. Radio-tracking.eu is the outcome of a feasibility study
financially supported by the Ministry of the Environment, Climate
Protection and the Energy Sector Baden-Württemberg, Germany.
AUTHORS' CONTRIBUTIONS
R.Z. invented the system and developed the algorithms for bearing
calculation. J.G., C.R., M.L., N.F. and T.N. provided development sup-
port, especially in the development regarding dislocation corrections
and monitoring of body temperature. J.G. and M.L. collected the test
data; bat foraging data were collected by J.G. J.G., M.L . and N.F. led
the writing of the manuscript. All authors interpreted the data and
contributed to the manuscript.
DATA AVAIL ABI LIT Y S TATEM ENT
Example data is provided online on Zenodo (Zenodo https ://doi.
org/10.5281/zenodo.3381909 (Gottwald, 2019)) and can be pro-
cessed using the r package “rad iotracki ngeu” (https ://github.com/
radio track ingeu/ radio track ingeu , Zenodo https ://doi.org/10.5281/
zenodo.3381316 (Zeidler, 2019)).
ORCID
Jannis Gottwald https://orcid.org/0000-0001-7763-1415
Ralf Zeidler https://orcid.org/0000-0002-3607-6512
Nicolas Friess https://orcid.org/0000-0003-0517-3798
Marvin Ludwig https://orcid.org/0000-0002-3010-018X
FIGURE 10 24-hr temperature curves of four dif ferent bat species
10
|
Methods in Ecology and Evoluon
GOTT WALD eT AL.
Christoph Reudenbach https://orcid.org/0000-0002-7476-3663
Thomas Nauss https://orcid.org/0000-0003-3422-0960
REFERENCES
Alexander, G. J., & Maritz, B. (2015). Sampling inter val affects the esti-
mation of movement par ameters in four species of African snakes:
Sampling interval affects estimation of movement. Journal of Zo ology,
297(4) , 309–318 . https ://doi.o rg /10.1111 /jzo.12 280
Bartolommei, P., Francucci, S., & Pezzo, F. (2013). Accuracy of conven-
tional radio telemetry estimates: A prac tical procedure of measure-
ment. Hystrix, The Italian Journal of Mammalogy, 23(2), 91–94. https ://
doi.org/10.4404/hystr ix-23.2-6376
Bauer, H.-G. (Ed.) (2012). Das Kompendium der Vögel Mitteleuropas: Ein
umfassendes Handbuch zu Biologie, Gefährdung und Schutz (Einbändige
Sonder ausgabe der 2, vollst. überarb. Auflage 20 05). Wiebelsheim:
AULA-Verlag.
Brook s, C., Bonyon go, C., & Harr is, S. (200 8). Effect s of global posi tioning sys-
tem collar w eight on zebra behav ior and locatio n error. Journal of Wildlife
Management, 72(2), 527–534. ht tps ://doi.o rg/10.2193/2007-061
Browning, E., Bolton, M., Owen, E., Shoji, A ., Guilford, T., & Freeman, R.
(2018). Predicting animal behaviour using deep learning: GPS data
alone accurately predict diving in seabirds. Methods in Ecology and
Evolution, 9(3), 681–692. ht tps ://doi.org/10.1111/2041-210X.12926
Cagnacci, F., Boitani, L., Powell, R. A ., & Boyce, M. S. (2010). Animal ecol-
ogy meets GPS-based radiotelemetry : A perfect storm of oppor tuni-
ties and challenge s. Philosophical Transactions of the Royal Society B:
Biological Sciences, 365(1550), 2157–2162. https ://doi.org/10.1098/
rst b.2 010.0107
Core Team, R. (2019). r: The r projec t for statistical computing. Retrieved
from htt ps ://www.r-proje c t.org / (accessed date 22 July 2019).
Crysler, Z. J., Ronconi, R. A., & Taylor, P. D. (2016). Differential f all mi-
grator y routes of adult and juvenile Ipswich Sparrows (Passerculus
sandwichensis princeps). Movement Ecology, 4(1), 1–8. https ://doi.
org/10.1186/s40462-016-0067-8
Dietz, C., Nill, D., & von Helversen, O. (2016). Handbuch der Fledermäuse
– Europa und Nordwestafrika (2nd ed.). Stutt gart : Kosmos.
Falconer, C. M., Mitchell, G. W., Taylor, P. D., & Tozer, D. C. (2016).
Prevalence of disjunct roosting in nesting bank swallows (Riparia ri‐
paria). The Wilson Jo urnal of Ornithol ogy, 128(2), 429–43 4. https ://doi.
org /10.1676/1 559-4 491-128 .2 .429
Fleming, C. H., Fagan, W. F., Mueller, T., Olson, K . A., Leimgruber, P., &
Calabrese, J. M. (2015). Rigorous home range estimation with move-
ment data: A new autocorrelated kernel density estimator. Ecology,
96(5), 1182–1188. https ://doi.org/10.1890/14-2010.1
Gaeddert, J. D. (2016). Liquid-dsp (version 1.3.0). Retrieved from http://
liqui dsdr.org/.
Gottwald, J. (2019). Example data from radio-tracking.eu projec t [Data
set]. Zenodo. https ://doi.org/10.5281/zenodo.3381909
Hallwor th, M. T., & Marra, P. P. (2015). Miniaturized G PS tags identif y
non-breeding territories of a small breeding migratory songbird.
Scientific Reports, 5(1), 11069. ht tps ://doi.or g/10.1038/sr ep1 1069
Kays, R ., Crofoot, M. C. , Jetz, W., & Wikelski , M. (2015). Terrestrial a nimal
tracking as an eye on life and planet. Science, 348(6240), aaa2478.
https ://doi.org/10.1126/scien ce.aaa2478
Kays, R., Tilak, S., Crofoot, M., Fountain, T., Obando, D., Ortega, A., …
Wikelski, M. (2011). Tracking animal location and activity wit h an au-
tomated radio telemetry system in a tropical rainforest. The Computer
Journal, 54(12), 1931–1948. https ://doi.org/10.1093/comjn l/bxr072
Knell, A . S., & Codling, E . A. (2012). Classif ying area-restricted search
(ARS) using a partial sum approach. Theoretical Ecology, 5(3), 325–
339. https ://doi.org/10.1007/s12080-011-0130-4
Laufer, C. (2015). The hobbyist's guide to the RTL‐SDR. Really cheap soft‐
ware defined radio: A guide to the RTL‐SDR and cheap software de‐
fined radio by the authors of the RTL‐SDR.com blog (2, print ed.). S.l.:
CreateSpace Independent Publishing Platform.
Montgom ery, R. A., Roloff, G. J., Ver Hoef, J. M., & Millspaugh, J. J. ( 2010).
Can we accurately characterize wildlife resource use when telemetry
data are imprecis e? Journal of Wildlife Management, 74(8), 1917–1925.
https ://doi.org/10.2193/2010-019
Rabinovich, V., & Alexandrov, N. (2013). Antenna arrays and automo‐
tive applications. New York, NY: Springer, New York. https ://doi.
org /10.1007/978-1-4614-1074-4
Řeřucha,Š.,Bartonička,T.,Jedlička,P.,Čížek,M.,Hlouša,O.,Lučan,R .,&
Ho r áček ,I.( 201 5). TheB A A R A(B iolo g ica l Aut omAt e dR Adio trac k ing )
system: A new approach in ecological field studies. PLoS ONE, 10 (2),
e0116785. https ://doi.org/10.1371/journ al.pone.0116785
Roeleke, M ., Teige, T., Hoffmeister, U., Klingler, F., & Voigt, C. C. (2016).
Habitat use of bats in relation to wind turbines revealed by GPS track-
ing. Scientific Reports, 6, 28961. https ://doi.org/10.1038/srep2 8961
Seidel, D. P., Doughert y, E., Carlson, C., & Getz, W. M. (2018). Ecological
metric s and methods for GPS movement data. International Journal
of Geographical Information Science, 32(11), 2272–2293. https ://doi.
org/10.1080/13658 816.2018.1498097
Smith, B . J., Hart, K. M., Mazzotti, F. J., Basille, M., & Romagosa, C. M.
(2018). Evaluating GPS biologging technology for studying spatial
ecolog y of large constricting snakes. Animal Biotelemetry, 6(1), 1–13.
https ://doi.org/10.1186/s40317-018-0145-3
Taylor, P. D., Crewe, T. L., Mackenzie, S . A., Lepage, D., Aubry, Y., Crysler,
Z., … Woodworth, B. K. (2017). The Motus Wildlife Tracking System:
A collaborative research network to enhance the understanding of
wildlife movement. Avian Conservation and Ecolog y, 12(1), 1–11. https
://doi.or g/10.5751/ACE- 00 953-120108
Thomas, B., Holland, J. D., & Minot, E. O. (2011). Wildlife tr acking tech-
nology options and cost considerations. Wildlife Research, 38(8), 653.
htt ps ://doi.org /10.1071/WR10211
Tomkiewicz, S. M., Fuller, M. R., Kie, J. G., & Bate s, K. K . (2010). Global posi-
tioning system and associated technologies in animal behaviour and eco-
logical research. Philosophical Transactions of the Royal Societ y B: Biological
Sciences, 365(1550), 2163–2176. https ://doi.org/10.1098/rstb.2010.0090
Walton, Z., Samelius, G., Odden, M., & Willebrand, T. (2018). Long-dis-
tance dispersal in red foxes Vulpes vulpes revealed by GPS track-
ing. European Journal of W ildlife Research, 64(6), 64. https ://doi.
org /10.1007/s10344 -018-1223-9
Weiser, A. W., Orchan, Y., Nathan, R., Charter, M., Weiss, A. J., & Toledo,
S. (2016). Characterizing the accuracy of a self-synchronized reverse-
gps wildlife localization s ystem. In 2016 15th ACM/IEEE International
Confere nce on Informati on Processing in S ensor Networ ks (IPSN) (pp. 1–
12). Vienna, Austria: IEEE. https ://doi.org/10.1109/IPSN.2016.7460662
Wyckoff, T. B., Saw yer, H., Albeke, S. E., Garman, S . L., & Kauffman, M.
J. (2018). Evaluating the influence of energy and residential devel-
opment on the migratory behavior of mule deer. Ecosphere, 9(2),
e02113. https : //doi.o rg /10.1002/ec s2.2113
Zeidler, R. (2017). Project – Radio-Tracking.eu. Retrieved from https ://
radio-track ing.eu/ (accessed date 18 July 2019).
Zeidler, R. (2019). radiotrackingeu/radiotrackingeu: Initial release
(Version v1.0). Zenodo. https ://doi.org/10.5281/zenodo.3381316
How to cite this article: Gottwald J, Zeidler R, Friess N,
Ludwig M, Reudenbach C, Nauss T. Introduction of an
automatic and open-source radio-tracking system for small
animals. Methods Ecol Evol. 2019;00:1–10. ht tp s : //d o i .
org /10.1111/2041-210X .13294