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First published online February 27, 2009
Journal of Experimental Biology 212, 823-834 (2009)
Published by The Company of Biologists 2009
doi: 10.1242/jeb.022137
Echolocation by two foraging harbour porpoises (Phocoena phocoena)
1 Fjord & Bælt, Margrethes Plads 1, DK-5300 Kerteminde, Denmark
2 Tierphysiologie, Zoologisches Institut, Universität Tübingen, Auf
der Morgenstelle 28, D-72076 Tübingen, Germany
3 Institute of Biology, University of Southern Denmark, DK-5230 Odense M,
Denmark
* Author for correspondence (e-mail: ursula.verfuss{at}meeresmuseum.de)
Accepted 11 December 2008
| Summary |
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Key words: harbour porpoise, Phocoena phocoena, biosonar, echolocation, foraging behaviour, signal pattern
| INTRODUCTION |
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Harbour porpoises (Phocoena phocoena) are mainly found in coastal
and near-shore environments. For them, as for probably all other toothed
whales (odontoceti), echolocation is an important sensory modality. They use
it almost constantly (Akamatsu et al.,
2007
) in orientation tasks
(Verfuß et al., 2005
),
allowing the perception of objects and landmarks based on acoustical images.
They also pursue prey with the help of echolocation
(Beedholm and Miller, 2007
;
Busnel and Dziedzic, 1967
;
Verfuß and Schnitzler,
2002
).
The use of echolocation during prey capture has been well studied in
insectivorous bats (reviewed by Kalko and
Schnitzler, 1998
; Miller and
Surlykke, 2001
; Schnitzler and
Kalko, 1998
; Schnitzler et
al., 2003
). Although various bat species use different types of
echolocation pulses, the pattern of echolocation pulse sequences emitted by
insectivorous bats is surprisingly similar. It can be divided into a search
phase and an approach phase (Griffin et
al., 1960
). The search phase contains the longest pulse durations
and intervals, both of which decrease during the approach phase. The approach
phase can be divided into an initial and a terminal part
(Melcón et al., 2007
).
The terminal part, which is often called the buzz, can sometimes be further
divided into a buzz I and a buzz II (Kalko
and Schnitzler, 1989
; Surlykke
et al., 1993
). In buzz I the pulse intervals continue to reduce
and in buzz II the intervals are minimal and remain constant at about 6
ms.
The biosonar of odontocetes has mainly been investigated in the context of
target detection (reviewed by Au,
1993
; Kastelein et al.,
1999
) and discrimination (reviewed by
Au, 1993
;
Kastelein et al., 1997
), and
not in the context of prey capture. Nevertheless, a few studies deal with the
echolocation behaviour of odontocetes during foraging. Click sequences
resembling the pattern of signals used by bats hawking insects have been
reported from odontocetes. Slow clicking with long intervals was attributed to
searching for prey and rapid sequences of clicks, coined bursts or buzzes,
were assumed to indicate the final stage of prey capture (e.g.
Akamatsu et al., 2005
;
Goodson et al., 1988
;
Goodson et al., 1994
;
Johnson et al., 2004
;
Johnson et al., 2006
;
Johnson et al., 2008
;
Jones et al., 2008
;
Madsen et al., 2002
;
Madsen et al., 2005
;
Miller et al., 1995
;
Miller et al., 2004
). Johnson
and colleagues correlated the echolocation behaviour of beaked whales with
prey capture by recording the click sounds of the whale together with the
echoes from the prey on a data logger attached to the back of the whale
(Johnson et al., 2008
). They
thus confirmed the correlation of buzzes with prey capture attempts.
Through geological time predator–prey interactions evolved between
bats and insects (reviewed by Miller and
Surlykke, 2001
). Some insects acquired selective audition and
evasive behaviours to escape predation by bats. Insects like green lacewings
and moths can detect ultrasound in the frequency range of the bats'
echolocation calls. Tympanate insects can respond to bat sound by turning away
(negative phonotaxis) or by diving passively or with power. Improved bat sonar
capabilities presumably evolved to counter avoidance responses by tympanate
insects (Miller and Surlykke,
2001
).
Such evolutionary predator–prey interactions have barely been
investigated for odontocetes. Mammal-eating orcas (Orcinus orca) in
the northeast pacific use their echolocation strikingly less than their
fish-eating relatives, probably so as not to warn their acoustically sensitive
marine mammalian prey (Barrett-Lennard et
al., 1996
). Also, northeast atlantic killer whales use less
intense clicks than do their northeast pacific cousins, perhaps to detect
echoes from herring before the herring senses the predator
(Simon et al., 2007
). The
extremely high frequency echolocation click sounds of harbour porpoises, on
the other hand, may have evolved so as not to be heard by killer whales
(Andersen and Amundin, 1976
).
Morisaka and Connor (Morisaka and Connor,
2007
) hypothesize that killer whale predation is the reason why
this acoustic feature also evolved in other odontocete species using high
frequency, narrow bandwidth clicks, like small dolphins
(Cephalorhynchus), the pygmy sperm whale (Kogia breviceps)
and the franciscana (Pontoporia blainvillei).
Many fish species can hear sound and some show a flight response to sound
stimuli (Canfield and Eaton,
1990
; Eaton et al.,
1995
). A few fish species, like American shad (Alosa
sapidissima) (Mann et al.,
1998
; Mann et al.,
2001
; Plachta and Popper,
2003
) detect and respond to ultrasound stimuli. Cod (Gadus
morhua) can be conditioned to detect ultrasound stimuli
(Astrup and Møhl, 1993
)
and to discriminate between long and short pulse intervals
(Astrup and Møhl, 1998
).
However, a recent study of unconditioned cod showed that they did not respond
behaviourally to intense ultrasonic stimuli
(Schack et al., 2008
). Whether
behaviours of fish to ultrasound evolved in response to odontocete predation
has been discussed (Astrup,
1999
), but still remains unknown.
This paper describes and compares the echolocation and swimming behaviour of two captive harbour porpoises during prey capture experiments that were repeated with one of them being blindfolded. We present for the first time a detailed analysis of the echolocation foraging sequence using synchronized video and high-frequency sound recordings. With these results and those of recent literature we propose phases for the echolocation behaviour of odontocetes during foraging and consider a possible evolutionary predator–prey scenario.
| MATERIALS AND METHODS |
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For investigating the echolocation and swimming behaviour of harbour porpoises during fish catches, both animals were trained to remain stationary at one end of the pool. During trials, one animal stayed with the trainer while the other animal was sent to the opposite end of the pool. Two types of trial were conducted: fish trials and no fish trials. In fish trials, as soon as the porpoise headed for the opposite end, a live brook trout (Salmon trutta f. fario) weighing between 20 and 85 g was thrown into the release area 1–5 m in front of a hydrophone array, causing a splash. No fish trials were run as controls. In no fish trials, a similar splash was generated with a boat hook – a wooden stick with a plastic hook end – simulating the splash from a fish. At most only one no fish trial per session was placed randomly in fish trials so as not to decrease motivation.
Both types of trial were conducted with Eigil and Freja being able to see. Trials were repeated with Freja while she was blindfolded with digestible gelatine suction cups covering her eyes. Sessions with Freja blindfolded were done shortly after she had finished eyecup training.
Experimental set up and trials
Synchronized video and high frequency sound recordings were taken from the
porpoises during experimental sessions. The experiments were done on days with
good water clarity and calm weather with no or little rain fall to ensure good
visibility and recording conditions. The set up used in this experiment was
the same as that used previously [see figures
1 and
2 in
Verfuß et al., 2005
(Verfuß et al., 2005
)].
Two in-air cameras and two underwater cameras were used. One camera (cam1) was
fixed on wires 5.3 m above the mean water surface level giving a top view of
part of the west end of the pool, the end where prey capture occurred. The
second camera (cam2) was fixed 9.4 m above the mean water surface level on the
Fjord & Bælt exhibition centre wall and was used to analyse the
porpoises' behaviour at the east end of the pool.
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Three HS150 hydrophones (Sonar Research and Development, Beverley, East Yorkshire, UK) with a frequency response up to 180 kHz (±6 dB) were used for recording echolocation behaviour. These were mounted in an array with 1 m spacing, submerged to a depth of 1 m, about 2 m in front of the pontoon at the receiving end of the pool. The array holding the hydrophones was built from PVC tubing to avoid strong echoes.
Signals from the hydrophones were amplified by 52 dB and high-pass filtered at 100 Hz using etec amplifiers (etec, Frederiksværk, Denmark). The sound was recorded on three channels of a RACAL Store 4D high-speed magnetic tape recorder (Racal Instruments GmbH, Bergisch Gladbach, Germany) at a speed of 60 in s–1 (=152.4 cm s–1), giving a bandwidth of about 300 kHz. Two of the three RACAL channels were set to 2 V, while the third channel was set to 0.5 V to increase amplification of weak echolocation signals.
The synchronization of all video and sound recordings was done with a custom-built VITC/LTC time code generator (Universität Tübingen, Tierphysiologie, Tübingen, Germany). The LTC time code was recorded on the fourth channel of the RACAL Store 4D tape recorder and the sound channels of the in-air cameras. The VITC time code was integrated in the underwater camera recordings.
Experiments were run on 34 days over the 2 years with 60 experimental sessions totalling 304 trials: 98 fish trials for Freja and 127 fish trials for Eigil, 18 no fish trials for Freja and 19 no fish trials for Eigil, as well as 38 fish trials and 4 no fish trials for Freja when blindfolded.
Video and sound analysis
All video and sound recordings were visually scanned for good quality,
defined as reasonably good images of the porpoise on both video cameras (cam1
and cam2), of the fish (if used) and of the catch or attempted catch in the
recordings of video camera 2. Catch attempts were defined as the porpoise
approaching the fish to a distance of less than 0.1 m, with the porpoise being
in the final stage of the echolocation foraging sequence (see Results), and
the fish having been able to escape in the last moment by a sudden movement
away from the porpoise. Catches/catch attempts recorded on the underwater
video cameras (cam3 and cam4) were preferred for analysis. The data of the
swim paths shown here are from cameras cam1 and cam2. The sound recordings
were selected for a reasonable signal to noise ratio of echolocation
clicks.
A total of 29 trials were chosen for detailed analysis of the echolocation behaviour, including 15 fish trials (five for Freja, five for Eigil, five for Freja when blindfolded), and 14 no fish trials (five for Freja, five for Eigil, four for Freja when blindfolded).
For video analysis, selected sequences were digitized with a frame grabber card (HASOTEK frame grabber FG42, Rostock, Germany). The video sampling rate was 25 images s–1, giving a 40 ms time interval between frames. Motion analysis was done frame by frame. The relative position of the tip of the porpoise's rostrum within each successive frame was determined from the video recordings of cam1 and cam2. For frames in which the porpoise was not visible, its position was interpolated. The same analysis was done with the fish in fish trials, using the central point of the fish's body to determine its position. The distance between the calculated positions of the porpoise and the fish was determined and defined as distance to fish (DF).
In navigational tasks (Verfuß et
al., 2005
) with the same set up, both porpoises showed
range-locking behaviour on landmarks near the west end of the pool. The time
interval between successive clicks decreased linearly with decreasing distance
to the end of the pool. In that study an arbitrary reference point was defined
at the west end of the pool to establish the use of landmarks. We used the
same reference point in this study to examine the influence of landmarks
during fish catch. This reference point was midway between the front edge of
the pontoon and the net, a point 1.5 m between these. The distance between the
calculated position of the porpoise and the reference point is defined as the
distance to reference (DR).
Absolute metric values for the animals' positions were obtained with the
help of custom-written software (3D and 3Drek, D. Menne©, Tübingen,
Germany) using the method of photogrammetry (see
Finsterwalder and Hofmann,
1968
; Schwidefsky and
Ackermann, 1976
). The method of photogrammetry allows the
determination of absolute positions of objects in a 3D environment. For the
surveillance cameras (cam1 and cam2), the 2D-horizontal movement of the
porpoise and the fish, respectively, was reconstructed. The third dimension,
swimming depth, was estimated from 0.2 m to 0.7 m below the water surface for
most of the traverse, or taken from the 3D motion analysis of the two
underwater cameras (cam3 and cam4) if suitable. Marked positions on the
pontoons enabled the software to calculate relative positions and distances in
the video images into absolute positions. Reconstruction of the porpoise's
swimming path was considered successful when the track from each camera
overlapped at the middle of the pool, which was common to both surveillance
camera views. Tidal differences that changed the distance between the cameras
and water surface were taken into account for each session. With this method,
distances could be calculated with a maximum error of 5%.
For sound analysis, sequences from chosen trials were played back at
16-fold reduced speed and digitized with a sampling rate of 51.2 kHz,
resulting in an effective sampling rate of 819.2 kHz. The click interval,
which is the time between two successive clicks as measured from the onset,
was measured with custom-made software (Sona-PC, B. Waldmann©,
Tübingen, Germany) at an accuracy of 156 µs. The software also showed
the onset of each video frame and its specific frame number, which were used
to correlate sound and video recordings. It was thus possible to correlate a
particular click or click interval with a distance from the porpoise to the
fish or to our arbitrary reference point, respectively. Analysis began from
the first click recorded in a trial and stopped after the fish was caught, or
the porpoise reached the hydrophone array in no fish trials,
5 m in front
of the reference point. The first and last click analysed therefore determined
the trial duration, the travelled distance and the total number of analysed
clicks within a trial as given in Table
1.
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Not all clicks of a click train were captured by the hydrophones. Harbour
porpoises have a directional sound beam pattern
(Au et al., 1999
) and pauses
in recordings occur not necessarily because of a lack of click production, but
because of the porpoise moving its beam away from the recording hydrophone.
Recordings from the three hydrophones confirmed beam scanning by our
porpoises. Therefore all click intervals longer than 120 ms, indicating that
the animal directed its sonar beam away from the hydrophone, were excluded
from the analyses.
Click trains, swim speed and statistical analysis
Click trains were divided into two sections, a before-splash section and an
after-splash section (Fig. 1).
In fish trials, the porpoises showed a clear reaction to the fish when closing
in on their prey (see Results) by suddenly shortening the click interval. Thus
each fish click train was further divided into far stage and near stage
(Fig. 1). In the after-splash
section, averages over five successive click intervals were calculated. The
transition from far stage to near stage was defined to be in the first such
group of five clicks, where the mean click interval values start to
continuously decrease over time to a value below 20 ms. The transition point
was defined as being at the longest click interval in the first mean.
The orientation tasks conducted previously
(Verfuß et al., 2005
),
performed with the same porpoises and the same set up, showed that the median
click interval decreased linearly with decreasing distance to reference from
26 to 12 m, revealing a range locking on a landmark near the reference point.
A comparable decrease of click interval was observed in the no fish trials of
the present study (see Results). As in Verfuß et al.
(Verfuß et al., 2005
),
the click interval/distance to reference data pairs were grouped into distance
to reference bins 1 m in length. The median click interval was determined for
each 1 m bin. Then the mean of the trial medians for each distance bin was
calculated separately for each animal, type of trial and click train section.
All mean values comprise the medians of at least three trials. As the near
stage was clearly a response to the fish, the assessment of a relationship
between the click interval and the reference point was omitted for this
stage.
For each porpoise, trial type and click train section, a regression analysis was performed on the mean click interval of the DR bins from 26 to 12 m. The slope of the regression plus 95% confidence interval were determined using SYSTAT (V10, SPSS, Chicago, IL, USA). For the after-splash data, the regression analysis was repeated for DR=18–12 m as only those distances were obtained for Eigil in fish trials. For the far stage, regression analyses on the mean click interval of the DF bins were also performed.
For the after-splash section of no fish trials, the mean ± s.d. of the trial median lag timeR for DR=18–12 m was determined for Eigil, Freja and Freja blindfolded. The lag timeR is defined as the time difference between the click interval and the corresponding two-way transit time to the focal object (here the reference point R). We calculated the two-way transit time between the outgoing click and the returning echo from the reference point by assuming the speed of sound in water to be 1.5 m ms–1, giving a slope of 1.3 ms m–1. For the far stage of fish trials, the regression analysis revealed no significant decrease in the click interval with decreasing distance to fish (or reference; see Results). Therefore, the mean ± s.d. of trial median click intervals for DR=18–12 m was determined for Eigil, Freja and Freja blindfolded. For the transition from far stage to near stage, the mean ± s.d. for the distance to fish and the click interval at the transition point were determined. The mean ± s.d. of the median lag timeF, the lag time calculated with reference to the fish as focal object, for DR=18–12 m was determined for Eigil, Freja and Freja blindfolded for the far stage of fish trials.
The swim speed was calculated as the running mean of 10 video frames (0.4
s) from the frame-by-frame speed. The mean ± s.d. of swim speeds within
DR=26–12 m was determined for each porpoise and each
task so they could be compared with swim speeds obtained previously
(Verfuß et al.,
2005
).
The click density is defined according to Schnitzler
(Schnitzler, 1967
) as the
number of clicks produced per metre travelled. It was calculated with the
formula click interval–1 x speed–1,
giving clicks per metre. The mean ± s.d. click density was determined
for DR=18–12 m for comparison with lag
timeR and click interval.
Mean swim speeds and click densities were tested for individual differences
and differences between Freja with and without eyecups using a mixed effect
model with `task' being a random variable, calculated with the programme R 2.5
(R Development Core Team,
2007
; Pinheiro and Bates,
2000
; Zuur et al.,
2007
). Differences between Freja with and without eyecups as well
as individual differences between mean lag timeR and mean click
interval were tested using a general linear model adopting a quasi-poisson
distribution (McCullagh and Nelder,
1991
). Task-specific differences in mean speed and mean click
density were also tested using a general linear model.
Multiple testing of a single null hypothesis required an alpha-level
adjustment for the general linear model results. We did this by correcting
P-values for the number of tests: two tests for lag timeR
and click interval (comparison between the two animals and between Freja
with/without eyecups), three tests for speed and click density (comparison
between the two tasks for Eigil, Freja and Freja blindfolded). We calculated
corrected P-values (Pcorr) using the equation
Pcorr=1–(1–Porig)k
(Sokal and Rohlf, 1995
) where
Porig is the originally derived P-value and
k is the number of tests conducted.
| RESULTS |
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The average swim speed was higher for both porpoises in foraging trials
(with and without fish) than in trials where the animals swam the same track
to perform a navigational task (Fig.
3A) (Verfuß et al.,
2005
). The porpoises increased their speed to a maximum near the
middle of the pool, after which the swim speed declined as they approached the
catch area (Fig. 3B).
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2: 0.56;
Fig. 3A). Freja's average swim
speed did not differ between fish and no fish trials
(Pcorr
0.633; expl.
2
0.17) and
she swam about half as fast with eyecups on
(Fig. 3A;
Table 1). The difference in
swim speed was highly significant [P=0.005; random effect (task):
variance=2.1x10–11;
residual=4.1x10–2]. There was no significant difference
between Freja and Eigil in swim speed [P=0.928; random effect (task):
variance=2.3x10–11; residual=
4.7x10–2].
Echolocation behaviour
The porpoises continuously emitted echolocation signals in all trials (Figs
4 and
5). In no fish trials click
interval decreased with decreasing distance to the reference point for most of
the track (Fig. 4,
Fig. 5A). When blindfolded,
Freja decreased click interval until she was about 19 m from the reference.
Here the click interval rose slightly and then decreased parallel to the
two-way transit time (Fig. 4B
left, arrow; Fig. 5A
right).
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2=0.63), and for
Freja versus Freja blindfolded (Pcorr=0.024,
expl.
2=0.62; Table
1).
In fish trials we also investigated separately the sections of the
echolocation sequences before and after the splash. Before the splash, Freja
blindfolded or not decreased click interval significantly with decreasing
distance to the reference point (DR=26–22
m/26–19 m without/with eyecups: R2=0.974/0.830,
P=0.002/0.002) thus indicating range locking
(Table 1). This is not obvious
for Eigil (DR=26–21 m: R2=0.455,
P=0.142), perhaps because the distance covered before the splash is
too short to show this effect. After the splash we discriminated two different
sections in the echolocation sequences. The far stages of fish trials began
with the splash and ended with the transition to the near stage, which was
characterized by a sudden change to shorter intervals
(Fig. 1). In the far stage,
Eigil and Freja blindfolded or not kept the mean click interval fairly
constant (Fig. 6B), independent
of testing over the distance to reference (Eigil,
DR=18–12 m: R2=0.262,
P=0.240; Freia, DR=21–12 m/18–12 m:
R2=0.106/0.041, P=0.358/0.662; Freia bf,
DR=18–12 m: R2=0.001,
P=0.956) or distance to fish
(Table 1;
DF measured within the corresponding
DR range given above: Eigil,
DF=12–6 m: R2=0.031,
P=0.706; Freia, DF=16–6 m/11–6 m:
R2=0.001/0.129, P=0.931/0.484; Freia bf,
DF=13–6 m: R2=0.368,
P=0.111). The slope of the regression was not significantly different
from zero in all cases (Table
1). There were no significant differences between the mean click
interval of Eigil versus Freja (Pcorr=0.168,
expl.
2=0.35), and of Freja versus Freja
blindfolded (Pcorr=0.070, expl.
2=0.49;
Table 1). With the beginning of
the near stage the click intervals decreased significantly with a steep slope
much greater than the slope of the two-way transit time (Eigil/Freja bf:
R2=0.959/0.959, P<0.001/=0.021; the
DF for Freja between 1 and 0 m was too short to conduct a
regression analysis; Fig. 6B;
Table 1). The click interval
reached minimum values of about 1.5 ms when the porpoises were less than 1 m
from the fish (Fig. 4;
Fig. 5B,C;
Fig. 6B;
Table 1). Nevertheless the
click interval was greater than the two-way transit time to the fish. The
transition from far to near stage was at DF=4.4±2.6
m for Eigil, at DF=1.9±0.8 m for Freja, and at
DF=3.9±1.7 m for Freja blindfolded. The click
interval at the transition of far to near stage was 57.5±14.4 ms for
Eigil, 48.3±16.0 ms for Freja and 41.5±14.4 ms for Freja
blindfolded (Table 1). The
porpoises continued echolocation after the fish was caught or had been able to
escape. The length of the click interval commonly increased again after the
capture or capture attempt (Fig.
4; Fig. 5B,C).
We did not systematically determine the click amplitude of the recorded sound sequences. However, the signal amplitude of clicks within near stage was at least 12 dB lower than in the far stage. The low amplitude of the final buzz made it difficult to record this part of a catch sequence entirely or sometimes even partly.
Click density
The click density arising from the inverse product of swim speed and click
interval describes how many clicks are emitted per distance travelled and was
determined for the after-splash section in no fish trials and the far stage
section of fish trials (Table
1). The two porpoises used a similar click density in the
different tasks [P=0.720; random effect (task):
variance=7.8x10–11;
residual=15.5x10–2]. Eigil had a significantly lower
click density in no fish trials compared with fish trials
(Pcorr=0.039, expl.
2=0.55), but for
Freja the click density did not differ (Pcorr
0.139,
expl.
2
0.45). Blindfolding produced a highly significant
effect; click density was at least twice as high with as without eyecups
[P<0.001; random effect (task):
variance=3.0x10–11;
residual=6.1x10–2;
Table 1].
| DISCUSSION |
|---|
|
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|---|
|
Search phase
In the search phase odontocetes are expecting echoes from prey within the
perceptual range of their biosonar system. We assume that the click pattern in
this phase is determined by environmental conditions if background targets are
within the perceptual range. This is the case in the present study where the
click pattern of the search phase is determined by range locking onto a
landmark. This is indicated by a reduction of click interval according to a
decrease of the two-way transit time between the landmark and the animal. The
data from no fish trials show that Eigil and Freja use a landmark close to the
reference point at the capture end of the pool
(Fig. 4;
Fig. 5A;
Fig. 6A;
Table 1) as in the orientation
tasks described previously (Verfuß
et al., 2005
).
Our studies of the acoustic behaviour of captive harbour porpoises during
orientation and prey capture might help explain recordings from free-ranging
porpoises equipped with acoustic tags. One such study was described by
Akamatsu et al. (Akamatsu et al.,
2005
) for a finless porpoise (Neophocoena phocaenoides).
This animal showed clear range-locking behaviour while swimming in an isolated
waterway (Fig. 7B, Search),
which started at about 40 m from a presumed prey capture
(Fig. 7B, Terminal). The
authors interpreted this behaviour as range locking on a potential prey target
after detection at the instant where the click intervals begin to decrease. A
similar behaviour was also described for a harbour porpoise in Danish waters
(Akamatsu et al., 2007
). We
interpret these recordings differently. We assume that during the reduction of
click intervals the animals are still in search phase and are range locked to
landmarks in the background. We think that the finless porpoise switches from
one landmark to another at the beginning of the echolocation sequence shown in
Fig. 7B marked S, as indicated
by the sudden rise in click interval as seen in the no fish trials of Freja
when blindfolded (Fig. 4B;
Fig. 5A;
Fig. 6A). Furthermore we feel
that prey detection is indicated by the switch to variable click intervals
around a mean (Fig. 7B, marked
D), as we will discuss later.
There are hardly any prominent landmarks within the perceptual range of the
odontocetes inhabiting open waters. We hypothesize that odontocetes in open
space situations will adjust their click interval in the search phase to a
specific search range, which may be the maximum perceptual range. This would
result in click intervals around a constant mean. Madsen et al.
(Madsen et al., 2005
) recorded
the echolocation behaviour of deep-diving beaked whales (Mesoplodon
densirostris) while foraging in open water with an acoustic data logger
attached to the animals. They report a stable click interval with values of
300–400 ms for the search phase. The authors calculated that these
values indicate a maximum search range of 275 m assuming a lag time of 20 ms
(Madsen et al., 2005
).
Approach phase
The approach phase starts after the detection of echoes from suitable prey.
These echoes contain information about the location and the nature of the
prey. According to the click pattern, the approach phase can be separated into
two parts. In the initial part the click intervals are distinctly longer than
in the terminal part. The rather fast transition from long intervals to
shorter intervals in the terminal part occurs at quite short distances to the
prey (on average between 1.9 and 4.4 m in the present study). The change in
click interval also causes a distinct shortening in lag time (click interval
minus two-way transit time between predator and prey), which may indicate that
the returning echoes are processed differently during the two parts of the
approach phase.
Initial part of the approach phase
In the present experiments, the porpoises were conditioned to perceive the
splash as a cue for fish. The splash occurred at distances of about
15–20 m between porpoise and fish. After detection they started to emit
clicks at intervals around a mean of between 47 and 55 ms in what we describe
as the initial part of the approach phase. In some sequences this switch from
decreasing intervals (typical for the search phase) to constant click interval
is clearly visible (Figs 1 and
4) thus indicating detection
shortly after the splash. We therefore conclude that in most trials the
porpoises detected the fish shortly after the fish was thrown into the
pool.
In the echolocation sequence of a foraging finless porpoise presented in
Fig. 7B
(Akamatsu et al., 2005
) we can
also identify a section with click interval oscillating around a constant mean
that we interpret as the initial part of the approach phase.
Morozov and colleagues (Morozov et al.,
1972
) describe the echolocation behaviour of free ranging
bottlenose dolphins while approaching and capturing a dead mackerel at
distances as far as 40 m. They measured the mean click interval and saw
range-locked behaviour during the approach up to target distances of about 4
m, with a 20 ms mean lag time. However, the distribution of click intervals is
right skewed, thus the median is shorter than the examined mean. The
calculation of the median also indicates that the reduction of click intervals
from 16 to 4 m is distinctly less steep as predicted from the curve of the
two-way transit time. Therefore we believe that at distances from 16 to 4 m
the dolphin is in the initial part of an approach phase with approximately
constant click intervals. We also believe that at distances greater than 16 m
the dolphins are range locked to the end of the pool and not to the fish (see
also Verfuß et al.,
2005
), again similar to the behaviour of our harbour porpoises in
the search phase.
In fish catch trials similar to the ones presented here, the same porpoises
as used in our study showed a change of emission level of the outgoing signal
with distance (Beedholm and Miller,
2007
). The porpoises decreased the source level with decreasing
distance (R) to their prey by a value close to 20 logR
meaning that the signal level at the fish would be fairly constant. Possible
consequences of this for the echolocator, the harbour porpoise, are discussed
by Beedholm and Miller (Beedholm and
Miller, 2007
). The nearly constant incident sound levels and click
intervals during the approach to the prey could be advantageous. By keeping
both click interval and sound pressure at the prey nearly constant the
predator could conceal its approach while closing in on the prey. This only
makes sense if the prey is able to hear and to react to the echolocation
signals of the predator. Mann and colleagues
(Mann et al., 1998
) showed
that the American shad, Alosa sapidissima, responded to
echolocation-like clicks over long distances. They speculated that ultrasonic
hearing in some fish prey could have evolved in response to selection pressure
by echolocating predators like dolphins and porpoises. However, interactions
between fish and echolocating odontocete predators remain to be
discovered.
The echolocation behaviour of foraging beaked whales that feed mainly on
squid (Santos et al., 2007
)
has been described by Madsen and colleagues
(Madsen et al., 2005
). We have
already mentioned that these toothed whales – living in open waters
– are not range locked during the search phase. Their data show that
these odontocetes use about the same constant click intervals in the search
phase and the initial part of the approach
(Fig. 7Ca). They could not find
a distance-dependent reduction in emission level in this initial part of the
approach phase. This does not contradict our assumptions, as it has been shown
that squid do not react to sound sequences similar to those emitted by beaked
whales even if exposed to high amplitude clicks with short interval
(Wilson et al., 2007
). We
therefore assume that the prey of beaked whales will not notice the
approaching danger so that there is no selective advantage in adjusting the
emission level. By using a similar source level and click interval in the
initial part of the approach phase as in the search phase the animals have the
advantage of a large perceptual range that allows them to search for their
next prey item while approaching the current one. However, beaked whales adapt
their click interval during the initial part of the approach if the echo
scenery is complex (Johnson et al.,
2008
). The shortening of click intervals may indicate clutter
echoes within the perceptual range, e.g. like those caused by schooling prey.
This would eliminate the need to search for other prey at longer distances
(Fig. 7Cb).
Terminal part of the approach phase
The terminal part of the approach phase starts with the sudden and rapid
shortening of click intervals (Fig.
1; Fig. 4;
Fig. 5B,C;
Fig. 6B). In analogy to
echolocating bats the terminal part may also be called the `buzz'
(Kalko and Schnitzler, 1998
).
In the present study, the buzz consists of two sections that differ in click
pattern. In the first section the click interval is reduced from about 50 ms,
sometimes in an oscillating manner, to intervals below 10 ms
(Fig. 4). In the second section
the click interval is short and kept quite constant at values between 1.4 and
1.6 ms. The transition from the initial part to the terminal part occurs at a
mean distance between 1.9 and 4.4 m. At the beginning of the second section of
the terminal part the animals are close to the prey, below about 1 m. Although
click interval shortens rapidly in the terminal part of the approach phase, it
is at no time shorter than the two-way transit time to the fish. The terminal
part ends shortly after the catch with a rapid increase of the click interval
(Fig. 4B). Naturally the animal
can continue to produce clicks after the catch as sound is generated in the
nasal air passages and emitted through the melon
(Cranford et al., 1996
;
Cranford and Amundin, 2004
;
Goodson et al., 2004
).
Buzzes have been recorded in the field from several odontocetes species
(e.g. Akamatsu et al., 2005
;
Goodson et al., 1994
;
Herzing, 2004
;
Madsen et al., 2005
;
Miller et al., 1995
). The
authors assumed that buzzes were associated with prey capture or attempted
prey capture. Our experiments, and other studies, demonstrate that the buzz is
connected with the final approach to a target
(Busnel and Dziedzic, 1967
;
Evans and Powell, 1967
;
Johnson, 1967
;
Madsen et al., 2005
;
Morozov et al., 1972
). Goodson
and colleagues (Goodson et al.,
1994
) investigated the echolocation behaviour of a solitary
bottlenose dolphin during foraging. They recorded a rapid increase in
repetition rate (the inverse of the click interval) preceding the final and
nearly constant high repetition rate of the buzz and interpreted this as
range-locking behaviour on the prey during the approach. According to this
assumption one can calculate a swim speed of 12.6 m s–1 or 45
km h–1 from the change in click interval. This speed is
unlikely during prey capture. Therefore we assume that the shortening of the
click interval corresponds to the beginning of the terminal part of the
approach phase and does not indicate range locking on the prey.
Two possible processing modes in the approach phase
The lag time, corresponding to the available time to process a click-echo
pair before emitting the next click, is calculated as the difference between
click interval and the two-way transit time. The distinct shortening of the
lag time at the transition from the initial part to the terminal part of the
approach phase may indicate a change in information processing mechanisms for
the estimation of range. In the initial part of the approach phase where the
porpoise is in the far stage (see Fig.
5C; Fig 6B) the lag
time is sufficiently long for the porpoise to process the range information in
each click–echo pair. With each new click the porpoise gets new distance
information. This type of information processing is termed the pulse-mode by
Au and Nachtigall (Au and Nachtigall,
1997
).
The constant mean click interval during the initial part of the approach (Fig. 6B; Fig. 7A) inevitably results in an increase of lag time. In our experiments the lag time doubles on average from about 24 to 48 ms if we assume an initial part to begin at 20 m and end at 1 m. This increase in lag time provides more time for information processing of click–echo pairs.
The terminal part of the approach begins with an abrupt and continued
shortening of the click interval. The fast reduction of click interval during
the final approach to the prey causes a continuous decrease of the lag time
down to values below 1.5 ms at click intervals of 1.5 ms when the prey is
reached. This strong reduction probably does not leave enough time for
pulse-mode echo processing. Therefore we assume that odontocetes use another
processing mode at these short lag times. Nordmark
(Nordmark, 1960
) suggested
that bats perceive pulse–echo trains with a changing time delay as a
kind of tone changing in pitch corresponding to the inverse of the delay
between pulse and echo. Thus this pitch would encode the two-way transit time.
For our porpoises the terminal phase began at distances to the fish of between
4.4 and 1.9 m. This would give average two-way transit times of 5.9–2.5
ms, which would correspond to a pitch frequency of 170–395 Hz. Close to
the prey at a distance of 37.5 cm and a two-way transit time of 0.5 ms the
corresponding pitch would be at 2000 Hz. We assume that dolphins can estimate
range by evaluating this increase in pitch with decreasing distance to the
target. We call this possible processing mode at short lag times the
pitch-mode. In this mode the sound pressure level of the clicks in the buzz is
low, therefore only a close object will return echoes strong enough for
processing. Whether porpoises perceive echo information during the terminal
phase as a two-way transit time pitch is not known and future investigations
are necessary to test this hypothesis.
Swim speed
Our data also reveal that the swim speed is task dependent. The porpoises
swam much faster when looking for fish. During no fish trials (6 m
s–1) the speed was double that during navigational tasks (3 m
s–1). A high swim speed was also used during fish trials.
Eigil clearly raised his swim speed after the splash in trials with and
without fish (Fig. 3B), which
suggests that Eigil connects the splash with a fish thrown into the water.
Another indication that the porpoises anticipate a fish in connection with the
splash is the clear scanning movements of Freja when blindfolded that start
near the release area, presumably a sign of searching for the fish. Eigil
increased his swim speed in fish trials later than in no fish trials perhaps
due to the delayed production of the splashes in fish trials compared with no
fish trials. This would explain the significantly lower mean speed (5.4 m
s–1) of Eigil in fish trials
(Fig. 3A;
Table 1). A swim speed of 6.2 m
s–1 was recorded from a wild harbour porpoise that was
presumed to be foraging (Lucke et al.,
2000
).
The influence of blindfolding
Freja uses the same echolocation pattern during foraging when blindfolded
with eyecups. She keeps similar click intervals and lag times during the
search and the initial and the final part of the approach compared with trials
with no eyecups (Fig. 4;
Fig. 5;
Fig. 6B;
Table 1). However, she swims
about half as fast with eyecups on than she does without
(Fig. 3A), which results in a
longer foraging sequence. Thus the click density doubles, increasing the
information gained per metre covered (Table
1). These results suggest that Freja uses multi-modal sensory
information, vision and echolocation, when possible during searching and the
initial part of the approach. In trials with Freja being blindfolded, we saw a
rapid increase in click interval near the middle of the pool
(Fig. 4B;
Fig. 5A;
Fig. 6A) and significantly
shorter lag times (calculated in relation to the reference point) during no
fish trials compared with no fish trials where she was not wearing eyecups
(Table 1). This suggests that
when blindfolded Freja is using landmarks that are closer to her for
orientation than the arbitrary reference point during search. She also seems
to use more landmarks when blindfolded. Perhaps she `feels her way'
acoustically through the pool when vision is lacking. Then again the eyecups
might just make Freja feel more insecure, resulting in a slower swim speed. We
have not done prey capture experiments in total darkness to test this.
| Footnotes |
|---|
| References |
|---|
|
|
|---|
Akamatsu, T., Wang, D., Wang, K. and Naito, Y.
(2005). Biosonar behaviour of free-ranging porpoises.
Proc. Biol. Sci. 272,797
-801.
Akamatsu, T., Teilmann, J., Miller, L. A., Tougaard, J., Dietz, R., Wang, D., Wang, K., Siebert, U. and Naito, Y. (2007). Comparison of echolocation behaviour between coastal and riverine porpoises. Deep Sea Res. Part II Top. Stud. Oceanogr. 54,290 -297.[CrossRef]
Amundin, M. and Andersen, S. H. (1983). Bony
nares air pressure and nasal plug muscle activity during click production in
the harbour porpoise, Phocoena phocoena, and the bottlenosed dolphin,
Tursiops truncatus. J. Exp. Biol.
105,275
-282.
Andersen, S. H. and Amundin, M. (1976). Possible predator-related adaptation of sound production and hearing in the harbour porpoise (Phocoena phocoena). Aquat. Mamm. 4,56 -57.
Astrup, J. (1999). Ultrasound detection in fish-a parallel to the sonar-mediated detection of bats by ultrasound-sensitive insects? Comp. Biochem. Physiol., Part A Mol. Integr. Physiol. 124,19 -27.[CrossRef][Medline]
Astrup, J. and Møhl, B. (1993). Detection of intense ultrasound by the cod Gadus Morhua. J. Exp. Biol. 182,71 -80.[Abstract]
Astrup, J. and Møhl, B. (1998). Discrimination between high and low repetition rates of ultrasonic pulses by the cod. J. Fish Biol. 52,205 -208.[CrossRef]
Au, W. W. L. (1993). The Sonar of Dolphins. New York: Springer.
Au, W. W. L. and Nachtigall, P. E. (1997). Acoustics of echolocating dolphins and small whales. Mar. Freshwater Physiol. Behav. 29,127 -162.[CrossRef]
Au, W. W. L., Kastelein, R. A., Rippe, T. and Schooneman, N. M. (1999). Transmission beam pattern and echolocation signals of a harbour porpoise (Phocoena phocoena). J. Acoust. Soc. Am. 106,3699 -3705.[CrossRef][Medline]
Barrett-Lennard, L. G., Ford, J. K. B. and Heise, K. A. (1996). The mixed blessing of echolocation: differences in sonar use by fish-eating and mammal-eating killer whales. Anim Behav. 51,553 -565.[CrossRef]
Beedholm, K. and Miller, L. A. (2007). Automatic gain control in harbor porpoises (Phocoena phocoena)? Central versus peripheral mechanisms. Aquat. Mamm. 33, 69-75.[CrossRef]
Brill, R. L., Sevenich, M. L., Sullivan, T. J., Sustman, J. D. and Witt, R. E. (1988). Behavioral evidence for hearing through the lower jaw by an echolocating dolphin (Tursiops truncatus). Mar. Mamm. Sci. 4, 223-230.[CrossRef]
Busnel, R.-G. and Dziedzic, A. (1967). Resultants metrologiques experimentaux de l'echolocation chez le Phocaena phocaena et leur comparaison avec ceux de certaines chauves-souris. In Animal Sonar System, Biology and Bionics (ed. R.-G. Busnel), pp. 307-356. Jouy-en-Josas: Laboratoire de Physiologie Acoustique.
Canfield, J. G. and Eaton, R. C. (1990). Swimbladder acoustic pressure transduction initiates Mauthner-mediated escape. Nature 347,760 -762.[CrossRef]
Cranford, T. W. and Amundin, M. (2004). Biosonar pulse production in odontocetes: the state of our knowledge. In Echolocation in Bats and Dolphins (ed. J. A. Thomas, C. F. Moss and M. Vater), pp. 27-35. Chicago, IL: The University of Chicago Press.
Cranford, T. W., Amundin, M. and Norris, K. S. (1996). Functional morphology and homology in the odontocete nasal complex: implications for sound generation. J. Morphol. 228,223 -285.[CrossRef][Medline]
Eaton, R. C., Hofve, J. C. and Fetcho, J. R. (1995). Beating the competition: the reliability hypothesis for Mauthner axon size. Brain Behav. Evol. 45,183 -194.[Medline]
Evans, W. E. and Powell, B. A. (1967). Discrimination of different metallic plates by an echolocating delphinid. In Animal Sonar Systems: Biology and Bionics (ed. R. G. Busnel), pp. 363-382. Jouy-en-Josas: Laboratoire de Physiologie Acoustique.
Finsterwalder, R. and Hofmann, W. (1968). Photogrammetrie. Berlin: Walter de Gruyter.
Goodson, A. D., Klinowska, M. and Morris, R. (1988). Interpreting the acoustic pulse emissions of a wild bottlenose dolphin (Tursiops truncatus). Aquat. Mamm. 14,7 -12.
Goodson, A. D., Klinowska, M. and Bloom, P. R. S. (1994). Enhancing the acoustic detectability of gillnets. In Gillnets and Cetaceans (ed. W. F. Perrin, G. P. Donovan and J. Barlow), pp. 585-595. Cambridge: Black Bear Press.
Goodson, A. D., Flint, J. A. and Cranford, T. W. (2004). The harbour porpoise (Phocoena phocoena) modeling the sonar transmission mechanism. In Echolocation in Bats and Dolphins (ed. J. A. Thomas, C. F. Moss and M. Vater), pp.64 -85. Chicago, IL: The University of Chicago Press.
Griffin, D. R. (1958). Listening in the Dark. New Haven, CT: Yale University Press.
Griffin, D. R., Webster, F. A. and Michael, C. R. (1960). The echolocation of flying insects by bats. Anim Behav. 8,141 -154.[CrossRef]
Herzing, D. L. (2004). Social and nonsocial uses of echolocation in free-ranging Stenella frontalis and Tursiops truncatus. In Echolocation in Bats and Dolphins (ed. J. A. Thomas, C. F. Moss and M. Vater), pp.404 -410. Chicago, IL: The University of Chicago Press.
Jensen, M. E. and Miller, L. A. (1999). Echolocation signals of the bat Eptesicus serotinus recorded using a vertical microphone array: effect of flight altitude on searching signals. Behav. Ecol. Sociobiol. 47, 60-69.[CrossRef]
Johnson, C. S. (1967). Discussion. In Animal Sonar Systems: Biology and Bionics (ed. R. G. Busnel), pp. 384-398. Jouy-en-Josas: Laboratoire de Physiologie Acoustique.
Johnson, M., Madsen, P. T., Zimmer, W. M. X., Aguilar de Soto,
N. and Tyack, P. L. (2004). Beaked whales echolocate on prey.
Proc. Biol. Sci. 271 Suppl.
6, S383-S386.
Johnson, M., Madsen, P. T., Zimmer, W. M. X., Aguilar de Soto,
N. and Tyack, P. L. (2006). Foraging Blainville's beaked
whales (Mesoplodon densirostris) produce distinct click types matched
to different phases of echolocation. J. Exp. Biol.
209,5038
-5050.
Johnson, M., Hickmott, L. S., Soto, N. A. and Madsen, P. T.
(2008). Echolocation behaviour adapted to prey in foraging
Blainville's beaked whale (Mesoplodon densirostris). Proc.
Biol. Sci. 275,133
-139.
Jones, B. A., Stanton, T. K., Lavery, A. C., Johnson, M. P., Tyack, P. and Madsen, P. T. (2008). Classification of broadband echoes from prey of a foraging Blainville's beaked whale. J. Acoust. Soc. Am. 123,1753 -1762.[CrossRef][Medline]
Kalko, E. K. V. and Schnitzler, H.-U. (1989). The echolocation and hunting behavior of Daubenton's bat, Myotis daubentoni. Behav. Ecol. Sociobiol. 24,225 -238.[CrossRef]
Kalko, E. K. V. and Schnitzler, H. U. (1993). Plasticity in echolocation signals of European pipistrelle bats in search flight: implications for habitat use and prey detection. Behav. Ecol. Sociobiol. 33,415 -428.
Kalko, E. K. V. and Schnitzler, H. U. (1998). How echolocating bats approach and acquire food. In Bat Biology and Conservation (ed. T. H. Kunz and P. A. Racey), pp.197 -204. Washington DC: Smithsonian Institution Press.
Kastelein, R., Schooneman, N. M., Au, W. W. L., Verboom, W. C. and Vaughan, N. (1997). The ability of a harbour porpoise (Phocoena phocoena) to discriminate between objects buried in sand. In The Biology of the Harbour Porpoise (ed. A. J. Read, P. R. Wiepkema and P. E. Nachtigall), pp.329 -342. Woerden, The Netherlands: De Spil.
Kastelein, R. A., Au, W. W. L., Rippe, H. T. and Schooneman, N. M. (1999). Target detection by an echolocating harbour porpoise (Phocoena phocoena). J. Acoust. Soc. Am. 105,2493 -2498.[CrossRef][Medline]
Ketten, D. R. (2004). Marine mammal auditory systems: a summary of audiometric and anatomical data and implications for underwater acoustic impacts. In Polarforschung 2/3 (ed. D. K. Fütterer), pp. 79-92. Bremerhaven: Deutsche Gesellschaft für Polarforschung e.V.
Lucke, K., Wilson, R., Teilmann, J., Zankl, S., Adelung, D. and Siebert, U. (2000). Advances in the elucidation of cetacean behaviour: a case study on a harbour porpoise (Phocoena phocoena). In The Behaviour and Sensory Abilities of Harbour Porpoises (Phocoena phocoena) in Relation to Bycatch in Gillnet Fishery (ed. J. Teilmann), pp. 87-105. Odense: University of Southern Denmark, Center for Sound Communication, Institute of Biology.
Madsen, P. T., Payne, R., Kristiansen, N. U., Wahlberg, M.,
Kerr, I. and Møhl, B. (2002). Sperm whale sound
production studied with ultrasound time/depth-recording tags. J.
Exp. Biol. 205,1899
-1906.
Madsen, P. T., Johnson, M., Aguilar de Soto, N., Zimmer, W. M.
X. and Tyack, P. L. (2005). Biosonar performance of foraging
beaked whales (Mesoplodon densirostris). J. Exp.
Biol. 208,181
-194.
Mann, D. A., Lu, Z., Hastings, M. C. and Popper, A. N. (1998). Detection of ultrasonic tones and simulated dolphin echolocation clicks by a teleost fish, the American shad (Alosa sapidissima). J. Acoust. Soc. Am. 104,562 -568.[CrossRef][Medline]
Mann, D. A., Higgs, D. M., Tavolga, W. N., Souza, M. J. and Popper, A. N. (2001). Ultrasound detection by clupeiform fishes. J. Acoust. Soc. Am. 101,3045 -3054.
McCullagh, P. and Nelder, J. A. (1991). Generalized Linear Models. London: Chapman & Hall.
Melcón, M. L., Denzinger, A. and Schnitzler, H.-U.
(2007). Aerial hawking and landing: approach behaviour in
Natterer's bats, Myotis nattereri (Kuhl 1818). J. Exp.
Biol. 210,4457
-4464.
Miller, L. A. and Surlykke, A. (2001). How some insects detect and avoid being eaten by bats: Tactics and countertactics of prey and predator. Bioscience 51,570 -581.[CrossRef]
Miller, L. A., Pristed, J., Møhl, B. and Surlykke, A. (1995). The click-sounds of narwhals (Monodon monoceros) in Inglefield Bay, Northwest Greenland. Mar. Mamm. Sci. 11,491 -502.[CrossRef]
Miller, P. J. O., Johnson, M. P. and Tyack, P. L.
(2004). Sperm whale behaviour indicates the use of echolocation
click buzzes "creaks" in prey capture. Proc. Biol.
Sci. 271,2239
-2247.
Morisaka, T. and Connor, R. C. (2007). Predation by killer whales (Orcinus orca) and the evolution of whistle loss and narrow-band high frequency clicks in odontocetes. J. Evol. Biol. 20,1439 -1458.[CrossRef][Medline]
Morozov, V. P., Akopian, A. I., Burdin, V. I., Zaitseva, K. A. and Sokovykh, Y. A. (1972). Tracking frequency of the location signals of dolphins as a function of distance to the target. Biofizika 17,139 -145.[Medline]
Neuweiler, G. (1983). Echolocation and adaptivity to ecological constraints. In Neuroethology and Behavioral Physiology (ed. F. Huber and H. Markl), pp.280 -302. Berlin: Springer-Verlag.
Nordmark, J. (1960). Perception of distance in animal echo-location. Nature 188,1009 -1010.[CrossRef][Medline]
Pinheiro, J. C. and Bates, D. M. (2000). Mixed-Effects Models in S and S-PLUS. New York: Springer.
Plachta, D. T. T. and Popper, A. N. (2003). Evasive responses of American shad (Alosa sapidissima) to ultrasonic stimuli. Acoust. Res. Lett. Online. 4, 25-30.[CrossRef]
Popper, A. N. and Fay, R. R. (1995). Hearing by Bats. New York: Springer.
R Development Core Team (2007). R: A Language and Environment for Statistical Computing. Vienna: R Foundation for Statistical Computing, http://www.r-project.org.
Santos, M. B., Martin, V., Arbelo, M., Fernández, A. and Pierce, G. J. (2007). Insights into the diet of beaked whales from the atypical mass stranding in Canary Islands in September 2002. J. Mar. Biol. Assoc. UK 87,243 -251.[CrossRef]
Schack, H. B., Malte, H. and Madsen, P. T.
(2008). The responses of Atlantic cod (Gadus morhua) to
ultrasound emitting predators: stress, behavioural changes or debilitation?
J. Exp. Biol. 211,2079
-2086.
Schnitzler, H. U. (1967). Discrimination of thin wires by flying horseshoe bats (Rhinolophidae). In Animal Sonar System, Biology and Bionics (ed. R. G. Busnel), pp. 69-87. Jouy-en-Josas: Laboratoire de Physiologie Acoustique.
Schnitzler, H. U. and Kalko, E. K. V. (1998). How echolocating bats search and find food. In Bat Biology and Conservation (ed. T. H. Kunz and P. A. Racey), pp.183 -196. Washington, DC: Smithsonian Institution Press.
Schnitzler, H. U., Moss, C. F. and Denzinger, A. (2003). From spatial orientation to food acquisition in echolocating bats. Trends Ecol. Evol. 18,386 -394.[CrossRef]
Schwidefsky, K. and Ackermann, F. (1976). Photogrammetrie. Grundlagen, Verfahren, Anwendungen. Stuttgart: Teubner.
Simon, M., Wahlberg, M. and Miller, L. A. (2007). Echolocation clicks from killer whales (Orcinus orca) feeding on herring (Clupea harengus) (L). J. Acoust. Soc. Am. 121,749 -752.[CrossRef][Medline]
Sokal, R. R. and Rohlf, F. J. (1995). Biometry: The Principles and Practice of Statistics in Biological Research. New York: Freeman.
Surlykke, A., Miller, L. A., Møhl, B., Andersen, B. B., Christensen-Dalsgaard, J. and Jorgensen, M. B. (1993). Echolocation in two very small bats from Thailand: Craseonycteris thonglongyai and Myotis siligorensis. Behav. Ecol. Sociobiol. 33,1 -12.[Medline]
Thomas, J. A., Moss, C. F. and Vater, M. (2004). Echolocation in Bats and Dolphins. Chicago: University of Chicago Press.
Verfuß, U. K. and Schnitzler, H.-U. (2002). F+E Vorhaben: Untersuchungen zum Echoortungsverhalten der Schweinswale (Phocoena phocoena) als Grundlage für Schutzmaßnahmen. FKZ-Nr.: 898 86 021. Tübingen: Universität Tübingen.
Verfuß, U. K., Miller, L. A. and Schnitzler, H. U.
(2005). Spatial orientation in echolocating harbour porpoises
(Phocoena phocoena). J. Exp. Biol.
208,3385
-3394.
Verfuß, U. K., Honnef, C. G., Meding, A., Dähne, M., Adler, S., Kilian, A. and Benke, H. (2008). The history of the German Baltic Sea harbour porpoise acoustic monitoring at the German Oceanographic Museum. In Marine Mammals and Seabirds in Front of Offshore Wind Energy, MINOS: Marine warm-blooded animals in North and Baltic Seas (ed. K. Wollny-Goerke and K. Eskildsen), pp.41 -56. Wiesbaden: Teubner Verlag.
Wilson, M., Hanlon, R. T., Tyack, P. L. and Madsen, P. T.
(2007). Intense ultrasonic clicks from echolocating toothed
whales do not elicit anti-predator responses or debilitate the squid
Loligo pealeii. Biol. Lett.
3, 225-227.
Zuur, A. F., Ieno, E. N. and Smith, G. M. (2007). Analysing Ecological Data. New York: Springer.
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