University of Groningen
Predator escape tactics in birds
van den Hout, Piet J.; Mathot, Kimberley J.; Maas, Leo R. M.; Piersma, Theunis
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Behavioral Ecology
DOI:
10.1093/beheco/arp146
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van den Hout, P. J., Mathot, K. J., Maas, L. R. M., & Piersma, T. (2010). Predator escape tactics in birds:
linking ecology and aerodynamics. Behavioral Ecology, 21(1), 16-25.
https://doi.org/10.1093/beheco/arp146
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Behavioral Ecology
doi:10.1093/beheco/arp146
Advance Access publication 5 November 2009
Predator escape tactics in birds: linking ecology
and aerodynamics
Piet J. van den Hout,a Kimberley J. Mathot,b Leo R.M. Maas,c and Theunis Piersmaa,d
Department of Marine Ecology, Royal Netherlands Institute for Sea Research, PO Box 59, 1790 AB Den
Burg, Texel, The Netherlands, bGroupe de Recherche en Écologie Comportementale et Animale,
Département des sciences biologiques, Université du Québec à Montréal, Case postale 8888, Succursale
Centre-ville, Montréal, Québec, H3C 3P8, Canada, cDepartment of Physical Oceanography, Royal
Netherlands Institute for Sea Research, PO Box 59, 1790 AB Den Burg, Texel, The Netherlands, and
d
Animal Ecology Group, Centre for Ecological and Evolutionary Studies, University of Groningen,
PO Box 14, 9750 AA Haren, The Netherlands
a
H
unting and escape strategies of predators and prey are
probably the result of a coevolutionary arms race
(Dawkins 1999). Yet, this interaction is asymmetric. An individual prey has more to lose by failure to avoid a predator
than predators by failing to catch a prey. Therefore, selection
pressures to avoid being killed should be particularly strong
for prey species.
Animals respond to approaching predators in many ways.
They can startle the predator, stand their ground, crouch
and stay put, or fly off (Caro 2005). For most birds, flight is
the predominant escape mode. A reduction of speed or maneuverability is likely to increase the chance of being depredated once airborne (Howland 1974; Witter et al. 1994).
Although it has become widely acknowledged that escape
flight performance is influenced both by the muscle power
available for fast forward flight and movements and by wing
loading (i.e., the body mass [BM]/wing surface ratio) (Howland 1974; Hedenström and Alerstam 1992; Hedenström and
Rosén 2001; Videler 2005), most experimental studies to date
have investigated the effect of wing loading on flight performance without measuring possible compensation for flight
capacity by changes in pectoral muscle size (Lima and Valone
1986; Witter et al. 1994; Gosler et al. 1995; Lima 1995;
Kullberg et al. 1996, 2002; Lilliendahl 1997, 2000; Carrascal
and Polo 1999; Burns and Ydenberg 2002; but see Lind 2001).
However, there is evidence that compensation for flight
capacity changes are possible: During migration, birds have
been shown to adjust the size and capacity of specific body
parts (Piersma and Drent 2003) including rapid reversible
adjustments of pectoral muscle relative to BM levels
Address correspondence to P.J. van den Hout. E-mail: piet.van.den
.hout@nioz.nl.
Received 7 April 2009; revised 10 September 2009; accepted 23
September 2009.
The Author 2009. Published by Oxford University Press on behalf of
the International Society for Behavioral Ecology. All rights reserved.
For permissions, please e-mail: journals.permissions@oxfordjournals.org
(Lindström et al. 2002; Dietz and Piersma 2007). Furthermore, by experimentally inducing molt gaps, Lind and
Jakobsson (2001) demonstrated that pectoral muscle size
and BM can be independently regulated in response to wing
loading. Such fine-tuning can additionally be influenced by
predation danger (van den Hout et al. 2006).
When discussing body composition adjustments to predation danger, we must distinguish between, on the one hand,
the mode of adjustment (adjustment in either overall BM or
pectoral muscle mass [PMM], or a combination of both)
and, on the other hand, the sensitivity to fuel load in terms
of predation costs, that is, the extent to which a decrease in
flight performance affects predation danger. Although a
change in mass components may be advantageous in terms
of flight performance, it will involve costs. For instance, a reduction in BM, though improving flight performance, also
increases the risk of starvation (McNamara and Houston
1990; Witter and Cuthill 1993). Therefore, responses to predation threat are expected to reflect a trade-off between the
benefits and costs of changes in BM components (Witter et al.
1995). The amount of energy stores that a bird is willing to
sacrifice may depend on the predation costs that the corresponding extra BM would entail. Predation costs include the
extent to which the negative impact of fuel load on flight
performance affects survival probability. Lind (2004) argued
that the importance of flight performance for predation danger increases as the distance from protective cover increases
because small increases in wing loading have little effect on
escape chances on such small distances. Generally, massdependent predation costs may be lower for species that can
feed close to protective cover than for species that forage in
areas devoid of protective cover (Dierschke 2003; Lank and
Ydenberg 2003).
Birds living in open habitats, on mudflats for example, may
be particularly sensitive to fuel load in terms of predation costs.
For such habitats, vegetation and other topographical
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In most birds, flight is the most important means of escape from predators. Impaired flight abilities due to increased wing
loading may increase vulnerability to predation. To compensate for an increase in wing loading, birds are able to independently
decrease body mass (BM) or increase pectoral muscle mass (PMM). Comparing nearshore and farshore foraging shorebird
species, we develop a theory as to which of these responses should be the most appropriate. We hypothesize that nearshore
foragers should respond to increased predation by increasing their PMM in order to promote speed-based escape. Instead,
farshore foragers should decrease BM in order to improve agility for maneuvering escape. Experiments on 2 shorebird species
are consistent with these predictions, but on the basis of the theoretical framework for evaluating effect size and biological
significance developed here, more experiments are clearly needed. Key words: aerodynamics, body mass, escape performance,
flight, pectoral muscle, phenotypic flexibility, raptors, risk management. [Behav Ecol 21:16–25 (2010)]
van den Hout et al.
•
Escape from predator attack
Escape scenarios: linking ecology and aerodynamics
The difference between nearshore and farshore escapers is
best explained by considering 2 major generalizations based
on the relative position of prey and predator, speed vectors between prey and predator when the prey detects the predator
(Hedenström and Rosén 2001), and escape destination (Lima
1993).
Nearshore foragers
Shorebird species that tend to forage in the close vicinity of
obstructive cover are often confronted with predators at close
range as the physical properties of the habitat supply the predator with opportunities for undetected approach (Metcalfe
1984). Individuals aiming to reach a safe destination, such
as water or salt marsh, require a speed-based accelerating escape (linear maneuverability) in order to reach that destination before the predator strikes. Such speed-based locomotion
requires the ability of generating a high velocity of shortening
in the locomotor muscles (Kumagai et al. 2000), whereas an
increase of such speed-based escape abilities would call for
a build up of fast-twitch muscle fibers (Rosser and George
1986). Such bird species are expected to respond to predation
danger by PMM increase, which allows them to save on energy
stores.
Measures for wing shape in this context include aspect ratio
(wing span2/wing area) (Warrick 1998; Hedenström and
Rosén 2001) and wingtip pointedness/roundedness and convexity (Monkkonen 1995; Lockwood et al. 1998; Burns and
Ydenberg 2002). The 2 measures are related: wing pointedness results in a high aspect ratio (Norberg 1989). Bird species
employing speed-based escape are expected to have relatively
low aspect wing ratios as the inertia of high aspect ratio wings
(which increases with the square of their length) may compromise the mass-specific power output generated by wing
flapping (Warrick 1998). Likewise, such bird species may have
rounder wingtips, which are said to maximize thrust from
flapping wings (Rayner 1993). Additionally, rounded wings
produce relatively more lift toward the wingtip where the wing
is moving faster but also more drag. These factors are likely to
enhance flight performance at low speeds, particularly at takeoff from the ground and maneuverability by differential wing
flapping (Swaddle and Lockwood 1998; Warrick et al. 1998).
Farshore foragers
The essential difference between the escape context of farshore and nearshore foragers is the distance between prey
Figure 1
Photographic illustration of fast pure rotational banks by dunlins
Calidris alpina chased by a peregrine falcon Falco peregrinus. Note that
neither of the birds shows the flapping velocity asymmetries (see
text). Instead, pronation/supination of the wing is apparent in most
of the birds, particularly by the 2 closely paralleled birds in the lower
middle of the picture. The photo, found on the World Wide Web, was
taken by an anonymous photographer.
and predator at the time the prey detects the predator. Farshore foragers typically avoid foraging near obstructive cover
(Rudebeck 1950–1951; Brown and Kotler 2007). This allows
birds to detect an approaching predator from a relatively
large distance, permitting relatively early take-off, and time
to gain speed and prepare maneuvers. Gregariousness has
additional advantages in this scenario as high levels of vigilance (‘‘many eyes’’) combined with an unobstructed view of
the horizon increases the chance of early detection (Krause
and Ruxton 2002) and provides time to recruit flock members
for a socially coordinated escape. Calidrid species (sandpipers) (Figure 1) are well-known for such united, erratic
display flights to form flocks which appear to pulsate and
maneuver as one organism (Rudebeck 1950–1951; Lima
1993), but time lags between detection and encounter with
the predator allow even relatively solitary foragers to team up
with such ‘‘escape units’’ (P.J.H., personal observation).
In such a scenario, turning maneuverability, rather than linear maneuverability, may be of paramount importance. Studies
that focus on maneuverability commonly address low-speed
maneuvering (Warrick and Dial 1998; Warrick et al. 1998),
and less is known about flight maneuvers that are initiated
at high speed. Warrick and Dial (1998) argue that at high
speeds, birds can exploit the acquired lift forces to produce
angle of attack asymmetries immediately, without preparation
(i.e., an upstroke). High aspect ratio wings are most suitable
for such maneuvers. ‘‘In addition,’’ they write, ‘‘by not driving
the wings through a downstroke while pronating/supinating,
the bird directs most of the lift on the outside wing perpendicular to the roll axis and could theoretically produce negative angles of attack on the inside wing. The result would be
a pure rotation bank, with the bird rolling around its center of
mass at high angular accelerations.’’ This would mean that, at
higher speeds, birds can economize on muscle power for wing
flapping, exploiting lift forces for turns. This is what the sandpipers in Figure 1 seem to do. At these high speeds, lift forces
on the hand wing are the dominant forces as further from the
center of gravity lever effects on the roll control will be stronger (Videler 2005). Now, inertia properties of the flight frame
put limits on the turning radii, which the birds can perform
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structures are not perceived as safe havens, but rather as obstructive cover, as these allow an undetected approach by predators (Piersma et al. 1993; Cresswell 1996). Vertical habitat
structures will generally be avoided (Zwarts 1988; Rogers
et al. 2006). However, due to their foraging specializations,
some species are forced to forage close to the shoreline, where
dunes, dikes, or vegetation obstruct their view of the horizon
(Metcalfe 1984).
In this paper, we compare these nearshore and farshore foraging species. Using aerodynamic theory, we predict differences in their responses to predation in terms of BM and PMM.
We also predict that species-specific morphological responses
to predation are not only related to their escape tactic and
related ecologies but may also be reflected in flight frame characteristics. Finally, we discuss molt, given that gaps in the wing
affect wing loading and may influence the perception of predation danger (Lind 2001), and thus mediate phenotypic
responses to predation threat. A brief description of how
the predictions can be tested will be followed by a discussion
of the results of such an experiment.
17
Behavioral Ecology
18
In the vertical direction, the force of gravity, Mg (g denoting
the acceleration of gravity), is balanced by the upward directed component of the lift force:
Mg ¼ LcosU:
ð2Þ
2
2
Using the trigonometric relation cos U 1 sin U ¼ 1, this
yields
M 2 g2 M 2 v4
1 2 2 ¼ 1;
L2
L r
ð3Þ
Solving for the radius r yields:
r ¼ v2 L2 M 2 2 2 g2
2 1=2
ð4Þ
Now, the lift force induced by flow around the wing is itself
proportional to the squared velocity
1
L ¼ qv2 SCl ;
2
ð5Þ
where q ¼ density of air at sea level ¼ 1.23 kg/m3, S ¼ wing
surface area, and Cl ¼ lift coefficient ¼ 0.5 (Hedenström and
Rosén 2001). Defining proportionality constant a (kgm21)
qSCl
;
2
ð6Þ
L ¼ av2 :
ð7Þ
a¼
we have
Inserting this into the expression for the radius, we find
r ¼
v2
a2 v4 M 2 2 g2
Therefore, for large velocities,
1=2 :
ð8Þ
limv/N rðvÞ ¼ limv/N
a2 v4
v2
M
1=2 ¼ a ;
2
2
M 2g
ð9Þ
the radius approaches its minimum, rmin ¼ M/a, which clearly
decreases with decreasing BM M. We will illustrate these calculations when discussing our experiments.
Howland (1974) explains that at some high velocity an additional effect must set in, namely that of a limit to the centrifugal acceleration that a bird can withstand. Given that the
animal is moving sufficiently fast that this limit is reached,
then for every increase in velocity it must also increase its
turning radius in proportion to the square of its velocity in
order to stay within the limit of constant centrifugal acceleration (in general the lift of a wing will be proportional to the
square of the velocity at which the bird moves). Above a certain level, speed will be lost at the expense of turning radius.
This constraint can be counteracted by BM decrease.
In conclusion, we predict nearshore foragers to be generally
speed-based escapers that respond to increased predation pressure by PMM increase. Farshore foragers are predicted to be
agility-based escapers that respond to increased predation
threat by a decrease in general BM.
Based on a comparative literature study among passerines,
Swaddle and Lockwood (1998) concluded that species with
relatively rounded wingtips and relatively short femora compared with tarsi were at a lower predation risk than species
with more pointed wingtips and relatively longer femora.
Burns and Ydenberg (2002) proposed that habitat-related
escape tactics in 2 closely related Calidrid species may have
contributed to differences in both wing and hind limb morphologies between the 2 species. Yet, they rightfully acknowledge that wing shape likely evolved under multiple, and
possibly conflicting, selection pressures, related to predation, migration, reproduction (display flight), and foraging.
For instance, it has been argued that the demands of migration may have set the stage for the high aspect ratio wings of
many long-distance migrants, whereas special foraging techniques may have contributed to differences in wing shapes
between coursing and hawking insectivorous bird species
(Warrick 1998). Thus, differences in wing shape due to
escape tactics may be subtle. We predict that speed-based
escapers have relatively low aspect ratio, or relatively
rounded wings, whereas socially coordinated escapers are
predicted to have relatively high aspect ratio or relatively
pointed wings. Finally, molt gaps decrease wing surface thus
increasing wing loading. As this will decrease escape flight
performance thereby increasing vulnerability to predation,
compensatory measures are expected to be similarly associated to the birds’ ecologies.
A first test of the predictions
Small flocks of birds may be randomly exposed to simulated
predator attacks, for instance by gliding a raptor model overhead. BM (using a balance) and pectoral muscle thickness
(PMT) (using ultrasonography) (Dietz et al. 1999a) may be
measured before and after the experiment, limiting disturbance effects by the researcher as much as possible. To examine possible relationships between escape tactic and responses
in pectoral muscle and BM, such experiments could be performed with different similar-sized species, with different ecologies (nearshore/farshore foragers). There are a number of
shorebird species that typically forage in nearshore areas, such
as rocky shores and sandy beaches (e.g., whimbrel Numenius
phaeopus, black turnstone Arenaria melanocephala, ruddy turnstone Arenaria interpres, purple sandpiper Calidris maritima,
sanderling Calidris alba, rock sandpiper Calidris ptilocnemis,
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when escaping from a predator. This means that through a decrease in BM alone, birds can decrease turning radii. This can
be mathematically demonstrated using aerodynamic theory as
follows.
Steady flight in still air requires balanced forces where lift
equals weight and thrust equals drag, as well as balanced
moments of these forces about the center of gravity (Videler
2005). Warrick et al. (1998) describe that for a bird to change
direction in a steady state turn (i.e., continuous lift production and nonflapping wings) it requires an initiating force
asymmetry, followed by an arresting force asymmetry. Disparate forces produced by the wings cause the bird to roll into
a bank (wings making an angle U to the horizontal), redirecting lift toward the desired direction of flight. Then, the initial
force asymmetry must be reversed to halt the rolling momentum. Now, the bird turns at a constant rate, and no further
force asymmetry is needed to maintain the bank once it has
been established. We express the balanced forces in the vertical transversal plane acting on a bird that initiates a gambit
by pronation/supination of the wings, thus engaging in a pure
rotation bank and demonstrate that the turning capabilities
are dominated by BM. We take equation 2 from Hedenström
and Rosén (2001) as a starting point (Equation 1). This shows
how to compute turning radius, r, of a bird circling with azimuthal velocity, v, from the radial forces acting on the bird.
These are the inward directed component LsinU of the lift
force L which balances the outward directed centrifugal force
Mv2/r, where M denotes BM. This leads to
Mv2
:
ð1Þ
r¼
L sin U
van den Hout et al.
•
Escape from predator attack
surfbird Aphrizia virgata, common sandpiper Actitis hypoleucos,
spotted sandpiper Actitis macularia, and a number of Charadrius plovers). Others are more typical of open areas, such as
red knot Calidris canutus, dunlin Calidris alpina, and western
sandpiper Calidris mauri.
We performed such an experiment in the indoor Experimental Shorebird Facility at the Royal Netherlands Institute
for Sea Research (NIOZ) with red knots (a farshore forager
species) and compared this to a similar experiment (same facility, similar setup) with ruddy turnstones (a nearshore forager
species) (van den Hout et al. 2006). We examined BM and
PMT changes in response to exposure to a model predator.
We only describe the methods of the red knot experiment,
referring to van den Hout et al. (2006) for the turnstone
experiment.
MATERIALS AND METHODS
model accompanied by digital playback of wader alarm calls.
This event lasted about 5 s. The stuffed model glided across
one side of the indoor mudflat, passing over the food tray
(see Mathot et al. 2009). The second event type involved presenting a model of a perched sparrowhawk supplied with
a built-in electromotor which allowed head movement. The
perched sparrowhawk was hidden behind a black curtain except during ‘‘perching’’ events, when the curtain was lifted
and the perched model was rolled into the mudflat arena,
for 1 min, approximately 0.5 m above the mudflat surface.
During the experimental periods, ‘‘gliding’’ and ‘‘perching’’
events were carried out once each day at unpredictable times
between 0930 and 1700 h with the constraint that events did
not occur within 90 min of each other in order to allow sufficient time for focal observations between events. Behavioral
responses to the raptor threats in this experiment, including
details of observational methods, were discussed in a separate
paper (Mathot et al. 2009).
In the previous experiment (van den Hout et al. 2006), it
was established that shorebirds are able to distinguish predators from nonthreatening disturbances. Having shown this
and trying to avoid any other disturbance of the red knots
in the experimental arena, we did not provide a nonthreatening disturbance as control. During all phases of the trials (i.e.,
habituation, control, and experiment), at 1800 h the mudflat
was briefly (10–30 min) flooded with seawater to help cleanse
the sandy substrate. During this time, the birds could rest on
an elevated roosting platform (Mathot et al. 2009). Food was
also replaced at this time. Trays of freshly thawed mudsnails
were provided in sufficient quantity to allow ad libitum feeding for the subsequent 24 h.
Morphological changes were measured as the differences between the onset and the end of each control and treatment
period. BM was measured to the nearest 0.1 g on a balance
(Sartorius, type 3862). Pectoral muscle size (pectoral muscle
thickness [PMT], to the nearest 0.1 mm) was measured by
P.J.H. and in the last 2 trials by Anne Dekinga, using an ultrasound apparatus with a 7.5-MHz linear probe (Pie 200, Pie
Medical Benelux BV, Maastricht, The Netherlands; for further
details, see Dietz, Dekinga, et al. 1999. As P.J.H. was aware of
the treatment that birds were exposed to, in each session of
ultrasound measurements, 3 dummy birds were randomly included to test for observer bias. There was no such observer
bias as treatment and control values did not differ for these
dummy birds (general linear models, F1,24 ¼ 0.139, P ¼
0.713). The measurements were otherwise ‘‘blind’’ in the
sense that no readings were made by the observer but only
ultrasound pictures that were subsequently interpreted by
a second observer. Ultrasound measurements showed a repeatability of 0.83 for P.J.H. and 0.80 for Anne Dekinga (Lessells
and Boag 1987; Dietz, Dekinga, et al. 1999). We computed
PMM (g) from PMT (mm) using the predictive equations
derived from a calibration exercise on red knot carcasses
(these birds died as a result of catching accidents on the Banc
d’Arguin, except for 3 birds that collided with a light house in
the German Wadden Sea): for the measurements taken by
P.J.H.: PMM ¼ –0.35 1 0.40 PMT (R2 ¼ 0.24, N ¼ 16, P ¼
0.030); for Anne Dekinga : PMM ¼ –9.58 1 0.28 PMT (R2 ¼
0.40, N ¼ 18, P ¼ 0.003). During the first experiment (which
started off with a control treatment), no pectoral muscle data
were obtained because of instrument failure. This limited the
comparisons involving PMT to 7 trials.
Data were analyzed using linear mixed effects (LMEs) models from the package ‘‘nlme’’ in R (v. 2.6.1). LMEs provide estimates of the influence of fixed effects on the mean and
random effects on the variance, accounting for the nonindependence of errors resulting from the repeated measures on
individuals. Statistically, trials are comprised of the successive
Downloaded from http://beheco.oxfordjournals.org/ at University Library on April 9, 2013
Using mistnets, 50 red knots were caught on Richel
(5316#57$N, 0523#82$E) and on Simonszand (5329#28$N,
0624#19$E), in the Wadden Sea, The Netherlands, on 8 August
and 3 September 2005, respectively. We selected adults of the
islandica subspecies (e.g., Nebel et al. 2000; Piersma 2007).
The birds were housed in aviaries at the NIOZ in 4 flocks of
12 to 13 birds. The aviaries measured 3.85 m by 1.85 m and
were 2.40-m high. Air temperature and photoperiod were determined by the ambient outdoor conditions. Each group of
experimental birds was set free in the Mokbaai, Wadden Sea
(5300#37$N, 0445#11$E) immediately after the experiments. From the beginning of their time in captivity, the birds
were fed ad libitum with 2–4 mm mudsnails (Hydrobia ulvae),
which had been collected from the Wadden Sea. Mudsnails
were stored frozen and thawed immediately before use
(Vézina et al. 2006).
Some of these birds were molting their primaries, and we
were aware that this might confound our results. Therefore,
to enable statistical control for molt later on, birds were
scored for growth of primaries (0 ¼ old, 1 ¼ shed, 2 ¼ quarter
grown, 3 ¼ half grown, 4 ¼ 3 quarters grown, and 5 ¼ fully
grown feather—Ginn and Melville 1983). To estimate the size
of the gap in the wing caused by missing or growing feathers,
we used the measurement of wing raggedness, which corresponds to the molt score such that the sum of the molt score
and the raggedness score is 5 for each new or growing feather.
As neither an old nor a fully grown feather causes a gap, both
have a raggedness score of zero (Bensch and Grahn 1993).
Although this measure does not account for the position of
the gap in the wing (Hedenström and Sunada 1999), it is
nonetheless adequate for exploring possible molt effects
within individuals.
The experiments took place from 21 August through 28
November 2005 in an indoor mudflat facility (7 3 7 3 3.5 m
high; see figure in Mathot et al. 2009). During the experiments,
a constant light:dark cycle was implemented (lights on from
0600 to 2100 h), with ‘‘moonlight’’ illumination being provided
during the dark phase. We carried out 8 trials, each with a flock
of 6 birds that were randomly selected from each of the 4 outdoor flocks. Each trial consisted of a 2-day habituation period,
followed by a 5-day control and a 5-day experimental period.
This time frame was used because it is expected to be sufficiently long to allow detectable changes in PMM and total
BM (Dietz, Piersma, and Dekinga 1999; Piersma et al. 1999;
van den Hout et al. 2006). The order of experimental and
control periods was determined at random for each flock, with
flocks receiving the experimental period first and last in 4 trials
each.
During the trials 2 event types were used to simulate predation danger. The first consisted of a gliding sparrowhawk
19
Behavioral Ecology
20
EXPERIMENTAL RESULTS
On the appearance of both the gliding and the perching sparrowhawk, red knots always took flight and remained airborne
for 34.7 6 1.3 s (mean 6 standard error of the mean [SEM],
N ¼ 240) after hawk flight events and 28.2 6 1.3 s (mean 6
[SEM], N ¼ 240) after hawk perching events.
The minimally adequate model for changes in both BM
and PMM included treatment and raggedness as fixed effects
(Table 1). Exposure to the raptor models resulted in average
BM reduction of 2.6% (P , 0.001; Table 2). When the control
preceded the predator treatment, BM increased with an average 4.8% (from 122.1 to 128.0 g) during the 5-day control
phase of the experiment and decreased by 2.3% (from
Table 1
Model selection for tests of responses of BM and PMT to raptor
exposure
Model (random ¼ ;1jorder&group/
individual) dependent variable
BM
PMT
Rank AIC
Rank AIC
8
Treat 1 order 1 rag 1 treat 3
order 1 treat 3 rag 1 order 3
rag 1 treat 3 order 3 rag
Treat 1 order 1 rag 1 treat 3 order 1 7
treat 3 rag 1 order 3 rag
Treat 1 order 1 rag 1 treat 3
6
order 1 treat 3 rag
Treat 1 order 1 rag 1 treat 3
5
order 1 order 3 rag
Treat 1 order 1 rag 1 treat 3 rag
4
Treat 1 order 1 rag 1 treat 3 order
3
Treat 1 order 1 rag
2
Treat 1 rag
1
2289 8
2196
2295 7
2202
2303 6
2209
2305 5
2209
4
3
2
1
2217
2217
2225
2232
2313
2314
2323
2330
Treat, treatment; order, treatment order; rag, raggedness. In the LME
package of R, the covariate raggedness is used as a fixed factor. The
minimal model, with lowest AIC value, was chosen for both
dependent variables.
128.0 to 125.1 g) during the subsequent 5-day predator phase.
In contrast, when the raptor models were presented first, despite a tendency for BM increase during the entire experimental period (see values with respect to baseline in Figure 2A),
BM at the end of the raptor treatment was not different from
starting mass, but subsequently increased during the control
phase by 2.7% (from 126.7 to 130.0 g; Figure 2A). Unlike BM,
pectoral muscle size was not affected by the raptor model
intrusions (P ¼ 0.562; Table 2; Figure 2B).
In the model testing for the effects of treatment on BM, the
random factor ‘‘group,’’ compounded with ‘‘order’’ (see
MATERIALS AND METHODS) was responsible for 56% of
the random error. This was around 23% for ‘‘individual’’
nested within ‘‘group&order’’ (Table 3). In the model addressing pectoral muscle as the response variable, these values were
33% and 49%, respectively (Table 3). Molt (measured in raggedness values) tended to affect BM (P ¼ 0.090; Table 2), but
this effect was not significant; neither was the interaction term
treatment 3 raggedness (P ¼ 0.950). Raggedness, however,
did influence PMT (P , 0.001; Table 2). Yet, neither treatment (P ¼ 0.562; Table 2) nor the interaction term treatment
3 raggedness significantly affected PMT (P ¼ 0.318). Analysis
of the interaction terms indicate that differences at individual
or group level in primary molt phase did not confound the
effects of predator exposure on either BM or PMT.
Table 2
LME test results for effects on values of BM and PMT
Fixed effects
Effect size
Dependent variable:
Treatment
Raggedness
Dependent variable:
Treatment
Raggedness
BM
20.026
20.010
PMT
20.005
0.039
Confidence interval
Degrees of freedom
t
P
20.036 to-0.015
20.022 to 0.002
1
1
24.962
21.735
,0.001
0.090
20.023 to 0.013
0.021 to 0.058
1
1
20.585
4.256
0.562
,0.001
The results for PMT were based on trials 2–8 only, due to instrument failure during the first trial.
Downloaded from http://beheco.oxfordjournals.org/ at University Library on April 9, 2013
treatments each carried out with a different ‘‘group.’’ Using
repeated measures, each individual served as its own control.
To remove body size related variation among individual birds,
all mass variables were standardized by dividing them by the
values at the start of the trial. We tested for differences in BM
and PMT between the predator treatment and the control,
using models with treatment, treatment order (control or
predator first), the interaction of treatment and treatment order as fixed effects, and individual within group within order
as a random effect. As treatment order could not be tested as
both a fixed factor and as part of a nested complex of random
factors (treatment order/group/individual), we compounded
order and group into unique combinations, leaving only 2
nesting levels (;1jtreatment order&group/individual).
Although alternating ‘‘treatment order’’ would serve to control for seasonal effects, including molt, we chose to include
raggedness of the wing as a covariate in the analysis (in the
LME package of R, the covariate, raggedness, is used in the
model statement, thus considered a fixed effect) to control
for possible effects of molt on the response variables of interest
(BM and PMT). Midpoint measurements of primary molt
would create too much disturbance to the experimental birds,
and consequently, we took molt scores immediately after each
experiment. However, as during the first 3 trials primary molt
data were taken immediately before the experiment, we interpolated these values to values expected at the end of a trial, by
calculating the speed of growth for each primary. These calculations were based on primary molt patterns estimated from
weekly measures of 55 red knots kept in the outdoor aviaries
at our institute in autumn 2001 and 2002.
Assumptions of normality and homoscedasticity were verified by visual inspection of probability plots. Raggedness values
were square root 1 0.5 transformed to meet requirements of
normality (Zar 1999). We ranked all possible models using the
Akaike Information Criterion (AIC) (Akaike 1974), and selected the highest ranked model (with lowest AIC) as our final
model.
van den Hout et al.
•
Escape from predator attack
21
Table 3
Random effects
Random effects
Dependent variable: BM
Group&order
Group&order/individual
(intercept)
Group&order/individual
(residual)
Dependent variable: pectoral
Group&order
Group&order/individual
(intercept)
Group&order/individual
(residual)
Standard
deviation
Relative contribution
to variance (%)
0.0398
0.0247
55.9
21.5
0.0254
22.7
muscle size
0.0334
0.0411
0.0248
32.6
17.9
49.4
Figure 2
Changes in BM (panel A) and PMT (panel B) due to simulated
raptor attacks compared with control treatment for each of the
experimental trials separately. Variance around the means is shown
by error bars (61 standard error). The values are averages of 6 birds
and were standardized to the values at the start of the trial (dashed
lines denote baselines). Treatment orders (predator or control first)
are depicted explicitly. Trial 1 for pectoral muscle is missing due to
instrument failure.
DISCUSSION
We used aerodynamic theory to develop predictions for the
morphological response to predation danger of different classes of bird species, based on differences in their ecologies. Escape speed should be critical for nearshore species owing to
the short predator detection distances, which should favor
higher PMM. In contrast, farshore species should favor maneuverability and decrease mass in response to predation danger. A
comparison of the red knot experiments with an earlier experiment with ruddy turnstones (van den Hout et al. 2006) provide preliminary evidence for species-specific morphological
responses to predation which match the differential ecologies
of those species.
After 5 days of exposure to simulated predator events, red
knots decreased their overall BM, whereas PMM remained unchanged. Ruddy turnstones showed a different morphological
response than red knots, increasing PMM without a significant
increase in BM (fat-free mass did not change either). Instant
responses to predator exposure also differed between these
species: whereas red knots as a rule immediately flew off, ruddy
turnstones generally responded by crouching and freezing.
The differences between red knots and ruddy turnstones in
morphological response to predation are consistent with the
predictions outlined earlier based on differences in their ecologies and related escape tactics. Ruddy turnstones feed in
shoreline habitats, mainly foraging in small and scattered
groups (Metcalfe 1986). They occur on beach-cast wrack
and near the cover provided by rocks and other habitat structures (Cramp et al. 1983; Metcalfe 1984; Fuller 2003). Here,
they are particularly vulnerable to surprise attacks by raptors
such as sparrowhawks Accipiter nisus L. and large falcons, Falco
species (Metcalfe 1984; van den Hout et al. 2008). When attacked by a raptor, ruddy turnstones have the option to freeze
in the cryptic environment of crevices. However, if capture is
imminent (Ydenberg and Dill 1986), they rely on a speedbased escape, often toward an open water surface (Whitfield
et al. 1988) or into saltmarsh vegetation (Lima 1993). In view
of the close range at which these species generally detect the
predator, the early stage of escape is decisive for survival. This
requires fast take-off and acceleration, that is, a speed-based
escape. Increasing power output by boosting pectoral muscle
best matches such an escape scenario.
In contrast, red knots tend to forage in large flocks in very
open mudflat habitats avoiding topographical structures that
would allow raptors to attack by surprise (Piersma et al.
1993; van den Hout et al. 2008). Other than ruddy turnstones
which are often ambushed by raptors, through the ‘‘many
eyes’’ available for scanning an unobstructed environment,
red knots, as a rule, have more time to prepare themselves
for an escape response. As soon as an aerial attacker is detected, red knots take flight as a flock and perform coordinated aerial escape flight maneuvers (Lima 1993; van den
Hout et al. 2008). As predicted, rather than responding to
predation danger by increasing the size of their pectoral
muscles as in ruddy turnstones (van den Hout et al. 2006),
red knots responded with a decrease in BM (though not at the
expense of PMM) in favor of turning maneuverability. Applying the earlier mathematical calculations, we visualized the
results of the red knot experiments in Figure 3. This figure
shows that the benefit for red knots is 2-fold. First, the BM
reduction directly reduces inertia and thus turning radius
(Origin to position A); second, by decreasing BM, whereas
Downloaded from http://beheco.oxfordjournals.org/ at University Library on April 9, 2013
Note that group and order were compounded to one random factor
(see MATERIALS AND METHODS). Note that R (nlme package for
mixed models) treats the covariate raggedness as a fixed effect.
22
keeping pectoral muscle size unchanged, red knots increase
power output and thus velocity, which leads to a further reduction in the turning radius (from A to B). Instead, the
ruddy turnstones increase PMM (van den Hout et al. 2006),
moving them away from the y axis along a turnstone-specific
isocline, which mainly results in higher speed.
The benefit of BM decrease for overall flight capacity can
also be demonstrated using the aerodynamic considerations
for flight performance (based on wind tunnel studies) in
Dietz et al. (2007). They predicted that for flight performance
to remain constant, PMM should scale allometrically with BM
to the power 1.25. In our experiment, in the control phase,
red knots obtained an average BM of 129.0 g and a PMM of
29.9 g. The birds that decreased BM to 126.0 g after the raptor
scares obtained a pectoral muscle of 29.7 g, 2.4% higher than
the 29.0 g that would follow from this allometric relationship.
Thus, red knots, after exposure to predators, as well as gaining
greater maneuverability during the predator phase of the
experiment, also achieved increased flight capacity
(PMM/BM1.25; Figure 4).
Our experiment was not designed to examine the effects of
primary molt (raggedness) on mass components. Instead, we
were confronted with some molting birds as a result of logistical (seasonal) constraints. Still, the examination of molt as
a covariate yielded an interesting insight. There are no many
studies on the effect of primary molt on pectoral muscle and
most address waterfowl with respect to their virtually flightless
period (Piersma 1988; Fox and Kahlert 2005, but see Lind and
Figure 4
Phase space with lines for equal flight capacity (PMM/BM1.25) (Dietz
et al. 2007), for ruddy turnstones (van den Hout et al. 2006) and red
knots (this study), showing that in response to raptor model
intrusions both species increase flight capacity, red knots by
decreasing BM and ruddy turnstones by increasing pectoral muscle
size (all data were log transformed). Vector directions are based on
average values. Small changes in BM (for ruddy turnstone) and
pectoral muscle size (for red knot), although insignificant,
contribute to the vector directions.
Jakobsson 2001). We now see that molt correlates with a significantly larger pectoral muscle size in a shorebird fully capable of flight. However, in our experiment the correlation
between molt and pectoral muscle size was independent of
the effects of predation threat on BM. Furthermore, there is
no evidence that the absence of effect on pectoral muscle size
is due to molt effects (Table 1).
As predicted, the difference in escape behavior of red knots
and ruddy turnstones is not only correlated with their different
ecologies but is also associated with differences in wing morphology. Although both red knots and ruddy turnstones are
long-distance migrants with the predicted long slender wings
(Alerstam and Lindström 1990; Marchetti et al. 1995), the
aspect ratio of ruddy turnstone wings is 10% lower (7.9 6
0.11, N ¼ 29) than of red knot wings (8.7 6 0.05, N ¼ 65;
t ¼ 25.85, degrees of freedom ¼ 39.6, P , 0.001), indicating
that ruddy turnstones have relatively shorter and broader
wings than red knots.
For red knots, maintaining coordinated movements with the
rest of the flock is critical for any given individual in order to
avoid being singled out in a one-to-one chase with the raptor
(Caro 2005). This means that even subtle differences in maneuverability performance would translate into large differences in the probability of being killed. In view of the risks
of being less agile than other flock mates, we expect selection
for prey to have the ability to monitor the state of conspecifics
in the same and different groups so that they assess relative
vulnerability and respond appropriately (Cresswell and Quinn
2004). In such a game-theoretic scenario, for birds facing
a trade-off between safety and energy even a subtle sacrifice
in energy stores could thus have a significant payoff in terms
of survival. However, the present experiment does not tell us
whether in nature a period of more than 5 days of elevated
danger would yield larger effects than we detected.
Downloaded from http://beheco.oxfordjournals.org/ at University Library on April 9, 2013
Figure 3
Isoclines reflecting turning radii as a function of velocity, as predicted
by the model of Hedenström and Rosèn (2001), shown for the
average of both orders (raptor control and vice versa) in the
experiment. This returns 129.0 g for control (thin curve) and 125.9 g
for the predator treatment (thick curve). Predicted minimum
turning radii for birds in the raptor treatment and the control are
determined by the asymptotes in the figure, yielding 14.67 m (thin
dashed line) and 14.32 m (thick dashed line), respectively.
Calculations of the asymptotic values were given earlier in the text.
The 2-fold benefit of a decrease in BM is shown qualitatively: Origin
to position A denotes the decrease in turning radius due to decreased
BM; A to B shows the additional decrease in turning radius due to
a relative increase in power output (see text). The ruddy turnstones
in van den Hout et al. (2006) would move along a turnstone-specific
isocline, toward higher speed, with a minor decrease in turning
radius (equivalent to the trajectory from A to B in this figure).
Behavioral Ecology
van den Hout et al.
•
Escape from predator attack
Proposing a research portfolio
This study provides preliminary support for the hypotheses
developed in the introduction. However, further studies are required. Although use of ultrasound equipment for measuring
pectoral muscles may be logistically unfeasible for many
researchers, dental alginate exists as a cost effect alternative
for obtaining coarse estimates of pectoral muscle size (Selman
and Houston 1996).
To test whether changes in body composition as detected in
experiments are biologically meaningful, additional experiments may be needed, in which flight performance parameters, such as linear acceleration, and turning speed and
radius are coupled to differences in BM and PMM, respectively.
Specific methods may depend on the size of the experimental
bird species. To our knowledge, in all flight performance studies, birds of which flight performance was tested accelerated
from a stationary position (Swaddle et al. 1999; Lind 2001;
Burns and Ydenberg 2002), thus basically addressing a
speed-based escape mode. Likewise, detailed studies of maneuverability typically involve maneuvering at relatively low
speed (Warrick 1998, Warrick et al. 1998). To our knowledge,
high-velocity maneuvers have never been studied in detail due
to logistical constraints. Even more logistically challenging,
but necessary for a full understanding of the proposed relationship between escape tactic and adaptive changes in body
composition due to raptor threat, would be to measure flight
parameters of birds involved in socially coordinated escape
flight (for inspiration, see Potts 1984).
Other tractable systems, in addition to nearshore and farshore shorebird foragers, for testing this hypothesis include
passerine taxa. The Emberizinae are a subfamily of the Passeriformes, which are notable for a high diversity of escape
tactics (Lima 1993). For instance, within Fringillidae, a diversity of escape tactic from herbaceous- and woody-vegetationdependent escape tactics is represented (Lindström 1989).
Several arboreal, socially feeding fringillids (crossbills Loxia
species, pine siskins Carduelis pinus, evening grosbeaks Coccothraustes vespertinus) employ highly coordinated flight and
flushing behavior. This may be related to the use of more
exposed feeding habitat due to weak familiarity with the
location and nature of protective cover of these nomadic
species (Lima 1993). We hope that this study will initiate
a portfolio of novel studies in phenotypic flexibility and predation in the context of a species’ ecology.
FUNDING
Natural Sciences and Engineering Research Council discovery
grant to Luc-Alain Giraldeau (to K.J.M.)
We are very grateful to Maarten Brugge and the crew of the research
vessel Navicula for help with the catching of the experimental red
knots and for fishing mudsnails, to Anne Dekinga for performing
ultrasound measures in the last 2 experimental trials, to Franc
xois
Vézina for assistance in the lab, to Jan van Gils for discussion and
suggesting the isocline approach, and several anonymous referees,
particularly Will Cresswell, for feedback. We thank Jeroen Reneerkens
and Maurine W. Dietz for valuable comments on a draft, and Tamar
Lok for statistical advice. The experiments complied with Dutch law
regarding animal experiments (DEC[DierExperimentenCommissie]licence NIOZ 04.04).
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