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First published online June 27, 2008
Journal of Experimental Biology 211, 2214-2223 (2008)
Published by The Company of Biologists 2008
doi: 10.1242/jeb.017525
Female mice respond differently to costly foraging versus food restriction

1 Department of Behavioral Biology, Center for Behavior and Neurosciences,
University of Groningen, Kerklaan 30, 9751 NN, The Netherlands
2 Aberdeen Centre for Energy Regulation and Obesity (ACERO), Aberdeen, UK
3 Center for the Integrative Study of Animal Behavior, Indiana University,
Bloomington, IN, USA
4 Centre for Isotope Research, University of Groningen, The Netherlands
* Author for correspondence (e-mail: k.a.schubert{at}rug.nl)
Accepted 23 April 2008
| Summary |
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Key words: foraging costs, food restriction, workload, daily energy expenditure (DEE), resting metabolic rate (RMR), allocation trade-offs
| INTRODUCTION |
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Several studies have manipulated foraging costs per reward in the
laboratory using a work-for-food design. In rodents, wheel running is
typically used as a proxy for foraging activity
(Perrigo, 1987
;
Perrigo and Bronson, 1983
;
Perrigo and Bronson, 1985
;
Vaanholt et al., 2007
),
whereas studies in avian species have required animals to fly short distances,
hop on perches or sift through chaff to receive food (reviewed by
Wiersma and Verhulst, 2005
).
Animals facing elevated foraging costs increase their activity or keep
activity constant (Vaanholt et al.,
2007
; Wiersma and Verhulst,
2005
). Food intake and DEE are decreased when a fixed reward
schedule is used (Bautista et al.,
1998
; Day and Bartness,
2001
; Deerenberg et al.,
1998
; Perrigo,
1987
; Vaanholt et al.,
2007
) but may be elevated when rewards are unpredictable
(Bautista et al., 1998
;
Wiersma et al., 2005
).
Various types of changes occur in response to manipulation of foraging
costs. Animals typically alter their time–activity budgets
(Deerenberg et al., 1998
;
Perrigo, 1987
), utilize stored
energy (Day and Bartness, 2001
;
Vaanholt et al., 2007
) and
reduce whole body mass and organ size
(Vaanholt et al., 2007
).
Reductions in resting metabolic rate are typical (reviewed by
Wiersma et al., 2005
). Even
more extreme savings may occur through hypothermia, which has been observed in
starving animals maintained on low levels of nutrition (e.g.
Daan et al., 1989
;
Gelegen et al., 2006
;
Hudson and Scott, 1979
) and
may also be possible under elevated foraging costs
(Perrigo and Bronson, 1983
;
Vaanholt et al., 2007
).
In addition to changes in patterns of energy use, high foraging costs have
secondary physiological consequences which could compromise fitness and
survival prospects of free-living animals. Most small mammals are sensitive to
food availability in scheduling their reproductive effort
(Wade and Schneider, 1992
),
and alterations in energy balance may reduce fertility and breeding success
(Johnston et al., 2006
).
Perrigo (Perrigo, 1987
) found
that high foraging costs are detrimental to breeding success of two species of
wild mice (Mus musculus and Peromyscus maniculatus). Along
with reductions in total expenditure, animals faced with high foraging costs
reallocate energy away from somatic repair [e.g. feather re-growth
(Wiersma and Verhulst, 2005
)],
protection from cellular damage by free oxygen radicals
(Wiersma et al., 2004
), and
immune function (Deerenberg et al.,
1997
). Trade-offs of this type can affect mortality risk and rates
of senescence.
Work-for-food experiments are a tool which has been used to mimic natural variation in foraging costs. This design simultaneously exposes animals to the dual energetic challenges of forced activity and reduced food intake. It has thus far remained unclear to what extent changes in physiological indicators of energy balance (e.g. body composition and metabolic rate) are the combined result of increased rates of energy turnover on the one hand and of food restriction on the other. To address this problem, we set out to explicitly separate these effects. We manipulated female laboratory mice by exposing them to low and high foraging costs and compared the latter to a group of inactive animals receiving a food ration matched to the intake of animals with high foraging costs. We measured activity, food intake, energy metabolism, body mass and composition, as well as secondary responses in estrous cyclicity and in primary immune response to a novel antigen challenge. Our hypothesis was that effects of high foraging costs are due to the combined effect of food restriction and high energy turnover. Therefore, we predicted that effects such as decreased immune response, and loss of ovarian cyclicity would be more dramatic in animals facing high foraging costs than either other group.
| MATERIALS AND METHODS |
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Experimental design
At the start of the experiment, animals were assigned to three experimental
groups (N=8 per group): (group 1) L, mice that faced low foraging
costs; (group 2) H, mice that faced high foraging costs; (group 3) R, mice
that did not have to forage for food, but were each pair-fed with a mouse from
the H group. At this time L and H mice were housed in Plexiglas cages
(20x20x30 cm) fitted with plastic running wheels (diameter 14 cm;
code 0131 Savic®, Kortrijk, Belgium). R mice remained in standard cages
without wheels. The study was divided into three phases: baseline, training
and workload phases. The start of the training phase was termed experimental
day 0. Time notation followed this convention throughout. Body mass and food
intake (to the nearest 0.1 g) were measured daily throughout the study,
starting 1–2 h prior to lights off so that the disturbance coincided
roughly with activity onset. This was also the time at which the R mice
received their food ration based on the food intake of the H mice over the
previous day. The weighing sequence was rotated daily. After weighing, we
hand-sifted bedding to count uneaten food blocks or pellets, which were always
removed. Running-wheel activity [RWA; in number of revolutions (revs)] was
logged in 2 min time intervals (bins) using a computerized event recording
system. We calculated travel distances in km day–1 and
estimated time spent running (h day–1) by counting the number
of 2-min bins with a value of >0. Maximum and mean running speeds were
estimated from the highest number of revolutions in a 2-min bin and from the
mean number of revolutions across all non-zero bins, respectively. Activity of
R mice housed without wheels was not measured.
In the baseline phase (days –27 to –1), all mice were kept on ad libitum food. Individual baseline reward rates (in revs pellet–1) were calculated by dividing mean RWA (revs day–1) by gross energy intake (kJ day–1) for each mouse over days –14 to –1 of this phase. This measure was then adjusted for the manufacturer's energy content of the rodent blocks given during the baseline phase and the precision pellets which would later be used during the training and workload phases (Table 1).
|
In the training and workload phases, all animals were switched to a diet of
45mg precision food pellets (TestDiet 5TUM/PJAI, Sandown Chemicals, Hampton,
Surrey, UK). Cages of L and H mice were connected to food dispensers (Med
Associates Pellet Dispenser ENV-203, Sandown Scientific, Hampton, UK) that
delivered food pellets on a fixed reward ratio (as described above) and were
linked to a steering computer (Series 3 Programmable Controller, General
Electric). On average, mice had to run 130±10 revs
pellet–1 (
17000revsday–1) to obtain
their baseline food intake. Foraging costs of the L mice remained constant at
their individual reward rate during the training and workload phases (days
0–40). Thus, when running the same amount as during the Baseline phase,
they would have received an amount of food similar to their mean intake during
that phase. In practice, L mice ran more during the training and workload
phases than during the baseline phase and received more pellets than they ate
each day. In the H group, foraging costs per reward increased over the
training phase: foraging costs were raised by 10% of the individual baseline
every other day, until they had doubled. Foraging costs then remained constant
at 200% of baseline, marking the start of the workload phase (day 21). Mice in
the R group did not forage to obtain food, but were pair-fed with animals from
the H group: each R-group mouse received a daily ration of precision pellets
matched to the previous day's intake of an individual H mouse (i.e. they were
`yoked controls').
Estrous cyclicity
Vaginal cytology was scored after daily weighing from day –27 to 28.
A vaginal swab was taken from each animal (while gently holding it by the
tail) using a paintbrush dampened with distilled water. Cells were smeared
onto a clean glass slide and stained with a drop of Methyl Blue dye (S.
Johnston, personal communication). A single observer blind to time and
treatment visually scored slides with a light microscope at 100x
magnification. Following Miller et al.
(Miller et al., 2004
), the
cycle phase was identified based on the proportion of leukocytes, nucleated
epithelial cells, and cornified epithelial cells counted in >100 cells per
smear. An animal was considered fertile in the baseline phase if it entered
estrous (
50% cornified cells per smear) on at least three occasions
between day –27 and –1, and at least once between day –7 and
–1. For statistical analyses, the day with the highest percentage of
cornified cells measured in a 1-week period (see Data analysis below) was used
as an estrous score.
Metabolic measurements
In the workload phase [days 25–28 (±1 day)] daily energy
expenditure (DEE; kJ day–1) of animals in their home cages
was estimated using the doubly labeled water method [DLW
(Lifson and McClintock, 1966
;
Speakman, 1997
)]. The protocol
followed Vaanholt et al. (Vaanholt et al.,
2007
). Mice were weighed to the nearest 0.1 g, briefly restrained
by the scruff of the neck, and injected i.p. with
0.1 g of enriched water
(37.6% 2H and 60.6% 18O). The precise dose injected was
quantified by weighing syringes to the nearest 0.0001 g before and after
injection. After a 1 h equilibration period
(Król and Speakman,
1999
) animals were bled at the tail tip, and an initial blood
sample (15 µl) was collected in duplicate glass capillary tubes, which were
immediately flame-sealed with a propane torch. Mice were then returned to
their home cages. Forty-eight hours after the initial sample
(Speakman and Racey, 1988
), a
final blood sample was collected in triplicate following the same
procedure.
After collecting final blood samples for DLW, metabolic rate was measured
overnight in an open-flow respirometry system
(Oklejewicz et al., 1997
;
Vaanholt et al., 2007
). Mice
were placed in transparent Plexiglas chambers (15x10x10 cm) with a
slice of apple and some home-cage bedding. They were fed a ration of the same
type and quantity of food they consumed the previous day. Measurements were
made for ca. 23 h under the same temperature and photoperiod conditions as in
the experimental room. We used an eight-channel system which sampled each
mouse over a 1 min interval once every 10 min and recorded differentials in
gas concentrations between excurrent chamber air and reference air (drier: 3
Å molecular sieve drying beads, Merck, Darmstadt, Germany).
O2 consumption
(
O2; ml
h–1; Servomex Xentra 4100 paramagnetic analyzer, Crowborough,
UK) and CO2 production
(
CO2; ml
h–1; Servomex 1440 infrared analyzer) were measured
simultaneously. Inlet airflow was set at 20 l h–1 (Brooks
Type 5850 mass flow controller, Rijswijk, The Netherlands). We calculated the
respiratory quotient (RQ) as
CO2/
O2.
Metabolic rate (MR; kJ h–1) was calculated from the formula
(Romijn and Lokhorst, 1961
):
![]() | (1) |
Resting metabolic rate (RMR; kJ h–1) was estimated as the lowest value of a 20 min running mean of MR (typically three measurement points) and later expressed as kJday–1. We also estimated the average daily metabolic rate (ADMR; kJ day–1) for animals in the metabolic chambers.
Mass spectrometry
Determinations of 2H:1H and
18O:16O ratios in blood samples were performed by mass
spectrometry at the University of Groningen's Center for Isotope Research
(Visser and Schekkerman,
1999
). Blood samples were prepared by microdistillation in a
vacuum line, first heating the broken tubes and then cryogenically trapping
the emerging water vapor with liquid nitrogen
(Nagy, 1983
). Water samples
were stored and then automatically injected into a Hekatech high temperature
pyrolysis unit (Gehre et al.,
2004
), in which the injected water was reacted with glassy carbon.
The resultant H2 and CO gases, emerging into a continuous He
flow-through system, were then led through a GC column to separate the two
gases in time and finally fed into a GVI Isoprime isotope ratio mass
spectrometer for the analysis of
18O and
2H. Measurements were corrected for memory effects using an
algorithm similar to the one described by Olsen et al.
(Olsen et al., 2006
). At least
three internal water standards chosen to cover the entire enrichment range of
the blood samples were prepared and analyzed following the same methods. We
measured samples in duplicate unless a flaw was detected in the flame-sealing
step. Typical relative duplo differences were below 2.5% for
2H, and 1% for
18O. If differences
exceeded 3% we critically examined the data and omitted the aberrant value,
performing further calculations on a single replicate. Otherwise, duplicate
values were averaged.
Initial isotope dilution spaces (mol) were calculated by the intercept
method (Coward and Prentice,
1985
); total body water was converted to grams using a molecular
mass of 18.020 for body water, and expressed as a percentage of body mass. The
rate of CO2 production (rCO2; moles
day–1) was calculated using Speakman's single-pool model
equation 7.17 (Speakman,
1997
):
![]() | (2) |
Immune challenge
On day 39 (±1 day), primary immune responsiveness was assayed by
challenging animals with a novel antigen, keyhole limpet hemocyanin (KLH).
After weighing, each mouse was injected s.c. with 0.1 ml of 0.9% sterile
saline containing 150 µg KLH (Calbiochem, Merck KGaA, Darmstadt, Germany;
#374811, lot #B304050). Blood samples were taken from the tail tip at 5 and 10
days after injection to measure anti-KLH immunoglobulin (IgG) production.
Samples of
100 µl were collected in unheparinized glass capillary
tubes and allowed to clot on ice. After removing clots, samples were
centrifuged at 2500 g for 1 h at 4°C. Serum was aspirated
and stored it at –80°C until analysis with an enzyme-linked
immunosorbant assay for anti-KLH IgG [analyzed at Indiana University by G. D.
following Demas et al. (Demas et al.,
1997
)]. Briefly, 96-well microtiter plates were coated with
antigen by incubating overnight at 4°C with 0.5 mg ml–1
KLH, washed, and then blocked with 5% nonfat dry milk overnight at 4°C to
reduce nonspecific binding. Plasma samples were diluted 1:20. Pilot data
showed that peak immune response occurred between day 10 and 15
post-injection; therefore, we only analyzed samples taken on day 10. Positive
control samples (pooled plasma from mice previously determined to have high
anti-KLH antibodies) and negative control samples (pooled sera from KLH-naive
mice) were also added in duplicate to each plate. Secondary antibody [alkaline
phosphatase-conjugated anti-mouse IgG diluted 1:2000 with phosphate-buffered
saline plus 0.1% Tween 20 (PBS-T; Cappel, Durham, NC, USA)] was added, and
plates were read with a 409 nm filter following the addition of the enzyme
substrate p-nitrophenyl phosphate (Sigma Chemical, St Louis, MO,
USA). Mean optical densities (OD) are expressed as a percentage of the plate
positive control OD for statistical analyses.
Body composition
Ten days after KLH injection, animals were sacrificed for carcass analysis
between 13:00 h and 17:00 h (GMT+1 h). Animals were killed by CO2
inhalation and immediately decapitated. Bodies were dissected to separate
organs, skin and the musculoskeletal system, and weighed to the nearest 0.0001
g. Samples were stored at –20°C until analysis. We determined dry
and lean dry organ masses by drying to constant weight at 103°C [European
Standard Protocol ISO 6496-1983(E)] followed by fat extraction with petroleum
ether (Boom BV, Meppel, The Netherlands) in a Soxhlet apparatus.
Data analysis
We tested two experimental hypotheses: that high foraging costs per
se alter behavior and physiology of female mice (HA1: H
females differ from L females), and that high foraging costs induce
quantitatively different responses than food restriction alone
(HA2: H females differ from R females). Because L and R mice
differed in two respects – both foraging activity and feeding regime
– we could not make a priori hypotheses about the differences
between them and did not statistically compare these groups. We tested
responses in the workload phase using unpaired t-tests. Some
baseline-phase parameters differed between groups, but including baseline
phase parameters as model covariates never yielded different results in
t-tests (ANCOVA; results not presented). Some additional comparisons
used general linear models (GLM).
Three animals died or became ill and were retrospectively excluded from the
study. Sample sizes for most analyses were therefore L=8, H=6 and R=7. Because
of technical problems, we further restricted analyses of DLW data to L=7, H=6
and R=5; for consistency, we used the same subset of mice for other analyses
related to energy metabolism. Data were analyzed using Statistica v. 6.1
(StatSoft, Inc., Tulsa, OK, USA). We checked data for normality and
arcsin-transformed proportional measures to sin–1 (
y)
before analysis (arcsin-sqrt). Two-tailed P-values of
0.05 were
considered statistically significant. Because most organ masses were
correlated within individuals, we analyzed body composition using a principal
components analysis [PCA; after Selman et al.
(Selman et al., 2002
)]. This
procedure addresses the problem of multiple statistical comparisons on
correlated data by creating a smaller number of uncorrelated response
variables (principal components) which account for the maximum amount of
variation in the data. We applied Varimax normalized rotation to factors with
Eigenvalues
1 and performed statistical comparisons on these rotated
factors.
|
| RESULTS |
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In order to obtain a constant amount of food, H mice would have needed to
double their activity, but they did not do this
(Fig. 2). Total activity in
workload phase did not differ significantly between L and H females
(Table 2), nor did their
activity rhythms differ (Fig.
3). L and H mice spent 7.1±0.5 and 8.0±0.3 h per day
running, respectively, and ran at maximum speeds of 4.4±0.3 vs
4.4±0.4 km h–1 (mean speeds: L=2.6±0.2,
H=2.4±0.3). The two groups did not significantly differ in the amount
of time spent running or in their running speeds (P>0.1). Although
total foraging effort was similar for females facing low and high foraging
costs, energy intake was significantly lower for H females
(Fig. 1,
Table 2). H females (and their
R yoked controls) consumed
25% less energy than L females in the workload
phase. H mice did not maintain their body mass and were significantly lighter
than both L and R females in the workload phase
(Fig. 1 and
Table 2).
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Energy metabolism
H mice used significantly less energy than L mice on a daily basis
(Table 3). They also used
significantly less energy than R mice when removed from the foraging task
(RMR, ADMR; Table 3), even
though they received the same amount of food at the start of the overnight
measurement. We estimated gross energy intake (GEI) during the workload phase
from food consumption and food energy content (measured using bomb
calorimetry; Table 1). The
ratio of DEE:GEI ranged from 0.72 to 0.80 across experimental groups and was
significantly higher in H than R mice
(Table 3). Estimated surplus
energy (S) was significantly lower in H than in R groups
(Table 3).
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Workload-phase metabolism – both RMR and DEE – was significantly predicted by whole body mass (Fig. 4). Experimental group had an additional, significant effect on DEE (GLM, mass F1,14=46.4, P<0.0001; group F2,14=15.0, P=0.0003; model R2=0.88; non-significant interaction removed). There was also an effect of group on RMR (GLM, group F2,15=6.9, P<0.01, R2=0.48; non-significant effects removed). These effects can be best understood from calculations of mass-specific energy expenditure. Most mass-specific metabolic parameters were virtually identical for H females and both other groups. The exception to this pattern was DEE, which was equal in L and H females, and significantly lower in R than in H mice (Table 3). Overall, H and R mice both saved energy by reducing body mass.
|
Body composition
We compared the body composition of H females to each of the other two
groups on day 50 (Tables 4,
5,
6). At this time, H mice had
experienced 3 weeks of increasing foraging costs and four weeks of foraging
costs at 200% of baseline. The wet masses of all organs were less in H mice
than in L mice (Table 4). Wet
organ masses were also lower in H than in R mice, but the differences were not
as large (Table 4). Organ
masses were highly positively correlated within individuals. To analyze
differences in overall body composition, we performed a principal components
analysis on the correlations between wet organ masses
(Table 5). The first three
components had Eigenvalues of
1, together explaining 74.7% of the total
variance in the data. After normalized Varimax rotation, PC1 had high positive
loadings for the major metabolically active tissues: the heart, liver, kidneys
and brain (Eigenvalue=5.86, percentage variance=53.3). PC1 also had positive
loadings for the muscles/skeleton and pelage. PC2 had a high negative loading
for the wet empty stomach mass (Eigenvalue=1.27, percentage variance=11.6),
and PC3 had high positive loadings for the lungs and intestine
(Eigenvalue=1.07, percentage variance=9.8). Comparing PC scores between
groups, we found that PC1 and PC3 were significantly reduced in H vs
L females (Table 6). High
foraging costs, therefore, reduced the size of metabolic organs,
musculoskeletal systems, lungs and emptied guts.
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All major body components were dramatically lighter in H mice compared to L
mice (Table 6). Whole body mass
at sacrifice, fresh mass, dry mass, lean dry mass and body fat were all
significantly reduced. Body fat was
77% lower in H females than in L
females. The fresh mass of the carcass – which was measured after
animals had been exsanguinated and the guts had been emptied – was about
30% lower in H mice than in L mice. Several body components were somewhat
lighter in H females than in R animals, but only whole body mass and lean dry
mass differed significantly between these groups. H females had 55% less body
fat on average than R females, but this difference was not statistically
significant. Intestine lengths (measured to the nearest 0.1 cm) did not differ
between the groups (mean ± s.e.m.: L=51.9±3.2,
H=52.6±3.0, R=55.3±3.0).
Estrous cyclicity
Our experimental manipulation of foraging costs and food intake markedly
influenced estrous cyclicity, a measure of reproductive readiness. We
restricted all comparisons to females that came into estrus regularly during
the baseline phase (L: 6/8, H: 6/6, R: 5/7). In the workload phase, females
facing high foraging costs all ceased to show signs of estrus. H females had a
significantly lower proportion of cornified cells than L females (independent
t-test on arcsin-sqrt transformed data; H vs L:
t10=–5.0, P=0.0006; H vs R:
t9=–1.9, P=0.09). They were therefore less likely to
come into estrus at least once during the final week of the workload
phase.
Estrous cyclicity was related to body mass, such that H and R groups had similar mean masses (30.7 and 30.8 g, respectively) on the last day they were observed in estrus. Since the decline in body mass was more rapid in H mice, this similarity in body mass suggests a body-mass threshold to maintaining fertility in the face of energy limitations. On average, H females were last observed in estrus on day 5, whereas the average last estrous day for R mice was day 19 (the estrous cycle was monitored until day 28). Most H females stopped cycling soon after they were subjected to foraging costs, while food restriction had a more gradual effect on fertility (R group). Treatment group significantly predicted last estrous day overall (Kruskal–Wallis test: H2,17=7.0, P=0.03), and H females continued cycling longer than L females (Kruskal–Wallis multiple comparisons H vs L: P=0.04).
Immunocompetence
An assay of primary immune response performed at the end of the study
suggested that the experimental groups differed in antibody production
(Fig. 5). Plasma anti-KLH IgG
levels at day 10 post-injection did not differ between H and L animals (power
analysis: partial
2=0.32, f=0.68, power=0.73), but
were lower in both than in R animals (ANOVA, F2,18=4.2,
P=0.03; LSD post-hoc test significant for both L and H
vs R). Food restricted mice without running wheels (R), therefore,
showed a more robust humoral immune response to a novel antigen than highly
active animals receiving sufficient food (L) or experiencing restricted
feeding (H). The strength of the immune response could not be attributed to
body mass or food intake on the day of injection (GLM; mass:
F1,19=0.1, P=0.79; food:
F1,19=1.5, P=0.24).
|
| DISCUSSION |
|---|
|
|
|---|
Our finding that female mice reduced energy expenditure when faced with
high foraging costs is similar to the results of other studies using a fixed
reward schedule (reviewed by Vaanholt et
al., 2007
; Wiersma and
Verhulst, 2005
). However, it does not match the prediction that
foraging costs should increase energy expended on food acquisition [see
schematic in Wiersma et al. (Wiersma et
al., 2005
)]. A negative relationship between foraging costs and
energy expenditure also differs from observations made by Speakman et al.
(Speakman et al., 2003
) in
free-living short-tailed field voles, which had higher metabolic rates when
wintering in poor quality habitat patches. There may be differences in the way
animals respond to fixed versus variable reward schedules, and thus
far, only variable rewards have been shown to elevate DEE
(Wiersma et al., 2005
;
Wiersma and Verhulst, 2005
).
Disparate effects of fixed and variable reward ratios on energy intake have
been attributed to differences in motivation
(Fotheringham, 1998
).
Particularly in rodents, it remains unclear to what extent limitations on the
intensity and duration of activity influence responses to fixed-reward
designs.
The female mice in our study ran between 20 000 and 25 000 revolutions per
day (
9–11 km day–1) in the workload phase, but
activity was not statistically different between groups. Foraging costs did
not affect total wheel-running activity. Together with the results of earlier
studies, our study provides evidence for limits on sustainable activity
levels. Perrigo and Bronson (Perrigo and
Bronson, 1983
) observed a response qualitatively equivalent to
ours in female CF-1 laboratory mice faced with foraging costs between 60 and
225 revs pellet–1 (in the same size running wheels). From 60
to 135 revs pellet–1, wheel-running activity gradually
increased with rising foraging costs. Above 135 revspellet–1,
however, mice seemed to reach an activity limit (of just over 15 000 revs
day–1), regardless of further elevations in foraging costs.
There may be sex or strain differences in running behavior. Independent of
ad libitum activity levels (see
Vaanholt et al., 2007
), limits
to total daily activity may constrain an animal's ability to cope with high
foraging costs.
Consequences of foraging costs
Our manipulation had clear effects on energy balance, which were most
dramatic in female mice facing high foraging costs. The ratio of DEE:GEI
approximates the proportion of consumed energy which would have been
assimilated given a net energy balance of zero. The actual assimilation
efficiency was probably higher [e.g. 79.1%
(Hambly and Speakman, 2005
)].
If we assume that animals actually absorbed 79.1% of gross energy intake, we
can compare estimated energy balance or energy surplus (S) between groups.
Based on this calculation, mice facing high foraging costs would have had no
surplus energy or have been in a negative energy balance. By contrast, females
facing low foraging costs or food restriction alone were at least `breaking
even'. This conclusion is supported by the fact that the high-cost group lost
body mass and showed almost totally depleted fat stores. By contrast, animals
in the other groups maintained or increased body mass during the experiment.
Similar to Vaanholt et al. (Vaanholt et
al., 2007
), we found that body composition was dramatically
affected by high-cost foraging, and females facing high foraging costs had
relatively smaller metabolic organs, muscles/skeleton, and skin/pelage. The
effect on body mass was less pronounced in food-restricted animals.
Changes in body mass over time were associated with reductions in energy
expenditure. Resting metabolic rate was positively correlated with whole body
mass in all groups, and female mice faced with both low and high foraging
costs had similar mass-specific metabolic rates in the workload phase.
Overall, our RMR estimates of 1.12 kJ g–1
day–1 for all groups in the workload phase were consistent
with Vaanholt's (Vaanholt et al.,
2007
) estimates of 0.98 kJ g–1
day–1 for male mice under workload conditions. We did not
observe additional reductions in mass-specific energy requirements, however.
Vaanholt et al. (Vaanholt et al.,
2007
) found that male mice on a high workload had reduced
mass-specific RMR and DEE compared with baseline conditions. One possible
explanation is that although our L group females were not food deprived, they
were `trained' and thereby decreased mass-specific energy requirements. Our
data also suggest that high foraging costs force mice to the limit of minimum
energy expenditure.
In principle, reducing body mass could have been one component of an
energy-saving strategy to prolong survival. Smaller muscles and metabolic
organs require less energy, and the cost of transport is reduced with lower
body mass (Rezende et al.,
2006
). Wiersma et al. (Wiersma
et al., 2005
) suggested that physiological changes made by
European starlings (Sturnus vulgaris) facing a flight-for-food
paradigm may be energy-saving `adjustments'. If body mass were not reduced in
this context, birds would have been faced with high flight costs,
theoretically reducing both food intake and foraging efficiency;
alternatively, they would have needed to drastically elevate DEE. Other
studies in birds have tested the hypothesis that loss of mass during nestling
care can reduce the energetic cost of foraging, thereby potentially increasing
reproductive output (e.g. Norbert,
1981
). Compensatory mechanisms reduce the impact of nutritional
stress on free-living organisms [i.e. small mammals
(King and Murphy, 1985
)].
Under home cage conditions, minimum energy expenditure may actually have
been lower than we estimated from respirometry measurements. Prior studies
have suggested that animals facing high foraging costs can reduce resting body
temperature (Perrigo and Bronson,
1983
; Vaanholt et al.,
2007
). In a pilot study using the same design as the present one,
we found that rectal temperatures of H mice (35.6±0.3°C) were less
than both L (37.2±0.2°C) and R (36.4±0.2°C) animals
(K.A.S., unpublished data). These differences were small but statistically
significant (N=8 per group). Measurements of core body temperature in
the present study also suggest that animals facing high foraging costs employ
daily heterothermy during periods of inactivity.
Trade-offs due to costly foraging
Female mice experiencing high foraging costs ceased to show estrous
cyclicity. This response also occurred in some food-restricted females at a
later time. Delaying or suppressing the estrous cycle during food restriction
(Bronson and Marsteller, 1985
)
is a strategy for curtailing reproduction at an early stage, and Perrigo and
Bronson (Perrigo and Bronson,
1983
) found that peripubertal laboratory mice on a workload
schedule showed fewer ovulatory cycles. Wild-type female mice (Mus
musculus and Peromyscus maniculatus) faced with high foraging
costs were also less likely to become pregnant
(Perrigo, 1987
). It is
interesting that in our study, females on a low workload continued to cycle.
This demonstrates that foraging effort does not limit reproductive readiness,
but that high foraging costs per reward have a negative influence on fitness
prospects.
The results of our immunocompetence assay were intriguing. Female mice
experiencing high foraging costs did not show compromised antibody production
relative to animals on low foraging costs. The fact that inactive, food
restricted mice actually showed higher antibody titers is more difficult to
interpret (these data match pilot findings using the same experimental design;
K.A.S. unpublished data). From an energetic perspective, one would have
expected anti-KLH antibody titers to be lowest in H group females. Primary
antibody production after KLH challenge has been shown to be metabolically
costly [although it dose not induce fever or sickness and does not affect
morphological traits such as body mass, adipose tissues, reproductive masses
or lymphoid tissues in house mice (Demas
et al., 1997
)]. Food restriction also reduces immunological memory
(Martin et al., 2007
) and
depresses acute phase response to LPS (a cell-mediated response) in hamsters
(Conn et al., 1995
) and mice
(Matsuzaki et al., 2001
). The
fact that primary immune response in our experiment was not dependent on
energy balance or body fat stores, therefore, is contrary to general findings
on the energetics of immunity (reviewed by
Demas, 2004
). Overall, these
results suggest that other factors may be responsible for the effects we
observed.
Although voluntary exercise typically enhances immune response [i.e.
delayed-type hypersensitivity (Bilbo and
Nelson, 2004
)], Moraska et al.
(Moraska et al., 2000
) showed
that rats forced to run on a treadmill mount a compromised primary immune
response to KLH. Although L and H females in our experiment could modulate
their own activity levels, they had to run in order to receive food pellets.
Thus, activity in this setting was not purely voluntary. As Vaanholt et al.
(Vaanholt et al., 2007
)
showed, high wheel running activity under work-for-food conditions increases
plasma corticosterone levels, which could be immunosuppressive. Such an effect
is probably responsible for the lower immune response of our two foraging
groups compared to the inactive, food-restricted group. Our results suggest
that immune function may be affected differently in an experimental context
linking activity with food intake (i.e. at different foraging costs), then
under simple manipulations of energy balance or activity.
| CONCLUSIONS |
|---|
|
|
|---|
LIST OF ABBREVIATIONS
| Acknowledgments |
|---|
| Footnotes |
|---|
Deceased 3 June 2007 | References |
|---|
|
|
|---|
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