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First published online June 12, 2009
Journal of Experimental Biology 212, 1995-1999 (2009)
Published by The Company of Biologists 2009
doi: 10.1242/jeb.026344
Temperature-induced elevation of basal metabolic rate does not affect testis growth in great tits
1 Netherlands Institute of Ecology (NIOO-KNAW), PO Box 40, 6666 ZG Heteren, The
Netherlands
2 Department of Biology, University of North Carolina, Chapel Hill, NC 27599,
USA
* Author for correspondence (e-mail: s.caro{at}nioo.knaw.nl)
Accepted 8 April 2009
| Summary |
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Key words: energy expenditure, respirometry, gonadal cycles, timing of reproduction, seasonal reproduction, phenology, supplemental factors, environmental cues, captive experiments, predictability, day length
| INTRODUCTION |
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To achieve breeding condition, birds have evolved response mechanisms to a
host of environmental stimuli, which function as signals heralding the
approach of suitable breeding times
(Murton and Westwood, 1977
).
These proximate factors have been sorted into classes that, combined,
orchestrate the life cycle in relation to environmental contingencies
(Jacobs and Wingfield, 2000
).
The seasonal change in length of day is considered as an initial predictive
cue because it allows the organisms to make long-term predictions about their
habitat. There is an outstanding amount of knowledge on the effect and the
mechanisms of photoperiodism, the main initial predictive cue, on bird
reproductive cycles (for reviews, see Ball
and Balthazart, 2002
; Dawson et
al., 2001
; Farner,
1985
; Murton and Westwood,
1977
; Sharp,
1996
). On the other hand, there are supplementary cues, such as
temperature, which enable fine-tuning of responses to initial predictive cues,
and also provide short-term predictive information about the environment
(Wingfield and Kenagy, 1991
).
The effect of temperature on the timing of breeding has been well documented
(McCleery and Perrins, 1998
;
Meijer et al., 1999
;
Nager and van Noordwijk, 1995
;
O'Connor, 1978
;
Perrins and McCleery, 1989
;
Salvante et al., 2007
;
van Noordwijk et al., 1995
;
Visser et al., 2003
), but the
proximate mechanisms that precede the behavioural response to temperature cues
are still poorly understood (Dawson,
2007
; Visser et al.,
2009
). The effect of temperature on gonadal growth is one striking
example. Perfito and colleagues (Perfito
et al., 2004
) have found a clear correlation between ambient
temperature and gonadal growth in the field in two song sparrow (Melospiza
melodia morphna) populations breeding at similar latitudes but at
different altitudes. However, temperature manipulation in captivity showed a
much less convincing influence, with a modest effect on testis volume that was
furthermore limited to one population
(Perfito et al., 2005
). Other
studies have shown that temperature influence on gonadal growth may depend on
the latitudinal origin of the population/species considered
(Silverin et al., 2008
;
Wingfield et al., 2003
;
Wingfield et al., 1996
;
Wingfield et al., 1997
) and
that temperature may influence gonadal regression rather than its
recrudescence (Dawson, 2005
;
Silverin et al., 2008
;
Wingfield et al., 2003
)
(M.E.V., A. Dawson, S.P.C. and S. V. Schaper, unpublished data). The effect of
temperature on spring gonadal growth and its synergetic effect with the energy
needed to achieve this several thousand-fold recrudescence require further
investigation. In the context of climate change, such knowledge is highly
advocated because an adaptive response to the new environmental
characteristics is necessary to maximize fitness components
(Visser et al., 2004
).
The aim of this study was two-fold; we wanted to (1) decipher the respective roles of photoperiod and temperature on male testis seasonal growth, and (2) see whether the temperature-associated energy requirements may impair testis recrudescence in great tits.
| MATERIALS AND METHODS |
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|
|
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|
Testis size measurements
Testis size was measured three times during the experiment: at the end of
week 5 (while males were exposed to short days: 8 h L:16 h D, and temperature
set at 15°C); at the end of week 8 (mid-long days: 13 h L:11 h D, and
temperature kept at 15°C) to assess the influence of mid-long days on
early testis development; and at the end of week 11 (mid-long days: 13 h L:11
h D, temperature set at 8 or 22°C) to assess the fine-tuning effect of
temperature on the on-going testis recrudescence. Males were unilaterally
laparotomized under anaesthesia with isoflurane (Forene, Abbott b.v.,
Hoofddorp, The Netherlands). Testis length and width were measured to the
nearest 0.1 mm, using a scale engraved in the ocular of a binocular. Testis
volumes were calculated using the equation:
V=4/3
2β where
is half the testis
width and β is half the testis length.
Basal metabolic rate measurements
We measured basal metabolic rate (BMR) in terms of oxygen consumption, over
four successive nights at weeks 11 and 12, in an open-circuit respirometer.
Birds were isolated in six sealed respirometer chambers (0.76 l) and placed in
the darkness of a climate cabinet (Sanyo MIR-553, Sanyo E&E Europe BV,
Etten-Leur, The Netherlands) at 26°C, i.e. within their thermoneutral
zone. Chamber allocation was randomized according to the temperature treatment
of the birds used. H2O and CO2 were removed from the
inlet air (blown into the animal chamber) respectively with Drierite® (6
mesh, Sigma-Aldrich Chemie b.v., Zwijndrecht, The Netherlands) and
Ascarite® (5–20 mesh, Fluka, Zwijndrecht, The Netherlands). Air flow
rate was set to 250 ml min–1 with flowmeters (Brooks
Instrument b.v., Ede, The Netherlands) previously calibrated using a soap
bubble method (Bubble-O-Meter, LLC, Dublin, OH, USA). Oxygen content of outlet
air was measured with an oxygen analyser (Servomex 4100, Servomex BV,
Zoetemeer, The Netherlands). Oxygen consumption (ml O2
min–1) was calculated as the difference in oxygen
concentration between air from the respirometer chambers and reference air
from an empty chamber. As only one oxygen analyzer was used, measurements
alternated between the six experimental plus one reference chamber every 7.5
min. The oxygen consumption was converted to metabolic rate (kJ 24
h–1) by assuming an energetic equivalence of 20 kJ
l–1 O2. As BMR could only be measured in six birds
every night, we decided to sample 24 of the 35 male great tits included in the
experiment, to avoid long time gaps between the first and the last measured
birds, which could have biased the testis sizes subsequently measured. These
24 males were equally divided between the cold and warm treatments.
After the first set of BMR measurements, temperature was set back to 15°C for one week (week 12). A second set of BMR measurements was then performed on the same 24 birds 5 days later to assess the long-lasting effects of the cold and warm treatments on BMR (Fig. 1).
|
0.05. | RESULTS |
|---|
|
|
|---|
BMR
BMR differed significantly between the groups at the end of the temperature
treatments, at week 11 (F1,21=16.93, P<0.001),
but this significant difference had gone 5 days later, when birds were again
held under the same temperature (15°C), at week 12
(F1,21=4.19, P=0.054;
Fig. 3). Comparing these two
sets of BMR measurements using a repeated measures ANOVA (temperature
treatments as a factor), the effect of treatment
(F1,22=12.85, P=0.002) and the interaction
between treatment and temporal effects (F1,22=9.47,
P=0.006) were significant (Fig.
3). There was, however, no significant overall temporal difference
between the BMR measurements (F1,22=0.82,
P=0.376).
|
Influence of BMR on testis growth
When including both temperature and BMR in the analysis of testis growth,
the overall effect of temperature was still not significant
(F1,68=1.03, P=0.313), and there was no overall
influence of the BMR level on testis growth (F1,68=0.351,
P=0.555).
| DISCUSSION |
|---|
|
|
|---|
Temperature as a constraint factor
Although males held under cold temperature (8°C) showed a significantly
higher mean BMR than males kept under warm treatment (22°C), their testis
growth rates did not differ. The cold temperature treatment induced a 20%
increase in BMR compared with the warm treatment, which is comparable to the
costs induced by follicle growth in starlings (Sturnus vulgaris)
(Vézina and Williams,
2002
) and is twice the increase in BMR after an immune challenge
in great tits and blue tits (Cyanistes caeruleus)
(Ots et al., 2001
;
Svensson et al., 1998
).
Furthermore, in the present experiment, birds were fed ad libitum,
which suggests that the difference in BMR may even have been higher if the
food resources had been limited. If testis recrudescence was a high
energy-consuming process, and temperature a limiting constraint factor, we
would have expected a reduction in the testis growth rate in birds exposed to
the cold treatment. As this was not observed, testis growth in great tits may
be considered as a low energy-demanding process. A few old studies
investigated the relationship between metabolic rate and testis development in
birds, but they generally came to the same conclusion, that testis development
is not energetically costly (for reviews, see
King, 1973
;
Walsberg, 1983
).
However, the exact metabolic costs of testis enlargement and maintenance
are notoriously hard to determine
(Greenman et al., 2005
). As an
example, the cost of gonadal growth may be met through reallocation of
resources among different physiological systems, rather than in an additive
manner (Vézina et al.,
2003
). In this respect, testis growth rate in our cold temperature
treatment group may have been maintained thanks to a reallocation of energy
originally dedicated to e.g. general maintenance or immunity. On the other
hand, the recrudescence of the testes may itself not be costly, but
sperm/steroid production and its consequences, like the immunosuppressive
effect of testosterone (Folstad and
Karter, 1992
), may well be. Because testes were not fully
developed at the end of the present experiment (see
Fig. 2), the production of
sperm and steroids may still have been low at this stage
(Silverin et al., 2008
) and,
therefore, their potential costs would not have been expressed.
Temperature as a cue
While the potential metabolic cost of testis recrudescence has still to be
discovered, temperature may also act as a cue predicting the optimal timing
for breeding and/or developing the gonads.
There are several lines of evidence that bird egg laying dates are partly
decided according to past ambient temperatures, including that in great tits
(McCleery and Perrins, 1998
;
Meijer et al., 1999
;
Nager and van Noordwijk, 1995
;
O'Connor, 1978
;
Perrins and McCleery, 1989
;
Salvante et al., 2007
;
Visser et al., 2003
;
Visser et al., 1998
). From an
ecological point of view, this makes sense as bird fitness is closely related
to their ability to match their reproduction with the annual, short period of
arthropod abundance, which is highly dependent upon temperature
(Visser and Holleman, 2001
;
Visser et al., 2006
).
On the other hand, the influence of temperature on sexual physiology is
still highly debated. Some studies have demonstrated a clear effect of
temperature on gonadal, generally testis, growth
(Engels and Jenner, 1956
;
Wingfield et al., 2003
), while
others produced more inconsistent results
(Dawson, 2005
;
Farner and Wilson, 1957
;
Perfito et al., 2005
;
Silverin and Viebke, 1994
;
Suomalainen, 1937
;
Wingfield et al., 1996
). Among
these studies, several support a potential latitudinal variation in the
physiological response to temperature cues, with birds from southern latitudes
relying more on temperature cues than birds from the north
(Silverin et al., 2008
;
Wingfield et al., 2003
;
Wingfield et al., 1996
;
Wingfield et al., 1997
). The
degree to which organisms use supplemental factors (e.g. temperature) to time
their sexual activity would depend on the predictability of their breeding
environment. This predictability is a function of varying degrees of constancy
(the habitat is predictable because it is always the same) and contingency
(the habitat is predictable in the degree of change between seasons)
(Colwell, 1974
;
Wingfield et al., 1992
). The
ratio between contingency and constancy (Ie: environmental information factor)
reflects the relative importance of supplemental factors as a source of
predictive information (Wingfield et al.,
1992
). Populations breeding at low latitudes generally have a
higher Ie than populations breeding at high latitude, meaning that these low
latitude populations are expected to closely rely on supplemental information
to time their breeding period.
In a recent paper, Silverin and colleagues
(Silverin et al., 2008
)
compared the predictability (Pr) and the Ie factors between different
populations of great tits breeding at different latitudes. They demonstrated
that populations breeding in southern Europe have higher Ie indexes than
populations breeding in northern Europe, and these populations were also the
most sensitive to temperature treatments in aviaries. Birds from Italy held
under warm temperature (20°C) grew gonads sooner than birds held under
cold temperature (4°C), while no temperature effect on physiological
development was observed in northern populations of the same species
(Silverin et al., 2008
). The
male great tits used in the present study originate from a population that has
a Pr of 0.95 and an Ie of 3.8 (Fig.
4; see supplementary material Table S1 for the breeding data of
the Dutch population). Both Pr and Ie of our long-term-studied Dutch
population are very high, and the Ie is similar to that found in southern
Europe (Silverin et al.,
2008
). The absence of a temperature effect on photoperiodically
induced testis development in great tits from the Netherlands is therefore
surprising and somewhat contradicts the predictability model.
|
One must, however, be very cautious when interpreting these models of predictability, as the calculations are based on the annual repartition of egg laying, while the conclusions are generally applied to gonadal development. This may lead to erroneous conclusions given that egg laying and gonadal development are, to some extend, two different processes, induced by different temporal decisions that are not necessarily closely correlated (S.P.C. and M.E.V., manuscript in preparation).
The overall temperature difference between the cold and warm treatments in
the study by Silverin and colleagues
(Silverin et al., 2008
) was
2°C more than in the present study, and in particular the cold treatments
differed by 4°C between studies [4 vs 20°C in Silverin et al.
(Silverin et al., 2008
); 8
vs 22°C in the present study]. Although we cannot exclude the
possibility that this slight temperature range difference may explain the
discrepancies in the results of the two studies, if the Ie factor could
reliably predict population sensitivities to temperature in a natural context,
we might expect that the somewhat unnatural 14°C temperature difference
between the treatments in our study would have been sufficient to induce
differential testis growth rates.
The effect of temperature on bird seasonal reproduction clearly needs more
investigation. We need to clarify how the sexual physiology is affected by
temperature, how temperature cues and constraints respectively affect male and
female pre-breeding development, and how the temperature effects on gonadal
growth and on laying dates can be linked. As climate change mainly influences
the supplementary cues species use to time reproduction, understanding its
consequences in terms of population adaptation will depend highly on our
knowledge of the mechanisms by which temperature, and its interaction with
photoperiod, affects the reproduction of organisms
(Visser et al., 2004
).
| Acknowledgments |
|---|
| Footnotes |
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