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First published online January 18, 2008
Journal of Experimental Biology 211, 459-465 (2008)
Published by The Company of Biologists 2008
doi: 10.1242/jeb.013219
Dietary protein influences the rate of 15N incorporation in blood cells and plasma of Yellow-vented bulbuls (Pycnonotus xanthopygos)
1 Department of Biology, Technion – Israel Institute of Technology, Haifa
32000, Israel
2 Department of Zoology and Physiology, University of Wyoming, Laramie, WY
82071, USA
3 Department of Biology, University of Haifa at Oranim, K. Tivon 36006,
Israel
* Author for correspondence (e-mail: elat{at}techunix.technion.ac.il)
Accepted 20 November 2007
| Summary |
|---|
|
|
|---|
15N=
15Ntissues–
15Ndiet
was also dependent on dietary protein content, and was lowest in birds fed the
diet with the highest protein content. Blood, plasma and excreta were enriched
in 15N relative to diet. In contrast, ureteral urine was either
significantly depleted of 15N in birds fed the diet with the lowest
protein content or did not differ in
15N from the diets with
the intermediate and high protein content. Thus, isotopic incorporation rates
and tissue-to-diet discrimination factors cannot be considered fixed, as they
depend on diet composition.
Key words: incorporation rate, stable isotopes, Yellow-vented bulbul, protein intake, diet reconstruction
| INTRODUCTION |
|---|
|
|
|---|
Tieszen et al. (Tieszen et al.,
1983
) hypothesized that tissues with high metabolic activity would
also have high rates of isotopic incorporation. The notion of the existing
relationship between animal basal metabolic rate (BMR) and its isotopic
fractional turnover rate was challenged by Voigt et al.
(Voigt et al., 2003
) and Voigt
and Matt (Voigt and Matt,
2004
). They studied carbon and nitrogen turnover rates in blood
and wing membrane of two nectarivorous bat species (Leptonycteris
curasoae and Glossophaga soricina), which have high
mass-specific BMRs. Hence, it was expected that the isotopic fractional
turnover rate of these species would also be high. Surprisingly, the turnover
rates of both elements were found to be the lowest measured so far in a
vertebrate. This study implies that N isotopic turnover rate might be
unrelated to the animal's BMR as was commonly thought. However, the diets used
in Voigt and colleagues' (Voigt et al.,
2003
) experiments had protein contents that were insufficient to
meet the bat's requirements (Herrera et al., 2006), and the bats lost mass.
When Mirón et al. (Mirón et
al., 2006
) fed Pallas' long-tongued bats (G. soricina)
diets with adequate protein levels, they had much higher levels of isotopic
incorporation than those reported by Voigt et al.
(Voigt et al., 2003
). The
contrast between the results of Voigt et al.
(Voigt et al., 2003
) and
Mirón et al. (Mirón et al.,
2006
) suggests that the dietary protein level is a controlling
factor in the rate of isotopic incorporation.
The idea of a relationship between metabolic rate and both C and N isotopic
incorporation rates was expanded upon by Carleton and Martínez del Rio
(Carleton and Martínez del Rio,
2005
) who interpreted `high metabolic activity' as high rates of
protein synthesis and catabolism. They tested the hypothesis that chronic cold
exposure, and hence an increase in metabolic rate, would increase the isotopic
incorporation rate of 13C and 15N in House sparrow
(Passer domesticus) red blood cells. They found that despite an
increased metabolic rate, cold exposure had no effect on 15N
incorporation rate, and had only a small effect on 13C
incorporation rate. They concluded that the relationship between metabolic
rate and the rate of isotopic incorporation into an animal's tissue is
indirect and probably mediated by protein turnover rate. Dietary proteins are
known to have a regulatory effect on protein synthesis and degradation
(Millward, 1989
;
Lobley, 2003
). Physiologists
have documented increases in protein synthesis resulting from increased
protein intake in fish (Millward,
1989
; Houlihan et al.,
1995
), domestic chickens (Dror
et al., 1997
) and mammals
(Yahya et al., 1994
;
Wessels et al., 1997
;
Williams et al., 2001
),
including humans (Foulliet et al.,
2001
). Hence, we should expect to find a correlation between
protein intake and N fractional isotopic turnover rate.
We conducted a feeding experiment on captive Yellow-vented bulbul
(Pycnonotus xanthopygos), a frugivorous bird of the Old World, to
test the conjecture that dietary protein influences the rate of isotopic
incorporation. Birds received diets that had similar caloric values and
similar
15N isotopic signatures but varied in their protein
content. Hence, we could isolate the effect of dietary elemental
concentrations on fractional N isotopic turnover rate in tissues. The goals of
the experiment were to determine the effect of protein intake on: (1) nitrogen
fractional turnover rate of red blood cells and plasma, and (2)
15N tissue–diet discrimination factors of blood cells,
plasma, excreta and ureteral urine. We hypothesized that the N fractional
isotopic turnover rate and the
15N tissue–diet
discrimination factors would increase with increasing protein intake. The
depletion in 15N in nitrogenated excreted products has often been
invoked as the cause of the tissue-to-diet enrichment in 15N
(Minagawa and Wada, 1984
;
Martínez del Rio and Wolf,
2005
). Thus, we also hypothesized that both ureteral urine and
excreta would be depleted of 15N relative to diet.
Isotopic incorporation data are commonly analysed using simple,
one-compartment models, with first-order kinetics
(Carleton and Martínez del Rio,
2005
; Mirón et al.,
2006
; Cerling et al.,
2007
). Cerling et al. (Cerling
et al., 2007
) challenged the use of these models and championed
the use of more complex multi-compartment models. We used our data and
information theoretic model comparison methods to evaluate Cerling and
colleagues' (Cerling et al.,
2007
) claim (Stephens et al.,
2007
). We used Akaike's information theoretic criteria to assess
whether evidence supported the use of one-compartment or two-compartment
models.
| MATERIALS AND METHODS |
|---|
|
|
|---|
|
Diet shift experiment
After consuming the first diet for 75 days, birds were divided randomly
into three groups; each bird received a diet containing a different amount of
casein protein (5 birds – low protein, 4 birds – medium protein, 4
birds – high protein; Table
1). Our diets fully satisfied the bird's nitrogen requirements
(Tsahar et al., 2005
). Again,
we used the same batch of each ingredient during the experiment; each was
mixed prior the experiments so that the diet throughout the experiment would
have the same isotopic signature. The birds received the second diet for 95
days. Blood and excreta samples were taken on the day prior to the dietary
switch (day 0) and then on days 2, 4, 9, 21, 35, 57, 80 and 95 of consuming
the casein diet. Blood was collected (
100 µl) in heparinized
microhaematocrit tubes by puncturing the brachial vein with a 28 gauge needle.
Plasma was separated from cells after centrifugation (micro-haematocrit
centrifuge model CL A4922X-1, International Equipment Co., Needham Heights,
MA, USA) for 3 min. Ureteral urine samples were collected on day 95 by briefly
inserting a closed-ended perforated cannula
(Goldstein and Braun, 1989
),
custom-made of polyethylene tubing (PE200), into the bird's cloaca. On the
same day, we also collected excreta samples for 24 h. Body mass was measured
every sampling day. Both excreta and ureteral urine were collected and stored
in a dilute (0.001 N) HCl solution. Birds were released at the capture site
upon completion of the experiment. Samples were kept frozen (–20°C)
until the end of the experiment. Plasma and blood cells were spread on glass
slides and oven dried for 3–4 days at 50°C. All dried samples were
scraped from the glass using a razor blade, and homogenized using a mortar and
pestle.
All samples were ground into a fine powder before being loaded (30–70
µg) into tin capsules. Isotope ratios of food were measured in a continuous
flow isotope ratio mass spectrometer (Finnigan Delta+XP, University of
Wyoming's Light Stable Isotope Facility) with samples combusted in a Costech
elemental analyser. The precision of these analyses was ±0.2
for both isotopes. Our standards were peptone
(
15N=5.60
, AIR, USGS40 8542) and glycine
(
15N=0.73
, AIR, IAEAN2). We included standards in
every run to correct raw values obtained from the mass spectrometer. Stable
isotope ratios were expressed using standard delta notation
(
15N) in parts per million (
) as:
![]() |
|
Statistical analyses
Preliminary diagnoses on the use of one- or two-compartment models were
performed using Cerling and colleagues'
(Cerling et al., 2007
)
reaction-progress approach. Briefly, we plotted ln(1–F), where
(1–F)=[
15N(t)–
15N(
)]/[
15N(0)–
15N(
)]
against time and assessed visually whether a single line or more than one line
was needed to describe the data. Isotopic incorporation data were then fitted
using a non-linear fitting routine (JMP®, version 6.0, SAS Institute,
Cary, NC, USA) to either one- or two-compartment models using the following
equations, respectively:
![]() | (1) |
![]() | (2) |
15N(0) and
15N(
) represent
the initial and asymptotic nitrogen isotopic compositions. Eqns
1 and
2 differ slightly from those used
in most isotopic incorporation studies
(Carleton and Martìnez del Rio,
2005
i=1/k, days) as a parameter to
describe incorporation rate. We chose to use this parameter for two reasons:
(1) it has a clear intuitive interpretation as the average retention (or
residence) time of 15N for the one-compartment model, and (2) the
non-linear routine used in our analysis gave asymptotic s.e.m. estimates. In
previous studies, such as those listed above, researchers estimated the
fractional rate of incorporation (k=1/
) and used it to estimate
the half-life of an element in a tissue
(t1/2=
xln(2)=ln(2)/k). This approach
does not allow for estimates of uncertainty in the calculation of these
half-lives. Our approach allows estimates of uncertainty in the calculation of
the parameter that isotopic ecologists care about – how long does an
element stay in a tissue? To assess the weight of evidence in favour of a one-
or a two-compartment model, we compared the Akaike's information criteria
corrected for small samples (AICc) of the two models and chose the model with
the lowest AICc value (Burnham and
Anderson, 2002
i=AICci–AICcmin, where AICcmin
is the lowest value in a comparison) as a measure of the plausibility of an
alternative model. They suggest that high values of
i (
i>2)
indicate low support for the alternative model [see p. 70 in Burnham and
Anderson (Burnham and Anderson,
2002
as an estimate of average
retention time, whereas if it supported a two-compartment model, we estimated
average retention time as:
![]() | (3) |
15N) as
15N(
)tissues–
15Ndiet.
Finally, we examined the effect of protein content in the diet on average
15N retention time and
15N (defined as
15N=
15Ntissues–
15Ndiet)
with one-way analysis of variance followed by Tukey–Kramer multiple
comparisons among means (P<0.05). We used one-sample Student's
t-tests to compare the
15N of plasma, cells,
excreta and ureteral urine with that of diet.
|
|
| RESULTS |
|---|
|
|
|---|
i values ranged from 2.1 to 15.8, suggesting
little support for the two-compartment model. Consequently, we used
to
characterize the residence time of 15N in plasma and blood cells.
The one-compartment model was not only better than the two-compartment model
but it also described the data adequately well
(r2>0.94; Fig.
2).
The protein content of the diet had a significant effect on the residence
time of 15N (F2,10=5.54 and
F2,10=4.73, P<0.05, for cells and plasma,
respectively; Fig. 3). As
predicted, 15N residence time was higher when birds ate the diet
with the lower protein content. Dietary protein content also had a significant
effect on
15N (F2,10=7.53 and
F2,10=9.58, P<0.01, for cells and plasma,
respectively; Fig. 4).
15N did not differ between the diets with low and medium
protein, but was significantly lower in the diet with the highest protein
content (Fig. 4). Blood, cells
and excreta were enriched in 15N relative to diet (one-sample
t>13, P<0.01; Fig.
5). In contrast, urine was either depleted of 15N
relative to diet (low protein diet, t=2.8, P<0.05;
Fig. 5) or did not differ
significantly from diet (medium and high protein diets, t=0.4 and
0.04, P>0.5, respectively; Fig.
5).
|
|
|
| DISCUSSION |
|---|
|
|
|---|
15N with higher
protein intake. Finally, we consider the implications of the effect of protein
intake on isotopic incorporation for the interpretation of ecological isotopic
data.
One, two,... How many compartments?
Isotopic ecologists have three questions in mind when they conduct an
isotopic incorporation experiment. (1) On average, what is the residence time
of an isotope in a tissue? (2) How much confidence can we place on this
estimate? (3) What are the factors that influence its value? Biologists
conduct isotopic incorporation studies on captive animals to answer these
three questions. Thus, the central parameter of interest that results from
isotopic incorporation experiments is the average retention time (
),
which can easily be transformed into the more widely used half-life
{t1/2=
[ln(2)]
(Carleton and Martínez del Rio,
2005
)}. In our study, the average retention time of 15N
in blood cells was almost fourfold longer than that in plasma. In
Yellow-vented bulbuls the isotopic composition of plasma is informative about
diet changes at the scale of less than a week, whereas cells reveal patterns
of resource use at the scale of from 20 days to a month.
Until recently, most isotopic incorporation studies used first-order,
one-compartment models (Eqn 1) to
describe isotopic incorporation data
(Martínez del Rio and Wolf,
2005
). Recently, Cerling et al.
(Cerling et al., 2007
)
questioned the general use of these simple models and proposed the use of an
alternative graphical approach to diagnose whether a data set revealed whether
models with more than one compartment/pool are needed to describe an isotopic
incorporation data set. This method is potentially important because using the
wrong model can lead to erroneous estimation of average residence time.
Cerling's approach relies on `linearizing' the isotopic incorporation data and
using least-squares linear regression on the resulting linear segments to
estimate the relative size of each pool/compartment and its
`decay'/incorporation constant (Fig.
1) (Ayliffe et al.,
2004
).
Although the need to use the correct model to describe isotopic
incorporation data is undeniable, the method proposed by Cerling et al.
(Cerling et al., 2007
) has
several shortcomings: (1) it does not allow an estimate of an isotope's
retention time (and a measure of how much confidence we can place in it) to be
derived; (2) one has to identify the linear segment for each component/pool
visually; (3) it relies on log-transforming data, which often leads to biased
estimation (Motulsky and Ransnas,
1987
); and (4) there is no quantitative criterion that permits the
finding out of whether one should use one, two or more compartments. Using
non-linear regression procedures to fit incorporation data to models of
increasing complexity overcomes problems 2 and 3
(Bates and Watts, 1988
). These
models are widely available in most statistical analysis packages. For
one-compartment models, the output of these programs includes various
estimates of standard error for
that can then be used to estimate a
confidence interval (e.g. Motulsky and
Christopoulos, 2003
). For more complex, multi-compartment models,
Eqn 3 can be used to estimate
average retention time (C.M.d.R. and R. A. Sprecher, unpublished
observations).
To overcome problem 4 we used the information theoretic approach advocated
by Burnham and Anderson (Burnham and
Anderson, 2002
) and widely adopted in ecological studies
(Hobbs and Hilborn, 2006
).
This approach has a strong theoretical foundation and is based on the idea
that we should adopt parsimonious models, which avoid under- and over-fitting
and give accurate approximations to the interpretable information in the data
available (Anderson and Burnham,
2001
). Our data supported the use of one-compartment over
two-compartment models for plasma and blood cells in Yellow-vented
bulbuls.
How does protein intake influence isotopic incorporation rate?
In Yellow-vented bulbuls, protein intake had a significant effect on both
15N incorporation rate and
15Ntissue–diet. Birds that consumed more
protein had significantly higher 15N incorporation rates and lower
15Ntissue–diet. Carleton and
Martínez del Rio (Carleton and
Martínez del Rio, 2005
) hypothesized that protein turnover
was a primary determinant of isotopic incorporation. If this hypothesis is
correct, then the same factors that influence protein turnover should
influence isotopic incorporation. Protein intake influences protein turnover
through the action of catabolic (glucagon, adrenaline and cortisol) and
anabolic hormones [insulin, IGF and growth hormone (reviewed by
Waterlow, 2006
)]. The
secretion of these hormones appears to be mediated by circulating amino acid
concentrations, which in turn are influenced by diet composition
(Waterlow, 2006
). The
differences in 15N incorporation rate among diets observed in
Yellow-vented bulbuls is consistent with the idea that protein turnover is a
determinant of isotopic incorporation rates.
Muramatsu et al. (Muramatsu et al.,
1987
) reported an increase in protein turnover with protein intake
at modest levels of protein intake in chickens. In these animals, the effect
of protein intake on both synthesis and catabolism was independent of protein
intake at high protein intakes (Muramatsu
et al., 1987
). Similarly, in blood cells isotopic incorporation
rate (as estimated by 15N retention time) increased from the low to
the medium diet, but did not differ between the diets with medium and high
protein levels. Tsahar et al. (Tsahar et
al., 2005
) estimated the maintenance nitrogen requirement (MNR)
for Yellow-vented bulbuls as
8.2 mg N per day. From daily consumption
measurements, we estimated that the daily nitrogen intake of birds on the low
protein diet was
97 mg N per day, which is more than an order of
magnitude higher than their MNR. We expect the effect of protein intake on
isotopic incorporation rate to be greater at lower nitrogen intakes, when N
intake rates approach MNR.
Our results were contrary to an assumption widely invoked in the stable
isotope literature: if animals satisfy isotopic mass balance, then
15Ntissue–diet can only be positive if (1)
the
15N of excreted nitrogen is more negative than that of
tissues (Minagawa and Wada,
1984
; Ponsard and Averuch,
1999
), and (2) at steady state, the
15N of
excreted products is equal to that of diet
(Martínez del Rio and Wolf,
2005
). Although we found that the
15N of
excreted nitrogen was more negative than that of tissues, in all cases the
15N of excreted nitrogen was significantly more positive
than that of diet (Fig. 5). The
15N of ureteral urine was, as expected, either more depleted
of 15N than diet or had the same
15N as diet. How
can we explain the widely observed positive value of
15Ntissue–diet if excreted nitrogen has a
more positive value than diet? And, how can we explain the difference in
15N between excreta and ureteral urine? There are two
alternative/complementary explanations: (1) isotopically light ammonia may
have been lost during the collection of excreta samples but not during the
collection of ureteral urine, and (2) birds lost isotopically light nitrogen
from ureteral urine through an unidentified venue.
Because excreta and urine samples were collected in an HCl solution (pH
3) which `traps' ammonia by turning it into ammonium chloride, the first
explanation seems unlikely. The second explanation invokes an unknown `sink'
of isotopically light nitrogen. We speculate that this sink is ammonia lost as
a gas through respiratory epithelia. Tsahar et al.
(Tsahar et al., 2005
)
demonstrated that in Yellow-vented bulbuls the amount of uric acid and ammonia
excreted in ureteral urine is much lower than the amount lost in excreta.
These authors suggested that these compounds are re-absorbed in the lower gut
as a mechanism of nitrogen conservation. It may be that Yellow-vented bulbuls
reabsorb isotopically light uric acid and ammonia preferentially, which would
explain the difference between the
15N of urine and excreta.
Some of the absorbed, isotopically light, ammonia may be then lost in breath.
In humans, a significant amount of ammonia is lost in exhaled air, and ammonia
levels in breath are routinely measured to diagnose renal diseases and
Helicobacter pylori infection
(Smith et al., 1999
;
Narasimhan et al., 2001
;
Kearny et al., 2002
). Although
this hypothesis is admittedly speculative, it has the virtue of being
testable. It requires measuring the contribution of exhaled nitrogen losses to
nitrogen balance and the isotopic composition of ammonia in breath. Although
the 15N trophic enrichment between tissues and diet is of enormous
value to ecologists (Roth and Hobson,
1999
; Post, 2002
),
explaining its magnitude remains an unsolved problem for physiologists (Gannes
et al., 1998; Adams and Sterner,
2000
; Robbins et al.,
2005
).
Ecological implications
The rate at which a tissue incorporates the isotopic signal of a diet
determines the time window during which ecologists can discern diet changes
(Pearson et al., 2003
;
Podlesak et al., 2005
). The
almost fourfold difference in isotopic incorporation between plasma and blood
cells is useful as it allows the finding out of diets at two contrasting
scales. Plasma will reveal the isotopic composition of foods eaten over the
last few days, whereas blood cells will reflect the average composition of
foods incorporated over approximately a month
(Hobson and Clark, 1992
;
Norris et al., 2004
;
Dalerum and Angerbjörn,
2005
). Blood cells and plasma are particularly valuable tissues in
isotopic studies because sampling them is minimally invasive
(Norris et al., 2005
).
Previous research documented the effect of tissue type
(Hobson and Clark, 1992
;
Dalerum and Angerbjörn,
2005
; Podlesack et al., 2005), growth rate
(Fry and Arnold, 1982
;
MacAvoy et al., 2005
) and body
mass (Carleton and Martínez del Rio,
2005
) on isotopic incorporation rate. Our results suggest that the
level of dietary protein also plays a role. Although we only documented an
effect on plasma and blood cells, two tissues commonly used in ecological
studies [Norris et al. (Norris et al.,
2005
) and references therein], it is likely that protein intake
influences the rate of isotopic incorporation in other tissues as well. The
effect of protein intake seems to be biologically significant. The average
retention time of 15N in birds fed on the low protein diet was
longer than that of birds fed on the high protein diet by 136% and 160% for
cells and plasma, respectively. Our results support Mirón M. and
colleagues' (Mirón et al.,
2006
) conjecture that protein intake influences isotopic
incorporation rates and suggests that the anomalously long isotopic retention
times found by Voigt et al. (Voigt et al.,
2003
) in nectar-feeding bats were the result of an experimental
diet with almost no protein. Our results demonstrate the effect of dietary
protein on isotopic incorporation in a single species. We hypothesize that
this effect may also be found among other species, and that species with low
protein intakes such as nectarivores and frugivores will have lower rates of
isotopic incorporation than species with high protein intakes, such as
carnivores (Tsahar et al.,
2006
). If our speculation is correct, isotopic field studies may
have to be informed by the dietary natural history of the animals studied,
including their seasonal diet changes.
LIST OF ABBREVIATIONS AND SYMBOLS
15N
)
15Ntissue–diet
)
i
i=AICci–AICcmin)

| Acknowledgments |
|---|
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|---|
|
|
|---|
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