University of Groningen
In ovo testosterone treatment reduces long-term survival of female pigeons
Matson, K. D.; Riedstra, B.; Tieleman, B. I.
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Journal of Animal Physiology and Animal Nutrition
DOI:
10.1111/jpn.12469
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Matson, K. D., Riedstra, B., & Tieleman, B. I. (2016). In ovo testosterone treatment reduces long-term
survival of female pigeons: a preliminary analysis after nine years of monitoring. Journal of Animal
Physiology and Animal Nutrition, 100(6), 1031-1036. https://doi.org/10.1111/jpn.12469
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DOI: 10.1111/jpn.12469
ORIGINAL ARTICLE
In ovo testosterone treatment reduces long-term survival of
female pigeons: a preliminary analysis after nine years of
monitoring
K. D. Matson1, B. Riedstra2 and B. I. Tieleman2
1 Resource Ecology Group, Department of Environmental Sciences, Wageningen University, Wageningen, The Netherlands, and
2 Groningen Institute for Evolutionary Life Sciences, University of Groningen, Groningen, The Netherlands
Summary
Early exposure to steroid hormones, as in the case of an avian embryo exposed yolk testosterone, can impact the
biology of an individual in different ways over the course of its life. While many early-life effects of yolk testosterone have been documented, later-life effects remain poorly studied. We followed a cohort of twenty captive
pigeons hatched in 2005. Half of these birds came from eggs with experimentally increased concentrations of
testosterone; half came from control eggs. Preliminary results suggest non-random mortality during the birds’
first nine years of life. Hitherto, all males have survived, and control females have survived better than testosterone-treated ones. Despite inherent challenges, studies of later-life consequences of early-life exposure in
longer-lived species can offer new perspectives that are precluded by studies of immediate outcomes or shorterlived species.
Keywords ageing, bird, egg, hormone, maternal effect, mortality
Correspondence Kevin D. Matson, Resource Ecology Group, Department of Environmental Sciences, Wageningen University, P.O. Box 47, 6700 AA
Wageningen, The Netherlands. Tel: +31 317481782; E-mail: kevin.matson@wur.nl
Received: 30 September 2015; accepted: 9 December 2015
Introduction
Exposure to steroid hormones impacts the biology of
animals in many ways. The specific nature of these
effects depends on, among other factors, timing. For
instance, both the ontogenetic stage at exposure and
the time elapsed since exposure can shape a hormone’s influence (Eising et al., 2006; Gil, 2008; Weinstock, 2008; Tobler et al., 2009; Riedstra et al., 2013).
One type of pertinent early-life experience is prenatal
(in utero or in ovo) exposure of offspring to maternal
hormones (Gil, 2008; Weinstock, 2008). Indeed,
female birds deposit steroid hormones in the yolks of
their eggs, and much research on this phenomenon
and its consequences has focused on testosterone, an
androgen whose presence in yolk was first reported by
Schwabl (1993).
Maternal yolk testosterone has benefits and costs
for offspring. These benefits and costs can manifest
themselves at different points in a bird’s lifetime, yet
most research focuses on early life (Sockman and Schwabl, 2000; Eising et al., 2006; Gil, 2008; Groothuis
and Schwabl, 2008). Variability in naturally deposited
concentrations of yolk testosterone is thought to serve
as a mechanism for developmental plasticity in offspring, so that offspring are as prepared as possible for
the post-hatch conditions they face (Gil, 2008). The
nature of those preparations, however, depends on
study species, sex and various experimental conditions. During the post-hatch period, nestling behaviour (e.g. begging), physiology (e.g. metabolism),
immunology (e.g. antibody production), morphology
(e.g. body size and colour) and other domains can be
influenced by prenatal testosterone exposure (Sockman and Schwabl, 2000; Pilz et al., 2004; Gil, 2008;
Tobler et al., 2009; Riedstra et al., 2013). While the
effects of absolute level and variability of testosterone
concentration on these domains are often considered
within a framework of Darwinian fitness (Eising et al.,
2006; Groothuis and Schwabl, 2008), effects on moreintegrative proxies, for example nestling survival
(Sockman and Schwabl, 2000; Pilz et al., 2004), are
also sometimes reported. On balance, young birds
might gain a survival advantage from increased testosterone, at least during the phase of parental dependency, but the broader biological context still matters.
Journal of Animal Physiology and Animal Nutrition 100 (2016) 1031–1036 © 2016 Blackwell Verlag GmbH
1031
In ovo testosterone reduces long-term survival of pigeons
As Gil (2008) concludes, more testosterone is probably
not always better, and costs borne by adults are especially unclear.
Later-life repercussions of yolk testosterone are
underexplored component of the cost–benefit balance
pertaining to testosterone’s effects on fitness (Gil,
2008). A few studies examine the relationship
between egg androgens and recruitment into local
breeding populations, but the results are mixed
(Tschirren et al., 2007; Hegyi et al., 2011; Ruuskanen
et al., 2012). Other studies that include measurements beyond the period of post-natal development
and into the period of sexual maturity in males and
females generally relate to the long-lasting organizing
effects of testosterone on behaviour, physiology,
immunology and secondary sexual differentiation
(Gil, 2008; Groothuis and Schwabl, 2008; Goerlich
et al., 2009; Riedstra et al., 2013). For example,
Tobler et al. (2009) show that experimentally
increasing testosterone concentration of eggs leads to
stronger primary and secondary antibody responses in
five- and seven-month-old Zebra finches (Taeniopygia
guttata), and Eising et al. (2006) show that a combined
androgen treatment (testosterone and androstenedione) of eggs leads to more-frequent sexual and
aggressive behaviours and more adult-like plumage in
ten-month-old Black-headed gulls (Larus ridibundus).
Both early- and later-life effects of yolk testosterone
can be sex specific (Adkins-Regan et al., 2013). Under
natural conditions, such sex specificity is obvious:
testosterone is predominantly a masculinizing mechanism and a driver of male biology (although during
avian development, estrogens also play a role in masculinization, e.g. Rochester et al., 2008). Yet in experimental studies, interactions between sex and
testosterone treatment are not always apparent. For
instance, in both examples cited above (Eising et al.,
2006; Tobler et al., 2009), the investigators tested for
and failed to find significant interactions of this type.
One long-term study that does show sex-specific
effects of in ovo testosterone treatment focuses on agespecific mortality in house sparrows (Passer domesticus)
over a 3.5-year period (Schwabl et al., 2011). This
study, which to the best of our knowledge is the only
study to date linking yolk testosterone and adult survival, suggests that elevated testosterone is protective
(i.e. reduces the mortality hazard) and that females
benefit more than males from this protective effect.
Given the dearth of long-term survival data, we
report the effects of in ovo testosterone treatment on
male and female survival until nine years of age in a
small cohort of homing pigeons (Columba livia domestica). Pigeons become sexually mature by approximately
1032
K. D. Matson, B. Riedstra and B. I. Tieleman
six months of age, raise multiple two-egg clutches per
year and have a maximum lifespan potential (MLSP)
of 35 years (Montgomery et al., 2011; Human Ageing
Genomic Resources, 2015).
Materials and methods
We studied twenty homing pigeons (twelve ♀, eight
♂) hatched late in 2005 (Table 1). Details about the
care and use of these birds have been published previously (van de Crommenacker et al., 2010), so we only
summarize key information here. Single-sex groups of
four individuals were housed separately in five covered, open-air aviaries. All birds were exposed to outside air temperature and natural photoperiod and
were provided with ad libitum food and water. Our
work with these animals complied with all applicable
institutional regulations (University of Groningen
Animal Experimentation Committee, license no.
5095) and Dutch and European laws.
Two experimental manipulations involved treating
only half of each sex (Table 1). The remaining birds
served as controls. Despite being nearly three years
apart, the two manipulations were balanced within
each sex and housing group. First, in 2005 we injected
freshly laid eggs either with 16 ng of testosterone in
0.1 ml sesame oil or with 0.1 ml sesame oil only. The
testosterone injection, designed as a uniform procedure to increase concentrations of the hormone in
both first and second eggs in the light of the overall
physiological range, was based on the data available in
2005 (relevant data from concurrent experiments are
available in Goerlich et al., 2009). Two eggs within a
clutch always received the identical injections, and all
clutches were produced by unmanipulated parental
pairs. The twenty individuals in this study hatched
from eggs that were first, second or from an unknown
position within their clutch. At the time of the second
manipulation in August 2008, the birds were adults.
On six consecutive days, we orally dosed individuals
either with 180 mg of lysozyme (L6876; Sigma, St.
Louis, MO, USA) in 1 ml phosphate-buffered saline
(PBS, P4417; Sigma) or with 1 ml of PBS only (van de
Crommenacker et al., 2010).
All other procedures were applied consistently to all
birds. These universal procedures included the following: weighing, behavioural testing, blood sampling,
cloacal and choanal swabbing, fasting, temporary isolation for quantifying food consumption and basal
metabolic rate, and de-worming. In 2006, all birds
received an injection of 0.5 ml of a 2% suspension of
sheep red blood cells. In 2008, all birds received an
injection of 2 ml/kg body mass of a 1.25 mg/ml solu-
Journal of Animal Physiology and Animal Nutrition 100 (2016) 1031–1036 © 2016 Blackwell Verlag GmbH
In ovo testosterone reduces long-term survival of pigeons
K. D. Matson, B. Riedstra and B. I. Tieleman
Table 1 Traits of the twenty individual homing pigeons in the study
Bird No.
Lay
Order
Hatch
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
1
?
1
2
1
?
1
2
1
?
1
1
2
1
?
1
2
1
1
1
25 Dec. 2005
30 Nov. 2005
22 Dec. 2005
24 Dec. 2005
23 Dec. 2005
22 Dec. 2005
25 Dec. 2005
24 Dec. 2005
23 Dec. 2005
24 Dec. 2005
24 Dec. 2005
23 Dec. 2005
26 Dec. 2005
23 Dec. 2005
20 Dec. 2005
26 Dec. 2005
26 Dec. 2005
24 Dec. 2005
22 Dec. 2005
22 Dec. 2005
Death
Age at
Death
(year)
Cause
Sex
Testo*
SRBC†
Lyso‡
LPS§
Group¶
6 Feb. 2011
2 April 2013
17 July 2013
29 Jan. 2011
28 Sept. 2012
–
17 July 2013
–
–
–
–
–
–
–
–
–
–
–
–
–
5.1
7.3
7.6
5.1
6.8
–
7.6
–
–
–
–
–
–
–
–
–
–
–
–
–
Euthanized
Died
Died
Died
Euthanized
–
Euthanized
–
–
–
–
–
–
–
–
–
–
–
–
–
F
F
F
F
F
F
F
F
F
F
F
F
M
M
M
M
M
M
M
M
Yes
Yes
Yes
Yes
Yes
Yes
No
No
No
No
No
No
Yes
Yes
Yes
Yes
No
No
No
No
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
No
No
No
Yes
Yes
Yes
No
No
No
Yes
Yes
No
No
Yes
Yes
No
No
Yes
Yes**
Yes
Yes
Yes
Yes**
Yes
Yes
Yes**
Yes
Yes
Yes**
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
1
5
2
1
2
5
1
2
5
1
2
5
3
4
3
4
3
4
3
4
Notes
Clutch mate of no. 5
Clutch mate of no. 4
Clutch mate of no. 9
Clutch mate of no. 8
*Testosterone, in ovo in 2005.
†Sheep red blood cells, injection in 2006.
‡Lysozyme, orally in August 2008.
§Lipopolysaccharide, injection in August 2008 or before. **Two injections.
¶Initial housing groups maintained until three of four groupmates died (only group 1 on 17 July 13); then groups 1 and 2 were merged to form a new
three member group.
tion of lipopolysaccharide (LPS; L7261; Sigma) dissolved in PBS (van de Crommenacker et al., 2010). A
subset (four ♀) had already received an earlier LPS
injection in a pilot study.
We used contingency tables and exact tests to evaluate associations between characteristics of the birds
(i.e. male/female, control/treatment) and their survival until nine years of age (i.e. alive/dead).
Results
By 1 January 2015, the 14 surviving pigeons were all
just over nine years of age (Table 1). Six birds, all
female, had died (median lifespan: 7.1 years, range:
5.1–7.6 years). The four sex by testosterone treatment
groups (control males, testosterone-treated males,
control females, testosterone-treated females) differed
in survival (Fisher–Freeman–Halton test of 4 9 2
table, n = 20, p = 0.011; if either member of each of
the two same-sex sibling pairs is discarded, n = 18,
p = 0.024; Freeman and Halton, 1951). Analogous
analyses revealed no significant effects of housing
group (i.e. aviary) or of lysozyme, the only other
experimental treatment not experienced by all twenty
pigeons.
While all males survived, control females survived
better than testosterone-treated ones (Fisher–Boschloo test of 2 9 2 table, test statistic = 0.080,
p = 0.039, power = 0.68; Lydersen et al., 2009). To
check the robustness of these results, we repeated the
analyses using Kaplan–Meier curve comparisons
(either the four sex by testosterone treatment groups
or only control and testosterone-treated females,
Fig. 1) and Cox proportional hazards regression analysis (only control and testosterone-treated females, as
males were invariable); all gave similarly significant
results (all p < 0.05).
Discussion
With their MLSP of 35 years, pigeons have served as a
model of longevity in studies of the physiology of ageing (Montgomery et al., 2011; Human Ageing Genomic Resources, 2015). Using such a model to study the
effects of early-life exposure to testosterone on mortality, the ultimate late-life consequence and an
Journal of Animal Physiology and Animal Nutrition 100 (2016) 1031–1036 © 2016 Blackwell Verlag GmbH
1033
In ovo testosterone reduces long-term survival of pigeons
K. D. Matson, B. Riedstra and B. I. Tieleman
Fig. 1 Survival of female pigeons hatched
from control and testosterone-treated eggs
over the nine-year study period. Males, none of
which have died, are not shown.
important determinant of lifetime reproductive success in long-lived species (Clutton-Brock, 1988), not
only offers new perspectives (Groothuis and Schwabl,
2008) but also presents notable challenges.
At the nine-year mark, the in ovo testosterone
treatment had exerted sex-specific effects on survival.
With testosterone-treated females dying before control females, in ovo testosterone treatment could limit
lifetime reproductive success. As in the study of
house sparrows by Schwabl et al. (2011), the precise
mechanisms mediating the effects of testosterone on
survival were impossible to pin down in the current
study (but for discussions of potential mechanisms,
see Gil, 2008; Groothuis and Schwabl, 2008; Schwabl
et al., 2011). Our pigeons were never allowed to
reproduce (sexes housed separately), but females
routinely laid eggs during most months in all years.
This one-sided investment in (attempted) reproduction could contribute to the sex specificity of our
results. Additionally, while our pigeons were isolated
from predators, the same cannot be said about parasites (pers. obs. of lice, ticks, intestinal worms,
haematozoa) or microbes more generally (Matson
et al., 2015). In the light of the long-lasting organizing effects of yolk testosterone on the immune system (Glick and Sadler, 1961; Gil, 2008; Tobler et al.,
2009), control and testosterone-treated females might
have responded differently to similar immunological
triggers (Schwabl et al., 2011).
1034
The apparent sex-specific testosterone effect discussed above could disappear in the future if most or
all testosterone-treated males die before the control
males. But this scenario would almost certainly result
in an overall negative effect of testosterone on survival. Furthermore, with only one treated female still
living, the effect of testosterone within females is
nearly fixed. (In fact, of the 720 possible permutations
of deaths of the remaining six females, only one outcome, that is if the sole surviving testosterone-treated
female outlives all five remaining control females,
would eliminate the significant effect of testosterone
on female survival.)
While yolk testosterone treatment negatively
impacted survival until nine years of age in female
pigeons, a similar treatment was previously found to
be protective in female house sparrows (Schwabl
et al., 2011). We can only speculate about the causes
of this discrepancy. As might be expected for two
species from different taxonomic orders, many lifehistory traits differ between pigeons and house sparrows (Human Ageing Genomic Resources, 2015).
Pigeons have a greater MLSP than house sparrows
(23 years), and other longevity data in these species
paint a similar picture (Montgomery et al., 2011; Schwabl et al., 2011; Human Ageing Genomic Resources,
2015). But rather than a single trait like longevity, a
species’ relative position on a multivariate ‘slow–fast’
life-history continuum (Ricklefs, 2000) might govern
Journal of Animal Physiology and Animal Nutrition 100 (2016) 1031–1036 © 2016 Blackwell Verlag GmbH
In ovo testosterone reduces long-term survival of pigeons
K. D. Matson, B. Riedstra and B. I. Tieleman
the costs and benefits of yolk testosterone experienced
by males and females in different age classes. Regardless, in combination, our current results and the contradictory results of Schwabl et al. (2011) allow us to
recapitulate and extend previous conclusions: these
studies of adult survival show that broader biological
context, including study species identity, matters and
that more testosterone is not always better, just as
with early-life consequences.
Practical considerations related to maintaining and
individually monitoring pigeons or other long-lived
animals for years or decades (e.g. space, costs) have
likely contributed to the focus on short-term studies
of early-life consequences (Gil, 2008). These same
considerations tend to constrain sample sizes, but in
the current study with six females per group, the
testosterone effect was clear. Of the six dead pigeons,
three were found dead from unknown causes. The
other three were found sufficiently close to death that
animal caretakers, who were blind to experimental
treatments and research questions, were compelled by
animal welfare regulations to euthanize the birds to
end their suffering. No decision to euthanize resulted
from an isolated traumatic injury (e.g. a broken wing)
but instead from more general indicators (e.g. extreme
weight loss, failure to move when approached). Notably, the last bird euthanized was the first death of a
control bird, thereby weakening the statistical results
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