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. 2020 Dec 21;11(1):214–226. doi: 10.1002/ece3.7015

Hematocrit, age, and survival in a wild vertebrate population

Thomas J Brown 1,, Martijn Hammers 2, Martin Taylor 1, Hannah L Dugdale 3, Jan Komdeur 2, David S Richardson 1,4
PMCID: PMC7790625  PMID: 33437424

Abstract

Understanding trade‐offs in wild populations is difficult, but important if we are to understand the evolution of life histories and the impact of ecological variables upon them. Markers that reflect physiological state and predict future survival would be of considerable benefit to unraveling such trade‐offs and could provide insight into individual variation in senescence. However, currently used markers often yield inconsistent results. One underutilized measure is hematocrit, the proportion of blood comprising erythrocytes, which relates to the blood's oxygen‐carrying capacity and viscosity, and to individual endurance. Hematocrit has been shown to decline with age in cross‐sectional studies (which may be confounded by selective appearance/disappearance). However, few studies have tested whether hematocrit declines within individuals or whether low hematocrit impacts survival in wild taxa. Using longitudinal data from the Seychelles warbler (Acrocephalus sechellensis), we demonstrated that hematocrit increases with age in young individuals (<1.5 years) but decreases with age in older individuals (1.5–13 years). In breeders, hematocrit was higher in males than females and varied relative to breeding stage. High hematocrit was associated with lower survival in young individuals, but not older individuals. Thus, while we did not find support for hematocrit as a marker of senescence, high hematocrit is indicative of poor condition in younger individuals. Possible explanations are that these individuals were experiencing dehydration and/or high endurance demands prior to capture, which warrants further investigation. Our study demonstrates that hematocrit can be an informative metric for life‐history studies investigating trade‐offs between survival, longevity, and reproduction.

Keywords: aging, biomarkers, birds, condition markers, hematocrit, life history, senescence, survival, trade‐offs, wild populations


Using long‐term data we investigated the association between haematocrit, longitudinal age and survival in a wild vertebrate population—the Seychelles warbler (Acrocephalus sechellensis). Haematocrit exhibited a distinctive age‐dependent pattern within‐individuals, and young individuals with high haematocrit had poorer survival prospects. This study highlights a novel physiological change with age that is indicative of individual condition in wild populations.

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1. INTRODUCTION

An organism's fitness is the product of many integrated physiological systems, and their interaction with the environment. Activity in one physiological system can limit resource availability and generate negative consequences (e.g., by‐products) for another (Harshman & Zera, 2007; Leroi, 2001; Ricklefs & Wikelski, 2002). These trade‐offs form the basis of life history. Physiological markers provide valuable insights into life‐history trade‐offs, condition, and senescence—particularly in wild populations, where complex environmental factors can weaken associations between life‐history traits and observed fitness (Nussey et al., 2008). Many physiological markers (oxidative stress, hormone regulation, etc.) yield complex and/or inconsistent associations with life history, survival, and reproductive success (e.g., Johnstone et al., 2017; Norris & Evans, 2000; Speakman & Selman, 2011; Wilder et al., 2016); thus, there is a continued need to identity and validate such markers.

Aerobic capacity, which contributes to endurance and performance, is a vital physiological trait for organismal health and fitness. Aerobic capacity depends on the oxygen‐carrying capacity of blood, which is determined by the concentration of hemoglobin and the rate of blood flow, which is inversely proportional to blood viscosity (Birchard, 1997; Calbet et al., 2006; Wagner, 1996). These properties are reflected by hematocrit or packed cell volume (PCV); the proportion of whole‐blood volume is comprised of erythrocytes. Hemoglobin and blood viscosity increase linearly and exponentially, respectively, with hematocrit (Hedrick et al., 1986). Blood becomes harder to circulate with increasing viscosity (i.e., requiring greater cardiovascular effort), but less viscous blood contains less hemoglobin. Therefore, intermediate hematocrit levels (ca. 40%) are optimal for maximum oxygen‐carrying capacity and endurance (Birchard, 1997; Jensen et al., 2013; Schuler et al., 2010).

Hematocrit levels observed in nature are variable (range ca. 30%–60%) within and between endothermic species (Stark & Schuster, 2012). For example, hematocrit is higher in species/individuals requiring greater blood oxygen storage and endurance (Lourdais et al., 2014; Minias, 2015; Yap et al., 2019). Similarly, hematocrit tends to increase within individuals in response to elevated oxygen demands, such as during altitudinal migration (Borras et al., 2010) and exercise regimes (reviewed in Yap et al., 2017). Elevated hematocrit occurs via the production of new erythrocytes (erythropoiesis) and/or the release of reticulocytes (immature erythrocytes) from the bone marrow, which is triggered by hypothalamus–pituitary–adrenal‐mediated stress (see Voorhees et al., 2013). More rapid (<1 hr) increases in hematocrit can occur due to a reduction in blood plasma volume (hemoconcentration), which happens during exercise and dehydration (Bury et al., 2019; Kaltreider & Meneely, 1940). In some mammal species, splenic reservoirs of erythrocytes can also increase hematocrit at the onset of stress and exercise (Böning et al., 2011).

Anemia—characterized by chronically low hematocrit and hemoglobin—occurs when an individual's rate of erythrocyte loss exceeds that of erythropoiesis, for example, during blood parasitism (O’Brien et al., 2001). However, anemia can occur without affecting hematocrit, since the release of reticulocytes, which are larger than mature erythrocytes, can rapidly complement hematocrit despite them having lower hemoglobin content (Fair et al., 2007). Anemia can also arise as a secondary outcome of competing physiological systems. For example, egg production in birds causes a reduction in hematocrit via an estrogen‐mediated suppression of erythropoiesis and hemodilution—an increase in blood plasma volume (Wagner, Prevolsek, et al., 2008; Wagner, Stables, et al., 2008; Williams et al., 2004). Therefore, both within‐individual increases and decreases in oxygen‐carrying capacity and associated factors (hematocrit and hemoglobin) have the potential to reflect a multitude of life‐history events and trade‐offs (for reviews, see Fair et al., 2007; Johnstone et al., 2017; Minias, 2015).

Uncertainty remains regarding associations between hematocrit, age, and senescence in wild animals. From birth to maturity, hematocrit increases with age (e.g., Cornell & Williams, 2017; Eklom & Lill, 2006; Trillmich et al., 2008), but few studies have determined the age dependence of hematocrit in adult life. This likely stems from the difficulty of obtaining samples of known‐age adults in many wild systems. In captive mice and humans, low hematocrit in extreme old age reflects senescence in erythrocyte renewal mechanisms (Boggs & Patrene, 1985; Gaskell et al., 2008). Similarly, cross‐sectional studies of other captive and wild vertebrates have observed lower hematocrit in old age, suggestive of senescence (Elliott et al., 2015; Jégo et al., 2014; Prinzinger & Misovic, 2010; Smucny et al., 2004). However, such observations may also arise from compositional changes in successive age classes of a population, for example, due to selective disappearance of individuals with high hematocrit. Longitudinal studies are needed to explicitly investigate within‐individual change with age (Elliott et al., 2015; Nussey et al., 2008).

Factors that cause hematocrit to deviate from the theoretical optimum (for oxygen‐carrying capacity and general health) could have long‐term impacts on the fitness of wild taxa. For example, experimental reductions in hematocrit in birds can result in reduced reproductive success (Fronstin et al., 2016) and flight performance (Yap et al., 2018). However, few studies have investigated associations between hematocrit levels observed under natural conditions in the wild and subsequent survival. Anemia results in lethargy and fatigue, but even minor decreases in oxygen‐carrying capacity could represent an energetic disadvantage that reduces survival prospects in wild settings. Conversely, more viscous blood, and the cardiovascular loading this creates, is linked to negative health impacts in humans (Brækkan et al., 2010; Coglianese et al., 2012; Stack & Berger, 2009; Walton et al., 2017). Extreme high or low hematocrit can also be a noncausal indicator of factors detrimental to self‐maintenance, such as stress, parasitism, and nutrient deficiencies (see Johnstone et al., 2017). Therefore, intermediate hematocrit levels are expected to be optimal for survival (e.g., Boffetta et al., 2013; Bowers et al., 2014).

The isolated Seychelles warbler (Acrocephalus sechellensis) population on Cousin Island provides an excellent model system for studying associations between hematocrit, age, and survival in a wild population. This system benefits from over 30 years of continuous monitoring and extremely accurate survival estimates of known‐age individuals that are not confounded by dispersal (Hammers et al., 2019; Komdeur, 1992; Richardson et al., 2007). Individuals have been captured and blood sampled repeatedly across their lifetime, providing a wealth of longitudinal physiological data (Hammers et al., 2015), including hematocrit. Here, we first assess the relationship between hematocrit and age. Based on previous findings across vertebrate taxa, we predict that hematocrit increases during early life up to maturity, followed by an age‐related decline. Crucially, we determine the relative contribution of longitudinal (i.e., within‐individual) and cross‐sectional (i.e., between‐individual) effects to any age patterns observed. Hematocrit is also likely to vary between and within individuals independently of age. We determine whether this variation is explained by other factors, namely sex and social status and breeding stage, and assess within‐individual repeatability of hematocrit. Lastly, we determine the relationship between hematocrit and annual survival probability. Given the potentially negative effects of both low and high hematocrit, we predicted that individuals with intermediate hematocrit values would have higher survival. Our study will therefore assess the validity of hematocrit as a marker of condition within wild animal populations, and explore its usefulness in terms of providing insights into the costs and trade‐offs that individual animals face during life.

2. METHODS

2.1. Study species and data collection

The Seychelles warbler is a small insectivorous passerine endemic to the Seychelles. Seychelles warblers can (exceptionally) reach ages of up to 19 years (Hammers & Brouwer, 2017), though the average life span is 5.5 years for individuals that reach fledgling age (Komdeur, 1991). The population of ca. 320 adult individuals on Cousin Island (29 ha, 4°209 S, 55°409 E) has been extensively monitored since 1986. Monitoring is carried out for ca. 6 months of each year (January–March, June–September) during the minor and major breeding seasons, respectively (Komdeur & Daan, 2005). Since 1997, nearly all individuals (>96%) have been ringed with a unique combination of a British Trust for Ornithology (BTO) metal ring and three color rings for identification (Richardson et al., 2001). Individuals are usually first caught and ringed as nestlings or dependent fledglings, before sexual maturity (<8 months old). Juveniles are assigned to age categories (fledgling 1–3 months, old fledgling 3–5 months, or subadult 5–8 months), based on behavior and eye color, which transitions from gray in fledglings to red‐brown in adults (Komdeur, 1992).

The population is structured into clearly defined territories that are defended year round. Breeding groups is comprised of one socially monogamous dominant pair (hereafter dominant breeders), but may also include 1–5 sexually mature subordinates (Richardson et al., 2002) which sometimes engage in helping behavior and cobreeding (Hammers et al., 2019). An Individual's social status in a given field season is determined through observations of behavior (see Komdeur, 2001).

During the breeding season, each territory is visited at least every 2 weeks and checked for the presence–absence of individuals identified by their color ring combination. Dominant females are followed for 15 min to determine whether an active nest is present. Once a nest is found, it is visited every 3 days for 15–60 min (to determine breeding stage) until completion or failure. For nests that were discovered during or after the start of incubation, the egg‐laying date is estimated from the timing of hatching (determined from provisioning observations) and/or fledging. Given that interisland dispersal is exceptionally rare (Komdeur et al., 2004) and resighting probabilities are close to one (Brouwer et al., 2009), birds that are not seen during a field season can be assumed dead (Hammers et al., 2013). The last day of a field season for which an individual is observed as present is taken as the date of death.

Individuals were captured using mist nets and conspecific playback (see Kingma et al., 2016 for details). Ca. 70 μl of blood was drawn with a microcapillary tube from the brachial vein. A small amount (ca. 10 ul) of blood sample was also stored in absolute ethanol at 4°C for future DNA extraction. This procedure is the routine, nonlethal way to sample blood from passerine birds and has been shown to have no measurable effect on condition or survival (Sheldon et al., 2008). Within ca. 3 hr of bleeding, microcapillary tubes were centrifuged for 8 min at 6,000 g to separate erythrocytes from plasma, white blood cells, and platelets. Hematocrit was measured (using sliding calipers ±0.01 mm) as the proportion of erythrocytes relative to whole‐blood volume. Between the years of 2003 and 2017, 1,383 hematocrit measurements were obtained from 733 individuals. DNA was extracted using a salt extraction technique following Richardson et al. (2001), and sex of the individual was confirmed using the PCR‐based method outlined by Griffiths et al. (1998).

2.2. Statistical analyses

All statistical analyses were performed with RStudio (v1.2.5033, RStudio Team, 2020). Firstly, we investigated the relationship between hematocrit and age across all samples with a generalized additive mixed model (GAMM) using the gamm4 package (v0.2–6). In this model, we fitted a nonparametric smoothing parameter for age to evaluate expected nonlinear relationships between hematocrit and age. Compared with linear mixed models (LMMs), which require prespecified functions between dependent and continuous predictor variables, GAMMs are more appropriate when the shape of age‐dependent patterns are unknown (Hammers et al., 2016). In addition to age, the model included factors known to influence hematocrit in avian taxa (see Fair et al., 2007): sex, social status (dominant breeders vs. subordinates + juveniles), and time of day of sampling. Sex differences are likely to depend on social status; thus, a two‐way interaction between sex and status was included. To control for nonindependent samples, individual identity, breed group identity, and catch year were included as random intercepts.

Age‐related patterns across populations can arise from selective disappearance, whereby certain phenotypes are associated with shorter life spans (Nussey et al., 2008). To control for selective disappearance effects, we repeated the model using only individuals that were dead at the time of analysis and included age at death as an additional factor (de Pol & Verhulst, 2006; van Hammers et al., 2019).

Our GAMM analysis revealed that dominant females had significantly lower hematocrit than dominant males and subordinates (male or female). This suggested an effect of reproductive anemia on hematocrit levels of dominant females, since they produce the majority of offspring and sampling coincided with the breeding seasons. To determine whether sex‐by‐status differences were maintained in individuals not engaged in reproduction, we repeated the model including only sexually mature individuals (>8 months old) sampled outside of known breeding attempts; either no egg was laid for that breed group or the individual was sampled >50 days from the breed groups lay date. For a given individuals breed group, we calculated the number of days between the estimated lay date and the date of sampling. For breed groups with two or more broods (which occurs if, e.g., the first brood was predated), the closest lay date from the sample date was selected. For individuals sampled during breeding attempts (<50 days from breed groups lay date), we expected hematocrit to be lowest nearer the lay date, and only in dominant females. Since hematocrit was expected to fluctuate nonlinearly across breeding stages, nonparametric smoothing parameters were fitted for days from lay date for males and females. Separate models were created for dominant breeders and subordinates to avoid the need for complex three‐way interactions between sex, status, and days from lay date. Individuals were rarely caught multiple times within the same breeding attempt; thus, this section of our analysis is cross‐sectional in nature.

To separate the role of between‐ versus within‐individual variation with age (i.e., cross‐sectional from longitudinal effects), we used the within‐subject centering method described by van de Pol & Wright, 2009. Briefly, age at sampling is split into two predictors, (a) mean age across all sampling events for a given individual (mean age), and (b) within‐individual deviation from mean age (∆ age). Our GAMM indicated a peak in hematocrit at ca. 1.5 years of age (see Results, Figure 1). To investigate the initial increase and subsequent decrease in hematocrit in more detail, we performed within‐individual centering for individuals <1.5 months and for individuals ≥1.5 months in separate analyses (following Hammers et al., 2016). This allowed us to compare the drivers of age‐related hematocrit patterns in early life versus later adulthood.

Figure 1.

Figure 1

Hematocrit in Seychelles warblers in relation to age and sex. The fit lines (solid = female, dashed = male) show nonparametric smoothing functions for age with 95% confidence intervals. Points (round = female, triangles = male) are means and 95% confidence intervals for each age (rounded years). Ages 12 and 13 are grouped for graphical purposes (denoted as 12 here). Within‐graph numbers represent sample sizes per age for females (lower) and males (upper)

We created linear mixed models using the lme4 package (v1.1‐21, Bates et al., 2014) with hematocrit as the response and mean age, ∆ age, sex, social status, and time of day of sampling as predictors. Age terms were entered as both linear and quadratic terms to test for possible nonlinear patterns. Two‐way interactions between ∆ age, sex, and status were included to determine whether within‐individual changes in hematocrit were dependent on these factors. Consistent with the GAMMs outlined above, individual identity, breed group identity, and catch year were included as random intercepts. Due to the relationship observed between hematocrit and breeding stage in dominant breeders (see Figure 2), we repeated the analysis excluding samples from breeding stages where hematocrit deviates from typical levels; 20 days before to 5 days after laying for dominant males, and 30–50 days after laying in dominant females. Using the rptR package (v0.9.22; Nakagawa & Schielzeth, 2010), we also calculated repeatability estimates for hematocrit within individuals to determine how consistent individual hematocrit levels are across repeated samples at different times.

Figure 2.

Figure 2

Hematocrit in Seychelles warblers in relation to days from lay date for dominant breeders (left) and subordinates (right). The fit lines (solid = female, dashed = male) show non‐parametric smoothing functions for days from lay date, and the shaded area is the 95% confidence interval for the smoothing functions. The annotations and dotted lines denote theoretical nest stages relative to lay date

Lastly, we investigated whether hematocrit predicts short‐term survival. We used a binominal generalized linear mixed models (GLMMs) to test the probability of surviving 1 year beyond the date of sampling (Y/N) in relation to hematocrit. Since hematocrit exhibited different age‐specific patterns in early life (<1.5 years) and adulthood (1.5–13 years; see Results), we investigated the relationship between hematocrit and survival for these two age groups in separate models. Where multiple hematocrit samples were taken per individual, only the last sample was selected, which allowed us to identify whether individuals facing imminent mortality have different hematocrit levels compared with those that survive. Additional fixed effects included age, sex, status, and quadratic functions of hematocrit and age. We also included an interaction term between age and hematocrit to see whether the effect of hematocrit on survival changed with age. Survival probability can vary between territories and years, for example, due to varying food availability (Brouwer et al., 2006; Spurgin et al., 2017); thus, breed group and catch year were also entered as random factors. Breed group was subsequently dropped as a random factor in the 1.5‐ to 13‐year group due to model convergence issues. As with the LMM analysis, we repeated models excluding samples from breeding stages where hematocrit deviates from typical levels in dominant breeders.

In all models, nonsignificant interaction terms were removed sequentially (in order of least significance) and only reported if of specific interest. All fixed effects remained in final models (regardless of significance) except for quadratic functions of continuous variables, which were removed when nonsignificant (see Whittingham et al., 2006). Parameter estimates and significance of removed effects were determined by re‐entering them into final models.

3. RESULTS

3.1. Cross‐sectional age

Hematocrit had a distinctive pattern with cross‐sectional age (Figure 1). Initially, hematocrit increased rapidly before reaching a peak at ca. 1.5 years of age. From 1.5 years onward (maximum age in this analysis is 13 years), hematocrit showed a consistent downward trajectory (Figure 1). This age‐dependent pattern was similar for both sexes (Figure 1) and fitting smoothed age terms for males and females separately resulted in poorer model fit (∆AIC > 4). Sex differences in hematocrit were dependent on social status (Table 1). For dominant breeders, which are the vast majority of individuals sampled ≥2 years of age, females had lower average hematocrit levels than males. Dominant females also had lower hematocrit than subordinates (male or female; Table 1, Figure S1). Individuals sampled in the early morning had higher hematocrit than those sampled in the late afternoon (Table 1). When the model was run on a subset of individuals known to be dead, including age at death as a predictor, we found that shorter‐lived individuals had significantly higher hematocrit (Table S1). Therefore, selective disappearance of individuals with high hematocrit contributed to the age‐specific pattern. Crucially, the effect of age was still significant when controlling for age at death (Table S1), indicating that within‐individual effects were also present.

Table 1.

Hematocrit in relation to cross‐sectional age and other factors in Seychelles warblers

Predictor β SE t p
Intercept 0.460 0.005 94.701 <.001
Sex (male) −0.003 0.003 −1.202 .230
Status (dominant) −0.021 0.003 −6.440 <.001
Sample time −0.002 0.000 −5.981 <.001
Sex × Status 0.028 0.004 7.612 <.001
Smoothed terms df F p
Age 7.805 16.73 <.001
Random factors 1,379 observations Variance
Individual identity 730 individuals <0.000
Breed group 747 breed groups <0.000
Catch year 14 years <0.000

Results are from a GAMM analysis with a nonparametric smoothing parameter for age. Significant effects are in bold.

3.2. Reproductive stage

We compared hematocrit of sexually mature (>8 months old) subordinates and dominant breeders. Outside of breeding attempts, dominant females had lower hematocrit than both dominant males and subordinate males and females (Table S2, Figure S1). During breeding attempts, the effects were more complex (Table S3). There was no evidence of reproductive anemia (i.e., a marked decrease in hematocrit) in dominate females sampled near their lay date, although hematocrit was lower at ca. 35–50 days after laying (Figure 2). The hematocrit of males exhibited a complex relationship with breed group lay date; hematocrit was highest at ca. 7 days prior to laying and was lowest 15–30 days postlaying (Figure 2). In contrast to dominant breeders, there was no significant difference between male and female subordinates sampled during breeding attempts (Tables S3 and S4, Figure 2). The hematocrit of subordinate males did not vary in relation to breed group lay date, but subordinate females exhibited a weak quadratic relationship with days from breed group lay date; peaking at the laying date (Figure 2). Importantly, the decline of hematocrit with increasing age persisted when the analysis was split between nonbreeding and breeding individuals, and (for the latter) when controlling for days from lay date (Figure S2).

3.3. Longitudinal age

Our within‐subject centering analysis, which separates within‐ and between‐individual contributions to age patterns, was consistent with the GAMM analysis. Below 1.5 years of age, hematocrit increased both within and between individuals with age in a quadratic pattern; a strong initial increase that plateaued at ca. 1 year of age (Table 2, Figure 3). From 1.5 years of age onward, hematocrit declined linearly with increasing age both within and between individuals (Table 2, Figure 3). All interactions with ∆ age were nonsignificant; thus, within‐individual increases (<1.5 years) and decreases (1.5—13 years) did not vary between individuals of differing sex or status. Consistent with the GAMM analysis, hematocrit was lower in dominant females and individuals caught later in the day (Table 2). All results were qualitatively identical when samples from dominant breeders caught during key breeding stages (where hematocrit deviated from typical levels; see Figure 2) were excluded from the analysis (Table S5).

Table 2.

Hematocrit in relation to cross‐sectional age (mean age) and longitudinal age (∆ age) in Seychelles warbler <1.5 years old and 1.5–13 years old

Predictor β SE t p
<1.5 years old
Intercept 0.393 0.010 40.92 <.001
Mean age 0.159 0.022 7.327 <.001
Mean age2 −0.085 0.016 −5.436 <.001
∆ Age 0.036 0.008 4.437 <.001
∆ Age2 −0.054 0.018 −3.09 .002
Sex (male) −0.005 0.003 −1.615 .107
Status (dominant) −0.014 0.007 −2.061 .040
Sample time −0.002 0.000 −3.276 .001
Sex × Status 0.017 0.008 2.143 .033
Random factors 637 observations Variance
Individual identity 506 individuals <0.000
Breed group 452 breed groups <0.000
Catch year 14 years <0.000
Predictor β SE t p
1.5–13 years old
Intercept 0.465 0.006 74.692 <0.001
Mean age −0.002 0.001 −3.608 .000
∆ Age −0.002 0.001 −2.715 .007
Sex (male) 0.026 0.002 10.677 <.001
Status (dominant) −0.013 0.003 −3.619 <.001
Sample time −0.002 0.000 −4.714 <.001
Random factors 742 observations Variance
Individual identity 405 individuals <0.000
Breed group 529 breed groups <0.000
Catch year 14 years <0.000

Parameters shown are from LMM analysis. Significant effects are in bold.

Figure 3.

Figure 3

Hematocrit in Seychelles warblers in relation to within‐individual differences in age (∆ Age) for individuals <1.5 years old and 1.5–13 years old. Thick black lines are the LMM (Table 2) predicted hematocrit ±95% CI relative to age. Raw data are hematocrit samples with thin gray lines connecting multiple samples from the same individual

For final LMMs (excluding all nonsignificant interactions and nonsignificant quadratic effects), we calculated repeatability of hematocrit within individuals. For individuals below 1.5 years of age, only 1.6% (p = .434) of variance was due to within‐individual consistency. From 1.5 years of age, within‐individual consistency was higher at 7.8% and approaching significance (p = .063).

3.4. Survival

A total of 263 out of the 1,383 samples taken were from individuals that died within the subsequent year. For young (<1.5 years of age), individuals with higher hematocrit were less likely to survive to the next year (Table 3, Figure 4). In contrast, hematocrit did not predict survival over the subsequent year for individuals 1.5–13 years of age (Table 3). Contrary to expectations, there was no quadratic effect of hematocrit on survival; only high hematocrit was associated with lower survival in young individuals. The effect of hematocrit on survival was not influenced by age in either age category. Survival probability was lower for males and subordinates from 1.5–13 years of age (Table 3). Repeating the analysis while excluding samples from dominant breeders caught at key breeding stages (where hematocrit deviated from typical levels; Figure 2) did not qualitatively change results (Table S6).

Table 3.

Survival in the Seychelles warbler in relation to haematocrit for individuals 1.5 years old and 1.5–13 years old

Predictor β SE z p
<1.5 years old
Intercept 5.016 1.283 3.909 <.001
Hematocrit −9.293 3.004 −3.093 .002
Sex (male) −0.224 0.224 −1.001 .317
Status (dominant) 0.565 0.369 1.533 .125
Age 0.459 0.395 1.161 .246
Random factors 506 observations Variance
Breed group 418 breed groups <0.000
Catch year 14 years 0.340
Predictor β SE z p
1.5–13 years old
Intercept 1.485 1.668 0.89 .3733
Hematocrit −1.398 3.684 −0.379 .7044
Sex (male) −0.557 0.254 −2.196 .0281
Status (dominant) 0.724 0.345 2.099 .0358
Age −0.009 0.043 −0.202 .8403
Random factors 408 observations Variance
Catch year 13 years 0.370

Results are from binominal GLMMs with survival to the following year (Y/N) as the response variable. Significant effects are in bold.

Figure 4.

Figure 4

The probability of young (<1.5 years of age) Seychelles warblers surviving one year after sampling relative to haematocrit. The fit‐line is a binomial regression between survival (Y/N) and haematocrit with 95% confidence limits. Raw data depicts the distribution of observed survival counts (1 = survived, 0 = deceased)

4. DISCUSSION

Hematocrit increased in juveniles up to 1.5 years of age, beyond which hematocrit declined with increasing age. Both longitudinal change and the selective disappearance of individuals with high hematocrit contributed to this age‐specific pattern. In early life (<1.5 years), hematocrit increased within individuals, but individuals with higher hematocrit were less likely to survive to the following year. After 1.5 years of age, hematocrit declined within individuals with advancing age. However, hematocrit did not predict survival in this older age range. In addition to age, hematocrit was lower in females compared with males, but only in dominant breeders (hematocrit did not significantly differ between subordinates and dominant males). The hematocrit of dominant breeders also varied with breeding stage—most notably, male hematocrit peaked in the days prior to the pair‐bonded females lay date. However, the relationship between hematocrit with both age and survival persisted when samples from dominant individuals caught during key breeding stages were excluded from analyses.

4.1. Age

Increases in hematocrit and oxygen‐carrying capacity during development have been observed in a range of vertebrates (Fair et al., 2007; Petschow et al., 1978; Trillmich et al., 2008). In birds, adult levels of hematocrit are usually achieved at late‐nestling age, presumably in preparation for fledging (Eklom & Lill, 2006a, 2006b). However, in the Seychelles warbler hematocrit continues to increase postfledging (up to 1.5 years). Our longitudinal and survival analyses confirmed that increases in hematocrit occurred within juveniles and were not due to juveniles with low hematocrit having lower annual survival, that is, selective disappearance. In this species, fledglings receive parental care (provisioning) for up to 3 months (Komdeur, 1996) and may delay dispersal from the natal territory (i.e., become subordinates) for 1–3 years (Hammers et al., 2013). Socially dominant individuals are expected to have higher aerobic demands (for territory defense and reproduction) than juveniles, which might explain why hematocrit increases up to 1.5 years of age. Interestingly, hematocrit levels at this age (1–3 years) were higher than levels across prime reproductive ages (ca. 4–7 years; Komdeur, 1996; Hammers et al., 2012), which could reflect elevated oxygen demands and/or stress in subordinates competing for dominant social positions at this age (Creel, 2001; Kingma et al., 2016).

We observed a gradual decrease in hematocrit within individuals with advancing age during most of adulthood. This relationship is similar to that observed in thick‐billed murres (Uria lomvia) by Elliott et al. (2015), the only other longitudinal study of hematocrit in a wild system to date, and concurs with results from cross‐sectional studies. For example, Jégo et al. (2014) found a decrease in hematocrit in roe deer (Capreolus capreolus) from the onset of actuarial senescence (8 years old). Thus, declining hematocrit could be indicative of physiological senescence (i.e., diminished ability to maintain circulating erythrocyte mass) in adult Seychelles warblers. By restricting endurance, such declines could contribute to lower survival in elderly life; onset of actuarial senescence in the Seychelles warbler is ca. 7 years old (Hammers et al., 2015). However, we did not find evidence of this in our study since only high hematocrit (not low hematocrit) was associated with lower survival, and only in young individuals. Alternatively, decreases in hematocrit could reflect other behavioral and/or physiological changes with age observed in wild vertebrates. For instance, gains in experience could relax demands for oxygen‐carrying capacity during foraging (Daunt et al., 2007; Zimmer et al., 2011). Furthermore, the intensity of stress responses—which can elevate hematocrit (Johnstone et al., 2012)—often decline with age (Lendvai et al., 2015; Wilcoxen et al., 2011). Such changes may be expected of older Seychelles warblers living in long‐established territories.

4.2. Sex and reproduction

We found that hematocrit was lower in female, compared with male, Seychelles warblers, but only for dominant breeders. This suggests an effect of reproduction on hematocrit, given that dominant breeders produce the vast majority of offspring in the population (Raj Pant et al., 2019; Richardson et al., 2001) and sampling coincided with peaks in breeding activity (Komdeur & Daan, 2005). A well‐documented phenomenon (see Fair et al., 2007) in female birds is reproductive anemia—a reduction in hematocrit during egg laying due to the pleiotropic effects of elevated estrogen (Wagner, Prevolsek, et al., 2008; Wagner, Stables, et al., 2008; Williams et al., 2004). Hematocrit declines observed in other species range from 5% to 10% (Davey et al., 2000; Morton, 1994) and can persist for several weeks, through incubation and chick‐rearing (Williams et al., 2004). In contrast to females, males can have elevated hematocrit prior to and during reproduction as a consequence of elevated testosterone, which stimulates erythropoiesis (Mirand et al., 1965). Therefore, sex differences may only occur during reproduction (e.g., Morton, 1994). This was not the case in our study since sex‐by‐status differences were similar both during and outside of breeding attempts. Additionally, there was no evidence of reproductive anemia (low hematocrit at egg laying) in dominant females. Taken together, these findings indicate that dominant females maintain hematocrit levels at a constant low level (relative to dominant males and subordinates of either sex). In other species, estrogen is positively related to territorial behaviors (e.g., singing and aggression) in females (Pärn et al., 2008; Woodley & Moore, 1999). This suggests that female dominance in Seychelles warblers might be accompanied by an upregulation of estrogen, which subsequently lowers hematocrit. However, we do not currently have data on estrogen dynamics in this species.

Sex differences in hematocrit were greatest prior to egg laying due to increased hematocrit in dominant males. Peak dominant male hematocrit coincided with his female partners fertile period (6 days prior to egg laying), during which testosterone levels of (pair‐bonded) dominant males is also highest (Van De Crommenacker et al., 2004). Therefore, elevated hematocrit in males may be a consequence of elevated testosterone (e.g., Buttemer & Astheimer, 2000; Ezenwa et al., 2012). A lack of elevated hematocrit in subordinate males supports this explanation, since subordinate males do not elevate testosterone levels during the female fertile period (Van De Crommenacker et al., 2004). Elevated hematocrit might also reflect broader behavioral and physiological changes during this period. For example, dominant—but not subordinate—males invest in energetically costly guarding of mates during their fertile period to prevent extra‐pair copulations (Komdeur, 2001). Thus, elevated hematocrit could reflect increased activity levels—and therefore higher oxygen demands—during this critical period for dominant males (see Hammond et al., 2000).

4.3. Survival

Intermediate hematocrit levels are predicted to be advantageous for survival, given that both high and low hematocrit are associated with increased mortality in humans and mice (Boffetta et al., 2013; Heller et al., 1998; Wagner et al., 2001). However, we found young Seychelles warblers with low hematocrit had the highest survival. This finding contradicts a study by Bowers et al. (2014), which found that house wren (Troglodytes aedon) nestlings with intermediate hematocrit had higher recruitment. However, in this study a more extreme lower range of hematocrit values (i.e., <30%) was apparent, likely due to age; neonates having lower hematocrit compared with juveniles and adults. Extreme‐low hematocrit in neonates likely reflects developmental immaturity, which would reduce the probability of successful fledging (Cornell et al., 2017).

In adulthood, low hematocrit can be indicative of anemia (Campbell, 1994), which in wild populations may increase mortality risk via lethargy and fatigue. However, these symptoms are also likely to preclude anemic individuals from being captured using mist nets. In our sample, only 11 individuals were caught with what are considered anemic hematocrit levels in captive avifauna (<35%; Campbell, 1994). However, the threshold of anemic hematocrit might be higher in wild populations, given that overall hematocrit can be higher in wild compared with captive populations (Sepp et al., 2010). Nevertheless, the ability to detect a negative survival effect of extreme‐low hematocrit in wild populations may be limited by an under‐representation of anemic individuals. Furthermore, hematocrit has been criticized as indicator of ongoing/recent anemia due to disproportionate effect of reticulocytes (Fair et al., 2007; O’Brien et al., 2001). These immature erythrocytes are larger and contain less hemoglobin, meaning hematocrit can recover more rapidly than oxygen‐carrying capacity following anemic episodes. Therefore, anemia could impact survival in wild populations without a detectable change in hematocrit values.

Higher hematocrit was associated with reduced survival probabilities in young individuals, despite nearly all hematocrit values falling within what is considered to be a healthy reference range for captive avifauna, 35%–55% (Campbell, 1994). Short‐term increases in hematocrit can result from dehydration/hemoconcentration, which in turn limit oxygen‐carrying capacity, or increase the cardiovascular effort required to maintain optimal oxygen‐carrying capacity, due to negative relationship between blood viscosity and flow rate. Several studies have observed a lowering of hematocrit (by ca. 2%–5%) in birds during endurance activities via an increase in blood plasma (hemodilution). In line with optimal hematocrit theory (Birchard, 1997), these authors suggest that hemodilution is an adaptive response to prolonged exercise, facilitating faster blood flow for less cardiovascular effort (Bury et al., 2019; Jenni et al., 2006; Yap et al., 2018). Thus, high hematocrit in young Seychelles warblers may reflect a failure to maintain optimal hematocrit, for example, due to dehydration. Alternatively, hematocrit could reflect physiological traits and/or life histories with potential costs to survival. For example, hematocrit has been positively associated with reproductive effort (e.g., Hõrak et al., 1998), male ornamentation (Saino et al., 1997), metabolic rate (Yap et al., 2019) and stress (Johnstone et al., 2012). However, further—ideally experiment—studies are needed to confirm the link between hematocrit and pace of life in the Seychelles warbler.

Our study provides novel insights into the dynamics of hematocrit, and its impact on survival, in a wild population. Hematocrit was highly variable within individuals and varied in relation to time of day and (in dominant breeders) breeding stage. This variation limits the utility of hematocrit as a marker of age or senescence. However, the overarching relationship observed with advancing age supports the concept of changing oxygen demands with age. Interestingly, we show that hematocrit can be an indicator of survival prospects in wild populations. Whether survival is directly impacted by (suboptimal) oxygen‐carrying capacity, or factors that increase hematocrit (dehydration, stress, etc.) remains to be tested. Since changes in erythrocyte mass occur over longer timescales than, for example, stress hormones and oxidative stress (Bonier et al., 2009; van de Crommenacker et al., 2017), hematocrit may be a better indicator an individual's baseline stress levels (Johnstone et al., 2012). However, short‐term changes in blood plasma volume can affect hematocrit levels independently of erythrocyte mass, which makes unraveling the drivers of elevated hematocrit difficult without data on additional blood metrics, such as plasma protein and hemoglobin concentrations (see Johnstone et al., 2017). Nevertheless, hematocrit can aid in quantifying physiological state or condition in wild vertebrates, which is a fundamental concept in the study of life‐history trade‐offs.

CONFLICT OF INTERESTS

None declared.

AUTHOR CONTRIBUTION

Thomas James Brown: Conceptualization (equal); Data curation (lead); Formal analysis (lead); Funding acquisition (equal); Investigation (equal); Methodology (equal); Writing‐original draft (lead); Writing‐review & editing (lead). Martijn Hammers: Conceptualization (equal); Funding acquisition (equal); Investigation (equal); Methodology (equal); Writing‐review & editing (equal). Martin Taylor: Investigation (equal); Methodology (equal); Supervision (supporting); Writing‐review & editing (equal). Hannah Dugdale: Funding acquisition (equal); Investigation (supporting); Methodology (supporting); Supervision (supporting); Validation (equal); Writing‐review & editing (equal). Jan Komdeur: Funding acquisition (equal); Writing‐review & editing (equal). David Richardson: Conceptualization (equal); Formal analysis (equal); Funding acquisition (equal); Investigation (equal); Methodology (equal); Supervision (lead); Writing‐review & editing (equal).

ETHICS APPROVAL

All fieldwork was conducted in accordance with local ethical regulations and agreements. The Seychelles Bureau of Standards and Department of Environment gave permission for sampling and fieldwork. Nature Seychelles gave permission to carry out research on Cousin Island.

Supporting information

Supplementary Material

ACKNOWLEDGMENTS

We thank Nature Seychelles for facilitating fieldwork on Cousin Island. This study would not have been possible without the contribution of many fieldworkers, laboratory technicians, students, and database managers during the whole study period. T.J.B. was funded by the UKRI Biotechnology and Biological Sciences Research Council Norwich Research Park Biosciences Doctoral Training Partnership (BB/M011216/1). M.H. was funded by a Netherlands Organisation for Scientific Research (NWO) VENI fellowship grant (863.15.020). The long‐term Seychelles warbler study was funded by the Natural Environment Research Council (NERC) grants to D.S.R (NE/F02083X/1) and D.S.R and H.L.D (NE/K005502/1), and NWO grants from the Dutch Science Council (NWO) to J.K., with D.S.R. and H.L.D. (NWO‐ALW 823.01.014, NER/I/S/2002/00712, NE/I021748/1, 854.11.003, and 823.01.014).

Brown TJ, Hammers M, Taylor M, Dugdale HL, Komdeur J, Richardson DS. Hematocrit, age, and survival in a wild vertebrate population. Ecol Evol.2021;11:214–226. 10.1002/ece3.7015

DATA AVAILABILITY STATEMENT

Data are available from the Dryad Digital Repository: https://doi.org/10.5061/dryad.7wm37pvrp

REFERENCES

  1. Bates, D. , Mächler, M. , Bolker, B. , & Walker, S. (2014). Fitting linear mixed‐effects models using lme4. Journal of Statistical Software, 67(1), 1–48. 10.18637/jss.v067.i01 [DOI] [Google Scholar]
  2. Birchard, G. F. (1997). Optimal hematocrit: Theory, regulation and implications. Integrative and Comparative Biology, 37(1), 65–72. [Google Scholar]
  3. Boffetta, P. , Islami, F. , Vedanthan, R. , Pourshams, A. , Kamangar, F. , Khademi, H. , Etemadi, A. , Salahi, R. , Semnani, S. , Emadi, A. , Abnet, C. C. , Brennan, P. , Pharoah, P. D. , Dawsey, S. M. , & Malekzadeh, R. (2013). A U‐shaped relationship between haematocrit and mortality in a large prospective cohort study. International Journal of Epidemiology, 42(2), 601–615. 10.1093/ije/dyt013 [DOI] [PMC free article] [PubMed] [Google Scholar]
  4. Boggs, D. R. , & Patrene, K. D. (1985). Hematopoiesis and aging III: Anemia and a blunted erythropoietic response to hemorrhage in aged mice. American Journal of Hematology, 19(4), 327–338. 10.1002/ajh.2830190403 [DOI] [PubMed] [Google Scholar]
  5. Bonier, F. , Martin, P. R. , Moore, I. T. , & Wingfield, J. C. (2009). Do baseline glucocorticoids predict fitness? Trends in Ecology and Evolution, 24(11), 634–642. 10.1016/j.tree.2009.04.013 [DOI] [PubMed] [Google Scholar]
  6. Böning, D. , Maassen, N. , & Pries, A. (2011). The hematocrit paradox – How does blood doping really work? International Journal of Sports Medicine, 32(4), 242–246. 10.1055/s-0030-1255063 [DOI] [PubMed] [Google Scholar]
  7. Borras, A. , Cabrera, J. , & Senar, J. C. (2010). Hematocrit variation in response to altitude changes in wild birds: A repeated‐measures design. The Condor, 112(3), 622–626. 10.1525/cond.2010.090113 [DOI] [Google Scholar]
  8. Bowers, E. K. , Hodges, C. J. , Forsman, A. M. , Vogel, A. L. , Masters, B. S. , Johnson, B. G. P. , Johnson, L. S. , Thompson, C. F. , & Sakaluk, S. K. (2014). Neonatal body condition, immune responsiveness, and hematocrit predict longevity in a wild bird population. Ecology, 95(11), 3027–3034. 10.1890/14-0418.1.Neonatal [DOI] [PMC free article] [PubMed] [Google Scholar]
  9. Brækkan, S. K. , Mathiesen, E. B. , Njølstad, I. , Wilsgaard, T. , & Hansen, J.‐B. (2010). Hematocrit and risk of venous thromboembolism in a general population. The Tromsø study. Haematologica, 95(2), 270–275. 10.3324/haematol.2009.008417 [DOI] [PMC free article] [PubMed] [Google Scholar]
  10. Brouwer, L. , Richardson, D. S. , Eikenaar, C. , & Komdeur, J. (2006). The role of group size and environmental factors on survival in a cooperatively breeding tropical passerine. Journal of Animal Ecology, 75(6), 1321–1329. 10.1111/j.1365-2656.2006.01155.x [DOI] [PubMed] [Google Scholar]
  11. Brouwer, L. , Tinbergen, J. M. , Both, C. , Bristol, R. , Richardson, D. S. , & Komdeur, J. (2009). Experimental evidence for density‐dependent reproduction in a cooperatively breeding passerine. Ecology, 90(3), 729–741. 10.1890/07-1437.1 [DOI] [PubMed] [Google Scholar]
  12. Bury, A. , Niedojadlo, J. , Sadowska, E. T. , Bauchinger, U. , & Cichoń, M. (2019). Contrasting response of haematological variables between long‐term training and short exercise bouts in zebra finches (Taeniopygia guttata). The Journal of Experimental Biology, 222(4), jeb193227 10.1242/jeb.193227 [DOI] [PubMed] [Google Scholar]
  13. Buttemer, W. A. , & Astheimer, L. B. (2000). Testosterone does not affect basal metabolic rate or blood parasite load in captive male White‐plumed Honeyeaters Lichenostomus penicillatus . Journal of Avian Biology, 31(4), 479–488. 10.1034/j.1600-048X.2000.310407.x [DOI] [Google Scholar]
  14. Calbet, J. A. L. , Lundby, C. , Koskolou, M. , & Boushel, R. (2006). Importance of hemoglobin concentration to exercise: acute manipulations. Respiratory Physiology and Neurobiology, 151(2–3), 132–140. 10.1016/j.resp.2006.01.014 [DOI] [PubMed] [Google Scholar]
  15. Campbell, T. W. (1994). Cytology In Ritchie B. W., Harrison G. J., & Harrison L. R. (Eds.), Avian medicine: Principles and applications (pp. 199–221). Winger. [Google Scholar]
  16. Coglianese, E. E. , Qureshi, M. M. , Vasan, R. S. , Wang, T. J. , & Moore, L. L. (2012). Usefulness of the blood hematocrit level to predict development of heart failure in a community. American Journal of Cardiology, 109(2), 241–245. 10.1016/j.amjcard.2011.08.037 [DOI] [PMC free article] [PubMed] [Google Scholar]
  17. Cornell, A. , Gibson, K. F. , & Williams, T. D. (2017). Physiological maturity at a critical life‐history transition and flight ability at fledging. Functional Ecology, 31(3), 662–670. 10.1111/1365-2435.12777 [DOI] [Google Scholar]
  18. Cornell, A. , & Williams, T. D. (2017). Variation in developmental trajectories of physiological and somatic traits in a common songbird approaching fledging. Journal of Experimental Biology, 220(21), 4060–4067. 10.1242/jeb.162248 [DOI] [PubMed] [Google Scholar]
  19. Creel, S. (2001). Social dominance and stress hormones. Trends in Ecology and Evolution, 16(9), 491–497. 10.1016/S0169-5347(01)02227-3 [DOI] [Google Scholar]
  20. Daunt, F. , Wanless, S. , Harris, M. P. , Money, L. , & Monaghan, P. (2007). Older and wiser: Improvements in breeding success are linked to better foraging performance in European shags. Functional Ecology, 21(3), 561–567. 10.1111/j.1365-2435.2007.01260.x [DOI] [Google Scholar]
  21. Davey, C. , Lill, A. , & Baldwin, J. (2000). Variation during breeding in parameters that influence blood oxygen carrying capacity in shearwaters. Australian Journal of Zoology, 48(4), 347–356. 10.1071/ZO00047 [DOI] [Google Scholar]
  22. Eklom, K. , & Lill, A. (2006a). Development of parameters influencing blood oxygen‐carrying capacity in nestling doves. Emu, 106(4), 283–288. 10.1071/MU05061 [DOI] [PubMed] [Google Scholar]
  23. Eklom, K. , & Lill, A. (2006b). Development pattern of blood oxygen carrying capacity in rainbow bee‐eater nestlings. Australian Journal of Zoology, 54(1), 1–7. 10.1071/ZO05063 [DOI] [Google Scholar]
  24. Elliott, K. H. , Hare, J. F. , Le Vaillant, M. , Gaston, A. J. , Ropert‐Coudert, Y. , & Anderson, W. G. (2015). Ageing gracefully: Physiology but not behaviour declines with age in a diving seabird. Functional Ecology, 29(2), 219–228. 10.1111/1365-2435.12316 [DOI] [Google Scholar]
  25. Ezenwa, V. O. , Stefan Ekernas, L. , & Creel, S. (2012). Unravelling complex associations between testosterone and parasite infection in the wild. Functional Ecology Ltd, 26(1), 123–133. 10.1111/j.1365-2435.2011.01919.x [DOI] [Google Scholar]
  26. Fair, J. , Whitaker, S. , & Pearson, B. (2007). Sources of variation in haematocrit in birds Sources of variation in haematocrit in birds. Ibis, July, 535–552. 10.1111/j.1474-919X.2007.00680.x [DOI] [Google Scholar]
  27. Fronstin, R. B. , Christians, J. K. , & Williams, T. D. (2016). Experimental reduction of haematocrit affects reproductive performance in European starlings. Functional Ecology, 30(3), 398–409. 10.1111/1365-2435.12511 [DOI] [Google Scholar]
  28. Gaskell, H. , Derry, S. , Andrew Moore, R. , & McQuay, H. J. (2008). Prevalence of anaemia in older persons: Systematic review. BMC Geriatrics, 8(1), 1 10.1186/1471-2318-8-1 [DOI] [PMC free article] [PubMed] [Google Scholar]
  29. Griffiths, R. , Double, M. C. , Orr, K. , & Dawson, R. J. G. (1998). A DNA test to sex most birds. Molecular Ecology, 7(8), 1071–1075. 10.1046/j.1365-294x.1998.00389.x [DOI] [PubMed] [Google Scholar]
  30. Hammers, M. , & Brouwer, L. (2017). Rescue behaviour in a social bird: Removal of sticky “bird‐catcher tree” seeds by group members. Behaviour, 154(4), 403–411. 10.1163/1568539X-00003428 [DOI] [Google Scholar]
  31. Hammers, M. , Kingma, S. A. , Bebbington, K. , van de Crommenacker, J. , Spurgin, L. G. , Richardson, D. S. , Burke, T. , Dugdale, H. L. , & Komdeur, J. (2015). Senescence in the wild: Insights from a long‐term study on Seychelles warblers. Experimental Gerontology, 71, 69–79. 10.1016/j.exger.2015.08.019 [DOI] [PubMed] [Google Scholar]
  32. Hammers, M. , Kingma, S. A. , Spurgin, L. G. , Bebbington, K. , Dugdale, H. L. , Burke, T. , Komdeur, J. , & Richardson, D. S. (2019). Breeders that receive help age more slowly in a cooperatively breeding bird. Nature Communications, 10(1), 1301 10.1038/s41467-019-09229-3 [DOI] [PMC free article] [PubMed] [Google Scholar]
  33. Hammers, M. , Komdeur, J. , Kingma, S. A. , Hutchings, K. , Fairfield, E. A. , Gilroy, D. L. , & Richardson, D. S. (2016). Age‐specific haemosporidian infection dynamics and survival in Seychelles warblers. Scientific Reports, 6(1), 29720 10.1038/srep29720 [DOI] [PMC free article] [PubMed] [Google Scholar]
  34. Hammers, M. , Richardson, D. S. , Burke, T. , & Komdeur, J. (2012). Age‐dependent terminal declines in reproductive output in a wild bird. PLoS One, 7(7), e40413 10.1371/journal.pone.0040413 [DOI] [PMC free article] [PubMed] [Google Scholar]
  35. Hammers, M. , Richardson, D. S. , Burke, T. , & Komdeur, J. (2013). The impact of reproductive investment and early‐life environmental conditions on senescence: Support for the disposable soma hypothesis. Journal of Evolutionary Biology, 26(9), 1999–2007. 10.1111/jeb.12204 [DOI] [PubMed] [Google Scholar]
  36. Hammond, K. A. , Chappell, M. A. , Cardullo, R. A. , Lin, R. , & Johnsen, T. S. (2000). The mechanistic basis of aerobic performance variation in red junglefowl. Journal of Experimental Biology, 203(13), 2053–2064. [DOI] [PubMed] [Google Scholar]
  37. Harshman, L. G. , & Zera, A. J. (2007). The cost of reproduction: The devil in the details. Trends in Ecology and Evolution, 22(2), 80–86. 10.1016/j.tree.2006.10.008 [DOI] [PubMed] [Google Scholar]
  38. Hedrick, M. S. , Duffield, D. A. , & Cornell, L. H. (1986). Blood viscosity and optimal hematocrit in a deep‐diving mammal, the northern elephant seal (Mirounga angustirostris). Canadian Journal of Zoology, 64(10), 2081–2085. 10.1139/z86-317 [DOI] [Google Scholar]
  39. Heller, D. A. , Ahem, F. M. , Stout, J. T. , & McClearn, G. E. (1998). Mortality and biomarkers of aging in heterogeneous stock (HS) mice. Journals of Gerontology – Series A Biological Sciences and Medical Sciences, 53(3), B217–B230. 10.1093/gerona/53A.3.B217 [DOI] [PubMed] [Google Scholar]
  40. Hõrak, P. , Ots, I. , & Murumägi, A. (1998). Haematological health state indices of reproducing Great Tits: A response to brood size manipulation. Functional Ecology, 12(5), 750–756. 10.1046/j.1365-2435.1998.00244.x [DOI] [Google Scholar]
  41. Jégo, M. , Lemaître, J.‐F. , Bourgoin, G. , Capron, G. , Warnant, C. , Klein, F. , Gilot‐Fromont, E. , & Gaillard, J.‐M. (2014). Haematological parameters do senesce in the wild: Evidence from different populations of a long‐lived mammal. Journal of Evolutionary Biology, 27(12), 2745–2752. 10.1111/jeb.12535 [DOI] [PubMed] [Google Scholar]
  42. Jenni, L. , Müller, S. , Spina, F. , Kvist, A. , & Lindström, Å. (2006). Effect of endurance flight on haematocrit in migrating birds. Journal of Ornithology, 147(4), 531–542. 10.1007/s10336-006-0076-2 [DOI] [Google Scholar]
  43. Jensen, K. H. , Kim, W. , Holbrook, N. M. , & Bush, J. W. M. (2013). Optimal concentrations in transport systems. Journal of the Royal Society Interface, 10(83), 20130138 10.1098/rsif.2013.0138 [DOI] [PMC free article] [PubMed] [Google Scholar]
  44. Johnstone, C. P. , Lill, A. , & Reina, R. D. (2017). Use of erythrocyte indicators of health and condition in vertebrate ecophysiology: A review and appraisal. Biological Reviews, 92(1), 150–168. 10.1111/brv.12219 [DOI] [PubMed] [Google Scholar]
  45. Johnstone, C. P. , Reina, R. D. , & Lill, A. (2012). Interpreting indices of physiological stress in free‐living vertebrates. Journal of Comparative Physiology B: Biochemical, Systemic, and Environmental Physiology, 182(7), 861–879. 10.1007/s00360-012-0656-9 [DOI] [PubMed] [Google Scholar]
  46. Kaltreider, N. L. , & Meneely, G. R. (1940). The effect of exercise on the volume of blood. Journal of Clinical Investigation, 19(4), 627–634. 10.1172/jci101165 [DOI] [PMC free article] [PubMed] [Google Scholar]
  47. Kingma, S. A. , Komdeur, J. , Hammers, M. , & Richardson, D. S. (2016). The cost of prospecting for dispersal opportunities in a social bird. Biology Letters, 12(6), 20160316 10.1098/rsbl.2016.0316 [DOI] [PMC free article] [PubMed] [Google Scholar]
  48. Komdeur, J. (1991). Cooperative breeding in the Seychelles warbler. Trends in Ecology and Evolution, 7(10), 330–331. [DOI] [PubMed] [Google Scholar]
  49. Komdeur, J. (1992). Importance of habitat saturation and territory quality for evolution of cooperative breeding in the Seychelles warbler. Nature, 358(6386), 493–495. 10.1038/358493a0 [DOI] [Google Scholar]
  50. Komdeur, J. (1996). Influence of age on reproductive performance in the Seychelles warbler. Behavioral Ecology, 7(4), 417–425. 10.1093/beheco/7.4.417 [DOI] [Google Scholar]
  51. Komdeur, J. (2001). Mate guarding in the Seychelles warbler is energetically costly and adjusted to paternity risk. Proceedings of the Royal Society B: Biological Sciences, 268(1481), 2103–2111. 10.1098/rspb.2001.1750 [DOI] [PMC free article] [PubMed] [Google Scholar]
  52. Komdeur, J. , & Daan, S. (2005). Breeding in the monsoon: Semi‐annual reproduction in the Seychelles warbler (Acrocephalus sechellensis). Journal of Ornithology, 146(4), 305–313. 10.1007/s10336-005-0008-6 [DOI] [Google Scholar]
  53. Komdeur, J. , Piersma, T. , Kraaijeveld, K. , Kraaijeveld‐Smit, F. , & Richardson, D. S. (2004). Why Seychelles Warblers fail to recolonize nearby islands: Unwilling or unable to fly there? Ibis, 146(2), 298–302. 10.1046/j.1474-919X.2004.00255.x [DOI] [Google Scholar]
  54. Lendvai, Á. Z. , Giraudeau, M. , Bókony, V. , Angelier, F. , & Chastel, O. (2015). Within‐individual plasticity explains age‐related decrease in stress response in a short‐lived bird. Biology Letters, 11(7), 20150272 10.1098/rsbl.2015.0272 [DOI] [PMC free article] [PubMed] [Google Scholar]
  55. Leroi, A. M. (2001). Molecular signals versus the Loi de Balancement. Trends in Ecology and Evolution, 16(1), 24–29. 10.1016/S0169-5347(00)02032-2 [DOI] [PubMed] [Google Scholar]
  56. Lourdais, O. , Gartner, G. E. A. , & Brischoux, F. (2014). Ambush or active life: Foraging mode influences haematocrit levels in snakes. Biological Journal of the Linnean Society, 111(3), 636–645. 10.1111/bij.12223 [DOI] [Google Scholar]
  57. Minias, P. (2015). The use of haemoglobin concentrations to assess physiological condition in birds: A review. Conservation Physiology, 3(1), cov007 10.1093/conphys/cov007 [DOI] [PMC free article] [PubMed] [Google Scholar]
  58. Mirand, E. A. , Gordon, A. S. , & Wenig, J. (1965). Mechanism of testosterone action in erythropoiesis. Nature, 206(4981), 270–272. 10.1038/206270a0 [DOI] [PubMed] [Google Scholar]
  59. Morton, M. L. (1994). Hematocrits in montane sparrows in relation to reproductive schedule. The Condor, 96(1), 119–126. 10.2307/1369069 [DOI] [Google Scholar]
  60. Nakagawa, S. , & Schielzeth, H. (2010). Repeatability for Gaussian and non‐Gaussian data: A practical guide for biologists. Biological Reviews, 85, 935–956. 10.1111/j.1469-185X.2010.00141.x [DOI] [PubMed] [Google Scholar]
  61. Norris, K. , & Evans, M. R. (2000). Ecological immunology: Life history trade‐offs and immune defense in birds. Behavioral Ecology, 11(1), 19–26. 10.1093/beheco/11.1.19 [DOI] [Google Scholar]
  62. Nussey, D. H. , Coulson, T. , Festa‐Bianchet, M. , & Gaillard, J.‐M. (2008). Measuring senescence in wild animal populations: Towards a longitudinal approach. Functional Ecology, 22(3), 393–406. 10.1111/j.1365-2435.2008.01408.x [DOI] [Google Scholar]
  63. O’Brien, E. L. , Morrison, B. L. , & Johnson, L. S. (2001). Assessing the effects of haematophagous ectoparasites on the health of nestling birds: Haematocrit vs haemoglobin levels in House Wrens parasitized by blow fly larvae. Journal of Avian Biology, 32(1), 73–76. 10.1034/j.1600-048X.2001.320110.x [DOI] [Google Scholar]
  64. Pärn, H. , Lindström, K. M. , Sandell, M. , & Amundsen, T. (2008). Female aggressive response and hormonal correlates – An intrusion experiment in a free‐living passerine. Behavioral Ecology and Sociobiology, 62(10), 1665–1677. 10.1007/s00265-008-0595-3 [DOI] [Google Scholar]
  65. Petschow, R. , Petschow, D. , Bartels, R. , Baumann, R. , & Bartels, H. (1978). Regulation of oxygen affinity in blood of fetal, newborn and adult mouse. Respiration Physiology, 35(3), 271–282. 10.1016/0034-5687(78)90003-8 [DOI] [PubMed] [Google Scholar]
  66. Prinzinger, R. , & Misovic, A. (2010). Age‐correlation of blood values in the Rock Pigeon (Columba livia). Comparative Biochemistry and Physiology Part A: Molecular and Integrative Physiology, 156(3), 351–356. 10.1016/j.cbpa.2009.07.028 [DOI] [PubMed] [Google Scholar]
  67. Raj Pant, S. , Komdeur, J. , Burke, T. A. , Dugdale, H. L. , & Richardson, D. S. (2019). Socio‐ecological conditions and female infidelity in the Seychelles warbler. Behavioral Ecology, 30(5), 1254–1264. 10.1093/beheco/arz072 [DOI] [PMC free article] [PubMed] [Google Scholar]
  68. Richardson, D. S. , Burke, T. , & Komdeur, J. (2002). Direct benefits and the evolution of female‐biased cooperative breeding in seychelles warblers. Evolution, 56(11), 2313–2321. 10.1111/j.0014-3820.2002.tb00154.x [DOI] [PubMed] [Google Scholar]
  69. Richardson, D. S. , Burke, T. , & Komdeur, J. (2007). Grandparent helpers: The adaptive significance of older, postdominant helpers in the Seychelles warbler. Evolution, 61(12), 2790–2800. 10.1111/j.1558-5646.2007.00222.x [DOI] [PubMed] [Google Scholar]
  70. Richardson, D. S. , Jury, F. L. , Blaakmeer, K. , Komdeur, J. , & Burke, T. (2001). Parentage assignment and extra‐group paternity in a cooperative breeder: The Seychelles warbler (Acrocephalus sechellensis). Molecular Ecology, 10(9), 2263–2273. 10.1046/j.0962-1083.2001.01355.x [DOI] [PubMed] [Google Scholar]
  71. Ricklefs, R. E. , & Wikelski, M. (2002). The physiology/life‐history nexus. Trends in Ecology and Evolution, 17(10), 462–468. 10.1016/S0169-5347(02)02578-8 [DOI] [Google Scholar]
  72. RStudio Team (2020). RStudio: Integrated development for R. RStudio, PBC; http://www.rstudio.com/ [Google Scholar]
  73. Saino, N. , Cuervo, J. J. , Ninni, P. , De lope, F. , & Moller, A. P. (1997). Haematocrit correlates with tail ornament size in three populations of the Barn Swallow (Hirundo rustica). Functional Ecology, 11(5), 604–610. 10.1046/j.1365-2435.1997.00131.x [DOI] [Google Scholar]
  74. Schuler, B. , Arras, M. , Keller, S. , Rettich, A. , Lundby, C. , Vogel, J. , & Gassmann, M. (2010). Optimal hematocrit for maximal exercise performance in acute and chronic erythropoietin‐treated mice. Proceedings of the National Academy of Sciences of the United States of America, 107(1), 419–423. 10.1073/pnas.0912924107 [DOI] [PMC free article] [PubMed] [Google Scholar]
  75. Sepp, T. , Sild, E. , & Hõrak, P. (2010). Condition indexes in greenfinches: Effects of captivity and diurnal variation. Physiological and Biochemical Zoology, 83(2), 276–282. 10.1086/648580 [DOI] [PubMed] [Google Scholar]
  76. Sheldon, L. D. , Chin, E. H. , Gill, S. A. , Schmaltz, G. , Newman, A. E. M. , & Soma, K. K. (2008). Effects of blood collection on wild birds: an update. Journal of Avian Biology, 39(4), 369–378. 10.1111/j.0908-8857.2008.04295.x [DOI] [Google Scholar]
  77. Smucny, D. A. , Allison, D. B. , Ingram, D. K. , Roth, G. S. , Kemnitz, J. W. , Kohama, S. G. , Lane, M. A. , & Black, A. (2004). Changes in blood chemistry and hematology variables during aging in captive rhesus macaques (Macaca mulatta). J Med Primatol 30:161–173, 2001. Journal of Medical Primatology, 33(1), 48–54. 10.1111/j.1600-0684.2003.00052.x [DOI] [PubMed] [Google Scholar]
  78. Speakman, J. R. , & Selman, C. (2011). The free‐radical damage theory: Accumulating evidence against a simple link of oxidative stress to ageing and lifespan. BioEssays, 33(4), 255–259. 10.1002/bies.201000132 [DOI] [PubMed] [Google Scholar]
  79. Spurgin, L. G. , Bebbington, K. , Fairfield, E. A. , Hammers, M. , Komdeur, J. , Burke, T. , Dugdale, H. L. , & Richardson, D. S. (2017). Spatio‐temporal variation in lifelong telomere dynamics in a long‐ term ecological study. Journal of Animal Ecology, 87(1), 187–198. 10.1111/1365-2656.12741 [DOI] [PMC free article] [PubMed] [Google Scholar]
  80. Stack, S. W. , & Berger, S. A. (2009). The effects of high hematocrit on arterial flow‐A phenomenological study of the health risk implications. Chemical Engineering Science, 64(22), 4701–4706. 10.1016/j.ces.2009.07.017 [DOI] [Google Scholar]
  81. Stark, H. , & Schuster, S. (2012). Comparison of various approaches to calculating the optimal hematocrit in vertebrates. Journal of Applied Physiology, 113(3), 355–367. 10.1152/japplphysiol.00369.2012 [DOI] [PubMed] [Google Scholar]
  82. Trillmich, F. , Rea, L. , Castellini, M. , & Wolf, J. B. W. (2008). Age‐related changes in hematocrit in the Galápagos sea lion (Zalophus wollebaeki) and the Weddell seal (Leptonychotes weddellii). Marine Mammal Science, 24(2), 303–314. 10.1111/j.1748-7692.2007.00177.x [DOI] [Google Scholar]
  83. van de Crommenacker, J. , Hammers, M. , Woude, J. , Louter, M. , Santema, P. , Richardson, D. S. , & Komdeur, J. (2017). Oxidative status and fitness components in the Seychelles warbler. Functional Ecology, 31(6), 1210–1219. 10.1111/1365-2435.12861 [DOI] [Google Scholar]
  84. van de Crommenacker, J. , Komdeur, J. , & Richardson, D. S. (2011). Assessing the cost of helping: The roles of body condition and oxidative balance in the seychelles warbler (Acrocephalus sechellensis). PLoS One, 6(10), e26423 10.1371/journal.pone.0026423 [DOI] [PMC free article] [PubMed] [Google Scholar]
  85. van de Crommenacker, J. , Richardson, D. S. , Groothuis, T. G. G. , Eising, C. M. , Dekker, A. L. , & Komdeur, J. (2004). Testosterone, cuckoldry risk and extra‐pair opportunities in the Seychelles warbler. Proceedings of the Royal Society B: Biological Sciences, 271(1543), 1023–1031. 10.1098/rspb.2004.2697 [DOI] [PMC free article] [PubMed] [Google Scholar]
  86. van de Pol, M. , & Verhulst, S. (2006). Age‐dependent traits: A new statistical model to separate within‐ and between‐individual effects. The American Naturalist, 167(5), 766–773. 10.1086/503331 [DOI] [PubMed] [Google Scholar]
  87. van de Pol, M. , & Wright, J. (2009). A simple method for distinguishing within‐ versus between‐subject effects using mixed models. Animal Behaviour, 77(3), 753–758. 10.1016/j.anbehav.2008.11.006 [DOI] [Google Scholar]
  88. Voorhees, J. L. , Powell, N. D. , Moldovan, L. , Mo, X. , Eubank, T. D. , & Marsh, C. B. (2013). Chronic restraint stress upregulates erythropoiesis through glucocorticoid stimulation. PLoS One, 8(10), e77935 10.1371/journal.pone.0077935 [DOI] [PMC free article] [PubMed] [Google Scholar]
  89. Wagner, E. C. , Prevolsek, J. S. , Wynne‐Edwards, K. E. , & Williams, T. D. (2008). Hematological changes associated with egg production: Estrogen dependence and repeatability. The Journal of Experimental Biology, 211(Pt 3), 400–408. 10.1242/jeb.011205 [DOI] [PubMed] [Google Scholar]
  90. Wagner, E. C. , Stables, C. A. , & Williams, T. D. (2008). Hematological changes associated with egg production: Direct evidence for changes in erythropoiesis but a lack of resource dependence? Journal of Experimental Biology, 211(18), 2960–2968. 10.1242/jeb.017897 [DOI] [PubMed] [Google Scholar]
  91. Wagner, K. F. , Katschinski, D. M. , Hasegawa, J. O. , Schumacher, D. , Meller, B. , Gembruch, U. , Schramm, U. , Jelkmann, W. , Gassmann, M. , & Fandrey, J. (2001). Chronic inborn erythrocytosis leads to cardiac dysfunction and premature death in mice overexpressing erythropoietin. Blood, 97(2), 536–542. 10.1182/blood.V97.2.536 [DOI] [PubMed] [Google Scholar]
  92. Wagner, P. D. (1996). Determinants of maximal oxygen transport and utilization. Annual Review of Physiology, 58(1), 21–50. 10.1146/annurev.physiol.58.1.21 [DOI] [PubMed] [Google Scholar]
  93. Walton, B. L. , Lehmann, M. , Skorczewski, T. , Holle, L. A. , Beckman, J. D. , Cribb, J. A. , Mooberry, M. J. , Wufsus, A. R. , Cooley, B. C. , Homeister, J. W. , Pawlinski, R. , Falvo, M. R. , Key, N. S. , Fogelson, A. L. , Neeves, K. B. , & Wolberg, A. S. (2017). Elevated hematocrit enhances platelet accumulation following vascular injury. Blood, 129(18), 2537–2546. 10.1182/blood-2016-10-746479 [DOI] [PMC free article] [PubMed] [Google Scholar]
  94. Whittingham, M. J. , Stephens, P. A. , Bradbury, R. B. , & Freckleton, R. P. (2006). Why do we still use stepwise modelling in ecology and behaviour? Journal of Animal Ecology, 75(5), 1182–1189. 10.1111/j.1365-2656.2006.01141.x [DOI] [PubMed] [Google Scholar]
  95. Wilcoxen, T. E. , Boughton, R. K. , Bridge, E. S. , Rensel, M. A. , & Schoech, S. J. (2011). Age‐related differences in baseline and stress‐induced corticosterone in Florida scrub‐jays. General and Comparative Endocrinology, 173(3), 461–466. 10.1016/j.ygcen.2011.07.007 [DOI] [PubMed] [Google Scholar]
  96. Wilder, S. M. , Raubenheimer, D. , & Simpson, S. J. (2016). Moving beyond body condition indices as an estimate of fitness in ecological and evolutionary studies. Functional Ecology, 30(1), 108–115. 10.1111/1365-2435.12460 [DOI] [Google Scholar]
  97. Williams, T. D. , Challenger, W. O. , Christians, J. K. , Evanson, M. , Love, O. , & Vezina, F. (2004). What causes the decrease in haematocrit during egg production? Functional Ecology, 18(3), 330–336. 10.1111/j.0269-8463.2004.00829.x [DOI] [Google Scholar]
  98. Woodley, S. K. , & Moore, M. C. (1999). Ovarian hormones influence territorial aggression in free‐living female mountain spiny lizards. Hormones and Behavior, 35(3), 205–214. 10.1006/hbeh.1999.1514 [DOI] [PubMed] [Google Scholar]
  99. Yap, K. N. , Dick, M. F. , Guglielmo, C. G. , & Williams, T. D. (2018). Effects of experimental manipulation of hematocrit on avian flight performance in high‐ and low‐altitude conditions. Journal of Experimental Biology, 221(22), jeb191056 10.1242/jeb.191056 [DOI] [PubMed] [Google Scholar]
  100. Yap, K. N. , Serota, M. W. , & Williams, T. D. (2017). The physiology of exercise in free‐living vertebrates: What can we learn from current model systems? Integrative and Comparative Biology, 57, 195–206. 10.1093/icb/icx016 [DOI] [PubMed] [Google Scholar]
  101. Yap, K. N. , Tsai, O. H. I. , & Williams, T. D. (2019). Haematological traits co‐vary with migratory status, altitude and energy expenditure: A phylogenetic, comparative analysis. Scientific Reports, 9(1), 6351 10.1038/s41598-019-42921-4 [DOI] [PMC free article] [PubMed] [Google Scholar]
  102. Zimmer, I. , Ropert‐Coudert, Y. , Kato, A. , Ancel, A. , & Chiaradia, A. (2011). Does foraging performance change with age in female little penguins (Eudyptula minor)?. PLoS One, 6(1), e16098 10.1371/journal.pone.0016098 [DOI] [PMC free article] [PubMed] [Google Scholar]

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Data Availability Statement

Data are available from the Dryad Digital Repository: https://doi.org/10.5061/dryad.7wm37pvrp


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