How to capture wild passerine species to study baseline corticosterone levels
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Baseline corticosterone levels have been suggested to be an effective tool to assess and monitor the health status of individuals and populations of wild birds. However, measuring baseline corticosterone levels in the field is difficult because the capture protocol may affect rates of corticosterone secretion. In passerine birds, two methods of capture are widely used: (1) passive netting consisting of monitoring mist-nets frequently to check if a bird has been caught; and (2) target netting consisting of installing a conspecific decoy and/or playing a tape-recorded conspecific song in the vicinity of a mist-net until the territorial bird is captured. Our objective here was to determine whether these methods of capture are effective at achieving non-disturbed baseline corticosterone levels in American Redstarts (Setophaga ruticilla). We found that passive netting was associated with elevated corticosterone levels, suggesting that hanging in a net for several minutes activates the HPA axis and, thus, elicits an adreno-cortical stress response. In contrast, target netting was not associated with an increase in corticosterone levels, regardless of the length of time between when the target bird first approached the net and when it was captured. Therefore, we suggest that researchers interested in estimated baseline corticosterone in this species use target netting and not passive netting.
KeywordsCorticosterone Capture Stress Field endocrinology
During the last decade, the use of glucocorticosteroid levels has been suggested as a useful and relevant tool to monitor the health status of individuals and populations in the wild (Cockrem 2006; Wikelski and Cooke 2006; but see Bonier et al. 2009). Indeed, corticosterone levels (the primary glucocorticosteroid in birds) often increase in response to energetic constraints and acute stressors and this rise is thought to promote behavioral and physiological adjustments that allow the individual to cope with these perturbations before becoming compromised (the concept of allostasis; McEwen and Wingfield 2003; Landys et al. 2006). Therefore, circulating corticosterone levels are likely to provide some information regarding the environmental situations and the stressors (acute or chronic) that individuals have to cope with (Wingfield et al. 1998; Landys et al. 2006; Bonier et al. 2009).
To confirm the relevancy of this endocrine tool in conservation, many studies have aimed to understand how reliably corticosterone levels can reflect environmental conditions and anthropogenic disturbance in wild vertebrates (Wasser et al. 1997; Marra and Holberton 1998; Cash and Hoberton 2005; Walker et al. 2006; Angelier et al. 2007; Jenni-Eiermann et al. 2008; Thiel et al. 2008; Bonier et al. 2009). Although chronic changes in corticosterone are informative regarding perturbations to environment, measuring corticosterone in the field is often difficult because it requires two steps (capturing the animal and collecting its blood), which are perceived as acute stressors, and thus, induce rapid and important changes in corticosterone levels (Wingfield et al. 1998). Therefore, blood samples collected beyond a few minutes after capture can represent an inaccurate measure of pre-handling baseline corticosterone levels. In this case, they may not mirror the environmental situation faced by an individual, but rather be its response to the acute stressor of capture and handling (Wingfield et al. 1982; Romero and Romero 2002; Romero and Reed 2005). Unfortunately, in most species and under most conditions, corticosterone levels rise after only a few minutes of exposure to a stressor. Therefore, to acquire unbiased corticosterone levels (baseline corticosterone levels), the birds must be sampled for blood quickly after capture (Wingfield et al. 1982; Schoech et al. 1999; Romero and Reed 2005; Müller et al. 2006). However, the method of capture itself can still be an acute stressor and, thus, can affect corticosterone levels (Romero and Romero 2002; Lynn and Porter 2008). In this study, we aimed to understand whether corticosterone levels are affected by two widely used methods of capture in a passerine species.
In many passerine species and during several specific life-history stages, it is impossible to use some capture methods to catch individuals (traps or others; Silverin 1998; Quillfeldt et al. 2007; Becker et al. 2006; Arnold et al. 2008), and consequently, birds are usually captured by using two alternative methods. First, birds can be captured by ‘target netting’ when they are territorial and responsive to a simulated territorial intrusion (STI; Holmes et al. 1989; Goymann et al. 2007). Second, birds can be captured by ‘passive netting’, which consists of setting up mist-nets in the locations where birds are most likely to forage or move, and then waiting for the birds to fly into the net. Sometimes, researchers diligently monitor the mist-net and are, therefore, often able to extract the bird from the net as soon as it is caught (called hereafter ‘permanently monitored passive netting’). Although permanently monitored passive netting allows for reliable assessment of baseline corticosterone levels, this method can only be conducted on one focal individual at a time, is relatively labor-intensive, and can limit one’s ability to catch a sufficient sample size of birds (Lynn and Porter 2008). To increase the probability of capturing multiple birds when passive netting, several mist-nets are usually set up at various locations and then monitored at regular and short time intervals to check if a bird has been captured (called hereafter ‘frequently monitored passive netting’). In this case, birds are likely to hang in a mist net for several minutes prior to handling, and this may make this method inappropriate for measuring baseline corticosterone levels if birds perceive this restraint in the net as an acute stressor (Marra et al. 1995; Romero and Romero 2002).
Although target netting is definitely appropriate for some studies, it may not always provide reliable baseline corticosterone levels (Landys et al. 2007). Indeed, the presence of a conspecific decoy may be perceived as an acute stressor for a territorial bird and, thus, activate its hypothalamo-ptuitary-adrenal (HPA) axis. Aggressive interactions can be life-threatening, and the presence of a competing conspecific may also result in the loss of territory or mate. Therefore, individuals may elicit an adrenocortical stress response to adjust their physiology and their behavior to the presence of a conspecific intruder (Wingfield et al. 1998; Landys et al. 2006). Circulating corticosterone levels would increase in response to a prolonged STI and not reflect baseline levels even if the bird is sampled for blood quickly after having been caught in the net (Van Duyse et al. 2004; Landys et al. 2007). Alternatively, STI may not represent an acute stressor for a bird, especially if this intrusion is very short or does not threaten the individual and, therefore, is unlikely to entail survival costs (Harding and Follett 1979; Wingfield 1985; Silverin 1998).
Several studies have investigated the influence of a STI on corticosterone values, but often report conflicting results (Harding and Follett 1979; Wingfield 1985; Wingfield and Lewis 1993; Wingfield and Hahn 1994; Sorenson et al. 1997; Silverin 1998; Astheimer et al. 2000; Van Duyse et al. 2004; Landys et al. 2007). Moreover, the influence of passive netting on corticosterone levels has, to our knowledge, only been reported in a few species (Silverin 1998; Romero and Romero 2002). Here, we set out to determine whether passive netting and target netting differentially influence baseline corticosterone levels in an intensively studied passerine species, the American Redstart (Setophaga ruticilla), during the non-breeding period. Redstarts were captured either by frequently monitored passive netting or by target netting. Moreover, several Redstarts were also captured by permanently monitored passive netting in order to assess baseline corticosterone levels with almost certainty for some birds (Romero and Romero 2002; Wilson and Holberton 2004).
Birds and study area
Our field study was carried out in 2008 from 5 February to 27 April at the Font Hill Nature Reserve, 13 km west of Black River, St. Elizabeth Parish, Jamaica. The American Redstart is a small migratory passerine bird that breeds in North America and overwinters in the Caribbean and Central America. American Redstarts begin arriving in Jamaica and establishing non-breeding territories in mid-September, and remain on those territories for 6–7 months until they depart on spring migration in April through mid-May. During this non-breeding period, Redstarts of both sexes are territorial and occur in a variety of habitat types that vary in suitability (see Marra and Holberton 1998; Marra and Holmes 2001; Studds and Marra 2007). In this study, 104 American Redstarts—83 females and 21 males—were captured and sampled for corticosterone in mangroves and scrubs during this period to test the relevancy of different methods of capture to assess baseline corticosterone levels. After capture and blood sampling, birds were released on their territories.
Redstarts were caught by using either target netting (n = 27), frequently monitored passive netting (n = 69), or permanently monitored passive netting (n = 8). After capture and blood sampling, birds were banded with an aluminum band and a unique combination of color bands for individual recognition. All these methods of capture were used over the whole study period and in both habitats and with both sexes. Moreover, each method of capture was as used in one habitat as in another (χ2 = 1.73, df = 3, P = 0.629).
Target netting consisted of using an STI to capture a territorial bird (Wingfield 1985; Holmes et al. 1989; Goymann et al. 2007). A stuffed decoy of an adult male American Redstart was placed in the center of the territory of a Redstart and accompanied by a playback of songs and chips broadcast from an mp3 player (I-Pod Nano; Apple) through a speaker placed alongside the decoy. The decoy and speaker were placed in the center and at the base of a mist-net. In this study, we monitored the duration of the STI process until the bird was caught in the mist-net (called hereafter ‘STI duration’, range: 40 s to 15 min, average: 6.35 min). At capture, the bird was immediately extracted from the mist-net and blood was collected as quickly as possible (range 2–6 min). The duration of this blood sampling process was also monitored (called hereafter ‘blood sampling duration’) starting from the time when the bird was hitting the net to the end of the blood sampling process.
Frequently monitored passive netting consists of setting up several mist-nets in the locations where birds are the most likely to forage or move, and then waiting for the birds to fly into the net. In this study, we set up between 4 and 12 mist-nests in several Redstart territories and then monitored the nets regularly to check if a bird was caught. Although, for practical and logistical reasons, we did not monitor the exact interval between two checks of a given mist-net, we monitored whether a net was checked at a high frequency (interval of 2–15 min between two net checks) or a low frequency (interval of 15–25 min between two net checks). After its discovery in a mist-net, the bird was immediately extracted from the net and blood was collected as quickly as possible (range 1–6 min). The duration of this blood sampling process was monitored (‘blood sampling duration’) starting from the time when the bird was discovered in the net to the end of the blood sampling process.
In addition, eight Redstarts were caught by permanently monitored passive netting. We set up from 1 to 3 mist-nets in the territory of a Redstart and these mist-nets were then monitored permanently until the bird hit one of the mist-nets. Then, the bird was extracted and bled within 3 min 30 s (maximum) of capture. For these birds, baseline corticosterone levels were therefore assessed with certainty (Wingfield et al. 1982; Romero and Reed 2005).
Blood sampling and hormone assay
We collected blood from the alar wing vein using a 27-gauge needle and heparinized microcapillary tubes (50–100 μl). Blood samples were stored at 4°C for up to 6 h until centrifuged for 10 min at 10,000g. Plasma was collected and then stored at −20°C until analyzed for corticosterone concentration by radioimmunoassay at the laboratory of Avian Biology at the University of Maine, USA, as previously described (Cash and Holberton 1999).
All analyses were performed with SAS statistical software (v. 9.01; SAS Institute). For all variables tested, normality assumptions were checked by running the Shapiro–Wilkes test for normality. There were no indications that normality assumptions were violated. Preliminary analyses showed that baseline corticosterone levels did not vary with date of sampling or habitat (mangrove vs logwood scrub) whatever the method of capture (P > 0.25 in all cases). In addition, baseline corticosterone levels and the adrenocortical response to stress have been reported not to vary between sexes in Redstarts (Marra and Holberton 1998) and we did not find any difference in baseline corticosterone levels between sexes in our study (Student’s test, t = −1.84, P = 0.12). Thus, data from both sexes and habitats were pooled for further analyses.
First, we tested for the influence of capture method on corticosterone levels by using a GLM (dependent variable: corticosterone levels; independent variable: method of capture). In this analysis, the method of capture is a four class factor (permanently monitored passive netting, target netting, frequently monitored passive netting at a high frequency of net checking, frequently monitored passive netting at a low frequency of net checking). Because our aim was to test whether frequently monitored passive netting and target netting were appropriate to assess baseline corticosterone level, we only considered the birds that were bled within 3 min 30 s (Romero and Romero 2002; F. Angelier et al., unpublished results) to assess baseline corticosterone levels in Redstarts for this analysis (total n = 76; i.e., permanently monitored passive netting, n = 7; target netting, n = 19; frequently monitored passive netting at a low frequency of net checking, n = 29; frequently monitored passive netting at a low frequency of net checking, n = 21). Second, we tested whether a STI affects corticosterone levels in Redstarts. Specifically, we tested for the influence of the STI duration on corticosterone levels by using regression analysis (dependent variable: corticosterone levels; independent variable: STI duration). For this analysis, we used the birds that were captured by target netting, but also the birds that were captured by permanently monitored passive netting (playback duration was logically considered to be 0 for these birds). Because our aim was to test whether the duration of the STI has an influence on baseline corticosterone levels, birds that were bled more than 3 min 30 s after capture were not included in this analysis (n = 26). Finally, we tested the influence of blood sampling duration on corticosterone levels. Because the influence of blood sampling duration on corticosterone level may differ with the method of capture, we included the method of capture as an independent factor in our model (GLM; dependent variable: corticosterone levels; independent variables: method of capture, blood sampling duration and their interaction). In this analysis, the method of capture is a three class factor (target netting, frequently monitored passive netting at a high frequency of net checking, frequently monitored passive netting at a low frequency of net checking). We did not include the birds that were caught by permanently monitored passive netting in this analysis (final sample size: n = 96) because all these birds were bled very quickly after capture (within 3 min 30 s) and reflect baseline corticosterone levels. They were therefore inappropriate to investigate the influence of blood sampling duration on circulating corticosterone levels.
In this study, we investigated the influence of frequently monitored passive netting on corticosterone levels by comparing corticosterone levels of birds that were sampled immediately after they hit the net (baseline corticosterone levels) with those of birds that have spent either up to 15 min or up to 25 min in the net before being sampled (frequently monitored passive netting). We showed that corticosterone levels respectively increased by an average of 115 and 220% when Redstarts spent up to 15 and 25 min in the net before being sampled for corticosterone, demonstrating that corticosterone levels increased with the time spent in the net. Therefore, we are confident that being caught in the net activates the HPA axis and that even a few minutes in the net can result in an increase in corticosterone secretion as previously reported in House Sparrows (Passer domesticus), White-crowned Sparrows (Zonotrichia sp.), and Pied Flycatchers (Ficedula hypoleuca) (Silverin 1998; Romero and Romero 2002). Interestingly, we found a large variance in corticosterone levels when birds were captured by frequently monitored passive netting, at either high or a low frequency, whereas we found a low variance in corticosterone levels when birds were captured by target netting and permanently monitored passive netting (Fig. 1). This large variance probably results from various time of restraint in the mist-net, but also from a high variability in the sensitivity of the HPA axis to stress between individuals (Cockrem and Silverin 2002). Some birds may have dramatically increased their corticosterone secretion after having been caught in the net, whereas others may have only slightly increased this secretion. This interpretation is supported by the fact that the HPA sensitivity to stress differs between individuals in American Redstarts (corticosterone levels vary between 10 and 90 ng/ml after a 30-min stress protocol; Marra and Holberton 1998; Angelier et al. 2009). Indeed, using frequently monitored passive netting is problematic when studying baseline corticosterone levels because the stress of being entangled in a net elicits an adrenocortical stress response which varies between individuals. Therefore, this method of capture can bias the results, and field endocrinologists should rather use permanently monitored passive netting to assess baseline corticosterone levels in the field, even if it limits the number of birds that can be captured in a given period of time (Lynn and Porter 2008).
Target netting and effect of STI
We did not find any relationship between the duration of a STI and circulating corticosterone levels in American Redstarts. Moreover, we did not find any difference in corticosterone levels between the birds caught by permanently monitored passive netting and those caught by target netting. Therefore, target netting did not elicit an HPA stress response in non-breeding Redstarts, and this method of capture is appropriate to assess baseline corticosterone levels in this species. This probably means that the presence of a conspecific is not an acute stressor for this species, at least during the non-breeding period. Accordingly, previous studies have shown that a STI does not elicit any change in corticosterone levels in several species (Harding and Follett 1979; Wingfield 1985; Wingfield and Hahn 1994; Silverin 1998). However, corticosterone levels can also be significantly and importantly affected by STIs in other species (Wingfield and Lewis 1993; Sorenson et al. 1997; Astheimer et al. 2000; Van Duyse et al. 2004; Landys et al. 2007). Therefore, the influence of the target netting method on corticosterone levels differs between species and we suggest that it may also depend on the environmental context and, possibly, on the physiological status of individuals (Schoech et al. 1999; Landys et al. 2007). In our study, the duration of the simulated territorial intrusion was not very long (max: 15 min) and we cannot exclude the hypothesis that a longer STI could have resulted in a HPA stress response: one can imagine that only the prolonged presence of a rival could be perceived as a stressor by Redstarts. However, this interpretation is unlikely because a long-term STI (up to 2 h) does not affect corticosterone levels in Song Sparrows (Melospiza melodia) (Wingfield 1985). Moreover, corticosterone is rapidly secreted (within 10 min) in response to a STI in Blue Tits (Cyanistes caeruleus) (Landys et al. 2007). Therefore, the duration of the STI is probably not the main factor determining whether individuals elicit a HPA stress response or not. Rather, it seems that STIs represent an acute stressor for some species, but not for others. Consequently, we recommend endocrinologists to conduct pilot studies to check that target netting can be used to assess baseline corticosterone in species for which no validation has been made.
Time of blood sampling
Not surprisingly, corticosterone levels in Redstarts increased quickly after only few minutes of handling. When using target netting with an STI, measured corticosterone levels were very elevated when blood was collected from 4 to 6 min of handling (maximum: 54.83 ng/ml), whereas corticosterone levels were never above 13 ng/ml when birds were sampled for blood within 3 min 30 s of capture. Therefore, we confirm that it is essential to collect blood very quickly after the beginning of capture and handling to monitor baseline corticosterone levels (Wingfield et al. 1982; Schoech et al. 1999; Romero and Reed 2005; Müller et al. 2006; Scriba and Goymann 2008). Interestingly, we did not find any relationship between blood sampling duration and corticosterone levels when Redstarts were captured by frequently monitored passive netting. This result could appear surprising since the increase in corticosterone level with handling duration has been reported in numerous species (Romero 2002; Bókony et al. 2009), including American Redstarts (Marra and Holberton 1998). However, this pattern only results from the fact that frequently monitored passive netting induces some important changes in corticosterone levels (Fig. 1) and creates a lot of noise in the corticosterone value data. Therefore, this last result demonstrates that the use of frequently monitored passive netting can definitely bias one’s measurement of baseline corticosterone levels, but, more importantly, can mask biological relevant relationships even when they are highly significant, such as the one linking corticosterone levels and blood sampling duration (Romero and Reed 2005; Müller et al. 2006; Scriba and Goymann 2008).
We emphasize that collecting baseline corticosterone levels in the field is complicated because capture and handling can represent an acute stressor for birds. First, it is essential to collect blood quickly after the start of handling (Wingfield et al. 1982; Romero and Reed 2005; Müller et al. 2006). Second, we show that target netting is a relevant technique to catch Redstarts for field endocrinologists interested in baseline corticosterone levels because this technique does not elicit a HPA stress response in this species. Third, passive netting is a relevant technique to catch birds, but only if the observer can extract the bird from the net as soon as it gets caught in the net because being entangled in a net elicits a HPA stress response (Silverin 1998; Romero and Romero 2002; this study). Thus, we highlight the need to consider the method of capture when studying baseline corticosterone levels in passerines.
Wie die Basislevel von Corticosteron bei Sperlingsvogelarten im Freiland gemessen werden sollten: Die Bedeutung der Fangmethode
Es wurde vorgeschlagen, dass die Basislevel von Corticosteron ein effektives Werkzeug darstellen, um den Gesundheitszustand von Individuen und Populationen wildlebender Vögel abzuschätzen und zu überwachen. Es ist jedoch schwierig, Basislevel von Corticosteron im Freiland zu messen, da die Fangmethode die Raten der Corticosteron-Sekretion beeinflussen könnte. Bei Sperlingsvögeln werden zwei Fangmethoden häufig angewendet: (1) passiver Netzfang, bei dem Japannetze öfters kontrolliert werden, um zu überprüfen, ob ein Vogel gefangen worden ist, und (2) gezielter Netzfang, bestehend aus der Installation eines Lockvogels derselben Art und/oder dem Abspielen eines auf Band aufgenommenen Gesangs eines Artgenossen in der Nähe eines Japannetzes, bis der territoriale Vogel gefangen ist. Unser Ziel war es zu ermitteln, ob diese Fangmethoden effektiv sind, um genaue, ungestörte Corticosteron-Basislevel von Schnäpperwaldsängern (Setophaga ruticilla) zu erbringen. Wir fanden heraus, dass passiver Netzfang mit erhöhten Corticosteron-Leveln verbunden war, was darauf hindeutet, dass das Hängen im Netz für einige Minuten eine adreno-corticale Stressantwort hervorruft. Im Gegensatz dazu war gezielter Netzfang nicht mit einem Anstieg der Corticosteron-Level verbunden, unabhängig vom Zeitabstand zwischen der ersten Annäherung des Zielvogels an das Netz und seines Fangs. Daher schlagen wir vor, dass Forscher, die daran interessiert sind, Corticosteron-Basislevel bei dieser Art abzuschätzen, gezielten Netzfang und nicht passiven Netzfang anwenden.
This study was supported by an NSF grant (0649679) to P.P. Marra and R.L. Holberton and an NSF grant (0717338) to P.P. Marra. We thank E. Corliss, J.L. Dowling, J.H. Junda, S.R. Sult and M.A. Thomas for their assistance in the field. We thank the Petroleum Corporation of Hill Nature Preserve, and Yvette Strong and Andrea Donaldson of the Jamaica National Environmental Planning Agency for their cooperation.
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