Skip to main content
Download PDF

Seasonal activity levels of a farm-island population of striated caracaras (Phalcoboenus australis) in the Falkland Islands

Animal Biotelemetry volume 8, Article number: 27 (2020) Cite this article

Abstract

Background

Animals need adaptive strategies to cope with seasonal changes in prey availability to survive and reproduce, which can include migrating, prey-switching, or reducing metabolic needs. Human settlements can disrupt spatiotemporal patterning in resource availability, which can affect animals’ foraging success, particularly for juveniles who are behaviorally developing and learning efficient foraging skills. Here, we investigate behavioral responses of juvenile striated caracaras, a near-threatened scavenging falconid, to seasonally migratory seabird prey and a farm settlement on Saunders Island, Falklands. We deployed accelerometer–GPS dataloggers (n = 27) to measure seasonal differences in daily and hourly vectorial dynamic body acceleration (VeDBA; an activity index measured in gravitational g) and space use, and investigated seasonal variation in body mass of the tagged subset and an additional 65 caracaras.

Results

Juvenile caracaras were overall similarly active in winter and summer. However, during winter, caracaras made the most of limited daylight by increasing average daytime activity (winter males: 0.16 ± 0.03 g, summer males: 0.09 ± 0.01 g, winter females: 0.12 ± 0.02 g, summer females: 0.08 ± 0.01 g). During winter, both sexes increased the percentage of daylight spent in high activity (winter males: 35 ± 5%, summer males: 21 ± 3%, winter females: 25 ± 6%, summer females: 16 ± 3%, p < 0.001) and ranged nearly 4 times farther (95% kernel density estimate winter: 2.36 ± 0.96 km2, summer: 0.61 ± 0.20 km2; p < 0.001). Furthermore, on a daily scale, males were 21% more active than females year-round (24-h average VeDBA: males 0.07 ± 0.01 g, females 0.06 ± 0.01 g; p < 0.01). We did not observe a significant seasonal difference in mass.

Conclusion

That caracaras’ daily activity and body mass did not vary between seasons suggests that wintering birds on Saunders are meeting resource requirements despite the absence of seasonally migratory prey. We hypothesize that human subsidies may mitigate the effect of seasonal food limitations. Further research should include studies on seasonal energetics to improve our understanding of baseline body condition, and comparative studies on other islands and including adults to understand the importance of human subsidies.

Background

Many predators face seasonal fluctuations in resource availability, due for instance to migratory prey [1], changes in prey vulnerability [2], or pulsed resources [3]. Life-history theory predicts that animals have adaptive strategies to cope with changes in prey availability [4, 5], such as migrating to more productive resource patches [6,7,8], prey-switching [9,10,11], or reducing metabolic needs [12, 13]. The introduction of human settlements to a landscape can disrupt naturally occurring spatial and temporal variation to which an animal is well-adapted [14], by suppressing natural food resources (e.g., hunting potential prey) or providing resources where historically there were none (hereafter “human subsidies”; i.e., subsidies sensu [15]).

While the effects of seasonal food availability have been investigated at the population level for several species [14, 16,17,18,19,20], less is known about the impact on individual life-history strategies [14], particularly during the juvenile stage when individuals are still behaviorally developing, learning judicious time–energy management, efficient foraging skills, and competitive strategies [21, 22]. Across many mammalian and bird species, juvenile mortality can be high [21, 23, 24], thus making it an important age class to study as impacts extend to population level effects. Here, we report on seasonal juvenile behavioral patterns of an endemic island predator in a system with fluctuating seabird prey and a relatively recent introduction of humans (i.e., since the mid-nineteenth century).

Striated caracaras (Phalcoboenus australis) are near-threatened falconids that inhabit the southern coasts of Patagonia and the outer Falkland Islands [25,26,27]. They are long-lived [Amy Wallace pers. comm] with extended periods of adolescence [28] and exhibit reverse sexual size dimorphism [KH unpubl. data]. During austral summer, caracaras primarily feed on eggs, chicks, and dead or dying adults of breeding colonial seabirds, the afterbirth, feces, and carrion of resident pinnipeds, and invertebrates including limpets and kelp fly larvae [17, 28,29,30]. During austral winter, when most seabirds migrate offshore, caracaras’ diets include native upland geese (Chloephaga picta), the feces and carrion of resident southern fur seals (Arctocephalus australis), southern sea lions (Mirounga leonina) and gentoo penguins (Pygoscelis papua), as well as beetles and subsidies provided by farms [17, 28, 31]. Since human occupation began in the Falklands in the mid-nineteenth century, many islands’ vegetation has changed dramatically due to farming [32], resident pinniped populations suffered a population decline from the sealing industry [33], and caracaras were persecuted to the point of near extinction [25, 34]. While the caracaras in the Falklands are now protected, a previous study posited that population recovery may be limited by winter food stress [31].

Animals must maintain a positive energy balance to survive [35] and partition their daily activities to do so; therefore, time–energy allocation and activity budgets provide valuable tools for assessing animals’ response to their environment [36]. Advancements in animal-borne datalogger technology now allow researchers to investigate fine-scale behavioral responses of wild animals [37,38,39]. Accelerometers, for example, record high-resolution three-dimensional movement, which can be used to calculate an index of activity, such as vectorial dynamic body acceleration (VeDBA, measured in gravitational g) [40, 41]. Furthermore, an animal’s time-activity budget can be estimated using a hidden Markov model (HMM) to decode behavioral state from acceleration [42, 43].

Our objective was to study juvenile caracaras’ activity levels in the presence and absence of seasonally migratory prey on Saunders Island, Falklands, which supports seven species of breeding seabirds during summer (hereafter the “seabird colonies site”) and has a farm settlement that provides human subsidies (e.g., animal feed, offal, and compost) year-round. To do this, we deployed animal-borne accelerometer and GPS dataloggers on 27 juvenile caracaras during summer and winter and investigated seasonal variation in body mass of the tagged subset and an additional 65 caracaras. If juvenile caracaras were food stressed and unable to forage optimally during winter, we predicted that caracaras would (1) have a higher daily activity index (i.e., 24-h average VeDBA); (2) engage in higher intensity daytime activity (i.e., average VeDBA during daylight); (3) range farther; and (4) have lower mass than during summer.

Results

Daily time–activity allocation

On a daily scale, caracaras were similarly active in winter and summer. We found no seasonal difference in the overall daily activity index (i.e., 24-h average VeDBA) for either sex. However, during winter, caracaras made the most of limited daylight by increasing their average daytime activity by 71% for males and 60% for females (winter males: 0.16 ± 0.03 g [n = 5], summer males: 0.09 ± 0.01 g [n = 5], winter females: 0.12 ± 0.02 g [n = 7], summer females: 0.08 ± 0.01 g [n = 7]; ANOVA, p < 0.001, t = 7.05). Furthermore, on a daily basis, males appear to be 21% more active than females year-round (24-h average VeDBA: males: 0.07 ± 0.01 g, females: 0.06 ± 0.01 g; ANOVA, p < 0.01, t = 3.35; Fig. 1). Tag version had a significant effect in both models; however, for the daily index (i.e., 24-h average VeDBA) tag version only accounted for an additional 13% of the variation (p = 0.039, t = 2.20), and for the daytime average VeDBA, tag version only accounted for an additional 6% of the variation (p < 0.05, t = 2.24).

Fig. 1
figure 1

Seasonal sex differences in 24-h average VeDBA per bird (n = 12 per season). VeDBA was binned by solar hour (i.e., 0–23) to show 24-h patterns in average VeDBA. Thin lines represent 1 day of data for individual males (solid) and females (dashed). Thick lines represent the mean average VeDBA for males (solid) and females (dashed). Gray shading denotes night (solar dusk to dawn). During daylight, winter VeDBA increased by 71% for males and 60% for females (Fig. 1a) in comparison to summer (Fig. 1b)

Full size image

Daily activity budgets

Hidden Markov models (HMMs) are dependent mixture models in which several distributions are used to account for an animal’s behavioral modes [42]. We found that a 4-state HMM fit the data best (Fig. 2a) while comprising clearly interpretable states: (1) rest (e.g., sleep or a similar motionless posture); (2) rest with noise (e.g., preening or daytime rest); (3) low activity (e.g., walking or raking); and (4) high activity (e.g., flight, running, or antagonistic behavior) (Fig. 2b). When coupled with the GPS data, resting states clustered at known roost sites and the highest activity seemingly occurred in flight (e.g., coming and going from the roost site).

Fig. 2
figure 2

Data-driven state-dependent distributions identified by fitting a joint hidden Markov model to VeDBA metrics (Fig. 2a), representative behaviors per state (Fig. 2b), and a sample 10-min time series of the state-labeled VeDBA values from a summer deployment (Fig. 2c)

Full size image

Using the state-labeled data, we found that during both seasons, over 90% of night was spent in resting states (i.e., states 1 and 2), even though winter nights were nearly two times longer (winter 13.2 h, summer = 7.2 h [mean]). Nearly all activity occurred during daylight hours (Fig. 1), thus we focused the remainder of our analysis only on daytime. Year-round, males spent a greater percentage of daylight hours in state 4 (i.e., high activity) than females (Fig. 3b); moreover, during winter, both sexes increased the percentage of daylight hours spent in state 4 (winter males: 35 ± 5%, summer males: 21 ± 3%, winter females: 25 ± 6%, summer females: 16 ± 3%; ANOVA, p < 0.001, t = 6.12; Fig. 3b). Similarly, we found that males spent a greater percentage of daylight hours in state 3 (i.e., low activity) year-round (males: 29% ± 5%, females: 24% ± 5%; ANOVA, p = 0.01, t = 2.75), though during winter both sexes increased the percentage of daylight hours spent in state 3 (winter males: 30 ± 5%, summer males: 28 ± 3%, winter females: 27 ± 6%, summer females: 21 ± 2%; ANOVA, p < 0.05, t = 2.25; Fig. 3b).

Fig. 3
figure 3

Boxplots show duration (Fig. 3a) and corresponding percentage (Fig. 3b) of daytime (i.e., solar dawn to solar dusk) spent in each activity state for summer (solid) and winter (dashed). Open circles (males) and triangles (females) reveal sex differences within corresponding boxplots. Year-round, males spent a greater proportion of daylight hours in states 3 and 4 than females. During winter, both sexes increased their proportion of time spent in states 3 and 4. Caracaras appear to spend the extra daylight of longer summer in resting states (Fig. 3a). Boxplot whiskers extend to the largest and smallest values (at most 1.5 * IQR [inter-quartile range])

Full size image

Daily space use

Caracaras ranges expanded significantly in winter. The winter daily range size (i.e., 95% kernel density estimate, KDE) was nearly 4 times larger than during summer (winter 2.36 ± 0.96 km2, summer 0.61 ± 0.20 km2; Wilcoxon rank sum test, p < 0.001), while their winter kernel core area of use (i.e., 50% KDE) increased by 58% (winter 0.19 ± 0.02 km2, summer 0.12 ± 0.04 km2; two-sample t test, p < 0.001; Fig. 4). For comparison, the mean 100% minimum convex polygon (MCP) for winter was an order of magnitude larger than during summer (winter: 10.8 ± 14.5 km2, summer: 0.45 ± 0.42 km2; Wilcoxon rank sum test, p < 0.01). During summer all tagged birds remained tightly clustered at the seabird colonies site (Fig. 4b), while in winter, caracaras were more loosely clustered at the farm settlement (Fig. 4a, lower right) and one bird traveled 16 km northwest to the seabird colonies site (blue points, Fig. 4b). Caracaras slept in social roosts at night during both seasons, though GPS tracks suggest interindividual variation in daytime space use.

Fig. 4
figure 4

Combined 24-h kernel home range (i.e., 95% KDE, white polygon) and core area of use (i.e., 50% KDE, black polygon) during winter (n = 5; Fig. 4a) and summer (n = 7; Fig. 4b) for all individuals with GPS units. The 100% MCP (gray outer polygon) is included for comparison. The gray rectangle on Fig. 4a represents the spatial extent of Fig. 4b inset, which is the seabird colonies site. The farm settlement is indicated on Fig. 4a. Colored points represent different individuals tracked for 24-h at 2-min sampling rates

Full size image

Seasonal mass

Contrary to our prediction, we found no statistically significant seasonal difference in juvenile caracaras’ mass, although there was a trend for both males and females to weigh less in winter (males summer: 1498 ± 169 g [n = 11], males winter: 1424 ± 104 g [n = 33]; females summer: 1772 ± 108 [n = 19], females winter: 1717 ± 121 g [n = 29]). Males weighed 17% less than females throughout the year (males: 1443 ± 125 g, n = 44, females: 1739 ± 118 g, n = 48; ANOVA, p < 0.05, F = 5.48).

Discussion

Juvenile striated caracaras on Saunders Island remain as active in winter as they are in summer, though they compress their activity into winter’s shorter daylight hours. These results suggest that during winter, juvenile caracaras on Saunders do not employ the energy-saving strategies that some species exhibit when faced with seasonal food scarcity [44,45,46,47]. Moreover, we found that male caracaras are more active than females in both seasons, a possible behavioral expression of the reverse sexual size dimorphism common in the Falconidae family [48, 49].

In the present study, not enough males wore GPS transmitters in winter to draw a statistically significant conclusion about differences in space use by sex. However, the one male sampled during winter traveled from the farm settlement to the seabird colonies, increasing his 95% KDE twofold over the ranges of females who remained at the settlement (male 95% KDE: 3.85 km2, female 95% KDE: 1.98 ± 0.54 km2 [n = 4]). On average, male caracaras in the Falklands weigh 200 g less than females, and as cost of transport scales positively with mass, we hypothesize their smaller size could facilitate their higher activity levels [50,51,52]. Since these are juvenile birds, they are not involved in breeding activity, so this cannot be due to nest provisioning. Notably, the seasonal daily ranges we measured were comparable to the multiday ranges reported in Harrington et al. (2018), which tracked 6 birds with GPS dataloggers over 5-20 days during December 2010 and 5 birds over 3-9 days during July–August 2012 and 2017.

That the caracaras’ daily activity and overall body mass did not vary between the seasons suggests that wintering birds on Saunders Island are meeting their resource requirements despite the absence of seasonally migratory seabird prey. We hypothesize that resources available at the nearby farm settlement may be mitigating the effect of seasonal food limitations.

However, juvenile caracaras appear to respond atypically to human subsidies. While human subsidies are available year-round at the Saunders settlement, juvenile caracaras only gather and roost at the farm settlement when resources associated with the breeding seabird colonies dwindle. For other species, predictable food resources have encouraged residency (e.g., [16, 53, 54]). Human subsidies have also encouraged corvids—scavenging predators that fill a similar ecological niche as the caracaras—and canids to reduce and shift their home ranges closer to subsidized resources [55, 56]. Caracaras on Saunders Island, on the other hand, have not become year-round residents at the settlement or reduced their home range to remain near the subsidies. Instead, they have increased winter ranges and leave the settlement as soon as their natural food supply increases (i.e., when the seabirds return to breed). This suggests that the human subsidies are less attractive to the birds than naturally available resources. Additionally, not all caracaras in the Falklands overwinter at farm settlements. For example, a 2012 austral winter survey counted 274 caracaras of all age classes on Steeple Jason Island, a nature preserve 80 km northwest of Saunders, where the caracaras were observed hunting terrestrial invertebrates, foraging in the intertidal and kelp wrack, and scavenging at gentoo colonies [57].

One limitation to our study was the use of two versions of our datalogger. While tag version was significant in modeling daily average VeDBA and daytime average VeDBA, when comparing R-squared values, we determined tag version did not explain an ecologically relevant proportion of the data. Biological factors explained 32% of the daily average VeDBA and 72% of the daytime average VeDBA, while tag version only explained an additional 13% and 6%, respectively. Additionally, when comparing between seasons measured by the same tag version, we achieved similar results. It is possible the effect was due to year and not tag version, though we were unable to include year and tag version in the same model because we did not use both tag versions in all years.

Conclusions

We used animal-borne dataloggers to better understand behavioral response to seasonal resource fluctuation. Combining GPS data with high-resolution accelerometry is especially useful for understanding activity states in an ecological context. In addition, HMMs provide a data-driven framework for evaluating unobserved activity states. While we did not find behavioral evidence of food stress, further research should include studies on seasonal energetics to improve our understanding of baseline body condition, and comparative studies of adult caracaras and islands without human subsidies. As many island-restricted species will likely face increased variation in resource availability in response to changing conditions including rising sea levels and human population expansion, we suggest that conservation managers consider seasonal activity budgets when developing species management plans.

Methods

Study area

This study was conducted on Saunders Island (51.37°S 60.09°W), a 127-km2 island in the northwest Falkland Islands archipelago that supports an estimated 50 to 100 caracaras year-round [31, KH unpubl. data]. During austral summer, the island supports over 25,000 breeding seabirds (see [17] for description) at the northwest end of the island. Following the breeding season, all seabirds at the colonies site—except the gentoos who roost near their breeding colonies throughout the year—migrate offshore. When this happens, caracaras vacate their summer roost and move 16 km SE to the 2.5-km2 farm settlement, where they overwinter at a roost adjacent to the settlement. The farm is owned and operated by a family of four and 2 co-workers who maintain approximately 6500 sheep, 200 dairy and beef cattle, approximately 400 cage-free chickens and ducks, and 22 farm dogs. Five sheep are processed each week for family use, and offal is left for the scavenging birds. The family also keeps two pigs in a small, open-air pigpen, which are fed two upland geese (Chloephaga picta) daily; many caracaras attend the feeding during winter and feed on scraps as available. The pig feeding, weekly sheep processing, and dogs’ bones appear to be the primary draw for the caracaras in winter [17]. The farmers have not observed caracaras predating the free-ranging farm animals at the settlement, although they have seen caracaras approach and pick at the nose and tails of recently birthed lambs [KH pers. comm.]. No seabirds roost or breed at the settlement.

Animal handling and instrumentation

From 2017 to 2019, we trapped 92 juvenile caracaras (Phalcoboenus australis, Gmelin 1788), 62 at the seabird colonies site during austral summer (December–February) and 30 at the farm site during austral winter (June–August). We targeted juvenile caracaras (i.e., second year birds, aged by plumage per [28]) to remove the effect of breeding on seasonal movement, activity levels, and mass. It was not possible to trap at both sites during the same season, because the birds seasonally migrate between the two sites [17]. Caracaras were trapped using a mutton-baited monofilament snare carpet that pulls tight around their metatarsus as the birds walk through the trap [58]. The trap is monitored continuously, and caracaras are removed immediately after snaring. All captured caracaras were weighed to the nearest 50 g using a hand-held scale and banded with colored alphanumeric plastic leg bands [17]. Approximately 50 μL of blood was collected from the brachial vein using a sterile 21 gauge hypodermic needle [59] and transferred immediately onto an 8-µm filter paper [60] for molecular sexing (modified protocol from [61]). Caracaras have distensible crops, thus we visually assessed crop size and categorized as not distended, partially distended, or distended, which allowed us to control for the added mass of food storage by restricting our mass analysis to birds that did not have distended crops. We observed no adverse effects of trapping and handling, with many individuals continuing to feed immediately upon release.

To 27 of those caracaras—13 at the seabird colonies site and 14 at the farm settlement—we attached custom-built Arduino-based archival dataloggers (TWLogger; [62]). We attached the loggers to the bird’s two central feathers using Tesa 4651 adhesive tape (Norderstedt, Germany) [63] (Fig. 5). The dataloggers were < 2% of birds’ body mass (1649.44 ± 177.08 g, mean ± SD [n = 27]); and we assumed that any unexpected behavioral effect of the dataloggers would be pervasive across our sample and thus not affect our comparative index. For all deployments, loggers recorded tri-axial acceleration (50-Hz sampling rate) data, which were used to calculate VeDBA and decode behavioral states. For 2018 and 2019 deployments, loggers also recorded GPS positions (2-min sampling rate), which were used to help validate behavioral state classifications and estimate utilization distributions and core areas of use. Prior to deployment, we spherically rotated all loggers to pass through all combinations of pitch and roll to record reference values to calibrate accelerometer data to account for inherent sensor variability (i.e., due to manufacturing) [64]. After deployment, all instrumented individuals resumed normal activity.

Fig. 5
figure 5

The TWLogger inertial movement datalogger with GPS prior to encapsulating in heat shrink for deployment (Fig. 5a), and a banded caracara wearing a tail-mounted TWLogger (Fig. 5b) while feeding on a gentoo penguin carcass at the seabird colonies site

Full size image

The present study occurred concurrently with TWLogger development, which was an iterative process. Tags deployed in 2017 (dimensions: L52 × W23 × H10 mm) used an inertial movement unit (IMU) that included a gyroscope in addition to accelerometer sensors and did not include a GPS module. Tags deployed in 2018 and 2019 were slightly larger (dimensions: L52 × W23 × H17 mm), included a GPS, and used a smaller IMU that omitted the gyroscope; this version consumed less power while maintaining similar accelerometer sensitivities. While the 2018/2019 tags weighed slightly more (2017: 20 g; 2018/2019: 25 g), both versions comprised a similar percentage of the average caracaras’ mass (2017: 1.2%; 2018/19: 1.5%).

To retrieve loggers, we recaptured birds using a mutton-baited single snare. Deployment durations ranged from 1.0 to 12.2 days (4.3 ± 3.6 days, mean ± SD), though logger battery durations ranged from 26 to 40 h. All but two loggers were recovered. Despite intensive efforts, we were unable to relocate one bird tagged during austral summer 2017 and another tagged during austral winter 2018. In both cases, the loggers would have been shed during their natural molt (Nov–Jan), if not before, preventing long-term consequences for the birds. Only one of 25 recovered loggers failed to record data.

Data processing

We obtained 24 complete datasets of tri-axial acceleration (winter n = 12, summer n = 12). Of these, 12 loggers also recorded GPS data (winter n = 5, summer n = 7). Each dataset represented one individual; thus, all observations were independent.

Prior to analysis, we processed acceleration data using purpose-written scripts in R (R v. 3.5.2). First, we used the spherical calibration function in the tagtools package [65] in R to calibrate the data using the reference values recorded prior to deployment. This allowed us to convert raw sensor values to acceleration in m s−2 while accounting for inherent sensor variability due to manufacturing effects. Next, we corrected any sampling rate variability, which accounted for less than 0.001% of the data. Because we were assessing hourly and daily scales and lower resolution acceleration data maintains high accuracy [66], we down sampled the data to 10-Hz to improve data processing speeds [67]. From the 2018 and 2019 deployments that included GPS units, we obtained 12 complete sets of tri-axial acceleration and GPS data. All GPS data were processed using an SDA filter (i.e., speed–distance–angle filter) [68] in R to remove aberrant positions, as environmental conditions may have affected accuracy of satellite fixes. GPS data were then rejoined to the dataset.

All dataloggers recorded data for greater than 24 h; although to ensure data were comparable on a daily scale and to minimize the effects of tag deployment, we clipped from the beginning of each dataset to make all files 24 h in length.

We classified each data point as day or night to assess diel patterning and standardize statistics such as daytime hourly VeDBA rates. We calculated solar periods (i.e., dawn, day, dusk, and night) using the maptools package in R [69] that performs sun ephemerides calculations using algorithms developed by the National Oceanic & Atmospheric Administration (NOAA). Solar dawn and dusk are defined as the time when the solar positioning is between 0 and 12 degrees below the horizon (nautical twilight). Night is defined as the time when the solar positioning is below 12 degrees on the horizon. For this analysis, “daytime” comprises dawn, day, and dusk periods. We calculated daytime length as the period between solar dawn and dusk and created 1-h solar time bins from zero to 23 beginning at solar midnight to facilitate seasonal comparisons.

VeDBA calculations

To calculate VeDBA (as described by [41]), we first calculated dynamic acceleration from each axis by subtracting static acceleration (i.e., smoothed acceleration over a 2-s window) from raw acceleration values. We then found the square root of the sum of squared dynamic acceleration of each axis. Using the 10-Hz VeDBA values, we calculated 24-h average VeDBA (i.e., daily activity index) and average daytime VeDBA per individual (i.e., VeDBA index subset to daylight hours and divided by day length). We reported VeDBA metrics in gravitational g.

State classifications

We used hidden Markov models (HMMs) to infer behavioral states from the 10-Hz acceleration data as they allow identification of relevant changes in behavioral intensity, i.e., activity versus rest, taking into account the serial dependence between observations [42, 70]. HMMs require an input metric that can be used to distinguish between movements that represent likely states. We selected VeDBA as our input metric [40, 42, 71]. Since VeDBA values are positive and continuous, we used gamma state-dependent distributions within the HMM.

For animal behavior data, formal model selection techniques tend to select more HMM states than seem biologically reasonable (i.e., additional states compensate for the inability to capture all the structure in such complex data); therefore, we first considered a simple (2-state) model and then built up complexity until a reasonable goodness-of-fit was achieved, but such that the model states were still biologically interpretable [72].

We used ecological knowledge (i.e., 675 h of observations over 3.5 years) and GPS positions to validate the model’s state classifications (e.g., known overnight roost sites where caracaras should be in a resting state). For daylight hours, we calculated absolute state durations (hours) and proportion of time spent in each state.

GPS calculations

We used the GPS data to calculate KDEs [73, 74] of the 95% home range and 50% core areas of use of all recorded locations for each individual bird (winter n = 5, summer n = 7) using the kernelUD and kernel.area functions in the adehabitatHR package in R [75]. To allow comparison between seasonal home ranges of different sizes, we used a fixed value smoothing parameter h (i.e., bandwidth) for each study area. To determine our smoothing parameters, we first subset the data by season and used the href method in the kernelUD function to calculate h per individual within a season. We then used the median h per season as our smoothing parameter [76]. For comparison, we also calculated 100% MCPs [77, 78] per bird using the mcp and mcp.area function from the adehabitatHR package.

Statistical analyses

We ran all statistical analyses in R (R v. 3.5.2). We tested for seasonal differences in 24-h average VeDBA, average daytime VeDBA, proportion of daylight hours spent in each behavioral state, and body mass using analyses of variance with season, sex, and device model as covariates. We selected the most parsimonious model to our data by comparing our initial model to subsequent models after removing non-significant fixed terms using likelihood-ratio tests. We report best model with tag version, but compare R-squared with and without tag version to understand importance. To compare KDEs and MCPs between seasons, we used two-sample t-tests and a Wilcoxon rank sum test, as our dataset contained only one year per treatment.

Funding

Support for this work was provided by Hawk Mountain Sanctuary Association, Falklands Conservation, the Falkland Islands Government Environmental Studies Budget, the Hawk Conservancy Trust, the Simpkins Family, and the National Geographic Society (awarded to B.M., grant #NGS-50069R-18).

Availability of data and materials

R scripts and TWLogger details are available on GitHub (http://github.com/Fahlbusch-Harrington/TWLogger). Raw data are available by email upon request to the corresponding author.

Abbreviations

GPS:

Global Position System

HMM:

Hidden Markov model

IMU:

Inertial movement unit

KDE:

Kernel density estimate

MCP:

Minimum convex polygon

VeDBA:

Vectorial dynamic body acceleration

References

  1. Elbroch LM, Lendrum PE, Newby J, Quigley H, Craighead D. Seasonal foraging ecology of non-migratory cougars in a system with migrating prey. PLoS ONE. 2013;8:e83375.

    PubMed  PubMed Central  Google Scholar 

  2. Metz MC, Smith DW, Vucetich JA, Stahler DR, Peterson RO. Seasonal patterns of predation for gray wolves in the multi-prey system of Yellowstone National Park. J Anim Ecol. 2012;81:553–63.

    PubMed  Google Scholar 

  3. Ostfeld RS, Keesing F. Pulsed resources and community dynamics of consumers in terrestrial ecosystems. Trends Ecol Evol. 2000;15:232–7.

    CAS  PubMed  Google Scholar 

  4. Roff DA. The evolution of life histories. New York: Chapman & Hall; 1992.

    Google Scholar 

  5. Stearns SC. The evolution of life histories. Oxford: Oxford University Press; 1992.

    Google Scholar 

  6. Alerstam T, Hedenström A, Åkesson S. Long-distance migration: evolution and determinants. Oikos. 2003;103:247–60.

    Google Scholar 

  7. Richter HV, Cumming GS. Food availability and annual migration of the straw-colored fruit bat (Eidolon helvum). J Zool. 2006;268:35–44.

    Google Scholar 

  8. Wysujack K, Greenberg LA, Bergman E, Olsson IC. The role of the environment in partial migration: food availability affects the adoption of a migratory tactic in brown trout Salmo trutta. Ecol Freshw Fish. 2009;18:52–9.

    Google Scholar 

  9. Bailey KM, Ainley DG. The dynamics of California sea lion predation on Pacific hake. Fish Res. 1981;1:163–76.

    Google Scholar 

  10. Harper GA. Numerical and functional response of feral cats (Felis catus) to variations in abundance of primary prey on Stewart Island (Rakiura). New Zealand Wildlife Res. 2005;32:597–604.

    Google Scholar 

  11. Sigler MF, Tollit DJ, Vollenweider JJ, Thedinga JF, Csepp DJ, Womble JN, Wong MA, Rehberg MJ, Trites AW. Steller sea lion foraging response to seasonal changes in prey availability. Mar Ecol Prog Ser. 2009;388:243–61.

    Google Scholar 

  12. Doucette LI, Brigham RM, Pavey CR, Geiser F. Prey availability affects daily torpor by free-ranging Australian owlet-nightjars (Aegotheles cristatus). Oecologia. 2012;169:361–72.

    PubMed  Google Scholar 

  13. Geiser F. Metabolic rate and body temperature reduction during hibernation and daily torpor. Annu Rev Physiol. 2004;66:239–74.

    CAS  PubMed  Google Scholar 

  14. Oro D, Genovart M, Tavecchia G, Fowler MS, Martínez-Abraín A. Ecological and evolutionary implications of food subsidies from humans. Ecol Lett. 2013;16:1501–14.

    PubMed  Google Scholar 

  15. Polis GA, Hurd SD. Linking marine and terrestrial food webs: allochthonous input from the ocean supports high secondary productivity on small islands and coastal land communities. Am Nat. 1996;147:396–423.

    Google Scholar 

  16. Gilbert NI, Correia RA, Silva JP, Pacheco C, Catry I, Atkinson PW, Gill JA, Franco AM. Are white storks addicted to junk food? Impacts of landfill use on the movement and behaviour of resident white storks (Ciconia ciconia) from a partially migratory population. Mov Ecol. 2016;4:7.

    PubMed  PubMed Central  Google Scholar 

  17. Harrington KJ, Pole-Evans S, Reeves M, Bechard M, Bobowski M, Barber DR, Rexer-Huber K, Lecomte N, Bildstein KL. Seasonal micro-migration in a farm-island population of striated caracaras (Phalcoboenus australis) in the Falkland Islands. Mov Ecol. 2018;6:4.

    PubMed  PubMed Central  Google Scholar 

  18. Donázar JA, Gangoso L, Forero MG, Juste J. Presence, richness and extinction of birds of prey in the Mediterranean and Macaronesian islands. J Biogeogr. 2005;32:1701–13.

    Google Scholar 

  19. Duhem C, Roche P, Vidal E, Tatoni T. Effects of anthropogenic food resources on yellow-legged gull colony size on Mediterranean islands. Popul Ecol. 2008;50:91–100.

    Google Scholar 

  20. Parra J, Tellería JL. The increase in the Spanish population of Griffon Vulture Gyps fulvus during 1989–1999: effects of food and nest site availability. Bird Conserv Int. 2004;14:33–41.

    Google Scholar 

  21. Wunderle JM. Age-specific foraging proficiency in birds. Curr Ornithol. 1991;8:273–324.

    Google Scholar 

  22. Greig SA, Coulson JC, Monaghan P. Age-related differences in foraging success in the Herring Gull (Larus argentatus). Anim Behav. 1983;31:1237–43.

    Google Scholar 

  23. Caughley G. Mortality patterns in mammals. Ecology. 1966;47:906–18.

    Google Scholar 

  24. Lack D. The natural regulation of animal numbers. The Natural Regulation of Animal Numbers. Oxford: Clarendon Press; 1954.

    Google Scholar 

  25. Woods RW, Woods A. Atlas of breeding birds of the Falkland Islands. Oswestry: Anthony Nelson; 1997.

    Google Scholar 

  26. Balza U, Lois NA, Raya Rey A. Status and reproductive outcome of the breeding population of Striated Caracaras (Phalcoboenus australis) at Franklin Bay, Staten Island, Argentina. Wilson J Ornithol. 2017;129:890–8.

    Google Scholar 

  27. Reeves M, Bildstein KL. Distribution and abundance of breeding striated caracaras in the Falkland Islands (Malvinas). J Raptor Res. 2018;52:309–16.

    Google Scholar 

  28. Strange IJ. The Striated Caracara Phalcoboenus australis in the Falkland Islands. Warrington: Philip Myers; 1996.

    Google Scholar 

  29. Harrington KJ, Bildstein KL. Predation of Southern Red Octopus (Enteroctopus megalocyathus) by Striated Caracaras (Phalcoboenus australis) in the Falkland Islands. J Raptor Res. 2019;53:220–2.

    Google Scholar 

  30. Catry P, Lecoq M, Strange IJ. Population growth and density, diet and breeding success of striated caracaras Phalcoboenus australis on New Island, Falkland Islands. Polar Biol. 2008;31:1167–74.

    Google Scholar 

  31. Rexer-Huber K, Bildstein KL. Winter diet of Striated Caracara Phalcoboenus australis (Aves, Polyborinae) at a farm settlement on the Falkland Islands. Polar Biol. 2013;36:437–43.

    Google Scholar 

  32. Tourangeau W, Sherren K, Delignières M. ‘We secured the tussac’: accounts of ecological discovery, exploitation and renewal in the Falkland Islands. People Nat. 2019;1:548–61.

    Google Scholar 

  33. Baylis AM, Orben RA, Arnould JP, Christiansen F, Hays GC, Staniland IJ. Disentangling the cause of a catastrophic population decline in a large marine mammal. Ecology. 2015;96:2834–47.

    PubMed  Google Scholar 

  34. Cawkell EM, Hamilton JE. The birds of the Falkland Islands. Ibis. 1961;103:1–27.

    Google Scholar 

  35. Brown JH, Gillooly JF, Allen AP, Savage VM, West GB. Toward a metabolic theory of ecology. Ecology. 2004;85:1771–89.

    Google Scholar 

  36. Christiansen F, Rasmussen MH, Lusseau D. Inferring activity budgets in wild animals to estimate the consequences of disturbances. Behav Ecol. 2013;24:1415–25.

    Google Scholar 

  37. Brown DD, Kays R, Wikelski M, Wilson R, Klimley AP. Observing the unwatchable through acceleration logging of animal behavior. Animal Biotelemetry. 2013;1:20.

    Google Scholar 

  38. Nathan R, Spiegel O, Fortmann-Roe S, Harel R, Wikelski M, Getz WM. Using tri-axial acceleration data to identify behavioral modes of free-ranging animals: general concepts and tools illustrated for griffon vultures. J Exp Biol. 2012;215:986–96.

    PubMed  PubMed Central  Google Scholar 

  39. Shepard EL, Wilson RP, Quintana F, Laich AG, Liebsch N, Albareda DA, Halsey LG, Gleiss A, Morgan DT, Myers AE, Newman C. Identification of animal movement patterns using tri-axial accelerometry. Endanger Species Res. 2008;10:47–60.

    Google Scholar 

  40. Qasem L, Cardew A, Wilson A, Griffiths I, Halsey LG, Shepard EL, Gleiss AC, Wilson R. Tri-axial dynamic acceleration as a proxy for animal energy expenditure; should we be summing values or calculating the vector. PloS ONE. 2012;7:e31187.

    CAS  PubMed  PubMed Central  Google Scholar 

  41. Bidder OR, Qasem LA, Wilson RP. On higher ground: how well can dynamic body acceleration determine speed in variable terrain. PloS ONE. 2012;7:e50556.

    CAS  PubMed  PubMed Central  Google Scholar 

  42. Leos-Barajas V, Photopoulou T, Langrock R, Patterson TA, Watanabe YY, Murgatroyd M, Papastamatiou YP. Analysis of animal accelerometer data using hidden Markov models. Methods Ecol Evol. 2017;8:161–73.

    Google Scholar 

  43. Papastamatiou YP, Watanabe YY, Demšar U, Leos-Barajas V, Bradley D, Langrock R, Weng K, Lowe CG, Friedlander AM, Caselle JE. Activity seascapes highlight central place foraging strategies in marine predators that never stop swimming. Mov Ecol. 2018;6:9.

    PubMed  PubMed Central  Google Scholar 

  44. Giroud S, Blanc S, Aujard F, Bertrand F, Gilbert C, Perret M. Chronic food shortage and seasonal modulations of daily torpor and locomotor activity in the grey mouse lemur (Microcebus murinus). Am J Physiol Regul Integr Comp Physiol. 2008;294:1958–67.

    Google Scholar 

  45. Vuarin P, Dammhahn M, Kappeler PM, Henry PY. When to initiate torpor use? Food availability times the transition to winter phenotype in a tropical heterotherm. Oecologia. 2015;179:43–53.

    PubMed  Google Scholar 

  46. Cuyler LC, Øritsland NA. Metabolic strategies for winter survival by Svalbard reindeer. Can J Zool. 1993;71:1787–92.

    Google Scholar 

  47. Riek A, Brinkmann L, Gauly M, Perica J, Ruf T, Arnold W, Hambly C, Speakman JR, Gerken M. Seasonal changes in energy expenditure, body temperature and activity patterns in llamas (Lama glama). Sci Rep. 2017;7:7600.

    PubMed  PubMed Central  Google Scholar 

  48. Bechard MJ, Sarasola JH, Helbig AJ. Morphometric Measures of male and female Spot-winged Falconets Spiziapteryx circumcinctus sexed using PCR Amplification Methods. In: Chancellor RD, Meyburg BU, editors. Raptors Worldwide. World Working Group on Birds of Prey and Owls & MME/BirdLife Hungary, Budapest; 2004.

  49. Newton I. Population ecology of raptors. London: A&C Black; 2010.

    Google Scholar 

  50. Goldstein DL. Estimates of daily energy expenditure in birds: the time-energy budget as an integrator of laboratory and field studies. Am Zool. 1988;28:829–44.

    Google Scholar 

  51. Pennycuick CJ. Mechanics of flight. In: Farner DS, King JR, editors. Avian Biology, vol. 5. New York: Academic Press; 1975. p. 1–75.

    Google Scholar 

  52. Krüger O. The evolution of reversed sexual size dimorphism in hawks, falcons and owls: a comparative study. Evol Ecol. 2005;19:467–86.

    Google Scholar 

  53. Plummer KE, Siriwardena GM, Conway GJ, Risely K, Toms MP. Is supplementary feeding in gardens a driver of evolutionary change in a migratory bird species? Glob Chang Biol. 2015;21:4353–63.

    PubMed  Google Scholar 

  54. Baskin Y. Trumpeter swans relearn migration. Bioscience. 1993;43:76–9.

    Google Scholar 

  55. Kristan WB III, Boarman WI. Effects of anthropogenic developments on common raven nesting biology in the west Mojave Desert. Ecol Appl. 2007;17:1703–13.

    PubMed  Google Scholar 

  56. Marzluff JM, Neatherlin E. Corvid response to human settlements and campgrounds: causes, consequences, and challenges for conservation. Biol Conserv. 2006;130:301–14.

    Google Scholar 

  57. Woods RW, Meiburg JA, Galloway D. Striated Caracaras Phalcoboenus australis on Steeple Jason, Falkland Islands: winter population, diet, feeding behaviour and potential problems of mouse eradication August–September 2012. Falkland Islands: Falklands Conservation survey report to F.I. Government. Stanley; 2012.

    Google Scholar 

  58. Collister A. Simple noose trap. Western Bird Bander. 1967;42.

  59. Owen JC. Collecting, processing, and storing avian blood: a review. J Field Ornithol. 2011;82:339–54.

    Google Scholar 

  60. Smith LM, Burgoyne LA. Collecting, archiving and processing DNA from wildlife samples using FTA® databasing paper. BMC Ecol. 2004;4:4.

    CAS  PubMed  PubMed Central  Google Scholar 

  61. Griffiths R, Double M, Orr K, Dawson R. A DNA test to sex most birds. Mol Ecol. 1998;7:1071–6.

    CAS  PubMed  Google Scholar 

  62. Fahlbusch JA, Harrington KJ. A low-cost, open-source inertial movement GPS logger for eco-physiology applications. J Exp Biol. 2019;222.

  63. Wilson RP, Pütz K, Peters G, Culik B, Scolaro JA, Charrassin JB, RopertCoudert Y. Long-term attachment of transmitting and recording devices to penguins and other seabirds. Wildl Soc Bull (1973-2006). 1997;25:101–6.

    Google Scholar 

  64. Wilson RP, White CR, Quintana F, Halsey LG, Liebsch N, Martin GR, Butler PJ. Moving towards acceleration for estimates of activity-specific metabolic rate in free-living animals: the case of the cormorant. J Anim Ecol. 2006;75:1081–90.

    PubMed  Google Scholar 

  65. DeRuiter S. tagtools: Tools for Working with Data from High-Resolution Biologging Tags. R package version R 3.4.3. 2018. http://www.animaltags.org/doku.php.

  66. Ladds MA, Salton M, Hocking DP, McIntosh RR, Thompson AP, Slip DJ, Harcourt RG. Using accelerometers to develop time-energy budgets of wild fur seals from captive surrogates. PeerJ. 2018;6:e5814.

    PubMed  PubMed Central  Google Scholar 

  67. Halsey LG, Green JA, Wilson RP, Frappell PB. Accelerometry to estimate energy expenditure during activity: best practice with data loggers. Physiol Biochem Zool. 2009;82:396–404.

    CAS  PubMed  Google Scholar 

  68. Freitas C, Lydersen C, Ims RA, Fedak MA, Kovacs KM. A simple new algorithm to filter marine mammal Argos locations. Marine Mammal Sci. 2008;24:315–25.

    Google Scholar 

  69. Bivand R, Lewin-Koh N. maptools: tools for reading and handling spatial objects. R package version 0.8-39. 2016. https://CRAN.R-project.org/package=maptools.

  70. Patterson A, Gilchrist HG, Chivers L, Hatch S, Elliott K. A comparison of techniques for classifying behavior from accelerometers for two species of seabird. Ecol Evol. 2019;9:3030–45.

    PubMed  PubMed Central  Google Scholar 

  71. Beltramino LE, Venerus LA, Trobbiani GA, Wilson RP, Ciancio JE. Activity budgets for the sedentary Argentine sea bass Acanthistius patachonicus inferred from accelerometer data loggers. Austral Ecol. 2019;44:397–408.

    Google Scholar 

  72. Pohle J, Langrock R, van Beest FM, Schmidt NM. Selecting the number of states in hidden Markov models: pragmatic solutions illustrated using animal movement. J Agric Biol Environ Stat. 2017;22:270–93.

    Google Scholar 

  73. Worton BJ. Kernel methods for estimating the utilization distribution in home-range studies. Ecol. 1989;70:164–8.

    Google Scholar 

  74. Worton BJ. Using Monte Carlo simulation to evaluate kernel-based home range estimators. J Wildl Manage. 1995;794-800.

  75. Calenge C. The package “adehabitat” for the R software: a tool for the analysis of space and habitat use by animals. Ecol Modell. 2006;197:516–9.

    Google Scholar 

  76. Peris A, Closa F, Marco I, Acevedo P, Barasona JA, Casas-Díaz E. Towards the comparison of home range estimators obtained from contrasting tracking regimes: the wild boar as a case study. Eur J Wildl Res. 2020;66:1–10.

    Google Scholar 

  77. Odum EP, Kuenzler EJ. Measurement of territory and home range size in birds. Auk. 1955;72:128–37.

    Google Scholar 

  78. Nilsen EB, Pedersen S, Linnell JD. Can minimum convex polygon home ranges be used to draw biologically meaningful conclusions? Ecol Res. 2008;23:635–9.

    Google Scholar 

Download references

Acknowledgements

We thank Hawk Mountain Sanctuary Association and Falklands Conservation for providing field support for this study. We thank the Falkland Islands Government Environmental Planning Department for providing our permit and the Pole-Evans family for being gracious hosts during our stays on Saunders Island. We thank Keith Bildstein for initiating Hawk Mountain Sanctuary’s longitudinal study of Striated Caracaras in the Falklands. We are also deeply appreciative of the time and energy contributed by Max Czapanskiy, Dave Cade, Jonathan Meiburg, Isabeau Pratt, Polly Harrington and Scott Hamilton toward improving this manuscript. This is Hawk Mountain Contribution to Conservation Science No. 330.

Author information

Authors and Affiliations

  1. Acopian Center for Conservation Learning, Hawk Mountain Sanctuary, Orwigsburg, PA, USA

    Katie J. Harrington & Jean-François Therrien

  2. Moss Landing Marine Laboratories, California State University, Moss Landing, CA, USA

    Katie J. Harrington & Birgitte I. McDonald

  3. Hopkins Marine Station, Stanford University, Pacific Grove, CA, USA

    James A. Fahlbusch

  4. Department of Business Administration and Economics, Bielefeld University, Bielefeld, Germany

    Roland Langrock

  5. Department of Ecology and Evolutionary Biology, Cornell University, Ithaca, NY, USA

    Jennifer L. Houtz

Authors
  1. Katie J. Harrington
    View author publications

    You can also search for this author in PubMed Google Scholar

  2. James A. Fahlbusch
    View author publications

    You can also search for this author in PubMed Google Scholar

  3. Roland Langrock
    View author publications

    You can also search for this author in PubMed Google Scholar

  4. Jean-François Therrien
    View author publications

    You can also search for this author in PubMed Google Scholar

  5. Jennifer L. Houtz
    View author publications

    You can also search for this author in PubMed Google Scholar

  6. Birgitte I. McDonald
    View author publications

    You can also search for this author in PubMed Google Scholar

Contributions

KH, JF, and BM conceptualized this study. KH and JF designed the dataloggers used in this study. KH conducted fieldwork. JH analyzed genetic data. KH, JF, RL and BM analyzed accelerometry data. KH wrote and prepared the original manuscript. KH, JF, RL, JFT, JH and BM reviewed and edited the manuscript. KH administered the project. KH obtained project funding. All authors read and approved the final manuscript.

Corresponding author

Correspondence to Katie J. Harrington.

Ethics declarations

Ethics approval and consent to participate

Caracara capture, handling, and instrumentation methods were conducted under Institutional Animal Care and Use Committee protocol (#1054) and complied with the conservation of Wildlife and Nature Ordinance of 1999, Section 9, License to carry out Scientific Research permit (#R22/2015, Falkland Islands Government).

Consent for publication

All authors agree consent to publish this work to Animal Biotelemetry.

Competing interests

The authors declare no competing or financial interests.

Additional information

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Harrington, K.J., Fahlbusch, J.A., Langrock, R. et al. Seasonal activity levels of a farm-island population of striated caracaras (Phalcoboenus australis) in the Falkland Islands. Anim Biotelemetry 8, 27 (2020). https://doi.org/10.1186/s40317-020-00214-y

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI: https://doi.org/10.1186/s40317-020-00214-y

Keywords

Animal Biotelemetry

ISSN: 2050-3385