- Research article
- Open Access
Resource partitioning between incubating and chick-rearing brown boobies and red-tailed tropicbirds on Christmas Island
© Navarro et al.; licensee Springer. 2014
- Received: 20 February 2014
- Accepted: 19 May 2014
- Published: 4 June 2014
In oligotrophic tropical marine environments, the main mechanism explaining the coexistence of sympatric seabirds is segregation by habitat or segregation by prey within the same habitat. Both types of segregation can play a role during the breeding season due to different constraints associated with different phases of the breeding cycle. By using stable isotope analyses, we investigated intra- and interspecific foraging segregation in two tropical seabird species, the red-tailed tropicbird Phaeton rubricauda and the brown booby Sula leucogaster, breeding sympatrically on Christmas Island, Indian Ocean. We compared isotopic values of δ13C and δ15N in blood from incubating and chick-rearing adults of both species.
The results showed small but significantly interspecific and intraspecific differences in δ13C and δ15N values. Differences in δ13C values suggest spatial segregation in the main foraging grounds between the two species during the breeding season as well as between incubating and chick-rearing brown boobies. In contrast, red-tailed tropicbirds probably exploited similar foraging habitats during both breeding stages. δ15N values did not indicate diet-related differences, neither within nor between species, suggesting a highly opportunistic feeding behavior to cope with the limited prey available in the oligotrophic marine environment.
Competition for prey in breeding red-tailed tropicbirds and brown boobies seems to be reduced by spatial segregation enabling both species to successfully reproduce in sympatry in an oligotrophic tropical marine environment.
- Feeding segregation
- Stable isotope analysis
- Tropical ecosystems
Tropical marine ecosystems are characterized by low productivity in comparison with non-tropical systems (Miller ). These oligotrophic ecosystems can only sustain relatively low densities of top marine predators such as seabirds, which mainly feed upon a few groups of prey species, generally flying fish (Exocoetidae) and squids (Ommastrephidae) (Ashmole and Ashmole ; Longhurst and Pauly ). Consequently, tropical seabirds must adapt their foraging behavior to mitigate potential competition for the limited food resources within their foraging areas (Spear et al. ; Cherel et al. ). The main mechanisms currently explaining the coexistence of sympatric tropical seabirds are segregation by feeding habitat or segregation by prey selection within the same habitat (Diamond ; Harrison et al. ; Cherel et al. ; Young et al. ). Both types of segregation can play a role over the course of the breeding season due to different constraints associated with different phases of the breeding cycle, e.g., incubation vs. chick rearing (Ashmole and Ashmole ; Cherel et al. ). So far, most studies on resource partitioning have been conducted in marine habitats of polar and temperate waters (Phillips et al. ; Forero et al. ; Masello et al. ; Navarro et al. ) and little is known about how sympatric seabirds of tropical waters reduce inter- and intraspecific competition for prey resources or whether the types of segregation shift over the course of the breeding season (Catry et al.; Cherel et al. ).
Recent analytical developments have provided useful tools to study feeding and foraging ecology in marine predators. In particular, the analysis of stable isotopes has been shown to be an effective technique to investigate the trophic structure of marine food webs and resource allocation of sympatric seabirds (Cherel et al. , Kojadinovic et al. ; Moreno et al. ). The principle underlying this approach is that stable isotope ratios of nitrogen (δ15N) and carbon (δ13C) in predators reflect those of their prey species in a predictable manner (Karnovsky et al. ). δ15N values show a stepwise enrichment between 3‰ to 5‰ with each trophic level and are reliable indicators of the consumer's trophic position (Inger and Bearhop ). δ13C values indicate consumer foraging areas discriminating between inshore/benthic and offshore/pelagic feeding (Forero and Hobson ; Inger and Bearhop ).
Fieldwork procedures and study species
The study was conducted on Christmas Island (Figure 1, 105° 40′ E; 10° 30′ S), a small (135 km2) tropical Australian island in the north-eastern Indian Ocean, 360 km south of Java, Indonesia. Red-tailed tropicbirds and brown boobies breed in sympatry on Christmas Island with seven other seabird species (Nelson ; Stokes ). Approximately 1,400 pairs of red-tailed tropicbirds and 6,000 pairs of brown boobies nest on the coastal terraces and limestone cliffs of this island (Stokes ). Egg-laying of both species occurs year-round peaking from June to October (Stokes ).
During the breeding period of 2007 (September to October), we collected 0.5 ml of blood from incubating and chick-rearing adults of both species. In red-tailed tropicbirds, we sampled 19 incubating birds (10 males and 9 females) and 21 chick-rearing adults (10 males and 11 females). In brown boobies, we sampled 19 incubating birds (10 males and 9 females) and 73 chick-rearing adults (37 males and 36 females). All individuals were sampled only once, either during incubation or during chick rearing. Blood was taken from the brachial vein using a 0.5-ml insulin syringe and preserved in 70% ethanol. Blood extraction is a method commonly used in bird studies that apparently have not negative effect on foraging behavior and survival (Angelier et al. ). All birds were caught at their nests using a 1-m-long noose pole and were individually color-marked on the head or breast with a green or blue sheep crayon to avoid sampling the same individual twice. The sex of brown boobies was determined by their sexual dimorphism (Nelson ), whereas red-tailed tropicbirds were sexed using molecular W chromosome-linked markers (Ellegren ).
Stable isotope analyses
Mean and SD of δ 15 N and δ 13 C values and range (minimum and maximum) C/N ratio in blood
0.29 to 0.32
0.31 to 0.32
0.29 to 0.32
0.30 to 0.33
0.31 to 0.32
0.31 to 0.34
0.30 to 0.32
0.30 to 0.32
0.31 to 0.32
0.29 to 0.32
0.31 to 0.32
0.29 to 0.31
These are from male and female brown boobies (BRBO) and red-tailed tropicbirds (RTTB) during the incubation and chick rearing period on Christmas Island, Indian Ocean. The mean values for each species during both breeding stages are indicated in italics.
Statistical analyses were conducted using IBM SPSS 21.0 (IBM SPSS). Prior to statistical tests, data were checked for normality and heteroscedasticity. ANOVA tests incorporating species, breeding stage (incubation and chick rearing) and sex were used to test for interspecific and intraspecific differences in δ15N and δ13C values. As neither sex nor the interaction of sex and breeding stage had significant effects on isotopic values, data from both sexes were pooled. Since stable isotope values differed between species, Student's t tests were used to compare the isotopic values for each species separately to determine differences between breeding stages. All tests were two-tailed and the threshold for significance was p < 0.05.
Isotopic comparison between species
Isotopic comparison between incubation and chick-rearing periods
At intraspecific level, we found that incubating brown boobies showed lower δ15N and higher δ13C values than chick-rearing brown boobies (Figure 2; Table 1; δ15N: t = 2.91, df = 90, p = 0.004; δ13C: t = −3.23, df = 90, p = 0.002; absolute differences; δ15N = 0.14‰, δ13C = 0.17‰). In contrast, red-tailed tropicbirds did not differ in δ15N and δ13C values between incubating and chick-rearing adults (Figure 2; Table 1; δ14N: t = 0.66, df = 38, p = 0.51; δ13C: t = 1.18, df = 38, p = 0.24).
The present study revealed both interspecific and intraspecific differences in δ13C and δ15N values. Even though absolute differences in the δ13C values between species as well as between incubating and chick-rearing brown boobies were small (<0.3‰), the isotopic results are supported by the available information about the foraging behavior of the two species and the energetic requirements during breeding. Given the evidence of a decreasing inshore-offshore δ13C gradient described for marine ecosystems (Hobson et al. ; Forero and Hobson ), the differences in δ13C values between the two study species and between incubating and chick-rearing brown boobies suggest the utilization of different foraging areas. In particular, the lower δ13C values of red-tailed tropicbirds suggest that they forage further offshore during both breeding stages than incubating brown boobies (higher δ13C values), which seem to use more inshore/coastal foraging areas. During incubation, brown boobies usually make relatively short foraging trips of only several hours and thus feed in areas close to their breeding sites (Nelson ; Dunlop et al. ; Lewis et al. ). In contrast, red-tailed tropicbirds perform long foraging trips, up to several days, to feed in waters far from their breeding colonies (Dunlop et al. ; Le Corre et al. ; Sommerfeld and Hennicke ). The intraspecific differences in δ13C values found between incubating and chick-rearing brown boobies suggest a shift in foraging habitat towards more distant foraging areas during chick rearing. Potentially, this is a consequence of different energetic demands during the two breeding stages. Brown boobies reproduce year-round (Nelson ; Stokes ) and hence incubating and chick-rearing adults are in demand of food at the same time. Since chick-rearing adults must find food not only for themselves but also for their chicks, i.e., they have higher energetic demands, they should try to reduce direct competition for food with conspecifics, e.g., by foraging in more distant waters (Ashmole and Ashmole ; Ashmole ; Birt et al. ). Alternatively, they could switch foraging areas to obtain prey of higher energetic value as it has been found in other seabirds (Ricklefs ; Shaffer et al. ; Navarro et al. ).
The fact that the absolute differences in δ13C values between the species and between incubating and chick-rearing boobies were relatively small may be explained by the fact that, despite spatial segregation in foraging habitat, there is still overlap in foraging areas as the opportunistically foraging birds (see below) will also take prey close to the island on their way to and from their more distant foraging areas. Moreover, the actual differences in distance between the different foraging areas might be small relative to the mobility of the prey and the relatively weak δ13C gradient in tropical waters (Catry et al. [2008, 2009]; Cherel et al. ). Thus, while the isotopic methods used in the present study suggest spatial segregation, further investigations using tracking devices would be helpful to quantify the habitat segregation/overlap between the species and breeding stages.
In the case of red-tailed tropicbirds, no significant differences in δ13C values were found between incubating and chick-rearing adults, indicating an overlap in the habitat used during both breeding periods. This can be attributed to the fact that in this species competition between incubating and chick-rearing congeners is always relatively low due to their off-shore foraging behavior (see above) and their small population size on Christmas Island (1,400 breeding pairs; Stokes ). Thus, shifts in foraging areas between breeding stages seems unlikely to result in substantially less competition and hence foraging even further away from Christmas Island seems to be unnecessary for chick-rearing red-tailed tropicbirds.
Differences in δ15N values generally reflect the exploitation of resources of different trophic levels by the consumers (e.g., Hobson et al. ; Inger and Bearhop ; Moreno et al. ). We found significant differences in δ15N values between the two species and between incubating and chick-rearing brown boobies. However, differences in δ15N between two consumers that segregate their diet, i.e. exploit prey of different trophic levels, are usually associated with δ15N values differing by 3‰ to 4‰ (Post ). In our case, the differences were about one magnitude lower and generally less than 0.4‰. Thus, while statistically significant, the differences in δ15N values are not biologically relevant and suggest that the two species, as well as incubating and chick-rearing brown boobies, exploit similar resources. The observed differences in the δ15N values can most likely be attributed to the influence of protein catabolism related to differences in foraging effort (Hobson et al. ; Cherel et al. ; Navarro et al. ), i.e., higher effort of off-shore foraging red-tailed tropicbirds vs. in-shore foraging brown boobies and of chick-provisioning vs. incubating brown boobies.
Thus, given the limited and homogenously distributed prey availability in their tropical marine foraging habitat, brown boobies and red-tailed tropicbirds seem to have a strong overlap in their diet during the breeding season and opportunistically exploit whatever prey is available, most likely flying fish and squid, the main and most abundant prey of tropical seabirds (e.g., Ashmole and Ashmole ; Ballance and Pitman ; Catry et al.). The resulting competition for prey is likely to be reduced by spatial segregation in foraging habitat, facilitating successful reproduction in sympatry in a tropical marine environment with unfavorable prey availability. Additional studies using tracking devices and examining isotopic references of the trophic resources of the species would help to further elucidate ecological mechanisms explaining the coexistence of red-tailed tropicbirds and brown boobies on Christmas Island.
The study was conducted within the framework of the Christmas Island Seabird Project (www.seabirdproject.cx), which was supported by the University of Hamburg Research Fund, Christmas Island Tourist Association, Island Explorer Holidays, CI Territory Week Committee, and CI Island Care. We thank Xavier Ruiz for their scientific support to this project. Funding for the analysis was provided by project SGR 2009 963 (Generalitat de Catalunya). Fieldwork was carried out under permission of Parks Australia North Christmas Island and Darwin and was approved by the Animal Ethics Committee of Charles Darwin University, Darwin, Australia. We thank Parks Australia North Christmas Island for their support in all aspects of the study and to M. van der Stap for her help in the field.
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