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Reproductive effort and foraging energetics in Adélie penguins MARK A. CHAPPELL, VAUGHAN H. SHOEMAKER, and DONALD N. JANES Biology Department University of California Riverside, California 92521 SHANE K. MALONEY School of Biological Sciences The University of New South Wales Kensington, New South Wales 2033 Australia We are examining the energetics, behavior, and foraging ac- tivities of Adélie penguins (Pygoscelis adeliae) at a rookery near Palmer Station. Our project concerns reproductive effort in males and females in species with monogamous breeding sys- tems and extensive parental care by both sexes. Adélies are good subjects for these studies because of their abundance, tameness, and accessibility. Reproductive effort is the investment of energy and materials a parent allocates to reproduction, as opposed to growth and maintenance. As such, it includes energy expenditures for courtship, incubation, and foraging to provide food for chicks, and the energy equivalence of eggs and of the overall mass change of the adults during the breeding season (because of extensive fasting, Adélie parents often lose 20 percent or more of their initial mass). Measurements of reproductive effort pro- vide important insights into the cost of reproduction—that is, the theoretically predicted decrease in future reproductive suc- cess caused by reproductive effort during a given breeding event. It is generally assumed that reproductive effort and cost of reproduction are correlated—if reproductive effort in a given breeding season is high, then the impact on future breeding success should also be high. Additionally, reproductive-effort data can be used to calculate the food resources adult penguins require for reproduction at different stages of the breeding cycle, and (together with information on the rate of food con- sumption by chicks) the total energy flux through a penguin colony. A major problem in studying reproductive effort is separating the energy allocated to reproduction from the rest of the par- ent's energy budget. In our study, we are using a combination of behavioral observations, isotopic measurements of body composition (ratio of lean to fatty tissue) and of field metabolic rates, and time-depth recorder data on foraging behavior to assess reproductive effort at various stages of the breeding cycle. Results from these methods will be analyzed along with data from previous metabolic and behavioral studies (e.g., Trivelpiece, Trivelpiece, and Volkman 1987; Chappell et al. 1989; Chappell, Morgan, and Bucher 1990) to provide quantitative estimates of reproductive effort. During the first field season (October 1990 through February 1991), we banded several hundred adults during the initial courtship phase and followed the progress of banded pairs throughout the breeding season. These studies provided back- ground data on incubation and foraging schedules, hatch dates, and chick growth rates. Body composition, field meta- bolic rates, and time-depth recorder studies were performed on well-known individuals at standardized times in the breed- ing cycle. Adélies began arriving in colonies in early October and most breeding adults were present by the end of the month. The first eggs appeared on 7 November, with the peak of egg-laying around 14-20 November. Hatching began on 9 December. The first fledgling occurred approximately 1 February 1991, and most chicks had departed to sea by 28 February. Censusing indicated that the 2,800 breeding pairs in the colonies we stud- ied produced approximately 5,600 eggs and 2,900 fledglings, for an egg-to-fledgling survival rate of about 52 percent. Most of this mortality occurred during incubation and the early stages of chick rearing as a result of nest flooding and predation by brown skuas. We also observed intense predation on adult penguins by leopard seals. Approximately 12.5 percent of banded adults disappeared during the season. We made 71 measurements of field metabolic rate. These were divided approximately evenly among males and females and among four stages of the breeding season (courtship, in- cubation, care of uncreched chicks, and care of creched chicks). We obtained an additional 20 measurements of body composi- tion. Behavioral observations and daily nest inspections indicated that cumulative incubation times were longer for males than for females, but the sexes shared chick feeding duties approx- imately equally, as reported previously (Ainley LeResche, and Sladen 1983; Trivelpiece et al. 1987). Proportional mass losses over the season were roughly equivalent in both sexes. These data suggest approximate equivalence in reproductive effort among males and females (as theory would predict for monog- amous breeders). These indirect estimates will be refined when field metabolic rates and body composition data have been ana- lyzed. We obtained time-depth recorder data from 27 birds during the chick-feeding stages. (An additional two failed to return from foraging; presumably they were killed by leopard seals). The sample population spent about 35-40 percent of the total period of time-depth recorder deployment in the water, even during the period when they were feeding creched chicks. These data contrast with other reports (Ainley et al. 1983; Trivelpiece et al. 1987) which indicate that parents of creched chicks spend more than 90 percent of their time at sea. We recorded about 8,400 dives deeper than 4 meters during roughly 430 hours of swimming. Of these dives, some 5,900 were assumed to be feeding dives (long duration, deep, usually with a substantial period spent at maximum depth) and the remainder were assumed to be traveling dives (short duration, shallow). Preliminary analysis of diving behavior did not reveal significant differences between males and females. Adélies at Palmer foraged throughout the day, but most frequently during the midday period (0800-1700 local time). The maximum re- corded depth was 87 meters. Most foraging dives were to 15- 50 meters, with a mean depth of about 26 meters (figure 1). The deepest depths were attained primarily during the daylight hours. Diving appeared to be aerobic, with a maximum ob- served submergence time of 2.7 minutes and a mean of about 1-1.2 minutes during foraging dives. Not surprisingly, there was a strong positive correlation between maximum dive depth and dive duration (figure 2). Surface intervals between dives were weakly correlated to dive duration. While foraging, Adé- 180 ANTARCTIC JOURNAL

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Page 1: Reproductive effort and foraging energetics in Adélie penguins fileReproductive effort and foraging energetics in Adélie penguins MARK A. CHAPPELL, VAUGHAN H. SHOEMAKER, and DONALD

Reproductive effortand foraging energetics

in Adélie penguins

MARK A. CHAPPELL, VAUGHAN H. SHOEMAKER,and DONALD N. JANES

Biology DepartmentUniversity of California

Riverside, California 92521

SHANE K. MALONEY

School of Biological SciencesThe University of New South WalesKensington, New South Wales 2033

Australia

We are examining the energetics, behavior, and foraging ac-tivities of Adélie penguins (Pygoscelis adeliae) at a rookery nearPalmer Station. Our project concerns reproductive effort inmales and females in species with monogamous breeding sys-tems and extensive parental care by both sexes. Adélies aregood subjects for these studies because of their abundance,tameness, and accessibility.

Reproductive effort is the investment of energy and materialsa parent allocates to reproduction, as opposed to growth andmaintenance. As such, it includes energy expenditures forcourtship, incubation, and foraging to provide food for chicks,and the energy equivalence of eggs and of the overall masschange of the adults during the breeding season (because ofextensive fasting, Adélie parents often lose 20 percent or moreof their initial mass). Measurements of reproductive effort pro-vide important insights into the cost of reproduction—that is,the theoretically predicted decrease in future reproductive suc-cess caused by reproductive effort during a given breedingevent. It is generally assumed that reproductive effort and costof reproduction are correlated—if reproductive effort in a givenbreeding season is high, then the impact on future breedingsuccess should also be high. Additionally, reproductive-effortdata can be used to calculate the food resources adult penguinsrequire for reproduction at different stages of the breedingcycle, and (together with information on the rate of food con-sumption by chicks) the total energy flux through a penguincolony.

A major problem in studying reproductive effort is separatingthe energy allocated to reproduction from the rest of the par-ent's energy budget. In our study, we are using a combinationof behavioral observations, isotopic measurements of bodycomposition (ratio of lean to fatty tissue) and of field metabolicrates, and time-depth recorder data on foraging behavior toassess reproductive effort at various stages of the breedingcycle. Results from these methods will be analyzed along withdata from previous metabolic and behavioral studies (e.g.,Trivelpiece, Trivelpiece, and Volkman 1987; Chappell et al. 1989;Chappell, Morgan, and Bucher 1990) to provide quantitativeestimates of reproductive effort.

During the first field season (October 1990 through February1991), we banded several hundred adults during the initialcourtship phase and followed the progress of banded pairs

throughout the breeding season. These studies provided back-ground data on incubation and foraging schedules, hatchdates, and chick growth rates. Body composition, field meta-bolic rates, and time-depth recorder studies were performedon well-known individuals at standardized times in the breed-ing cycle.

Adélies began arriving in colonies in early October and mostbreeding adults were present by the end of the month. The firsteggs appeared on 7 November, with the peak of egg-layingaround 14-20 November. Hatching began on 9 December. Thefirst fledgling occurred approximately 1 February 1991, andmost chicks had departed to sea by 28 February. Censusingindicated that the 2,800 breeding pairs in the colonies we stud-ied produced approximately 5,600 eggs and 2,900 fledglings,for an egg-to-fledgling survival rate of about 52 percent. Mostof this mortality occurred during incubation and the earlystages of chick rearing as a result of nest flooding and predationby brown skuas. We also observed intense predation on adultpenguins by leopard seals. Approximately 12.5 percent ofbanded adults disappeared during the season.

We made 71 measurements of field metabolic rate. Thesewere divided approximately evenly among males and femalesand among four stages of the breeding season (courtship, in-cubation, care of uncreched chicks, and care of creched chicks).We obtained an additional 20 measurements of body composi-tion.

Behavioral observations and daily nest inspections indicatedthat cumulative incubation times were longer for males thanfor females, but the sexes shared chick feeding duties approx-imately equally, as reported previously (Ainley LeResche, andSladen 1983; Trivelpiece et al. 1987). Proportional mass lossesover the season were roughly equivalent in both sexes. Thesedata suggest approximate equivalence in reproductive effortamong males and females (as theory would predict for monog-amous breeders). These indirect estimates will be refined whenfield metabolic rates and body composition data have been ana-lyzed.

We obtained time-depth recorder data from 27 birds duringthe chick-feeding stages. (An additional two failed to returnfrom foraging; presumably they were killed by leopard seals).The sample population spent about 35-40 percent of the totalperiod of time-depth recorder deployment in the water, evenduring the period when they were feeding creched chicks.These data contrast with other reports (Ainley et al. 1983;Trivelpiece et al. 1987) which indicate that parents of crechedchicks spend more than 90 percent of their time at sea. Werecorded about 8,400 dives deeper than 4 meters duringroughly 430 hours of swimming. Of these dives, some 5,900were assumed to be feeding dives (long duration, deep, usuallywith a substantial period spent at maximum depth) and theremainder were assumed to be traveling dives (short duration,shallow). Preliminary analysis of diving behavior did not revealsignificant differences between males and females. Adélies atPalmer foraged throughout the day, but most frequently duringthe midday period (0800-1700 local time). The maximum re-corded depth was 87 meters. Most foraging dives were to 15-50 meters, with a mean depth of about 26 meters (figure 1).The deepest depths were attained primarily during the daylighthours. Diving appeared to be aerobic, with a maximum ob-served submergence time of 2.7 minutes and a mean of about1-1.2 minutes during foraging dives. Not surprisingly, therewas a strong positive correlation between maximum dive depthand dive duration (figure 2). Surface intervals between diveswere weakly correlated to dive duration. While foraging, Adé-

180 ANTARCTIC JOURNAL

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Figure 1. Relationship between time of day and depth and fre-quency of diving for Adélie penguins foraging near Palmer Station,Antarctica. The two horizontal axes represent time of day (in 1-hour intervals) and maximum dive depth (in 1-meter intervals),respectively. The vertical axis is the frequency of occurrence ofeach combination of time and depth. The figure excludes data fromtraveling dives (see text) and from all dives with maximum depthsless than 5 meters. N =5,900 dives by 27 penguins.

lies spent most of their time submerged; typical foraging boutslasted 20-60 minutes and included 10-40 dives. Travel timebetween colonies and foraging sites varied widely. Some birdstraveled for 2-3 hours before commencing foraging dives, butmany others began foraging activities within 10-15 minutes ofdeparture.

This research was largely supported by National ScienceFoundation grant DPP 89-17066. We are grateful to the PalmerStation staff and to members of other research teams for theirinvaluable assistance at various stages of our work.

Figure 2. Relationship between dive duration and maximum depthfor Adélie penguins during foraging near Palmer Station, Antarc-tica. The two horizontal axes represent maximum dive duration (in10-second intervals) and maximum dive depth (in 1-meter inter-vals), respectively. The vertical axis is the frequency of occurrenceof each combination of dive duration and maximum depth. Thefigure excludes data from traveling dives (see text) and from alldives with maximum depths less than 5 meters. N = 5,900 dives by27 penguins.

References

Ainley, D.C., R.E. LeResche, and W.J.L. Sladen. 1983. Breeding biologyof the Adëlie penguin. Berkeley: University of California Press.

Chappell, M.A., K.R. Morgan, S.L. Souza, and T.L. Bucher. 1989.Convection and thermoregulation in two Antarctic seabirds. Journalof Comparative Physiology, 159B, 313-322.

Chappell, M.A., K.R. Morgan, and T.L. Bucher. 1990. Weather, micro-climate, and energy costs of thermoregulation for breeding Adéliepenguins. Oecologia, 83, 420-426.

Trivelpiece, W.Z., S.C. Trivelpiece, and N.J. Volkman. 1987 Ecologicalsegregation of Adélie, gentoo, and chinstrap penguins at KingGeorge Island, Antarctica. Ecology, 68, 351-361.

Natural history of Ross Seaemperor penguin colonies

GERALD L. KOOYMAN, PAUL J . PONGANIS,and PHILIP H. THORSON

Physiological Research LaboratoryScripps Institution of OceanographyUniversity of California, San Diego

La Jolla, California 92093

PATRICE ROBISSON

Centre d'Etudes Biologiques des Animaux SavageCentre National de la Recherche Scientifique

Beauvoir-sur-Niort, France

In this third season (1986, 1989) of the study of emperorpenguin colonies in the Ross Sea, we introduced several newprocedures, all of which were highly successful. The first wasdeployment of the field camp at Cape Washington by twin-otter. This precluded the need for an air drop or long traverse,and the camp was established by 15 October, the earliest sitingof the camp yet. This early arrival was possible because of thefirst-ever transport of the twin-otter to the Antarctic withinan Air Force C5 from Port Hueneme, California to McMurdoSound with a stopover in Christchurch, New Zealand.

It was also an exceptionally early beginning for U.S. Navyhelicopter operations when three of the team were transportedto Cape Crozier on 11 October for an early season census ofthe emperor penguin colony. The colony has grown signifi-cantly in the last few years and now numbers about 300 chicks.A count later in the season on 18 December, just before fledg-ing, indicated that chick mortality had been low since October.

For the first time in a single season, the other five colonies

1991 REVIEW 181