Reproduction, Growth and Development in Captive Beluga (Delphinapterus leucas) Todd R. Robeck,1n Steven L. Monfort,2 Paul P. Calle,3 J. Lawrence Dunn,4 Eric Jensen,5 Jeffrey R. Boehm,6 Skip Young,7 and Steven T. Clark8 1SeaWorld Texas, San Antonio, Texas 2Conservation and Research Center, National Zoological Park, Smithsonian Institution, Front Royal, Virginia 3Wildlife Conservation Society, Bronx, New York 4Mystic Aquarium, Mystic, Connecticut 5U.S. Navy Marine Mammal Program, San Diego, California 6John G. Shedd Aquarium, Chicago, Illinois 7Vancouver Aquarium Marine Science Centre, Vancouver, British Columbia 8Corporate Zoological Operations, Orlando, Florida Recent success propagating captive beluga has resulted from combined efforts by North American zoos and aquariums to manage disparate collections as a single population. This success has provided a tremendous opportunity to increase our understanding of beluga reproductive biology. Blood samples were collected on a weekly to biweekly basis from 23 female and 12 male beluga, ranging in age from 2?15 years, for analysis of serum progesterone (P) and testosterone (T), respectively. Peri-parturient observational data, including food intake, duration and signs of labor, and nursing patterns were collected from 15 days prepartum to 30 days postpartum during 21 births. Total body lengths and weights were collected from 10 captive-born beluga. For female beluga, the mean (7SD) age, body length, and weight at ?rst conceptions were 9.172.8 years, 318.079.1 cm, and 519784 kg. Thirty-?ve luteal phases and 13 conceptions were detected from January?June, and 70% of luteal phases and 80% conceptions occurred from March?May. The mean luteal phase and total estrous cycle lengths were 30.076.5 days and 48.074.6 days, respectively. For male beluga, the mean age that males sired their ?rst calf was 13.372.6 years. Compared to younger males (o8 years of age, 0.95 ng/ml), levels of T secretion in older males (48 years of age, 5.0 ng/ml) were elevated signi?cantly only during the interval from Grant sponsor: Wildlife Conservation Society; Grant sponsor: Busch Entertainment Corporation. nCorrespondence to: Todd R. Robeck, DVM, PhD; SeaWorld Texas, 10500 SeaWorld Drive, San Antonio TX 78251. E-mail: Todd.Robeck@SeaWorld.com Received 5 May 2004; Accepted 3 September 2004 DOI 10.1002/zoo.20037 Published online in Wiley InterScience (www.interscience.wiley.com). Zoo Biology 24:29?49 (2005) c 2005 Wiley-Liss, Inc. January?April. Highest T concentrations (6.274.9 ng/ml) were recorded from January?March, whereas nadir concentrations (1.171.0 ng/ml) were detected from August?September. The mean gestation length was 475.0720.4 days (n? 9). For parturition, the mean time from the ?rst appearance of ?uke or rostrum to delivery, delivery to placental passage, and delivery to nursing were 4.472.9 hr, 7.671.8 hr, and 43745 hr, respectively. All cows had decreased food intake on the day of delivery, with 44% having zero intake. Peak 24-hr nursing activity occurred 3.972.7 days post-partum. Growth (i.e., body weight and length) as a function of age were well described by the Gompertz model (r2? 0.91, 0.93). Based on the model, growth in body weight and length were signi?cantly greater in males compared to females. Predicted birth weight (88.9 kg) was similar for both sexes, however, and male calves were predicted to be shorter (154.3 cm) than female calves (160.7 cm). The results provide the ?rst descriptions of captive beluga reproductive physiology, including endocrinology, peri-parturient beha- vior, growth, and reproductive maturity. This knowledge is important for helping to maintain genetically diverse, self-sustaining populations of captive beluga whales. Zoo Biol 24:29?49, 2005. c 2005 Wiley-Liss, Inc. Key words: mondontidae, cetacean age and growth, testosterone, progesterone, captive cetaceans INTRODUCTION Historically, beluga (Delphinapterus leucas) has been one of the most important food sources for Inuit?s living in the arctic [Heide-Jrgensen, 1990]. Despite the continued reliance on this species, little information has been collected concerning their basic reproductive physiology. For the most part, existing information has been derived from observation of wild stocks or post-mortem analysis of animals collected during native harvests [Brodie, 1971; Braham, 1984; Burns and Seaman, 1986; Doidge, 1990; Heide-Jrgensen, 1990; Heide-Jrgensen and Teilmann, 1994; Hier and Heide-Jrgensen, 1994]. Assuming accurate methods exist for aging the animals harvested [Clark et al., 2000], and despite access restricted by season, this type of data has been used to document certain biological functions including reproductive seasonality, growth, and development. Free-ranging male and female beluga have been estimated to be reproductively mature between 4?7 and 6?9 years of age, respectively [Brodie, 1971; Braham, 1984; Heide-Jrgensen and Teilmann, 1994]. The species is believed to exhibit reproductive seasonality with breeding observed from April?May, although slight geographical variation exists [Brodie, 1971; Heide- Jrgensen and Teilmann, 1994]. Estimates of total gestation length range widely from 330 days (Western Greenland) [Heide-Jrgensen and Teilmann, 1994] toB435 days (Canadian) [Brodie, 1971], and lactation is believed to last approximately 24 months [Brodie, 1971]. Hier and Heide-Jrgensen [1994] evaluated serum collected post mortem during May and September to describe mean serum testosterone (T) levels of 4.14 nmol/l (1.19 ng/ml) and 0.96 nmol/l (0.27 ng/ml) in mature and immature males, respectively. In addition, serum progesterone (P) in pregnant females was 27.9 nmol/l (9.15 ng/ml). Thirty-two beluga currently reside in nine North American zoological institutions [L. Garibaldi, personal communication]. Since 1988, these facilities have been involved in a coordinated captive breeding management effort that has 30 Robeck et al. resulted in the birth of 21 calves. The ready animal access inherent in zoological settings, combined with the high tractability of beluga, provides a unique opportunity to conduct systematic research to study the reproductive biology of this species. Nevertheless, the only beluga reproductive biology publications to date have been limited to descriptions of suckling behavior, nursing patterns, and preliminary data on gestational steroid hormones [Drinnan and Sadler, 1981; Calle et al., 1993, 1996; Russell et al., 1997]. Peak 24-hr nursing activity was described to occur at B7?10 days of age, and suggested that abnormal nursing patterns could provide an early indicator of calf distress [Cook et al., 1992; Russell et al., 1997]. Peak gestational P (60?66 ng/ml) and estradiol (30?31 pg/ml) concentrations occurred by 4 months of pregnancy [Calle et al., 1993, 1996]. With known ages and the ability to collect accurate serial morphometric measurements and serum samples (for reproductive hormone assays), captive populations provide a unique opportunity to improve our understanding of reproductive biology in this species [Clark et al., 2000]. The objectives of our research with captive beluga were to quantify seasonal endocrine changes in females (serum P) and males (serum T); to establish the age of sexual maturity; to document behaviors during parturition and the peri-parturient interval; to compare and contrast nursing patterns in normal and clinically distressed calves, and; to characterize growth rates in captive born calves and compare these data to estimates of growth rates in wild beluga. MATERIALS AND METHODS Animals and Sample Collection Blood samples were obtained by voluntary presentation or during routine venipuncture as part of medical or management procedures from 23 female and 12 male beluga for various intervals from 1983?1998. The animals were located at nine different facilities: John G. Shedd Aquarium, Chicago, IL; Mystic Aquarium, Mystic, CT; Point De?ance Zoo and Aquarium, Point De?ance, WA; SeaWorld of Texas, San Antonio, TX; SeaWorld of California, San Diego, CA; SeaWorld of Florida, Orlando, FL; US Navy Marine Mammal Program, San Diego, CA; Vancouver Aquarium Marine Science Centre, Vancouver, B.C.; and New York Aquarium, Wildlife Conservation Society, Brooklyn, NY. The US Navy Marine Mammal facility and the New York Aquarium are natural salt water systems ranging in temperature from 13?211C and 1.7?281C, respectively. All other facilities housed animals in manufactured salt water at temperatures ranging from 17?201C. The blood sampling periods for individual animals ranged from 2?15 years. Many of the samples or observational data were based on the availability of stored samples or animal records. During the main sampling period (1996?1998), 17 females ranging from 8?30 years were bled weekly to bi-weekly for 2 years (Table 1). In addition, 304 serum samples were collected from 10 males that were bled biweekly to quarterly over a maximum of 15 years (1983?1998). The males? ages ranged from 3?21 years at sampling onset (Table 2). Reproduction in Captive Beluga 31 T Radioimmunoassay Male beluga serum or heparinized plasma was analyzed in duplicate using a double-antibody [125I] RIA (ICN, Costa Mesa, CA) for T according to the instructions provided except all reagent volumes were halved. The antiserum cross- reacts 100% with T, 3.4% with 5a-dihydrotestosterone, 2.2% with 5a-androstane- 3b-17b-diol, 2.0% with 11-oxotestosterone, and o1% with all other steroids tested. P Radioimmunoassay Female beluga serum or heparinized plasma was analyzed in duplicate using a double-antibody [125I] RIA that cross reacts with a wide variety of P metabolites. All female serum extracts were analyzed using [125I] RIA described previously for P [Brown et al., 1994; Wasser et al., 1994]. The monoclonal antiserum cross-reacts 100% with P, 96% with 5a-pregnane-3b-ol-20-one, 36% with 5a-pregnane-a-ol-20- one, 15%, with 17a-hydroxyprogesterone, 13% with pregnenolone, 7% with TABLE 1. Details of captive female beluga Animal ID EDOBa Facility housed Date range of serum samples Samples (n) Conceptions during sampling (n) Calves with observational data (n) Female 1 1983 Mysb 04/95?09/98 61 0 0 Female 2 1986 VCc 06/95?03/98 21 0 0 Female 3 1985 SWTd No Samples 0 0 2 Female 4 1985 SWT No Samples 0 0 0 Female 5 1986 SWT No Samples 0 0 1 Female 6 1986 JGSe 02/95?06/98 25 1 1 Female 7 1970 WCSf 03/90?09/98 141 1 1 Female 8 1983 Mys 06/95?06/98 29 0 0 Female 9 1986 SWT 09/92?06/97 43 1 1 Female 10 1982 WCS 02/92?08/98 110 1 1 Female 11 1986 SWT 01/92?06/97 47 2 3 Female 12 1986 SWT No Samples 0 0 4 Female 13 1967 Navyg 02/88?08/96 49 0 0 Female 14 1981 JGS 02/96?06/98 77 1 4 Female 15 1983 Mys 02/95?09/98 73 0 0 Female 16 1980 WCS 02/91?08/98 113 1 2 Female 17 1989 PtDh 03/97?12/98 48 0 0 Female 18 1985 SWT No Samples 0 0 0 Female 19 1986 JGS 07/92?06/98 37 1 1 Female 20 1978 Navy 04/88?08/96 44 0 0 Female 21 1984 PtD 02/96?11/98 106 0 0 Female 22 1986 SWT 05/93?05/97 40 0 1 Female 23 1977 SWT No Samples 0 0 2 aEstimated date of birth. bMystic Aquarium cVancouver Aquarium. dSeaWorld of Texas. eJohn G. Shedd Aquarium. fNew York Aquarium, Wildlife Conservation Society. gUS Navy Marine Mammal Program. hPoint De?ance Zoo and Aquarium. 32 Robeck et al. 5b-pregnane-3a-ol-20-one, 5% with 5b-pregane-3a,17a-diol, 20a-one, and o1% with pregnanediol-3a-glucuronide and all other steroids tested. Endocrine Data Analysis Estimates of luteal phase and estrous cycle durations were limited to females that were blood sampled a minimum of every 2 weeks. For each individual female, P concentrations that exceeded 3 ng/ml and were at least 2.0 the mean non-pregnant P concentration for that particular individual were considered presumptive evidence of luteal activity. When a sample below this threshold was serially adjacent to a sample above the threshold, the beginning or end of a luteal phase was de?ned as median point between these two samples. The value with the highest concentration during a period of luteal activity was considered the peak. An estrous cycle was de?ned as the number of days between the beginning of two successive luteal phases. All of the cycle characteristics were calculated for each individual animal and then the data were pooled to determine mean values for the population. To determine seasonal estrous activity, any month(s) in which peak P of a luteal phase occurred was given a value of one. For analysis, all monthly data were combined across years to develop a composite 12-month period. Peri-parturient Observations Data were not available for all females for each set of observations. For peri- parturient food intake, values (kg/d) obtained from each animal?s record (recorded as a standard husbandry practice) were utilized. For trend analysis, mean food intake was determined for all animals 15 days before and after parturition (Day 0). The date and time of the following events were recorded for each birth: ?rst vaginal discharge, appearance of ?uke or rostrum, delivery, and placental passage. For live calves, initial postpartum nursing time and total daily nursing were recorded. TABLE 2. Details of captive male beluga Animal ID EDOBa Facility housed Date range of serum samples Samples (n) Calves sired (n) Age at ?rst conception Male 1 1985 SWTb 02/88?01/94 43 1 12 Male 2 1987c WCSd 02/91?09/94 45 0 NA Male 3 1983 VCe 07/91?02/94 7 1 16 Male 4 1982 JGSf 01/94?06/94 15 3 9 Male 5 1985 SWT 05/86?04/81 12 1 13 Male 6 1986 JGS 09/90?03/11 6 0 NA Male 7 1969 WCS 02/79?07/94 9 2 17 Male 8 1975 Navyg 03/84?08/92 48 0 NA Male 9 1979 SWT 02/88?04/92 60 4 12 Male 10 1980 WCS 04/85?12/94 59 2 12 aEstimated date of birth. bSeaWorld of Texas. cCaptive born. dNew York Aquarium, Wildlife Conservation Society. eVancouver Aquarium. fJohn G. Shedd Aquarium. gUS Navy Marine Mammal Program. Reproduction in Captive Beluga 33 Nursing data were collected with 24-hr observations beginning immediately postpartum and continuing for 30 days. Age, Growth, and Morphometry Total body length and weight were collected from 10 captive-born beluga (4 females, 6 males, 2 neonates) maintained at SeaWorld parks from August 1992 until January 2003. Total body length was assessed as per Norris [1961], whereas body weights were obtained using a hydraulic scale (Model 747-915-40; Emery Winslow Scale Company; Seymour, CT). Total body length (cm) and weight (kg) parameters were used to construct age-based growth models. A number of growth models have been used in the examination of size at age. For the present study, both the von Bertalanffy and Gompertz models were examined for ?t. The Gompertz model provided an adequate ?t as evidenced by an examination of the residuals. Additionally, due to the prevalence of this particular model in cetacean age and growth studies [Perrin and Henderson, 1984; Doidge, 1990; Read and Gaskin, 1990; Read et al., 1993; Ferrero and Walker, 1995; Fernandez and Hohn, 1998], we concluded its use for this dataset would be most appropriate because it would allow intraspeci?c comparison of growth parameters to those currently in the literature [Doide, 1990; Heide-Jrgensen and Teilmann, 1994]. The speci?c form of the Gompertz model used was taken from Fitzhugh [1975] WTorTL ? Winf or Linf x?exp?  b x exp?  k x t?? where WT or TL is the weight or total length of the animal at age, Winf or Linf is the asymptotic weight or length growth value for this particular dataset, b is the integration constant, k is the growth rate constant, and t is age (in years). Expectedly, each animal?s growth data were auto-correlated (runs test for trend data categorized by animal, P-valueso0.01). Therefore, the nonparametric statistical technique of bootstrapping, described in Clark and Odell [1999], was necessary to eliminate the problems associated with autocorrelation [Sokal and Rohlf, 1995]. The bootstrapping technique allowed calculation of parameter estimates, standard errors (SE), and 95% con?dence intervals (CI). These calculations then provided the opportunity to analyze model parameter estimated gender and study-based differences. Statistical Analysis Descriptive statistics were applied to the data using Microsoft Excel (Microsoft, Redmond, WA). Kruskal-Wallis one-way ANOVA on ranks and Duncan?s multiple comparison test were used to compare mean monthly serum T values for mature males and to compare mean serum T levels between adult and immature males during the breeding season. Student?s t-tests were used to compare the time interval from ?ukes or rostrum presentation to parturition, and delivery to initial nursing in primiparous vs. multiparous animals. These data analyses were carried out using the SigmaStat for Windows (SPSS Statistical Software, San Rafael, CA). Morphometric statistical analyses were accomplished using the SYSTAT statistical package (version 8.0 for Windows, SPSS Statistical Software, 1998). Data are presented as mean7SD; Po0.05 was considered signi?cant. 34 Robeck et al. RESULTS Serum T Parallel displacement curves were obtained by comparing serial dilutions (range? undiluted  1:32) of pooled beluga serum and T standard preparations. Recovery of known amounts of unlabeled T (range? 0.05?5.0 ng/ml) added to a pool of diluted beluga serum was 123.4711.9% (y? 0.06? 1.0x, r2? 0.99). RIA of elutes after HPLC [Monfort et al., 1991] showed that all immunoreactivity was associated with a single peak that co-eluted with T. Beluga serum was diluted (1:4? 1:8) and assayed (25 ml) in duplicate. Inter- and intra-assay variation were 8.5% and o10%, whereas assay sensitivity was 0.05 ng/ml. Serum P Parallel displacement curves were obtained by comparing serial dilutions (range? undiluted  1:32) of pooled beluga serum and P standard preparations. Recovery of known amounts of unlabeled P (range? 3.75?240 pg/ml) added to a pool of diluted beluga serum was 106.8713.3% (y?1.09? 1.1x, r2? 0.99). RIA of elutes after HPLC [Monfort et al., 1991] showed that 480% of immunoreactivity was associated with a single peak that co-eluted with P. Beluga serum was diluted (neat?1:2) and assayed (100 ml) in duplicate. Inter- and intra-assay variation were 12.0% and o10%, whereas assay sensitivity was 3.75 pg/ml. Samples that had been collected before the study-sampling period were assayed for P by a commercial lab using RIA. Because different methods were used for sample analysis, only samples assayed by the same method were used to determine mean concentrations. Despite concentration differences, correlation between commercial lab results and the monoclonal P RIA during the luteal phase and early pregnancy was 0.73 (Po0.01). Twenty of the 22 females (91%) sampled exhibited a total of 54 P peaks (34.4744.5 ng/ml), which were presumed to represent luteal phase activity or pregnancy. Two of the females did not secrete elevated P during the study. Thirteen conceptions and 10 births occurred during the serum P sampling period. Female Reproductive Maturity The mean age, length, and weight when luteal concentrations of serum P were ?rst detected was 6.971.5 year (n? 9), 31879 cm (n? 6), and 519783 kg (n? 6), respectively. The mean age, length, and weight at ?rst conception were 9.172.8 year (n? 16), 328717 cm (n? 7) and 561772 kg (n? 7), respectively. The mean age at ?rst conception for animals (n? 6) housed with proven sires during the season when the ?rst conception occurred was 8.073.4 years. Of these females, 4 of 6 conceptions occurred during their ?rst ovarian cycle at the age of 6 years. The oldest age for conception in a multiparous female was 20 years. Seasonality During periods when data were collected throughout the breeding season, all but two of the reproductively mature females exhibited at least one elevated serum P value indicative of luteal activity. The mean number of luteal events for each animal per season was 1.370.4 (n? 35). All but two luteal events occurred between January and July, and 70.4% occurred in March, April, and May (Fig. 1). Conceptions Reproduction in Captive Beluga 35 (n? 13) occurred from February to June and 80.6% occurred in March, April, and May (Fig. 1). Estrous Cycle and Pregnancy Characteristics Mean luteal phase and estrous cycle durations were 30.076.5 days (n? 20) and 47.874.6 days (n? 4), respectively. The mean number of cycles that occurred before a conception was 0.670.5 (n? 10). The mean gestation length was 475.0720.4 days (n? 9). Month Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Te st os te ro ne n g/ m l 0 2 4 6 8 10 12 Adult Juvenile Lu te al P ha se a nd C on ce pt io ns 0 2 4 6 8 10 12 14 16 18 Luteal Peaks Conceptions Fig. 1. Demonstrates seasonal variations in female (top graph) and male (lower graph) reproductive parameters. For the female, the bar charts illustrate frequency of luteal activity and conceptions. For the male the graph compares monthly mean values of T between adult (Z8 years) and juvenile (o8 years) beluga. T-values were signi?cantly different (Po0.05) between adult and juvenile males during Jan?May, July, and August. 36 Robeck et al. Male Sexual Maturity and Seasonality The youngest male to sire a calf was 9 years old, and the mean age at which males ?rst sired a calf was 13.372.6 years (n? 8). Thus, all animalso8 years of age were considered sexually immature. Based on this division, peak serum T production in adult males occurred from January?April (Fig. 1). The months of January, February, and March (mean? 6.274.9 ng/ml) had signi?cantly higher median (5 ng/ ml) values (Po0.01) than the nadir months of August and September (median? 0.9 ng/ml; mean? 1.171.0 ng/ml). Comparisons between median serum T from mature and immature animals on a month-to-month basis show signi?cant differences (Po0.05) during January?May, July, and August (Fig 1). Peri-parturient Observations From 1990?1999, a total of 25 pregnancies resulted in 21 births. Fourteen of the pregnancies produced male calves (56%), nine were female (36%) and the sexes of two were undetermined. One female aborted twin male calves at approximately 11 months of gestation. Three cows experienced dystocia and calves were delivered with manual assistance. Of the 21 unassisted births, 18 were live births, two died shortly after birth, and one was stillborn. Two calves were born in a head?rst presentation (9.5%), and one of these calves died shortly after birth. The mean time from ?rst observed vaginal discharge to appearance of ?ukes and the subsequent interval until birth was 3.272.6 hr (range? 0.2?8 hr, n? 17) and 4.472.9 hr (range? 0.4?12.4 hr, n? 18), respectively. The mean time from delivery to placental passage was 7.671.8 hr (range? 4.6?11.8 hr, n? 18). The mean and median time from parturition until the onset of nursing was 43.0745.4 hr (range? 5.3?144.0 hr, n? 15) and 22.7 hr, respectively. The time period from ?rst ?uke appearance to birth and the subsequent interval until the ?rst postpartum nursing tended to be longer in primiparous cows (4.471.9 hr, n? 5; 52.3762.1 hr, n? 4, respectively) compared to cows delivering their second calf (2.770.7 hr, n? 5; 19.1715.3 hr, n? 4, respectively). For all animals with available data (n? 16), food intake decreased close to and on the day of parturition (Fig. 2). Seven of 16 (44%) beluga had zero food intake on the day of parturition. After parturition, ?rst consumption of food by cows occurred at 1.871.0 days (range? 1?4 days) and food intake returned to normal pre- parturient levels by 6.273.4 days (range? 1?14 days, n? 14). Two of the animals were not included in this data set, however, because their food consumption had not returned to normal baseline levels by 15 days postpartum. Age, Growth, and Morphometry Of 18 live births, one died within 30 days from a congenital heart defect, and a second died within 60 days from an infection; another two animals died before the age of 2 years from infectious disease. Thus, 14 of 22 births (63.6 %) resulted in calves that reached 2 years of age. Mean 24-hr nursing time for normal calves (i.e., those surviving for 42 years) is illustrated in Figure 3. In addition, nursing patterns of the four calves that died before the age of 1 year were compared to nursing pro?les of normal calves (Fig. 3). Animal 1 had a period of increased nursing activity around Day 18; this animal was diagnosed with pulmonary nocardiosis and despite treatment died at 60 days [Robeck et al., 1994]. Animal 2 had prolonged elevations of nursing time from Day 6 to Day 12, but this animal died at Day 29 from a Reproduction in Captive Beluga 37 congenital heart defect [L. Dalton, unpublished data]. Animal 3 consistently exhibited a below-average nursing pattern and died by 6 weeks of age from a bacterial infection. Animal 4 did not nurse initially, was administered supportive care and antibiotics on Day 5, began nursing by Day 10, but eventually died from a bacterial infection. For normal calves, the period from parturition to peak nursing time was 3.972.7 d (range? 1?10 days, n? 13), but for calves that died before the age of 1 year, peak nursing occurred 5.072.4 days post-partum (range? 3?8 days, n? 4). The mean body weight and length of beluga calves up to 5 days of age was 61.874.5 kg (n? 5) and 148.076.2 cm (n? 3), respectively. Days Post Partum -15 -10 -5 0 5 10 15 K ilo gr am s/d ay -2 0 2 4 6 8 10 12 14 16 18 20 22 24 Fig. 2. Pre- and post-partum food consumption in captive beluga (n? 16). 38 Robeck et al. Total body length and weight The relationship between body weight and total length was exponential (r2? 0.94; Fig. 4). The overlap of the 95% CI for male and female parameter M in u te s N ur si n g 0 20 40 60 80 100 Normal Animal Mean Animal 1 M in u te s N ur si n g 0 20 40 60 80 100 Normal Animal Mean Animal 3 M in u te s N u rs in g 0 20 40 60 80 100 Normal Animal Mean Animal 2 Days Post Partum 0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 M in u te s N u rs in g 0 20 40 60 80 100 Normal Animal Mean Animal 4 Fig. 3. Nursing pro?les (minutes of nursing/day) for calves surviving after (pooled mean data? normal animal mean) or dying before (individual data?Animals 1?4) 1 year of age. Reproduction in Captive Beluga 39 estimates (Table 3) indicated a lack of sexual dimorphism at this age, which permitted analyses to be conducted on combined sex data. Present study parameter estimates differed from those reported in the literature (Table 4). Age and body weight Weight at age was described by a Gompertz model (r2? 0.91 for the sexes combined dataset) and was sexually dimorphic (Fig. 5). Sexual dimorphism was more apparent than in the total length model. The predicted growth curves for males and females were clearly different in shape and there was an absence of overlap between the parameter estimates 95% CI for both maximum predicted length (WTN) and growth rate constant (k) (Table 3). Model-estimated weights at birth for the combined sexes data was 88.9 kg, whereas gender-speci?c models returned estimated birth weights of 70.7 kg and 107.8 kg for males and females, respectively. Present study parameter estimates were signi?cantly different to those reported by Heide-Jorgensen and Teilmann [1994] (Table 4). Age and total body length A Gompertz function adequately described the relationship between age and total body length (r2? 0.93 for the sexes combined dataset) and suggested growth dynamics in total length were sexually speci?c (Fig. 6). Body length at birth for both 0 50 100 150 200 250 300 350 400 450 100 125 150 175 200 225 250 275 300 325 Total length (cm) W ei gh t (k g) wt = 0.00279 * tl 2.08 r2 = 0.94; n = 9 Fig. 4. Exponential relationship between body weight (kg) and total length (cm) in captive beluga. Data combined for sex (males: n? 5; females: n? 4). 40 Robeck et al. sexes combined was predicted by the model to be 158.7 cm. The predicted body length of females at birth was slightly greater than that for males (160.7 and 154.3, respectively). Theoretical maximum body length was greater for males (333.2 cm) than females (284.1 cm). The steeper incline of the male growth curve derived from the model-predicted growth curve (Fig. 6) provided visual evidence of support for gender differences in asymptotic length. The male growth rate constant (k) was less than the female, whereas growth rate constants of either sex were substantially greater than those reported in the literature (Table 5). DISCUSSION Similar to ?ndings for age at ?rst pregnancy for wild beluga [Heide-Jrgensen and Teilmann, 1994; Braham, 1984], we found the mean age of ?rst ovulation was 6.9 years for captive females. The mean age for ?rst pregnancies in captive beluga was 9.1 years, however, which is later than their wild counterparts that apparently conceive during their ?rst estrous cycles. In captive populations, the inconsistent availability of breeding males may arti?cially lengthen the period between the ?rst estrous cycle and ?rst pregnancy. This is supported by the observation that 67% of captive females (n? 6) maintained in the presence of a proven breeding male became pregnant at 6 years of age. These data support previous speculation [Heide- Jrgensen and Teilmann, 1994] that given the right social environment, beluga can conceive during their ?rst season of cyclic ovarian activity. Similar to the maximum age of reproduction for wild female beluga (21 years) [Brodie, 1971] the maximum age of reproduction for captive females was 20 years. Although this may be due to reproductive senescence [Brodie, 1971], the captive population of female beluga is too young to establish if or when senescence occurs. The ability to serially collect hormonal data enabled us to begin to describe the reproductive biology of captive beluga. We estimated a luteal phase of 30 days and a TABLE 3. Parameter estimates with associated 95% CI of the weight and total length morphometric relationship for captive belugas at SeaWorld parks with comparisons to data from previous studiesa A B This study Heide- Jorgensen and Teilmann [1994] Doidge [1990] This study Heide- Jorgensen and Teilmann [1994] Doidge [1990] Both genders 0.002794 0.000514 0.000031 2.080 2.37 2.85 95% CI 0.001339?0.004249 1.983?2.177 Males 0.002224 0.000295 0.000002 2.132 2.47 3.37 95% CI 0.000778?0.003670 2.013?2.252 Female 0.004750 0.000137 0.003515 2.0000 2.21 2.03 95% CI 0.000051?0.009448 1.812?2.188 aWeight in kg, length in cm. Males: n? 5; Females: n? 4. Length Morphometric relationship weight?A n total lengthB; where A was the initial value of weight when total length was 0 and B was the exponential growth factor. Reproduction in Captive Beluga 41 T A B L E 4. P ar am et er es ti m at es w it h as so ci at ed 95 % C I of th e G om pe rt z no n- lin ea r re la ti on sh ip be tw ee n to ta l le ng th an d ag e fo r ca pt iv e be lu ga s fr om S ea W or ld pa rk s w it h co m pa ri so ns to da ta fr om pr ev io us st ud ie sa T L N b k T hi s st ud y B ur ns an d Se am an [1 98 5] D oi dg e [1 99 0] H ei de - Jo rg en se n an d T ei lm an n [1 99 4] T hi s st ud y B ur ns an d Se am an [1 98 5] D oi dg e [1 99 0] H ei de - Jo rg en se n an d T ei lm an n [1 99 4] T hi s st ud y B ur ns an d Se am an [1 98 5] D oi dg e [1 99 0] H ei de - Jo rg en se n an d T ei lm an n [1 99 4] B ot h ge nd er s 33 0 0. 73 0. 43 95 % C I 32 0? 34 0 0. 66 ?0 .8 0 0. 33 ?0 .5 3 M al es 33 3 42 7 34 9 48 3b /4 34 c 0. 77 0. 74 0. 71 0. 95 b /0 .7 5c 0. 47 0. 14 0. 28 0. 22 b /0 .2 1c 95 % C I 32 2? 34 4 0. 71 ?0 .8 2 0. 38 ?0 .5 6 F em al es 28 4 35 9 33 0 38 5b /3 75 c 0. 57 0. 68 0. 60 0. 62 b /0 .6 5c 0. 71 0. 30 0. 27 0. 27 b /0 .3 1c 95 % C I 27 3? 29 5 0. 46 ?0 .6 7 0. 50 ?0 .9 1 a L en gt h in cm .a ge in ye ar s. M al es :n ? 5; fe m al es :n ? 4 G om pe rt z no n- lin ea r re la ti on sh ip :T L ? T L in f  [e xp ( b  ex p ( k  t) ); w he re T L w as th e to ta ll en gt h of th e an im al at ag e, T L in f w as th e as ym pt ot ic to ta ll en gt h gr ow th va lu e, b w as th e in te gr at io n co ns ta nt ,k w as th e gr ow th ra te co ns ta nt , an d t w as ag e (i n ye ar s) . b W es t G re en la nd . c W hi te an d K ar a Se as . total estrous cycle length of 47 days, which is longer than the bottlenose dolphin (30 days) [Brook, 2000] and the killer whale (40 days) [Walker et al., 1988]. Future efforts should be directed toward conditioning beluga for daily urine sample collections, which will permit more detailed analysis of the various components of the estrous cycle. Similar to most populations of wild beluga, our peak conception period occurred in March, April, and May [Brodie, 1971; Heide-Jrgensen and Teilmann, 1994]. Using hormone data, however, we were able to demonstrate that female beluga are seasonally polyestrous, with animals exhibiting up to two ovulations per season. For animals that conceived during the breeding season, approximately 50% conceived during the second estrous cycle. This suggests that in the wild there would be more than one opportunity for female beluga to conceive during the breeding season. Gestation estimates of wild beluga have varied from 330 days to a maximum of 441 days [Brodie, 1971; Sergeant, 1973; Heide-Jrgensen and Teilmann, 1994]. This variation seems to depend on population location and methodology used to extrapolate conception dates. Relying on hormone data, we were able to estimate conception within a 2-week period and determined a longer mean gestation period of 475720 days. The reason that captive animals seem to have a longer gestation than wild animals is unknown, but may re?ect the inaccuracy of methodologies employed previously. 0 50 100 150 200 250 300 350 400 0.0 0.5 1.0 1.5 2.0 2.5 3. 0 3 .5 4.0 4 .5 5. 0 Age (years) W ei gh t (k g) females: wt = 528.7 * e ?1.589 * e r2 = 0.92; n = 4 -028 * age males: wt = 371.91 * e ?1.65 * e r2 = 0.97; n = 5 -0.79 * age Fig. 5. Gompertz non-linear relationship between weight (kg) and age (years) by sex for captive beluga (males: n? 5; females: n? 4). Reproduction in Captive Beluga 43 TABLE 5. Gompertz non-linear relationship between weight and age by sex parameter estimates for captive belugas from SeaWorld parks with comparisons to data from previous studiesa WTN b k This study Heide- Jorgensen and Teilmann [1994] This study Heide- Jorgensen and Teilmann [1994] This study Heide- Jorgensen and Teilmann [1994] Both genders 383 1.46 0.53 95% CI 375?391 1.39?1.53 0.45?0.60 Males 372 483b/434c 1.66 0.95b/0.75c 0.79 0.22b/0.21c 95% CI 357?387 1.60?1.72 0.71?0.87 Female 529 385b/375c 1.59 0.62b/0.65c 0.28 0.27b/0.31c 95% CI 273?295 1.34?1.84 0.20?0.35 aLength in cm. age in years. Males: n? 5; females: n? 4. Gompertz non-linear relationship: TL?TLinf [exp (b exp (k t)); where TL was the total length of the animal at age, TLinf was the asymptotic total length growth value, b was the integration constant, k was the growth rate constant, and t was age (in years). bWest Greenland. cWhite and Kara Seas. 0 50 100 150 200 250 300 350 400 0.0 0.5 1.0 1.5 2.0 2 .5 3.0 3 .5 4.0 4 .5 5.0 Age (years) To ta l l en gt h (cm ) males: wt = 333.2 * e ?0.766 * e r2 = 0.96; n = 5 -0.47 * age females: wt = 284.1 * e ?0.568 * e r2 = 0.93; n = 4 -0.51 * age Fig. 6. Gompertz non-linear relationship between total length (cm) and age (years) by sex for captive beluga (males: n? 5; females: n? 4). 44 Robeck et al. The present study is the ?rst to demonstrate seasonal differences in serum T levels in mature beluga males. In contrast to T concentrations observed in other seasonally reproductive cetaceans spinner dolphin (Stenella longirostris) [T. Robeck, 1984], Paci?c white-sided dolphin (Lagenorhynchus obliquidens) [M. Yoshioka, unpublished], and similar to cetaceans that produce spermatozoa throughout the year (e.g., bottlenose dolphins [Tursiops truncatus] and killer whales [Orcinus orca]) [Schroeder and Keller, 1989; Robeck et al., 1995], mean monthly T concentrations never dropped below 1 ng/ml. Although minimum T levels required to maintain sperm production are unknown for this species, the observed minimum mean of 1 ng/ml suggests that some degree of spermatogenesis may occur throughout the year. This would agree with the observation of Heide- Jrgenson and Teilmann [1994] that although epididymal spermatozoa concentra- tions are higher in May, spermatozoa are still present in October. In bottlenose dolphins, peak sperm production occurs approximately 60 days after peak serum T levels [Schroeder and Keller, 1989]. Although further study is required to determine the timing of spermatogenesis, based on a 60-day interval, the occurrence of peak T from January?March in captive beluga suggests that peak sperm output may occur from March?May. This is a logical suggestion because the timing of peak sperm production in the male would coincide with the occurrence of estrous cycles in the female. The earliest age that a captive male sired a calf was 9 years (mean? 13 years) is in agreement with the estimate for wild beluga of 8?9 years of age [Brodie, 1971], but is contrary to the 6?7 years of age estimate for Greenland beluga [Heide-Jrgenson and Teilmann, 1994]. Peri-parturient behaviors exhibited by beluga during Stage 1 and Stage 2 of labor were similar to those reported for other cetaceans, but there were differences in the timing and duration of these events. For example, beluga remain in Stage 2 labor longer (range? 0.4?12.4 hr) than killer whales (range? 1?4 hr) [Robeck et al., 2001], and bottlenose dolphins (range? 0.8?4.0 hr) [Joseph et al., 2000]. Because it is not uncommon for beluga to experience dystocia, it is important to consider normal delivery times when evaluating the progression of labor. Most peri-parturient reproductive problems of captive cetaceans (e.g., dystocia, stillbirth, weak calf, poor maternal care) occur during labor and within a few hours of birth [Robeck et al., 2001]. Thus, being able to accurately predict the timing of parturition is an important management tool. Although some species of cetaceans have been noted to inconsistently exhibit reduced food intake before birth, food intake in beluga is consistently decreased on the day of parturition. Killer whales [Katsumata et al., 1998] and bottlenose dolphins [Terasawa et al., 1999] exhibit a consistent decline in rectal temperature on the day of parturition, but the predictive value of this approach has not been evaluated in beluga. Within individual animals, we saw differences in the time from delivery to nursing for their ?rst (53 hr) compared to their second calf (19 hr). This ?nding supports the hypothesis proposed by Russell et al. [1997], stating that cows are able to reduce the time it takes to ?rst nurse their newborn calf as they become more experienced. This implies that the cow, to a large degree, is responsible for providing the calf with the best opportunity to learn to nurse. Nursing patterns among normal calves were similar, with an initial peak total nursing time around Day 4, after which they gradually decreased reaching Reproduction in Captive Beluga 45 a plateau around 20 days after parturition. Russell et al. [1997] observed a slightly longer time to peak postpartum nursing time of 7?10 days. A similar nursing pattern has been observed in killer whales [Asper et al., 1988; Clark and Odell, 1999], bottlenose dolphins [Read et al., 1995], and Paci?c white-sided dolphins [Dalton et al., 1995]. Although some authors attribute this early peak in nursing to a need for increased caloric intake [Russell et al., 1997], we speculate that it is related to the learning curve required for the calf to become ef?cient at obtaining milk. Normal calves are born with fat reserves that provide a caloric buffer during this learning process. As the calf grows, it is reasonable to assume its caloric demand will rise accordingly. Reduced nursing time may actually re?ect more ef?cient nursing by the calf, as well as possible changes in milk quality during lactation. In addition, a neonatal calf does not have the ability to handle large volumes of milk during any one feeding. Thus, as the animal?s nursing ef?ciency improves and the digestive functional capacity increases, total nursing time decreases. In support of the hypothesis of Russell et al. [1997] that total nursing time can serve as an indicator of clinical stress in calves, we saw abnormal nursing patterns in four calves that were clinically ill (Fig. 3). Nursing patterns have proven diagnostically useful for evaluating the health of calves from all cetaceans bred in captivity [Cook et al., 1992; Robeck et al., 1994; Dalton and Robeck, 1995; Robeck and Dalton, 2002]. Once normal nursing patterns have been determined for a species, they may be useful indicators of the health of the calf or cow [Amundin, 1986]. Our indications of sexual dimorphism corroborate results reported from wild beluga [Burns and Seaman, 1986; Heide-Jorgensen and Teilmann, 1994], although Doidge [1990] found little, if any, gender-based bias in growth in length. Indeed, sexually dimorphic growth patterns in cetaceans are not lacking from the literature [Best, 1970; Christensen, 1984; Cockcroft and Ross, 1990; Read et al., 1993]. Analyses of growth in total body length in the present study were consistent with those seen in wild beluga [Burns and Seaman, 1986; Doidge, 1990; Heide- Jorgensen and Teilmann, 1994] in that adult males were larger than females, but grow at a slower rate. Yet, our data suggested that male beluga reach lighter asymptotic weights than females while growing faster in this regard, and this contrasts to what has been reported for wild animals [Heide-Jorgensen and Teilmann, 1994]. Captive beluga seem to follow similar body length, but not body weight growth patterns, compared to their wild counterparts. Because adult male beluga are both larger and heavier than females, this discrepancy warrants further discussion. Previous investigators describing growth in other cetacean species have experienced similar paradoxes, albeit when describing body length and not weight [Best, 1970; Christensen, 1984; Duf?eld and Miller, 1988; Cockcroft and Ross, 1990; Read et al., 1993; Read and Tolley, 1997]. In general, two hypotheses are presented to explain this disparity. One theory is that adolescent male cetaceans may experience a rapid growth spurt. This would answer the question of how young male beluga end up heavier than females upon reaching adulthood, whereas our model suggests otherwise. It is possible that we failed to capture this growth spurt simply because many of the animals had not yet achieved this milestone within the study period. The other hypothesis discounts the growth spurt and presents the argument 46 Robeck et al. that males end up larger (or in this case, heavier) than females simply because they continue to grow after the females have reached asymptotic weight. If either of these hypotheses holds true for growth in body weight, as well as length, then it may explain our observed data. Similarities and differences notwithstanding, the results from the present study must be viewed cautiously due to the restrictive nature of the range of the data set and the obvious environmental differences between captive and wild beluga. Results from further captive studies may provide useful tools for assessing baseline life history information pertaining to age and growth dynamics of not only captive, but also wild beluga. As our animals continue to mature, continued monitoring of growth and subsequent analyzes should permit more de?nitive conclusions on attributes of sexual dimorphism and differences between growth in captive-born and wild beluga. CONCLUSIONS In conclusion, we have found that for female beluga, the mean age, length, and weight at ?rst conception were 9.172.8 years, 318.079.1 cm, 519784 kg. Beluga are seasonally polyestrous with 80% of conceptions occurring in March?May. The mean luteal phase and total estrous cycle length were 30.076.5 days and 48.074.6 days, respectively. The mean gestation length was 475.0720.4 days. For beluga males, the highest serum T values (6.274.9 ng/ml) were recorded from January?March with the lowest from August?September (1.171.0 ng/ml). At parturition, times of ?rst appearance of ?ukes or rostrum to delivery, delivery to placental passage, and delivery to nursing were 4.472.9 hr, 7.671.8 hr, and 43745 hr, respectively. Food intake decreased consistently on the day of labor with 44% of parturient females exhibiting zero intake. Mean 24-hr peak nursing occurred on Day 3.972.7 days, and nursing patterns, as compared to mean ?normal? consumption, can be used as an indicator of calf or cow stress or health. Based on the models, captive beluga exhibited gender-biased differences in growth in body length and weight. Predicted body weight at birth for either sex and body length at birth for male and female calves was 88.9 kg, and 154.3 and 160.7 cm, respectively. ACKNOWLEDGMENTS The authors acknowledge and thank the veterinarians, curators, keepers, trainers, and laboratory and veterinary technicians at all the institutions whose assistance made this project possible. We also thank Dr. L. Dalton, SeaWorld of Texas, for his assistance. We thank C. Potter, Smithsonian Institution and Kendall Mashburn, National Zoo?s Conservation and Research Center for technical assistance and Dr. B. Joseph, The Point De?ance Zoo and Aquarium, for support of the collaborative whale management program. We thank K. Ramirez and Dr. M. Greenwell at the John G. Shedd Aquarium for their assistance during this project. We thank Dr. R. Cook, C. McClave, J. Smith, K. Walsh, M. Hiatt, and G. Skammel at the Wildlife Conservation Society for their assistance during this project. This project was funded in part by a grant from the Wildlife Conservation Society?s Species Survival Fund and by Busch Entertainment Corporation. This is a SeaWorld Technical contribution number 2004-02-T. Reproduction in Captive Beluga 47 REFERENCES Amundin M. 1986. Breeding the bottlenose dolphin. Intl Zoo Yearb 25:263?71. Asper ED, Young WG, Walsh MT. 1988. Ob- servations on the birth and development of a captive-born killer whale. Intl Zoo Yearb 27:295?304. Best PB. 1970. The sperm whale (Physeter catodon) off the west coast of South Africa: 5. Age, growth and mortality. Investigational Report of the Division of Sea Fisheries of South Africa 79:1?27 Braham HW. 1984. Review of reproduction in the white whale, Delphinapterus leucas, narwhale, Monodon monoceros, and irrawaddy dolphin, Orcaella brevirostris, with comments on stock assessment. In: Perrin WF, Brownell RJ Jr, Demaster DP, editors. Reproduction in whales, dolphins and porpoises, Special Issue 6. Cam- bridge: International Whaling Commission. p 81?90. Brodie PF. 1971. A reconsideration of aspects of growth, reproduction and behavior of the white whale (Delphinapterus leucas) with reference to the Cumberland Sound, Baf?n Island, popula- tion. J Fish Res Bd Can 28:1309?18. Brook FM. 2000. Sonographic testicular and ovarian assessment in the bottlenose dolphin, Tursiops truncatus aduncus. In: Duf?eld D, Robeck TR, editors. The bottlenose dolphin breeding workshop. Silver Springs, MD: AZA Marine Mammal Taxon Advisory Group. p 207?21. Brown JL, Wasser SK, Wildt DE, Graham LH. 1994. Measurement of fecal estrogen and pro- gesterone metabolites for assessing ovarian activity in felids. Biol Reprod 51:776?86. Burns JJ, Seaman GA. 1986. Investigations of beluga whales in western and northern Alaska II. Biology and ecology. Fairbanks, Alaska: Report by the Alaska Department of Fish and Game. 129 p. Calle PP, Cook RA, McClave C, Palma S. 1993. Circulating gestational progesterone and estra- diol concentrations, parturition, and placental descriptions of two beluga whales (Delphinap- terus leucas). Proc IAAAM 24:61. Calle PP, Cook RA, Robeck TR, Young SJF, Jones MH. 1996. Circulating gestational proges- terone and estradiol concentrations in Beluga whales (Delphinapterus leucas). Proc AAZV 1996:340?2. Clark ST, Odell DK. 1999. Nursing parameters in captive killer whales (Orcinus orca). Zoo Biol 18:373?84. Clark ST, Odell DK, Lacinak CT. 2000. Aspects of growth in captive killer whales (Orcinus orca). Mar Mamm Sci 16:110?23. Christensen I. 1984. Growth and reproduction of killer whales, Orcinus orca, in Norwegian coastal waters. In: Perrin WF, Brownell RJ Jr, Demaster DP, editors. Reproduction in whales, dolphins and porpoises. Special Issue 6. Cambridge: International Whaling Commission. p 253?8. Cockcroft VG, Ross GJB. 1990. Age growth, and reproduction of bottlenose dolphins Tursiops truncatus from the east coast of southern Africa. Fish Bull 88:289?302. Cook RA, Calle PP, McClave C, Palma S. 1992. Health care and medical problems of a captive bred and mother reared beluga whale (Delphinapterus leucas). Proc. IAAAM 23:107?10. Dalton LM, Robeck TR. 1995. Multifocal pyo- granulomatous pneumonia in a killer whale calf. Proc IAAAM 26:84?5. Dalton LM, Robeck TR, Young WG. 1995. Growth and development of a paci?c white- sided dolphin (Lagenorhynchus obliquidens). Proc IAAAM 26:89?91. Doidge DW. 1990. Age-length and length-weight comparisons in beluga, Delphinapterus leucas. Can Bull Fish Aquatic Sci 224:59?68. Drinnan RL, Sadler RMFS. 1981. The suckling behavior of a captive beluga (Delphinapterus leucas) calf. Appl Anim Ethol 7:179?85. Duf?eld DA, Miller KW. 1988. Demographic features of killer whales in oceanaria in the United Stated and Canada, 1967?1987. Rit Fiskideildar 11:297?306. Fernandez S, Hohn AA. 1998. Age, growth, and calving season of the bottlenose dolphins, Turiops truncatus, off coastal Texas. Fish Bull US 96:357?65. Ferrero RC, Walker WA. 1995. Growth and reproduction of the common dolphin, Delphinus delphis Linnaeus, in the offshore waters of the North Paci?c Ocean. Fish Bull US 93:483?94. Fitzhugh HA Jr. 1975. Analysis of growth curves and strategies for altering their shape. J Anim Sci 42:1036?51. Heide-Jrgensen MP. 1990. Small cetaceans in Greenland: hunting and biology. N Atl Studies 2:55?8. Heide-Jrgensen MP, Teilmann J. 1994. Growth, reproduction, age structure and feeding habits of white whales (Delphinapterus leucas) in West Greenland waters. Bioscience 39:195?212. Hier R, Heide-Jrgensen MP. 1994. Steroid hormones and prolactin in white whales (Delphi- napterus leucas) from West Greenland. Bio- science 39:227?38. Joseph BE, Duf?eld DA, Robeck TR. 2000. Summary data on reproduction of bottlenose dolphins in controlled environments. In: Duf?eld D, Robeck TR, editors. The bottlenose dolphin breeding workshop. Silver Springs, MD: AZA Marine Mammal Taxon Advisory Group. p 43?56. Katsumata E, Katsumata H, Tobayama T, Usuki S. 1998. Body temperature in reared killer whales, Orcinus orca. Korea Kwangiu, Republic of Korea: Recent Progress in Molecular and Comparative Endocrinology Asia and Oceania Society of Comparative Endocrinology. p 448?52. 48 Robeck et al. Monfort SL, Arthur NP, Wildt, DE. 1991. Monitoring ovarian function and pregnancy by evaluating excretion of urinary oestrogen conjugates in semi-free-ranging Przewalski?s horses (Equus przewalskii). J. Reprod Fertil 91:155?64. Norris KS. 1961. Standarized methods for measur- ing and recording data on the small cetaceans. J Mamm 42:471?76. Perrin WF, Henderson JR. 1984. Growth and reproductive rates in two populations of spinner dolphins, Stenella longirostris, with different histories of exploitation. In: Perrin WF, Brownell RJ Jr, DeMaster DP, editors. Reproduction in whales, dolphins and porpoises, special Issue 6. Cambridge, Eng: International Whaling Com- mission. p 417?30. Read AJ, Gaskin DE. 1990. Changes in growth and reproduction of harbour porpoises, Phocoe- na phocoena, from the Bay of Fundy. Can J Fish Aquatic Sci 47:2158?63. Read AJ, Tolley KA. 1997. Postnatal growth and allometry of harbour porpoises from the Bay of Fundy. Can J Zool 75:122?30. Read AJ, Wells RS, Hohn AA, Scott MD. 1993. Patterns of growth in wild bottlenose dolphins, Tursiops truncatus. J Zool 231: 107?23. Read K, Mann J, Weiner J, Hecker N. 1995. Infant development in two aquarium bottlenose dol- phins. Zoo Biol 14:135?47. Robeck TR, Atkinson S, Brook F. 2001. Chap 11: Reproduction In: Dierauf L, Gulland F, editors. CRC handbook in marine mammal medicine. Boca Raton: CRC Press. p 193?236. Robeck TR, Dalton LM. 2002. Zygomycotic infections in bottlenose dolphins, (Tursiops trun- catus), a killer whale (Orcinus orca), and paci?c white-sided dolphins (Lagenorhynchus obliqui- dens) caused by Saksenaea vasiformis and Apophysomyces elegans. J Zoo Wild Med 33: 356?66. Robeck TR, Dalton LM, Young WG. 1994. Systemic nocardiosis in a 6-week-old beluga calf. Proc IAAAM 25:109. Robeck TR, Gross T, McBain J. 1995. Prelimi- nary results on radioimmunoassay determination of serum testosterone concentrations in the killer whale (Orcinus orca). Proc IAAAM 26: 72?3. Russell JM, Simonoff JS, Nightingale J. 1997. Nursing behavior of beluga calves (Delphinap- terus leucas) born in captivity. Zoo Biol 16: 247?62. Schroeder JP, Keller KV. 1989. Seasonality of serum testosterone levels and sperm density in Tursiops truncatus. J Exp Zool 249:316?21. Sergeant DE. 1973. Biology of the white whales (Delphinapterus leucas) in western Hudson Bay. J Fish Res Board Can 1065?90. Sokal RR, Rohlf FJ. 1995. Biometry, 3rd edition. New York: WH Freeman and Company. Terasawa F, Yokoyama Y, Kitamure M. 1999. Rectal temperature before and after parturition in bottlenose dolphins. Zoo Biol 18:153?6. Walker LA, Cornell L, Dahl KD, Czekala NM, Dargen CM, Joseph BE, Hsueh AJW, Lasley BL. 1988. Urinary concentrations of ovarian steroid hormone metabolites and bioactive follicle-sti- mulating hormone in killer whales (Orcinus orca) during ovarian cycles and pregnancy. Biol Reprod 39:1013?20. Wasser SK, Monfort SL, Southers J, Wildt DE. 1994. Excretion rates and metabolites of oestra- diol and progesterone in baboon (Papio cynoce- phalus cynocephalus) faeces. J Reprod Fertil 101:213?20. Wells RS. 1984. Reproductive behavior and hormonal correlates in Hawaiian spinner dolphins, Stenella longirostris. In: Perrin WF, Brownell RJ Jr, Demaster DP, editors. Repro- duction in whales, dolphins and porpoises, Special Issue 6. Cambridge: International Whaling Commission. p 465. Reproduction in Captive Beluga 49