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Diving behavior of immature Steller sea lions (Eumetopias jubatus).

Abstract--Understanding the ontogenetic relationship between juvenile Steller sea lions (Eumetopias jubatus) and their foraging habitat is key to understanding their relationship to available prey and ultimately their survival. We summarize dive and movement data from 13 young-of-the-year (YOY) and 12 yearling Stener sea lions equipped with satellite dive recorders in the Gulf of Alaska and Aleutian Islands (n=18), and Washington (n=7) from 1994 to 2000. A total of 1413 d of transmission ([bar]x=56.5 d, range: 14.5104.1 d) were received. We recorded 222,073 dives, which had a mean depth of 18.4 m (range of means: 5.8-67.9 m; SD=16.4). Alaska YOY dived for shorter periods and at shallower depths (mean depth=7.7 m, mean duration=0.8 min, mean maximum depth=25.7 m, and maximum depth=252 m) than Alaska yearlings ([bar]x=16.6 m, 0=1.1 min, [bar]x= 63.4 m, 288 m), whereas Washington yearlings dived the longest and deepest (mean depth=39.4 m, mean duration=1.8 min, mean maximum depth=144.5 m, and maximum depth= 328 m). Mean distance for 564 measured trips was 16.6 km; for sea lions [less than or equal to] 10 months of age, trip distance (7.0 km) was significantly less than for those >10 months of age (24.6 km). Mean trip duration for 10 of the 25 sea lions was 12.1 h; for sea lions [greater than or equal to] 10 months of age, trip duration was 7.5 h and 18.1 h for those >10 months of age.

We identified three movements types: long-range trips (>15 km and >20 h), short-range trips (<15 km and <20 h) during which the animals left and returned to the same site, and transits to other haul-out sites. Long-range trips started around 9 months of age and occurred most frequently around the assumed time of weaning, whereas short-range trips happened almost daily (0.9 trips/day, n=426 trips). Transits began as early as 7 months of age, occurred more often after 9 months of age, and ranged between 6.5 and 454 km. The change in dive characteristics coincided with the assumed onset of weaning. These yearling sea lion movement patterns and dive characteristics suggest that immature Steller sea lions are as capable of making the same types of movements as adults.


Steller sea lions range throughout the North Pacific Ocean rim and are declining in numbers in most of Alaska and Russia (Loughlin et al., 1992; Laughlin and York 2000). Studies of mitochondrial DNA suggest that at least two stocks exist: an eastern stock (California through southeast Alaska) and a western stock (Prince William Sound and areas west) (Bickham et al., 1996; Loughlin, 1997). For the western U.S. stock (west of 144[degrees]W), counts of adults and juveniles have fallen from about 110,000 individuals in the late 1970s to about 25,000 individuals in 2000--a decline of almost 80%. Although the numbers of sea lions that died were greater from the late 1970s to the early 1990s than at present, the rate of decline has remained high. As a result of this decline the U.S. government designated the western stock as "endangered" in 1997 under the U.S. Endangered Species Act; the eastern stock is designated as "threatened." Reasons for the decline in numbers are unknown but may be linked to reduced availability of prey caused indirectly by environmental changes or commercial fishing activities, or both (Loughlin and Merrick, 1989; Merrick, 1995). Severe environmental perturbations and commercial fishing, both resulting in changes in the abundance or availability of prey, have been implicated in the alteration of pinniped foraging behavior and declines in pinniped abundance (e.g. Trillmich and Ono, 1991; Melin, 2002). One method for studying the effect of reduced prey availability on pinnipeds is to measure diving behavior and foraging ecology by using either a time-depth-recorder (Kooyman et al., 1983; Gentry and Kooyman, 1986) from which dive data are retrieved after the animal returns from a feeding trip (e.g. Goebel et al., 1991; Boyd et al., 1994; Werner and Campagna, 1995), or by using a satellite-linked time-depth recorder (SLTDR; the newer version is called a "satellite dive recorder" SDR), which transmits dive and transmitter-status information to orbiting satellites and thus eliminates the need to recapture the animal (e.g. Merrick et al., 1994).

Few data are available concerning the foraging ecology of Steller sea lions. Merrick et al. (1994) and Merrick and Loughlin (1997) presented information on the dive characteristics and foraging behavior of a small sample of Steller sea lions in Alaska; Loughlin et al. (1998) provided similar information for Steller sea lions off the Kuril Islands, Russia. Merrick et al. (1990) and Brandon (2000) presented information on female pup-attendance behavior of sea lions with VHF radio-transmitters off the Kuril Islands and Alaska, respectively. These studies showed that during the breeding season, adult female Steller sea lions generally spent about half their time at sea on relatively brief (18-20 h) foraging trips. Dives tended to be shallow ([bar]x=21 m), brief ([bar]x=1.4 min), and frequent (about 13/h). Observations during winter showed that females with suckling yearlings (17-22 months of age) had feeding trips of about 2.3 days, whereas those with young-of-the-year (5-10 months of age) had trips lasting 0.9 of a day; time on shore for lactating females of both groups averaged 14.2 hours (Porter, 1997). Baba et al. (2000) were able to follow a yearling Steller sea lion for 5 months using two location-only satellite transmitters; one was attached to the top of the head and the other on the back. This animal traveled from Hokkaido to Sakhalin Island and throughout the southern Okhotsk Sea. No dive data were obtained.

Our objective is to present a description of the diving behavior of juvenile Steller sea lions for the western stock of Steller sea lions in Alaska and the eastern stock in Washington state. We deployed SDRs on juvenile Steller sea lions over a broader geographical range in Alaska and over a wider range of dates, providing a more comprehensive picture of the diving behavior of young Steller sea lions. Additionally, SDRs are now smaller and of higher quality, so that more detailed information on diving behavior is available. We then provide in the "Discussion" section a comparison of the accounts in the present study to those we published earlier on adult female diving behavior (e.g. Merrick and Loughlin, 1997).

Materials and methods

We captured 25 free-ranging Steller sea lions of both sexes from approximately 6-22 months of age at rookeries and haul-out sites in the Aleutian Islands and Gulf of Alaska (Table 1, Fig. 1) throughout the year from 1994 to 2000, and during 1995-2000 at Shilshole Marina in Puget Sound, near Seattle, Washington. Animal age was estimated by using mid-June as the presumed birth date (Pitcher and Calkins, 1981) and published accounts of mass, standard length, and girth at age (Calkins et al., 1998). Some juveniles before 1996 were chemically immobilized with [] injected intramuscularly by a dart fired from a pneumatic gun (Loughlin and Spraker, 1989). Those animals were not weighed; therefore exact dosage levels were not determined. However, dosages were most likely between 1.5 and 2.5 mg/ kg. Once a sea lion was immobilized, intramuscular injection of 3-10 cc of Dopram was administered to stimulate respiration and facilitate recovery. After 1996, young sea lions were captured on land with a hoop net and physically restrained. During all years a SLTDR or SDR was glued to the pelage on the animal's back with fast-setting epoxy resin (Loughlin et al., 1987), and two plastic cattle ear tags with the same identification numbers were attached, one to each front flipper. The instruments were not recovered and were expected to be shed during or before molt.


Instrument description and programming

We used 0.5-watt ST-6 SLTDRs (packaged by Wildlife Computers, Redmond, WA), which provide dive depth, dive duration, and transmitter status. Further development by Wildlife Computers resulted in 0.25-watt ST-10 and ST-16 SDRs which could provide five messages: 1) dive depth, 2) dive duration, 3) transmitter status, 4) proportion of time at depth, and 5) a time line. Messages are sent at prescribed intervals; transmission interval at sea is every 43 sec and on land it is every 1 min 28 sec. The number of transmissions (and thus messages received) while the sea lion is at sea depends on the length of exposure of the instrument's salt-water switch at the surface. Location data are not sent by the transmitter but are calculated by Service-Argos, Inc. from the received message. Additional information on these instruments and their capabilities can be found in Merrick et al. (1994). The satellite tracking system (Argos) is described in detail in Fancy et al. (1988) and Stewart et al. (1989). Additional information can be obtained from the manufacturer at their web site (

The ST-6 SLTDR stored, summarized, and transmitted dive data as histograms. Individual dives and surface intervals were not provided; therefore sampling frequency for measuring dive behavior was not a consideration (e.g. Boyd, 1993). Software programming of the SLTDR subdivided each day into four 6-h periods (2100-0300 h, 0300-0900 h, 0900-1500 h, and 1500-2100 h local time). Frequency histograms were summarized separately for dive depth and dive duration for each of the four time periods. The SLTDRs recorded dive depth information in six separate"bins": 4-10 m, 10-20 m, 20-50 m, 50-100 m, 100-250 m, and >250 m. We used 4 m as the minimum depth for a dive based on earlier studies in Alaska (Merrick et al., 1994). Dive-duration bins were 0-60 sec, 60-120 sec, 120-180 sec, 180-240 sec, 240-360 sec, and >360 sec.

The ST-10 and ST-16 units used the same 6-h periods as the ST-6. However, the ST-10 and ST-16 SDRs subdivided dive depth information into 14 bins: 4 m; 4-6 m, 6-10 m, 10-20 m, 20-34 m, 34-50 m, 50-74 m, 74-100 m, 100-124 m, 124-150 m, 150-174 m, 174-200 m, 200-250 m, and >250 m. Dive duration also contained 14 bins at one-minute intervals (e.g. 1-2 min, 2-3 min, 3-4 min, etc.). The 14 time-at-depth bins coincided with dive-depth bins (e.g. 0, 4, 4-6, 6-10, etc. and the last was >200). However, the first bin was set to zero to determine if an animal was on land based on the proportion of dry readings of the salt-water switch during a 6-hour period. Time-at-depth was calculated as the proportion of time that dives occurred within a particular depth bin ofa 6-h period while the sea lion was at sea (e.g. if an animal was at sea for 3 hours during a 6-h period and spent half its dive time in bin 50-74, the value in bin 50-74 would be 25%).

We deployed ten ST-10 and ST-16 SDRs (Table 1) which transmitted time-line messages in bins of 20-min periods (there are 72 periods of 20-min each in a 24-h day). These messages provide information on whether the instrument was wet or dry >10 min of a 20-rain period for each of the 72 periods. Time-line messages thus allow calculation of time spent at sea and on land.

Maximum dive depth in a 24-h period, from midnight GMT to midnight GMT, was provided in the status message. This is a separate message that provides information on transmitter status, including a pressure offset, battery status, number of transmissions to date, at-surface data, date, time, ID of message, and a saltwater conductivity reading. All 25 transmitters that we deployed transmitted a status message.

The ST-6 SLTDRs were on 24 h/day and transmitted a maximum of 400 transmissions/day. To save battery power the instrument had a 6-h haul-out period; that is, it would turn off only if the transmitter was "dry" for 6 hours, indicating that the animal was on land. The ST-10 and ST-16 SDRs had 3-h haul-out periods; the ST-10 had a maximum of 250 transmissions/day, and the ST-16 had a maximum of 325/day. Both the ST-10 and ST-16 had duty cycles of 4 h on and 2 h off during a 24-h period to distribute transmissions during different times of the day and to ensure recording of information in all bins. All duty cycles started at midnight, with an offset of +13 h from GMT for Alaska.

Location data

Locations were estimated by the Service-Argos, Inc. classification scheme, where location class (LC) 3 is accurate to <150 m, LC 2 is accurate 150 m- [less than or equal to] 350 m, LC 1 is accurate 350 m-1000 m, and LC 0 is accurate >1000 m. LCs A and B have no assigned accuracy range (Service-Argos, 1984; Keating, 1994). However, after our analysis, Vincent et al. (2002) used an algorithm published by McConnell et al. (1992) to filter satellite locations and found that both filtered and unfiltered LC A locations were of a similar accuracy to LC 1 locations for four gray seals (Halichoerus grypus). Because of the large variance in our samples associated with LC A locations, we excluded them (and the LC Bs) from our analyses. We sorted location data by date and time line to determine the locations for each trip.

Data analysis

Data analysis followed that of Merrick et al. (1994) and Merrick and Loughlin (1997). Analysis of the number of dives was prepared by summing counts of dives from the histograms. Median depths and durations of dives were calculated by using the range midpoint of a bin (e.g. 7 m for a 4-10 m bin) as the depth for all dives in the bin. We recognize that this approach invokes a possible error for dive profiles in large increment bins (e.g. 50-100 m) where the mean dive depth is the same, 75 m, regardless of whether the animal made most of its dives between 51 and 60 m or if it made most of its dives between 90 and 100 m. This error is inherent in the data collection process and could not be eliminated with the instruments used in our study. We also recognize that more locations will be recorded when the animals are at the surface for long periods or when transiting to different locations. However, because of the repetitive transmission of the histogram data and the usual short duration of short-range trips, there should be no inherent behavior-based bias in the dive data reported. Differences in dive depth and duration between locations were tested by using the Pearson chi-square tests or analysis of variance (ANOVA) (F-statistic), and P-value differences less than 0.05 were considered significant. Analysis of trip distance and duration were analyzed by using a repeated measures ANOVA, and because the distances were skewed, they were log-transformed to examine differences among groups.

Trips were defined and measured for distance by using an integrated process of the SDR data. For animals deployed with ST6 SDRs, which did not contain time line data sets (n=15), trip distances were extracted by using a combination of the dive histogram, duration histogram, and land or sea data sets to estimate arrival and departure times as well as locations calculated at sea or on land. Once arrival and departure times were estimated, the location data were examined to confirm that all locations calculated during that trip were wet locations. We then had all locations for an individual trip and from those locations we filtered out all A and B locations and imposed a swim speed filter (3 m/s). Finally, we reported the maximum straight-line distance from the departure site. For animals with ST10/16 SDRs, we were able to extract arrival and departure times from the time-line messages. However, if a day of time-line data was not received, we referenced the time-at-depth data, depth, and duration histograms to reconstruct the missing day of data. Once arrival and departure times were calculated we then followed the protocol stated above.


We report on SDR data obtained from 25 (13 male, 12 female) young-of-the-year and juvenile (estimated ages of <2 yr) Steller sea lions from Washington state, Gulf of Alaska, and Aleutian Islands, Alaska (Table 1). Most (22 of 25) were caught during October-March 1995-2000 and the remainder during May-July (Table 1). Mean number of days of transmission received from the SDRs was 56.8 d (range 14.5-104.1 d).

Dive characteristics

We recorded over 222,073 dives for young-of-the-year and juvenile Steller sea lions which had a mean dive depth of 18.4 m (range of means: 6.1-67.0 m; SD=16.23). Alaska young-of-the-year dived to shallower depths and for shorter periods (mean depth=7.7 m, SD=1.7; mean duration=0.8 min, SD=0.1; mean maximum depth=25.7 m, SD=16.9; and maximum depth=252 m) than did Alaska yearlings (mean depth=16.6 m, SD=10.9; mean duration=1.1 min, SD=0.4; mean maximum depth=63.4 m, SD=37.7; and maximum depth=288 m), whereas Washington yearlings dived the deepest and the longest (mean depth=39.4 m, SD=14.9; mean duration=1.8 min, SD=0.6; mean maximum depth=144.5 m, SD=32.6; and maximum depth=328 m). Alaska animals dived to much shallower depths (mean depth= 10.3 m) than animals from Shilshole, WA. There was no significant difference in the mean dive depths among locations in Alaska (P=0.8). Alaska animals, in comparison to the Washington animals, had a significantly greater proportion of dives in the 4-10 m depth bin (70%, P<0.001) than in the deeper depth bins.

We compared the proportion of dives in the shallowest bin (depth bin 4-10 m) for animals captured in Washington state versus Alaska using a generalized linear model with a binomial link function (McCullagh and Nelder, 1989). The proportion of shallow dives was significantly greater (P<0.001) among the Alaskan animals (81.4%) than among the Washington state animals (43.8%). Among the Washington state animals, the proportions of dives in the 1020 m depth bin (20.4%) and the 20-50 m depth bin (19.4%) were similar; proportions of dives in the deeper depth bins were progressively fewer (Fig. 2). Maximum and mean-maximum dive depth were also greater for young sea lions from Washington that dived to 141.5 m (SE=11.4) mean-maximum depth versus 33.8 m (SE=7.2) for Alaska sea lions (F=63.4, 23 and 24 df; P<0.001) (Table 2). We plotted the maximum depth for each 24-h period by the number of days in which the Argos satellite received a status message (which contains maximum depth for 24 hours) and found that with one exception (PTT 14078), Washington yearlings consistently dived deeper than their Alaska counterparts (Fig. 3, A and B). Two of three Alaska young-of-the-year were shallow divers and the third dived to 250 m once and beyond 100 m on numerous occasions late in the tracking period (Fig. 3C). The maximum depth for all sea lions that we studied was 328 m for a juvenile sea lion that was equipped with a SDR at Shilshole, WA (PTT 21106); the deepest dive for a yearling Alaska sea lion was 288 m (PTT 14078) (Fig. 3).


Mean dive duration was 1.1 min for all young sea lions (n=226,497 dives). Dive duration was significantly longer for Shilshole sea lions ([bar]x=1.75 min; range: 0.95-3.10) compared to Alaska sea lions ([bar]x=0.85 min; range: 0.61-1.86; F=24.5, 23 and 24 df; P<0.001). Few dives were greater than 6 min (Fig. 4). There was a significant positive linear relationship between dive duration and dive depth ([r.sup.2]=0.89, F=7.06, 1 and 23 df, P<0.001), and a significant positive relationship between sea lion mass at the time of capture and mean dive duration ([r.sup.2]=0.46, F=3.86, 1 and 20 df, P<0.001) but not girth ([r.sup.2]=0.10, F=1.62, 1 and 14 df, P=0.22). The relationship between dive duration and dive depth for males was not different from that for females (F=1.16, 2 and 21 df, P=0.33). The positive relationship between dive duration and mass was likely driven by the greater mass of the male sea lions because the relationship was not statistically significant when the analysis was restricted to females.


Dive depth and duration showed an interesting ontogenetic trend. Alaska animals 7-10 months old typically had a mean dive duration of <1 min and a mean dive depth of about 10 m; by 11-12 months of age both increased, almost doubling in most cases (Fig. 5). Although sample size was small, this ontogeny of diving to deeper depths for longer periods at about 11-12 months of age was evident in the percentage of time at depth (Fig. 6). There was a higher proportion of time spent in the deeper depth bins during May and June (at age 11 and 12 months, respectively) than when younger, and the proportion of time hauled out was reduced for the older animals. Interestingly, the decrease in dive depth and dive duration for two Washington animals at 23 months of age (Fig. 5) corresponded with movement from inside Puget Sound to deeper waters off the Washington coast.


The greatest proportion of all diving (37%) occurred during 2100-0300 h; the least (about 16%) during 0900-1500 h (Fig. 7). There were no periods when young-of-the-year or juvenile sea lions from any location did not dive. The frequency distribution of dives was similar in all time periods for all age groups from Alaska and Washington (Fig. 7).


Distance and duration of trips at sea

Mean distance of trips at sea for 564 measured trips of the 25 study animals was 16.6 km (SD=44.9 kin; range: <1-447.3 km; median=4.2 km). For sea lions 10 months of age, the mean distance of all trips was 7.0 km (n=257 trips; range=0.1-260.7 km; SD=lg.0 km; median=2.7 kin) (Fig. 8); for sea lions >10 months of age, the mean distance of all trips was 24.6 km (n=307; range: <1-447.3 kin; SD=57.2 km; median=5.6 km) (Fig. 8). Averaged across individual animals, the mean distance of trips at sea ranged between 2.3 and 55.6 km; for the younger animals this range was 4-17 km and 2-55 km for the older animals. The repeated-measures ANOVA on the logarithm of trip distance showed that the older sea lions traveled significantly farther (P<0.001) than younger animals and that there were neither significant gender (P = 0.6) nor gender x age interaction effects (P=0.19).


Trip distance increased with age. For example, we captured a 9-month-old male sea lion (bearing transmitter identification number PTT 21094, Table 1) near Kodiak Island in March 200. It had short trip distances (<10 km) which tended to concentrate near the capture site and nearshore (Fig. 8). As the animal matured through April and May, trip distance progressively increased until the sea lion was swimming over 50 km offshore beyond the 100-m depth contour and had a maximum dive depth >150 m (Table 2; Fig. 8).

Trip duration was measured for 10 of 25 animals with SDRs containing time-line data (it was not possible to calculate trip duration for 15 SDRs with the earlier SLTDRs that did not transmit time-line data). Mean trip duration for these 10 animals was 12.1 hours (n=544; SD=23.83 h; range: 1-344 h; median=7.3 h). For animals [less than or equal to] 10 months of age, the mean trip duration was 7.5 hours (n=307; SD=7.5 h; range: 1-81.3 h; median=6 h) and for sea lions >10 months of age, the mean duration of all trips was 18.1 hours (n=237; SD=34.2 h; range: 1-344 h; median=10.3 h). Averaged across individual animals, the mean duration of trips at sea ranged between 6.2 to 21.4 hours; this range was 6.2 to 17.2 hours for the younger animals and 10.3 and 21.4 hours for the older animals. The analysis of the repeated-measures ANOVA on the logarithm of trip duration showed that the older sea lions had longer trip durations (P<0.001). We could not test for gender and gender x age effects because there were no measured trip durations for females >10 months. Among the younger animals, there was no gender difference in mean trip duration (P=0.11).

Types of movement

We identified three types of movements for the sea lions at sea: long-range trips (>15 km and >20 h), short-range trips (<15 km and <20 h), and transits to other haul-out sites (Fig. 9). Long-range trips most likely were foraging trips and began around 9 months of age. These trips had a mean of 48.7 km (SD=55.7 km; max=240.8 km) and may coincide with the assumed onset of weaning; they represented 6% of all trips to sea. The most numerous trips (88%) were short-range foraging trips (x=3.6 km; SD=0.4; max=21.0 km), which happened almost daily (0.9 trips/d, n=426 trips). Transits were movements from one haul-out site to another haul-out site; these trips were characterized as the straight line distance from one haul-out site to another and began as early as 7 months of age but occurred more often after 9 months of age. Transit trips represented 6% of all trips at sea and had a mean distance of 66.6 km (SD=83.7 km; range: 6.5-341.9 km).



The differences in diving behavior between young Steller sea lions in Washington and those off Alaska are intriguing. Possible reasons for these differences include variable habitat type, prey resources, or morphological or genetic differences. However, there is no evidence, based on morphology or genetics, to either support or refute differences in the diving behavior that we observed. The evidence of genetic differences between the western and eastern stock of Steller sea lions is based on mtDNA haplotype differences for a segment of the mitochondrial D-loop which does not code for any structural proteins (Bickham et al., 1996; Loughlin, 1997).

One morphological difference between the two stocks is a progressive increase in mass of Steller sea lion pups from east to west (Merrick et al., 1995), but whether this difference in mass continues with increasing age is unknown. Large animals typically dive deeper and longer than smaller (and younger) animals (Schreer and Kovacs, 1997). Larger animals have less drag per unit of mass and generally have more blood than smaller ones and thus are able to store more oxygen. Larger animals also have lower mass-specific metabolic rates than their smaller counterparts and thus expend less energy and use less oxygen stores (Schreer and Kovacs, 1997). Our sample size of sea lions of comparable age is small; however, we compared the mean mass of three Washington sea lions to the mean mass of three Alaska sea lions of approximately the same age (Table 1) and found that the Alaska animals had less mass than those in Washington (108 kg vs. 145 kg). Whether or not this difference in mass can account for the differences we saw in diving characteristics for animals of similar age (Fig. 3, A and B) is unknown.

The differences in diving characteristics between animals tracked in coastal waters of Puget Sound, Washington, and those tracked in Alaska waters are most likely linked to localized differences in prey habitat. The primary prey of Steller sea lions across their range are fish and cephalopods, both of which have a broad but predictable range in temporal, spatial, and seasonal nearshore availability. Typically, each species makes predictable migrations seasonally from pelagic to nearshore waters where they form large spawning concentrations. The prey are then further concentrated by local transition boundaries such as frontal zones and bathymetric features such as submarine channels (Sinclair et al., 1994). Steller sea lions appear to have the foraging flexibility to take advantage of both the predictable behavioral traits of these prey species, as well as the localized oceanographic conditions that enhance prey concentrations (Sinclair and Zeppelin, 2002).

The primary prey of Steller sea lions in Alaska waters is walleye pollock (Theragra chalcogramma), which is consumed year-round (Sinclair and Zeppelin, 2002). Walleye pollock is replaced as a dominant year-round prey item by Pacific whiting (Merluccius productus) in Pacific Northwest waters (Gearin et al., 1999). Both species are semidemersal and can be found from near surface waters to depths >1200 m, depending on localized conditions (Hart, 1973; Eschmeyer et al., 1983). The greatest abundances of both species are available to Steller sea lions in nearshore waters over the continental shelf and perhaps as the prey become more available during nighttime diurnal vertical movements.

The physical features of Puget Sound, along with its complex bathymetry and the extensive channels and canyons, provides extensive microhabitat for both predator and prey species to express the full extent of their depth range. In this respect, Puget Sound is comparable to the Gulf of Alaska where Pacific cod (Gadus macrocephalus) is the predominant winter prey item for Steller sea lions. Pacific cod is thought to be consumed during spawning when it appears to concentrate in the deep nearshore channels and gullies of the Gulf of Alaska (Sinclair and Zeppelin, 2002).

The differences in dive depths that we report also could be typical of the variability among individuals. Boveng et al. (1996) analyzed TDR data for six dive-related variables and found that dive duration was the least variable and vertical distance (dive depth) was the most variable among individual Antarctic fur seals (Arctocephalus gazella). In our study, there was high individual variability in both dive depth and maximum depth and little variability in dive duration--results similar to those of Boveng et al.'s (1996) study.

A female Steller sea lion nurses her pups during the day, stays with the pup for the first week, then goes to sea on foraging trips. Maternal pup-attendance patterns seem to vary over the sea lion's geographic range; the average range of time for foraging trips during lactation are from about 24 h to 2 d at the southernmost rookery at Ano Nuevo Island, California (Higgins et al., 1988; Hood and Ono, 1997; but note that some of this variability may have been the result of El Nino conditions during part of the Higgins et al. study period), about 25 h at Lowrie Island, 19 h at Fish Island, 11 h for Chirikof Island, and 7 h in the Aleutian Islands (Brandon, 2000).

Ontogeny of diving ability has been studied in two other otariids. Baker and Donohue (2000) used data loggers (which they termed "time wet recorders") to measure time spent in the water and diving behavior of northern fur seal (Callorhinus ursinus) pups on St. Paul Island, Alaska. These pups began spending substantial time in the water at approximately 40-50 d of age that coincided with growth of the under fur and increases in sea surface temperature. Time spent in the water increased up to about 100 d of age; diving to depth did not occur until they were much older and about to migrate. Homing and Trillmich (1997) conducted an extensive study on the ontogeny of diving behavior in Galapagos fur seals (Arctocephalus galapagoensis), a species that weans no sooner than 2 years of age. They found that in young the development of diving behavior was closely linked to dependence on the mother and that substantial diving activity did not occur until one year of age; but even then the young fur seals were still nutritionally dependent on their mothers and did not dive as deep, or for as long, as mature females. The weaning date for Stellar sea lions is unknown but is assumed to be between 4 and 12 months, and most pups are weaned just before the next breeding season (11-12 months) (Porter, 1997). The change in diving characteristics that we report is interesting in that it coincides with this period. Prior to weaning these pups forage in the company of their mother and learn to forage on their own; the need to dive deep for long periods to acquire food is compensated by nursing from the mother. Once weaning occurs, the yearlings are forced to explore more areas to acquire food for needed energy. Dives become deeper and longer as these yearlings forage at different depths within the water column. Just before their first birthday, many of these young sea lions are capable of diving to the same depths and for the same duration as those of many adults; they also begin to forage at greater distances and for longer periods. Juveniles that we studied had a mean dive depth of 18.4 m and dive duration of 1.1 rain compared to adult females in Alaska that had a mean dive depth of 21 m and dive duration of 1.4 min (Merrick and Loughlin, 1997). Maximum depth in our study was 328 m for a Washington juvenile and 288 m for an Alaska juvenile. Maximum depth information for adult females in Alaska was not provided by the instruments used by Merrick and Loughlin (1997); their maximum depths were characterized by bin data only. They showed that about 5% of dives by adult females in winter were greater than 250 m. In another study, adult females in Alaska were equipped with early-style SLTDRs that had features that recorded time-depth information and these SLTDRs showed that the females frequently dived to 200 m or more (Merrick et al., 1994).

Schreer and Kovacs (1997) summarized maximum dive depth and dive duration for air-breathing vertebrates and developed predictive allometric equations for both parameters based on body mass. We fitted our Steller sea lion body mass data to these equations to estimate maximum dive depth (27.33[[M.sub.b].sup.0.46]), where [M.sub.b] represents body mass in kilograms, and maximum dive duration (6.22[[M.sub.b].sup.0.10]). We found that the maximum dive depth equation provided reasonably close estimates but that dive durations were typically overestimated (Table 3). In some cases measured and estimated maximum dive depth values differed by large amounts (e.g. sea lion PTT 14071), perhaps because the deployment period was brief, before deep dives occurred. For others (e.g. PTT 14074) the difference may have been due to the young animal's continued dependence on the female for nourishment; deeper dives do not occur until weaning. In addition, we note that our dive duration data were stored in bins of 1-min intervals (from 1 to 6 min in the early instruments and from 1 to 14 min in the recent ones); the exact duration of each dive is unknown.

Movement patterns also suggest that the swimming ability of juvenile sea lions is comparable to that of adults. It is not unusual for young sea lions to travel distances as great as 1784 km from the natal rookery; as they approach adulthood they generally remain within 500 km of their natal rookery (Raum-Suryan et al., 2002). In our study some young sea lions traveled several hundred kilometers between sites while presumably searching for food or venturing from the natal rookery site.

Further analysis of our SDR data is warranted to more fully understand sea lion diving behavior and its relationships with oceanographic parameters, daily and season change, and behavioral features as discussed by Fedak et al. (2001). The time allocation at depth (TAD) index described by them will be a useful method for interpretation of our SDR (and TDR) data. Further analysis of our SDR data is needed to determine if such a study is possible.
Table 1

Satellite transmitter number (PTT number), deployment location,
age, sex, and morphometric measures of 25 Steller sea lions studied
for diving behavior in Alaska and Washington, 1994-2000. The ten
ST-10 and ST-16 SDRs we deployed that transmitted time-line messages
are shown with **. 1 = Washington State area; 2 = Kodiak area;
3 = Shumagin Islands; 4 = Unimak Pass area; 5 = Sequam area.
n/d = no data obtained. PTT the satellite transmitter
identification number. Est.= estimated.

 code Age Deployment
PTT number (regional) (months) Sex date

14073 1 12 M 6/8/95
14084 1 11 F 5/5/99
14085 1 19 M 1/5/00
14087 1 16 F 10/3/97
14089 1 16 F 10/3/97
21103 ** 1 22 M 3/30/00
21106 ** 1 22 M 3/30/00
14071 2 6 M 12/2/94
14074 2 6 M 12/6/94
14077 2 18 M 12/9/94
14078 2 18 F 12/7/94
14079 2 7 F 1/14/96
14080 2 7 M 1/16/96
14170 ** 2 21 M 3/12/00
21094 ** 2 9 M 3/12/00
14076 3 21 F 3/1/96
14081 3 9 M 3/2/96
14072 4 22 F 4/13/95
14075 4 8 F 2/25/96
14164 ** 4 9 M 3/8/00
14167 ** 4 9 F 3/9/00
14111 ** 5 9 F 2/29/00
14114 ** 5 9 F 2/29/00
14116 ** 5 9 F 2/29/00
14163 ** 5 9 M 2/29/00

 Length of
 transmission Mass Girth Length
PTT number (d) (kg) (cm) (cm)

14073 51.67 86.26 n/d 151
14084 50.22 77.18 102 159
14085 14.50 154.36 133 193
14087 68.99 122.45 113 171
14089 55.58 111.11 122 173
21103 ** 63.80 139.23 128 192
21106 ** 83.28 143.31 119 192
14071 19.61 92.00 n/d n/d
14074 53.13 79.80 n/d n/d
14077 39.63 n/d n/d n/d
14078 57.99 n/d n/d n/d
14079 27.11 94.90 115 155
14080 79.04 106.20 115 156
14170 ** 93.99 Est. 95-105 n/d 150
21094 ** 66.40 62.20 90 145
14076 52.21 103.70 111 n/d
14081 45.02 n/d 144 n/d
14072 56.35 116.10 n/d n/d
14075 31.76 104.00 123 140
14164 ** 97.61 79.60 n/d n/d
14167 ** 29.67 100.20 n/d 155
14111 ** 61.71 87.00 108.5 151
14114 ** 52.53 85.80 108 157
14116 ** 56.61 76.20 102.5 148
14163 ** 104.14 109.00 113 156

Table 2

Summary of dive parameters from satellite dive recorders
(SDRs) deployed on Stellar sea lions in Washington and Alaska,
1994-2000. "PTT" is the satellite transmitter identification number.

 Mean max. Mean max. Max. Mean
 dive depth dive depth depth depth
 PTT (m) (n) (m) (m)

Washington 14073 77.68 38 168 31.99
 14084 154.12 34 288 47.29
 14085 187.67 12 280 67.94
 14087 164.37 53 256 33.21
 14089 144.00 46 200 44.76
 21103 124.22 18 256 23.59
 21106 159.09 44 328 26.92
Alaska 14071 10.44 18 12 7.20
 14074 11.07 30 20 7.24
 14077 28.57 21 144 9.67
 14078 125.74 23 288 35.00
 14079 12.80 20 44 7.13
 14080 15.80 59 24 7.60
 14170 41.87 47 180 10.23
 21094 48.90 31 152 11.67
 14076 51.69 26 144 9.29
 14081 11.76 34 20 7.25
 14072 68.98 49 100 18.69
 14075 8.00 15 12 7.01
 14164 26.09 44 60 9.46
 14167 20.73 11 60 7.01
 14111 17.76 25 40 6.44
 14114 13.75 16 16 5.84
 14116 24.24 17 40 6.70
 14163 65.55 49 252 10.94
Mean 62.42 135.36 18.42
SE 11.50 3.23 3.23

 Mean Mean Mean
 depth duration duration
 PTT (n) (min) (n)

Washington 14073 10,746 0.96 11,241
 14084 5183 1.69 5047
 14085 1991 3.10 2025
 14087 14,287 1.69 14,572
 14089 9682 1.82 9659
 21103 6920 1.40 5431
 21106 11,839 1.61 11,647
Alaska 14071 1541 0.61 1732
 14074 3044 0.72 2954
 14077 4745 0.81 5146
 14078 4186 1.82 3657
 14079 7546 0.71 8482
 14080 17,236 0.96 18,056
 14170 17,741 0.91 19,447
 21094 9745 0.79 9388
 14076 11,593 0.86 12,739
 14081 8717 0.70 9013
 14072 12,597 1.06 11,931
 14075 5424 0.67 4869
 14164 16,352 0.96 16,426
 14167 2985 0.81 3022
 14111 10,919 0.72 10,903
 14114 5846 0.68 6256
 14116 7359 0.73 7739
 14163 13,849 0.82 15,204
Mean 1.10
SE 0.11

Table 3

The recorded mass, recorded maximum dive depth, and recorded
maximum dive duration for individual young Steller sea lions in
Alaska and Washington from this study and the estimated maximum dive
depth (27.33[M.sub.b.sup.0.46]) and estimate maximum dive duration
(6.22 [M.sub.b.sup.0.1]) based on allometric equations in Schreer and
Kovacs (1997). PTT number is the satellite transmitter identification
number. Est.= estimated. n/a = no data obtained.

 Maximum Est. maximum
PTT number Mass (kg) depth (m) depth (m)

14073 86.26 168 212.38
14084 77.18 288 201.79
14085 154.36 280 277.57
14087 122.45 256 249.52
14089 111.11 200 238.61
21103 139.23 256 264.70
21106 143.31 328 268.24
14071 92.00 12 218.77
14074 79.80 20 204.91
14077 n/a 144 n/a
14078 n/a 288 n/a
14079 94.90 44 221.91
14080 106.20 24 233.70
14170 Est. 95-105 180 Est. 222.02-232.48
21094 62.20 152 182.72
14076 103.70 144 231.15
14081 n/a 20 n/a
14072 116.10 100 243.48
14075 104.00 12 231.46
14164 79.60 60 204.67
14167 100.20 60 227.53
14111 87.00 40 213.22
14114 85.80 16 211.86
14116 76.20 40 200.60
14163 109.00 252 236.51

 Maximum Est. maximum
PTT number duration (min) duration (min)

14073 >6 9.71
14084 >6 9.61
14085 >6 10.30
14087 >6 10.06
14089 4-6 9.96
21103 13 10.19
21106 14 10.22
14071 2-3 9.78
14074 >6 9.64
14077 >6 n/a
14078 >6 n/a
14079 >6 9.81
14080 >6 9.92
14170 >14 Est. 9.81-9.91
21094 >14 9.40
14076 >6 9.89
14081 >6 n/a
14072 >6 10.01
14075 >6 9.90
14164 >14 9.64
14167 3-4 9.86
14111 8-9 9.72
14114 7-8 9.71
14116 5-6 9.59
14163 >14 9.94


Field assistance was provided by numerous NMML staff; logistical support was provided by Alaska Helicopters and the captain and crew of the U.S. Fish and Wildlife Service research vessel Tiglax. The manuscript was improved by comments from D. DeMaster, G. Duker, T. Gelatt, R. Hobbs, M. Lander, J. Lee, R. Ream, E. Sinclair, and two anonymous reviewers.

Literature cited

Baba, N., H. Nitto, and A. Nitta.

2000. Satellite tracking of young Steller sea lion off the coast of northern Hokkaido. Fisheries Sci. 66:180-181.

Baker, J. D., and M. J. Donohue.

2000. Ontogeny of swimming and diving in northern fur seal (Callorhinus ursinus) pups. Can. J. Zool. 78:100-109.

Bickham, J. W., J. C. Patton, and T. R. Loughlin.

1996. High variability for control-region sequences in a marine mammal: implications for conservation and biogeography of Steller sea lions (Eumetopias jubatus). J. Mammal. 77:95-108.

Boveng, P. L., B. G. Walker, and J. L. Bengtson.

1996. Variability in Antarctic fur seal dive data: implications for TDR studies. Mar. Mamm. Sci. 12:543-554.

Boyd, I. L.

1993. Selecting sampling frequency for measuring diving behavior. Mar. Mamm. Sci. 9:424-430.

Boyd, I. L., J. P. Y. Arnould, T. Barton, and J. P. Croxall.

1994. Foraging behaviour of Antarctic fur seals during periods of contrasting prey abundance. J. Animal Ecol. 63:703-713.

Brandon, E. A. A.

2000. Maternal investment in Steller sea lions in Alaska. Ph.D. diss., 137 p. Texas A&M University, Galveston, TX.

Calkins, D. G., E. Becker, and K. W. Pitcher.

1998. Reduced body size of female Steller sea lions from a declining population in the Gulf of Alaska. Mar. Mamm. Sci. 14:232-244.

Eschmeyer, W. N., E. S. Herald, and H. Hammann.

1983. A field guide to Pacific coast fishes of North America, 336 p. Boston Houghton Mifflin Company, Boston, MA.

Fancy, S. G., L. F. Pank, D. C. Douglas, C. H. Curby, G. W. Garner,

S. C. Amstrup, and W. L. Regelin.

1988. Satellite telemetry: a new tool for wildlife research and management. U.S. Fish and Wildl. Serv. Resour. Publ. 172:154.

Fedak, M. A., P. Lovell, and S. M. Grant.

2001. Two approaches to compressing and interpreting time-depth information as collected by time-depth recorders and satellite-linked data recorders. Mar. Mammal Sci. 17:94-110.

Gearin, P., S. Jeffries, S. Riemer, L. Lehman, K. Hughes, and L. Cooke.

1999. Prey of Steller's sea lions, Eumetopias jubatus, in Washington state. In Abstracts of the 13th biennial conference on the biology of marine mammals, Wailea, Hawaii November 28 December 3, p. 65. Soc. Marine Mammalogy, Wailea, HI.

Gentry, R. L., and G. L. Kooyman.

1986. Methods and dive analysis. In Fur seals, maternal strategies on land and at sea (R. L. Gentry and G. L. Kooyman eds.), p 28-40. Princeton Univ. Press, Princeton, NJ.

Goebel, M. E., J. L. Bengtson, R. L. DeLong, R. L. Gentry, and T. R. Loughlin.

1991. Diving patterns and foraging locations of female northern fur seals. Fish. Bull. 89:171-179.

Hart, J. L.

1973. Pacific fishes of Canada. Bull. Fish. Res. Board Can. 180, 740 p.

Higgins, L. V., D. P. Costa, A. C. Huntley, and B. J. LeBoeuf.

1988. Behavioural and physiological measurements of maternal investment in the Steller sea lion, Eumetopias jubatus. Mar. Mamm. Sci. 4:44-58.

Hood, W. R., and K. A. Ono.

1997. Variation in maternal attendance patterns and pup behaviour in a declining population of Steller sea lions (Eumetopias jubatus). Can. J. Zool. 75:1241-1246.

Horning, M., and F. Trillmich.

1997. Ontogeny of diving behavior in the Galapagos fur seal. Behaviour 134:1211-1257.

Keating, K.A.

1994. An alternative index of satellite telemetry location error. J. Wildl. Manage. 58:414-421.

Kooyman, G. L., J. O. Billups, and D. W. Farwell.

1983. Two recently developed recorders for monitoring diving activity of marine birds and mammals. In Experimental biology at sea (A. G. Macdonald and I. G. Priede, eds.) p. 187-214. Academic Press, New York, NY.

Loughlin, T. R.

1997. Using the phylogeographic method to identify Steller sea lion stocks. In Molecular genetics of marine mammals (A. Dizon, S. J. Chivers, and W. F. Perrin, eds.), p. 159-171. Spec. Publ. 3 of the Soc. Mar. Mammal.

Loughlin, T. R, J. L. Bengtson, and R. L. Merrick.

1987. Characteristics of feeding trips of female northern fur seals. Can. J. Zool. 65:2079-2084.

Loughlin, T. R., and R. L. Merrick.

1989. Comparison of commercial harvest of walleye pollock and northern sea lion abundance in the Bering Sea and Gulf of Alaska. In Proceedings of the intornational symposium on the biology and management of walleye

pollock, Nov. 14-16, 1988, Anchorage, Alaska, p. 679-700. Alaska Sea Grant Rep. 89-01, Univ. Alaska, Fairbanks.

Loughlin, T. R., A. S. Perlov, J. D. Baker, S. A. Blokhin, and A. G. Makhnyr.

1998. Diving behavior of adult female Steller sea lions in the Kuril Islands, Russia. Biosph. Cons. 1:21-31.

Loughlin, T. R., A. S. Perlov, and V. A. Vladimirov.

1992. Range-wide survey and estimation of total number of Steller sea lions in 1989. Mar. Mamm. Sci. 83:220-239.

Loughlin, T. R., and T. Spraker.

1989. Use of Telazol to immobilize female northern sea lion (Eumetopias jubatus) in Alaska. J. Wildl. Dis. 25: 353-358.

Loughlin, T. R., and A. E. York.

2000. An accounting of the sources of Steller sea lion mortality. Mar. Fish. Rev. 62(4):40-45.

McConnell, B. J., C. Chambers, and M. A. Fedak.

1992. Foraging ecology of southern elephant seals in relation to the bathymetry and productivity of the southern ocean. Antarctic Science 4:393-398.

McCullagh, P., and J. A. Nelder.

1989. Generalized linear models, 2nd ed., 261 p. Chapman and Hall, London.

Melin, S. R.

2002. The foraging ecology and reproduction of the California sea lion (Zalophus californianus californianus). Ph.D. diss., 150 p. Univ. Minnesota, St. Paul, MN.

Merrick, R. L.

1995. The relationship of the foraging ecology of Steller sea lions (Eumetopias jubatus) to their population decline in Alaska. Ph.D. diss., 171p. Univ. Washington, Seattle, WA.

Merrick, R. L., R. Brown, D. G. Calkins, and T. R. Loughlin.

1995. A comparison of Stenersealion, Eumetopias jubatus, pup masses between rookeries with increasing and decreasing populations. Fish. Bull. 94:753-758.

Merrick, R. L., and T. R. Loughlin.

1997. Foraging behavior of adult female and young-of-the-year Steller sea lions in Alaskan waters. Can. J. Zool. 75: 776-786.

Merrick, R. L., T. R. Loughlin, G. A. Antonelis, and R. Hill.

1994. Use of satellite-linked telemetry to study Steller sea lion and northern fur seal foraging. Polar Res. 13: 105-114.

Merrick, R. L., M. K. Maminov, J. D. Baker, and A. G. Makhnyr.

1990. Results of U.S.-U.S.S.R. joint marine mammal research cruise in the Kuril and Aleutian Islands 6 June-24 July 1989. U.S. Dep. Commer. NOAA Tech. Memo. NMFS F/NWC-177, 63 p.

Pitcher, W., and D. G. Calkins.

1981. Reproductive biology of Steller sea lions in the Gulf of Alaska. J. Mammal. 62:599-605.

Porter, B.

1997. Winter ecology of Steller sea lions (Eumetopias jubatus) in Alaska. M.S. thesis, 84 p. Univ. British Columbia, Vancouver, B.C., Canada.

Raum-Suryan, K. L., K. W. Pitcher, D. G. Calkins, J. L. Sease, and T. R. Loughlin.

2002. Dispersal, rookery fidelity, and metapopulation structure of Steller sea lions (Eumetopias jubatus) in an increasing and declining population in Alaska. Mar. Mamm. Sci. 18:746-764.

Schreer, J. F., and K. T. Kovacs.

1997. Allometry of diving capacity in air-breathing vertebrates. Can. J. Zool. 75:339-358.


1984. Location and data collection system user's guide, 36 p. Service-Argos, Toulouse, France.

Sinclair, E. H., T. R. Loughlin, and W. Pearcy.

1994. Prey selection by northern fur seals (Callorhinus ursinus) in the eastern Bering Sea. Fish. Bull. 92:144-156.

Sinclair, E. H., and T. K. Zeppelin.

2002. Seasonal and spatial differences in diet in the western stock of Steller sea lions (Eumetopias jubatus). J. Mamm. 83:973-990.

Stewart, B. S., S. L. Leatherwood, P. K. Yochem, and M. P. Heide-Jorgensen.

1989. Harbor seal tracking and telemetry by satellite. Mar. Mamm. Sci. 5:361-375.

Trillmich, F., and K. A. Ono eds.

1991. Pinnipeds and El Nino, responses to environmental stress. Ecological studies 88, 293 p. Springer-Verlag, Berlin.

Vincent, C., B. J. McConnell, V. Ridoux, and M. A. Fedak.

2002. Assessment of Argos location accuracy from satellite tags deployed on captive gray seals. Mar. Mamm. Sci. 18: 156-166.

Werner, R., and C. Campagna.

1995. Diving behaviour of lactating southern sea lions (Otaria flavescens) in Patagonia. Can. J. Zool. 73:1975-1982.

Manuscript approved for publication 29 October 2002 by Scientific Editor.

Manuscript received 4 April 2003 at NMFS Scientific Publications Office.

Fish Bull 101:566-582 (2003).

Thomas R. Loughlin

Jeremy T. Sterling

National Marine Mammal Laboratory Alaska Fisheries Science Center, NMFS

7500 Sand Point Way, NE Seattle, Washington 98115

E-mail address (for T. R. Loughlin:

Richard L. Merrick,

Northeast Fisheries Science Center, NMFS

166 Water Street Woods Hole, Massachusetts 02543

John L. Sease

Anne E. York

National Marine Mammal Laboratory Alaska Fisheries Science Center, NMFS

7600 Sand Point Way, NE Seattle, Washington 98115
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Author:Loughlin, Thomas R.; Sterling, Jeremy T.; Merrick, Richard L.; Sease, John L.; York, Anne E.
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Date:Jul 1, 2003
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