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Volume 11 Pages 1 - 57 (April 1995)

Citation: Jameson J.R. (1995) Some Preliminary Observations on the Foraging of Sea Otters off the Outer Coast of Washington State, USA . IUCN Otter Spec. Group Bull. 11: 7 - 9

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Some Preliminary Observations on the Foraging of Sea Otters off the Outer Coast of Washington State, USA

J.R. Jameson

Wildlife Biologist (Research), National Biological Service, 200 SW 35th Street, Corvallis, OR 97333, USA

Abstract: Since reintroduction of sea otters began in 1969 off the Olympic Peninsula of Washington State, USA, the population has increased to 360. We begun studying the natural history of this populaton in Summer 1994. This paper presents some of our findings on foraging behaviour and food habits. Clams and crabs predominate, with the addition of snails. Mean dive times of about 56 seconds for females and 68 seconds for males were found, with 89% of dives successfully obtaining prey. Prior to 1995 this area has received little predation pressure from sea otters, and we anticipate seeing a very different array of prey items at the new site.

INTRODUCTION

In 1969 and 1970 a total of 59 sea otters (Enhydra lutris kenyoni) (Kenyon, 1969; Wilson et al. 1991) was released off the west coast of the Olympic Peninsula of Washington State (Jameson et al. 1982); all had been translocated from Amchitka Island, Alaska. In 1969 the otters were released directly to the open ocean which resulted in the death of at least 16 individuals. Mortality was probably higher because some carcasses undoubtedly went undiscovered. In 1970 release procedures were changed, and the 30 otters were allowed to acclimate for several days in floating pens prior to release. All were liberated in excellent condition. Thus, the initial nuclear population in Washington could never have been larger than 43 otters and may have dropped to less than 10 individuals by the early 1970's. No surveys were conducted to assess the success of this translocation until 1977 (Jameson et al., 1982, 1986). Since then, however, the population has grown at an average rate of about 16% yr-1. In August of 1994 360 otters were counted during the annual survey.

The National Biological Service in cooperation with the Washington Department of Fish and Wildlife began a study of the natural history of the Washington population in summer 1994. Data have been collected on time/activity budgets, reproduction, movements, and foraging. In this report I want to briefly present some of our findings on foraging behavior and food habits. Much of the information is still preliminary and subject to modification as additional data are collected. The project is scheduled to last for 3 years from the beginning date in July 1994.

METHODS

During the period from 8 June to 20 July 1994, 21 sea otters were captured on the outer coast of Washington’s Olympic Peninsula, 7 independent females (6 adult and 1 subadult) and 9 independent males (7 adult and 2 subadult). Five pups were also taken, 3 females and 2 males. All otters were weighed and when an individual was anesthetized several morphometric measurements, blood samples and a premolar were collected. Most were marked with PIT tags, and all but small pups were tagged with plastic flipper tags. Radio transmitters were implanted in 17 individuals.

Foraging data were collected by observing focal animals with 50-80X telescopes and binoculars. Observation bouts continued as long as the focal animal could be seen. Data recorded included dive time, surface time, prey item, and prey number. Prey items were grouped by taxa and summed over all records. Results are presented as percentages of total number of foraging dives and total number of prey items (Table 1). When possible, instrumented otters were selected for observation, but when none were in the observation area data were collected from unmarked animals. Mean dive times were calculated for each sex and age class (Table 2).

RESULTS

Over 4000 foraging dives were observed and over 10000 prey items noted during the period (Table 1). Data were analyzed by frequency of occurrence and by number. Bivalves predominated in both analyses at 34% and 29% respectively. Crabs were next by occurrence, and snails were the third most frequently occurring prey item. However, when analyzed by number the ranking changes with crabs ranking third, sea urchins fourth and snails second just below bivalves. This is because sea otters often capture more than a single item when feeding on snails and urchins. Unidentified prey predominated in every analysis. This category is comprised of items too small or too nondescript to be identified accurately.

Table 1: Summary of sea otter foraging data collected in Washington, summer 1994.
Data are grouped by major taxonomic group
Group Occurence Prey number Prey not counted Prey number + prey not counted Percent occurence Percent by number Percent prey number + prey not counted

Bivalve 1364 2657 182 2839 33.85 29.18 28.01
Crab 461 661 50 711 11.44 7.26 7.02
Snail 431 2603 53 2656 10.70 28.58 26.21

Gumboot Chiton

70 73 0 73 1.74 0.80 0.72

Sea Urchin

65 293 11 304 1.61 3.22 3.00

Worm

41 62 10 72 1.02 0.68 0.71

Sea Star

18 18 0 18 0.45 0.20 0.18

Sea cucumber

7 7 0 7 0.17 0.08 0.07

Kelp

2 2 0 2 0.05 0.02 0.02

Unidentified Prey

1569 2720 722 3452 38.94 29.98 34.06

Octopus

1 1 0 1 0.02 0.01 0.01

Total

4029 9107 1028 10135 100.00 100.00 100.00

Clams, crabs, snails and small unidentified items account for 95% of the prey by occurrence, and number. Therefore, at least by the measure used here, most of the remaining items are of little importance to sea otters in Washington. Only one Octopus spp. was observed in our sample; but, we have noted several times, incidental to other work, sea otters feeding on large octopus.  These may take an hour to consume and sometimes are not completely eaten before the feeding individual becomes sated. The importance of octopus is probably under estimated in our sample.

Dive times were analyzed for all age classifications except pups (Table 2). The mean grouped dive time for females was 56.1 seconds (SE = 0.34), and 58.8 (SE = 1.07) for grouped males. Adult females spent an average of 57.4 (SE = 0.38) seconds submerged when foraging, only slightly more than grouped females. Adult males spent 71.1 (SE = 3.11) on an average foraging dive somewhat longer than the group mean. Subadult females spent 44.5 (SE = 1.11) seconds on an average dive about 12 seconds less than adults. Subadult males were submerged an average of 55.8 (SE = 1.05) about 15 seconds less than adult males.

Table 2: Analysis of dive times (in seconds) for foraging sea otters in Washington, summer 1994
 

Mean

Number of
Dives

Standard
Deviation

Standard
Error

Maximum

Minimum


all female

56.1

5109

24.56

0.34

307

3

all males

58.8

637

27.00

1.07

181

3

 

adult females

57.4

4229

25.22

0.38

307

3

adult males

71.1

127

35.15

3.11

181

16

 

subadult females

44.5

215

16.28

1.11

83

5

subadult males

55.8

510

23.59

1.05

107

3

 

juvenile female

48.2

74

14.34

1.67

74

17

             

all sea otters*

56.5

5855

24.8

0.32

307

3


* includes 109 records where sex was unknown


DISCUSSION

Bowlby et al. (1988) present data on sea otter foraging in the same general area where our data were collected. No major differences in prey consumed were noted between studies. Clams, and crabs predominated in their study as they did in the current study. The notable exception is the abundance of snails observed in this study and the absence of snails in Bowlby et al. (1988). We do not know whether this reflects a change in food habits since the 1988 study or a difference in data collection methods.

Mean dive times calculated for this study are similar to those presented by Bowlby et al. (1988) even though their sample sizes were much smaller. Ages were not determined in their study, but the average dive time for females was 56.8 (SD = 32.4) seconds and in this study 56.1 (SD = 24.6). Interestingly, the mean foraging dive calculated by Bowlby et al. (1988) for males of 68.6 (SD = 28.3) is similar to the value for adult males in this study. Sea otters in both studies successfully obtained prey on 89% of foraging dives. We will concentrate foraging effort in 1995 in a new area just recently occupied by sea otters. Prior to 1995 this area has received little predation pressure from sea otters, and we anticipate seeing a very different array of prey items at the new site.

REFERENCES

Bowlby, C. E., Troutman, B. L. and Jeffries, S. J. (1988). Sea otters in Washington: distribution, abundance, and activity patterns. Final Report. Washington Department of Wildlife, Marine Mammal Investigations, Tacoma. 133 pp.
Jameson, R. J., Kenyon, K. W., Johnson, A. M. and Wight, H. M. (1982). History and status of translocated sea otter populations in North America. Wildl. Soc. Bull. 10: 100-107.
Jameson, R. J., Kenyon, K. W., Jeffries, S. J. and VanBlaricom, G. R. (1986). Status of a translocated sea otter population and its habitat in Washington. The Murrelet 67: 84-87.
Kenyon, K. W. (1969). The sea otter in the eastern Pacific Ocean. N Am. Fauna 68: 1-352.
Wilson, D. E., Bogan, M. A., Brownell, R. L. Jr., Burdin, A. M. and Miminov, M. K. (1991). Geographic variation in sea otters, Enhydra lutris. J. Mammal. 72: 22-36.

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