Database
 

Thresholds Database > Population density of sea otters, North Pacific Ocea

Certainty of shift: Demonstrated
Location: Arctic, Alaska, USA, North Pacific Ocean, Alaska, Aleutian Islands
System Type: Social-Ecological
Regime Shift Category: 3a
Ecosystem Type
Algal/Sea grass beds
Spatial Scale
Landscape/Local
Type of Resource Use
Not Applicable
Number of Possible Regimes
2
Ecosystem Service
Traditionally food and fibre (fur)
Time Scale of Change
Decades
Resource Users
Traditional harvesters (Aleuts) 
Reversibility of Shift
Reversible

Background

Once distributed across the Pacific Rim, sea otters were hunted to near extinction in the 18th and 19th centuries. Less than 1000 remained by the early 1900's in the Aleutian Archipelago. A predator-prey population model is used to describe the top-down control that sea otters have in kelp forests.

Alternate Regimes

1. High density of sea otters,

Low density of macroinvertebrates (e.g. sea urchins, limpets, chitons)

High density of macrophytes, fish and harbour seals

2. No sea otters
High density of macroinvertebrates

Low density of kelp, fish and harbour seals

Fast or Dependent Variable(s)
Densities of macrophytes, seals and fish
Slow or Independent Variable(s)
Densities of sea urchins (slower) and sea otters (slowest)
Disturbance or Threshold Trigger(s)
Level of hunting of sea otters
External / Internal Trigger
External

Mechanism

Sea otters feed on macroinvertebrates, especially sea urchins, keeping their population in check. When some populations of sea otters were harvested to extinction in the Aleutian Archipelago, the macroinvertebrate populations grew unchecked. The macroinvertebrates grazed heavily on kelp leaving little food or shelter for fish, which declined in number. In turn, the harbour seals, which feed predominantly on fish, also declined in number. The threshold density of sea otters required to shift the system back to State 1 is unknown. Also, the threshold density of macroinvertebrates that can be sustained before the numbers of macrophytes, fish and harbour seals declines is unknown.

Management Decisions in Each Regime

State 1: No control on otter harvesting by Aboriginal Aleuts.

State 2: Sea otters were protected in the early 1900's. The Alaska Department of Fish and Game reintroduced animals to southern Alaska in 1968-1971.

Contact
Jacqui Meyers

Email
jacqui.meyers@csiro.au

CSIRO Sustainable Ecosystems,
PO Box 284,
Canberra ACT 2601

Keywords
empirical data, model, population harvesting, sea otters, seals, predator-prey interactions, Aleutian Islands, kelp, sea-urchins, colonization, bottom-up forces, top-down forces, recruitment, predation, Alaska, herbivores, oceans, populations

References

Estes, J. A., and D. O. Duggins. 1995. Sea Otters and Kelp Forests in Alaska - Generality and Variation in a Community Ecological Paradigm. Ecological Monographs 65, no. 1: 75-100. (E, M)

Estes, J. A., and J. F. Palmisano. 1974. Sea otters: Their role in structuring nearshore communities. Science 185: 1058-60. (E)

Simenstad, C., J. Estes, and K. Kenyon. 1978. Aleuts, sea otters, and alternative stable-state communities. Science 200: 403-11. (E)