Database
 

Thresholds Database > Lake eutrophication, Lake Washington, USA

Certainty of shift: Demonstrated
Location: North America, United States of America (USA), Lake Washington
System Type: Social-Ecological
Regime Shift Category: 4a
Ecosystem Type
Lake
Spatial Scale
Landscape/Local
Type of Resource Use
Fisheries
Number of Possible Regimes
2
Ecosystem Service
Water quality, fishing, recreation, ecotourism
Time Scale of Change
Months
Resource Users
Fishers and the general public, industry, transportation companies 
Reversibility of Shift
Reversible

Background

Lake Washington lies parallel to Puget Sound and is separated from it by a line of hills. In 1916, the level of Lake Washington was permanently lowered, with the construction of a locked ship canal connecting the lake with Puget Sound. It is a large, deep lake (18km long and 65 metres deep).

Alternate Regimes

1. Clear water, benthic fish species and macrophytic vegetation

2. Eutrophic, blue-green algae, turbid, loss of benthic fish, transmission of typhoid to humans

Fast or Dependent Variable(s)
Plant and fish species composition, level of oxygen in the water
Slow or Independent Variable(s)
Phosphorus and nitrogen concentrations
Disturbance or Threshold Trigger(s)
Nutrient input from sewage effluent
External / Internal Trigger
External

Mechanism

High phosphorus and nitrogen input from sewage increased turbidity and density of phytoplankton and zooplankton. The level of dissolved oxygen decreased with an associated loss of benthic fish species and macroinvertebrate prey species.

Management Decisions in Each Regime

State 1: From the 1890's, untreated sewage was piped directly into Lake Washington, and by 1922, there were 30 outfalls, servicing 50,000 people. At the same time, it was also the source of drinking water for many people. In 1907, a serious outbreak of typhoid occurred.



State 2: Following a public vote, in an attempt to improve the water quality of the lake, the sewage was diverted from the lake into Puget Sound from 1958. Secondary treatment plants were established, which decomposed the organic materials, but still released inorganic nutrients. As the sewage was removed from the lake, Daphnia, which feeds on the algae, increased in number helping to remove the algal blooms as well as providing a food supply for fish. The quality of this deep, cold lake improved quickly after being flushed with low-phosphate water.



Contact
Jacqui Meyers

Email
jacqui.meyers@csiro.au

CSIRO Sustainable Ecosystems,
PO Box 284,
Canberra ACT 2601

Keywords
Pollution, biomanipulation, emprical data, model

References

Edmondson, W. T. 1991. The Uses of Ecology: Lake Washington and Beyond. U.S.A.: University of Washington Press. (E)

Carpenter, S. R., D. Ludwig, and W. A. Brock. 1999. Management of Eutrophication for Lakes Subject to Potentially Irreversible Change. Ecological Applications 9, no. 3: 751-71. (M)