Threats

Eutrophication

The risk of Perry Lakes experiencing severe algal blooms.

Dr Don McFarlane · Science Lead, FoPL

Photo: Ian Stewart

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>50%

Whadjuk Noongar country, the 1962 Commonwealth Games transformation, and the community stewardship story that began in 2021.

~60 kg

of phosphorus enters West Lake annually via the Herdsman Main Drain

≥50%

of the time, dissolved oxygen falls below trigger levels

Carp

confirmed in West Lake — risk of spread to East Lake via the balance pipe

What is eutrophication?

Phosphorus is the main driver of eutrophication at Perry Lakes. When levels rise too high, conditions become favourable for toxic cyanobacteria — the same blue-green algal blooms that have made Lake Monger (Galup) largely uninhabitable for birdlife in summer. Once a lake experiences a bloom, cyanobacteria leave behind cysts that make future blooms more likely. Prevention is critical.

Perry Lakes no longer overflows into the Subiaco Main Drain, which means even low concentrations of phosphorus entering the lakes can accumulate over time. Since 2023, when the Herdsman Main Drain was diverted into West Lake, phosphorus inputs have increased significantly — the drain delivers an estimated 60–100 kg of phosphorus per year.

Perry Lakes no longer overflows into the Subiaco Main Drain, which means even low concentrations of phosphorus entering the lakes can accumulate over time. Since 2023, when the Herdsman Main Drain was diverted into West Lake, phosphorus inputs have increased significantly — the drain delivers an estimated 60–100 kg of phosphorus per year.

“Eutrophication is an excess of nutrients which causes a dense growth of plant life.”

Toxic cyanobacteria (Anabaena) at Lake Galup — a situation we are working to prevent at Perry Lakes. Photo: FoPL

Current phosphorus status

How often key water-quality measures exceed safe trigger levels across both lakes and the inflowing drain. Higher percentages mean more frequent exceedance.

Analyte West Lake East Lake Herdsman Main Drain
Total P — % of time exceededTrigger 0.06 mg/L · range 0.04–43 mg/L 67% 50% 44%
Total N — % of time exceededTrigger 1.5 mg/L · range 0.4–3.4 mg/L 20% 30% 56%
Dissolved oxygen (saturation) — % below trigger 64% 50% 71%
Total dissolved solids (salinity)mg/L 638 673 469
pH 7.24 7.75 7.27

Percentage of times each analyte exceeded the 95% trigger level for freshwater toxicants (ANZG 2018). Data: 6 June 2018 – 19 December 2023. Source: Town of Cambridge. exceeds trigger   within range

The phosphorus balance

To keep phosphorus levels stable, FoPL needs to remove as much phosphorus as enters the lake each year — approximately 100 kg. The most practical way to do this is by harvesting aquatic plants like bulrush (Typha) and water fern (Azolla), which naturally absorb phosphorus as they grow.

Other contributing factors

Carp disturbance

Bottom-feeding carp stir up lake sediments and remobilise stored phosphorus back into the water column, increasing bloom risk. Electrofishing management is required to keep numbers down.

Microcystis forms its telltale red scum at Lake Jualbup, Shenton Park. Photo: FoPL

Reed encroachment

Bulrush and water-fern growth, fuelled by excess nutrients, reduces the open water that waterbirds depend on. Harvesting this plant material also removes phosphorus from the system.

Bulrush (Typha) encroaching on open water at West Lake. Photo: FoPL

Possible solutions

A combination of management actions, applied together, can hold phosphorus in balance and reduce the risk of a toxic bloom.

  1. Harvest and remove plant material — bulrush (Typha) is the most suitable. At least 100 kg of phosphorus must be removed annually to maintain the status quo.
  2. Adjust pumping rates so part of each lake dries each autumn, allowing oxidisation and phosphorus loss through the aquifer.
  3. Plant vegetation that shades the lake — toxic algae grows faster in warm, sunlit water.
  4. Reduce phosphorus additions to turf around the lakes, including Alderbury Reserve.
  5. Add crushed limestone and/or ironstone gravel to inlet areas of West and East Lake to remove phosphorus on entry.
  6. Ensure streets in the Subiaco Main Drain catchment are swept several times each year.
  7. Remove carp through electrofishing to reduce sediment disturbance and phosphorus remobilisation.
  8. Consider additions of PhosLock™ when phosphorus levels become excessive or when a bloom occurs.
  9. Investigate pumping nutrient-rich water from East Lake into the Subiaco Main Drain inlet.

Further reading

A combination of management actions, applied together, can hold phosphorus in balance and reduce the risk of a toxic bloom.

  • Australian and New Zealand Government (2018). Guidelines for fresh and marine water quality. waterquality.gov.au
  • GHD (2019). Perry Lakes Environmental Baseline Assessments: Baseline Surface Water and Sediment Quality. Report to the Town of Cambridge.
  • McFarlane, D., Bourke, S. and de Castro Tayer, T. (2019). Hydrochemical implications of wetland drying and augmentation options at Perry Lakes. Report to the Town of Cambridge.

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