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Trin Warren Tam-boore wetland | City of Melbourne Urban Water

Trin Warren Tam-boore wetland

Royal Park

The Trin Warren Tam-boore wetland has been constructed in Royal Park, four kilometres north of Melbourne’s central city. The five-hectare wetland takes stormwater from surrounding suburbs, cleans it, and stores it to irrigate the park.


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Spanning 170 hectares, Royal Park is the largest and most unique parkland in inner city Melbourne. Set aside as a reserve in 1845, Royal Park is known for its remnant native landscapes, wide variety of sports fields and large spaces for recreation. It plays an important role in ensuring that indigenous flora and fauna are retained in the inner city. This includes the endangered skink population in the park’s west.The system consists of two linked ponds or wetlands – an S-shaped treatment wetland and a larger storage wetland. Completed in 2006, it was upgraded in 2008 to include an additional five megalitre storage tank underneath Ross Straw Field.

The Commonwealth Government funded the wetland as an environmental initiative for the 2006 Commonwealth Games. Melbourne Water also provided funding through the Living Rivers program.

What benefits has the wetland and stormwater harvesting system provided?

  • Reduced stormwater pollutant and runoff levels entering Moonee Ponds Creek and Port Phillip Bay. Monitoring shows that the system is exceeding expectations for pollutant and sediment removal.
  • Reduced reliance on drinking water for irrigation. The system provides up to 160 megalitres of stormwater per year, or 89 per cent of the park’s irrigation needs.
  • Created a variety of different habitats, which has resulted in greater biodiversity.
  • Enabled sports fields to remain green all year round, which has enhanced community health and wellbeing.
  • Created a space for community enjoyment and recreation. Boardwalks, footpaths and interpretive signage have allowed people to connect with the landscape.

 

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Wetlands

Project location

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Project details

How does the system work?

The wetland takes stormwater from surrounding suburbs and processes it to Class A standard – safe for human contact but not drinking.

Water is diverted from Brunswick Creek before in enters the main drain under the wetland. As the water slows down before being diverted, sediment and litter drop out and are retained in a sediment pond. The water then flows into the shallow S-shaped treatment wetland. This treatment wetland tracks the water slowly through 70,000 aquatic plants.

The plants, microorganisms living on their stems and the pond sediment all treat the stormwater by absorbing nitrogen and other pollutants. The treated water flows through pipes under Oak Street into the storage wetland. Water to be used for irrigation is passed through an ultra violet disinfection unit. The excess is returned to the drainage system, which flows under the Tullamarine Freeway into Moonee Ponds Creek.

 

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Timeline

Royal Park Master Plan proposes wetland 1984
Master Plan includes stormwater harvesting system 1997
Concept designs 2004
Construction 2005-06
Testing and commissioning 2006
Construction of additional tank 2008
Irrigation network expansion 2010

Project Partners

This was a large-scale project that required a range of skills and consultants to complete. In addition to in-house experts at the City of Melbourne, we worked with external designers, engineers and landscape architects to complete this project. We also worked closely with our funding partner, Melbourne Water.

Cost

Total: $8,140,000 over six years, including several upgrades to the system

Wetlands: $5,140,000

Underground tanks at Ross Straw Field: $1,800,000

Irrigation network expansion: $550,000

Wetlands pumping station upgrade and additional tank at McPherson Oval: $650,000

PLANNING AND DESIGN

Research

Master Plan

The Royal Park Master Plan was completed and endorsed by the City of Melbourne in 1997. It recommended the construction of a wetland system in the west of the park to provide a reliable water source for irrigating the sports fields. The Master Plan also noted that creating the wetlands would increase amenity and restore indigenous vegetation.

Soil contamination assessment

Soil contamination testing was undertaken and revealed asbestos. Removing the asbestos caused delays and increased the cost of the project.

MUSIC modelling

Undertaken by the Ecological Engineering as part of their conceptual design for the Commonwealth Games Village

Community consultation and participation

Constructing a wetland in Royal Park was a significant change in the land use, so we carried out extensive consultation. The Royal Park Master Plan Implementation Advisory Committee, carried out the consultation. The Committee included City of Melbourne staff, stakeholders and community members. It met regularly with the Environment Protection Authority, Melbourne Zoo, the Office of Commonwealth Games Coordination and Melbourne Water.

After the construction was complete, we invited the community to help plant the vegetation in the wetland.

 

This wetland concept drawing was used during community consultation.

This wetland concept drawing was used during community consultation.

Design challenges and constraints

To improve the ecology and biodiversity of the area

By constructing a wetland as the stormwater treatment and storage method, we have actually improved the local environment. The diversity of habitat in the wetlands supports a variety of plants and animals.

To create a visually appealing landscape that provides for education and recreation

The site is very close to the 2006 Commonwealth Games athlete’s village. This heightened the focus on creating a space that provides amenity as well as showcasing the Australian environment. Royal Park is a heavily used recreational area, so we also had to make sure this area was not reduced.

Constrained footprint

The wetland had fit within the footprint of the pre-existing sporting oval, and we needed to keep the mature gum trees around the oval. Under the oval was the existing main drain that connected the open Brunswick Creek to the Moonee Ponds Creek. We needed to cover the drain, so we placed the main storage pond on top of it.

 

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Careful design can minimise maintenance and operational costs

The wetland system has been designed to maximise the use of gravity for water flow, reducing the need for pumps. Pumps have a running cost associated with electricity use and also require maintenance over time. To reduce the cost of waste disposal, sediment taken out of the sediment pond during cleaning is dried on site before being transferred to a waste management facility.

SYSTEM COMPONENTS

Diversion weir and silt trap

Stormwater is diverted from the Brunswick Creek via an underwater diversion pipe in the weir wall. As the water slows down before being diverted, sediment and litter drop out and are retained in a sediment pond. The water gathers in front of the weir. The decrease in speed allows larger sediment to settle out. A trash rack also captures larger floating litter. Larger flows go over the weir and continue down the pre-existing main drain into the Moonee Ponds Creek.

The trash rack is inspected regularly to ensure that large debris is not blocking the water flow or adding pollution to the water. Additional inspections are carried out following major storms because there is a greater likelihood of blockages caused by debris at these times.

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Treatment wetland

Size: 0.8 hectares

Depth: 0.15 metres to 1.5 metres

Plants: indigenous ephemeral wetland plants

The S-shaped wetland is the main treatment element in the stormwater harvesting system. Water flows from the diversion point and passes through the wetland, where sediments continue to drop out or are trapped by the vegetation and removed by the microorganisms.

The S-shape has been designed to gain the maximum flow distance for the water while keeping the system’s footprint to a minimum. The design replicates a billabong, with footbridges for pedestrians.

These tasks are performed regularly to maintain stormwater wetland and storage efficiency:

  • Removal of floating debris
  • Removal of invasive plant species and weeds
  • Control of pests
  • Maintaining clear drain and pipe openings
  • Removal of sediments and solids.

We also seek specialist advice regularly to assess the performance and wellbeing of the wetland plants.

Stormwater is cleaned as it flows through the plants in the S-shaped treatment wetland.

Stormwater is cleaned as it flows through the plants in the S-shaped treatment wetland.

Storage wetland

Storage volume: 13.4 mega litres

Depth: maximum 1.85 metres (useable depth 1.3 metres)

Plants: Indigenous wetland and ephemeral plants

The storage wetland is significantly larger than the treatment wetland because it stores the treated water. The design is based on an open water lagoon and contributes greatly to the biodiversity in the area.

The storage wetland is excavated during construction

The storage wetland is excavated during construction

Tank

Location: underneath Ross Straw Field, south of the wetlands

Storage volume: five megalitres

Type: Stormtech system with yellow drainage arches and Scoria rock fill

Maintenance: The tank needs infrequent inspection because the inflow water from the treatment wetland is so clean.

The additional storage tank was added in 2008 to increase the total capacity of the system.

Ross Straw underground tank construction1

The underground storage tank during construction

Ross Straw underground tank construction2

The underground storage tank is filled with arches and scoria for structural stability. This is a cost-effective method for storing water underground.

 

Pumps

Five pumping stations move water around the system. The first pump station is located on Manningham Street, at the southern end of the storage wetland. This station takes treated water from the wetland and delivers it to McPherson Baseball Field, Ross Straw Field and to the Oak Street tank refill hydrant.

The first pump station contains:

  • Three centrifugal pumps (single-stage pumps with 3-phase electric motors and bronze impellers)
  • A hydrostatic level sensor to ensure that when the storage wetland reaches the minimal drawdown level the pumps shut down
  • A pH sensor
  • Electrical Conductivity (EC) salinity sensor to monitor water quality and shut down the pumps if required
  • Turbidity sensor
  • Ultra violet unit to disinfect water before it is used for irrigation, with a capacity of 114,000 litres per hour.

 

The second pump station is located at Ross Straw Field and distributes water through the irrigation network, via a vertical multistage pump.

The third pumping station is at the McPherson Baseball Field. It delivers irrigation water to:

  • The golf course
  • Northern sports fields in the park (Western Oval, Ransfield Oval, Ryder Oval and McAllister Oval)
  • Brens Oval, Smith Oval, Walkers Oval and Poplar Oval storage tanks for night time irrigation.

 

The fourth and fifth pumping stations operate the nightly irrigation in the north and south sections of the park, and transfer water to the trees along Royal Parade.

UV disinfection unit and pumps inside the pump room.

UV disinfection unit and pumps inside the pump room.

Irrigation network

An extensive underground irrigation network transports treated stormwater from the storage wetland to a number of smaller tanks throughout Royal Park. The reticulated PVC pipework is divided into two systems, north of the tram line and south of the tram line.

For health reasons, irrigation with recycled water can only occur at night, so the water is transferred through the network during the day and stored in smaller tanks until night. By gradually transferring water to different sections of the park throughout the day, flow rates through the system are maximised.

The irrigation network operates automatically and is controlled by a central system. Our  maintenance teams monitor the central system via remote terminals (mobile devices or laptops). They alter irrigation schedules and check live water quality data from the on-line testing units.

Royal Park irrigation network

Areas irrigated by the Trin Warren Tam-Boore wetlands

Construction image gallery

 

ONGOING MANAGEMENT

Testing and Commissioning

Once construction was complete, we tested that all elements in the system were functioning correctly and fixed any problems. Some of the problems that arose during testing are listed below.

Ducks eating the vegetation during establishment.

To solve this problem, we grouped sensitive plants under netting to allow establishment in the first six months.

Plants were drowning during establishment.

To address this, we kept the water level lower than the design level by not inserting the outlet control baffle into the outlet structure until the second year of operation.

Access to maintain the pumps in the wet well was challenging due to the well’s depth and configuration. Maintenance was expensive and risky.

The solution involved redesigning the system to use pumps in the pump shed external to the wet well. Pumps are now maintained with easy access in the pump shed.

We couldn’t replace the UV lamp because there wasn’t enough space between the units and the shed walls to pull out the lamps.

The system was reconfigured in the pump shed to allow the lamps to be pulled out the doorway.

Maintenance

Melbourne Water owns and maintains the sediment pond, diversion weir, trash rack, treatment wetland and storage pond.

The rising main route is walked and inspected monthly to check for leaks. If a pump continual operates or cycles (when tanks are full and no irrigation is scheduled), this may indicate a leak in the rising main.

The centralised control system is inspected daily during the irrigation season to check all sensor connections.

Pump maintenance:

  • Check pumps for any abnormal operation once per month
  • Check pumps, pipework and valves for any leaks, loose fittings once per month
  • Check for general operation of pumps once per month
  • Check pressure tank pre-charge pressure (using pressure gauge) and pressure operation (start/stop) every six months
  • Check valves for isolation performance annually
  • Check and record flow meter readings and pump settings annually.

Monitoring

During the warmer months, the centralised irrigation system is monitored daily to ensure that it is functioning correctly and all parts of the park are receiving adequate water. Every three months, the sensor connections are inspected.

During normal operation the water quality is monitored on-line for turbidity, pH and salinity. This ensures that the water is fit for irrigation. Monitoring of other water quality indicators is also conducted, with expected pollutant reductions of:

Total suspended solids: 77%

Total phosphorus: 60%

Total nitrogen: 45%

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