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Water for the environment can be used to manage water levels in Reedy Lake and Hospital Swamps, which connect to the Barwon River. The environmental entitlement for the lower Barwon wetlands does not provide access to water held in storage. Instead, it allows water to be diverted from the Barwon River into Reedy Lake and Hospital Swamps when river levels are above 0.7 m AHD. High water levels in the Barwon River can also result in the natural wetting of the wetlands.

Proportion of water entitlements in the Lower Barwon Wetlands held by private users, water corporations and environmental water holders on 30 June 2020

Traditional Owners
Environmental water holder

System map

Environmental watering objectives in the Lower Barwon wetlands

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Provide habitat for fish breeding and growth and improved conditions for migration and dispersal when wetlands are connected to the Barwon River

Reduce carp populations
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Provide suitable feeding and breeding habitat for waterbirds, including mudflats and shallow water for wading birds, flooded vegetation and wetland fringes

Maintain waterbird breeding events
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Increase the waterbug population and its biomass
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Provide flushing inflows to remove accumulated salts

Maintain surface water and groundwater interactions
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Increase the diversity of ecological vegetation communities in the wetlands and increase the recruitment of aquatic vegetation

Increase the growth and extent of coastal saltmarsh, herbfields and lignum shrubland ecological vegetation communities

Retard colonisation of tall reed in low-lying areas and increase open-water habitat

Provide varying water levels and conditions to promote soil salinisation and support the persistence and growth of threatened, salt-dependent ecological vegetation communities

Environmental values

Reedy Lake and Hospital Swamps form part of the internationally recognised Port Phillip Bay (Western Shoreline) and Bellarine Peninsula Ramsar site, which is used by many thousands of migratory birds from around the world. The wetlands support 47 known threatened plant and animal species and communities. These include some of Victoria’s rarest species (such as the brolga, orange-bellied parrot, Australasian bittern, growling grass frog, Australian grayling and dwarf galaxias) and subtropical and temperate coastal saltmarsh communities. Reedy Lake also supports a range of vegetation communities, including coastal saltmarsh, herbfields and reed beds.

Reedy Lake was naturally a partly ephemeral system, but river regulation meant the lake was nearly permanently wet from the 1970s until 2016. This long-term wetting resulted in a decline in biodiversity, so wetting and drying regimes are now recommended to maintain the lake’s ecological character and diverse habitats.

Following a four-year (2016-17 to 2019-20) watering regime trial at Reedy Lake, the Lower Barwon Review in 2020 proposed to implement a long-term, seasonally adaptive water regime that avoids complete drying. At Reedy Lake, this means having the wetland full for a quarter of all years and having a partial drawdown in summer and autumn in three-quarters of all years. The review’s recommendations informed 2023-24 watering actions and future directions.

Hospital Swamps comprises five wetland basins that support important ecological processes and significant ecological values, including large areas of threatened coastal saltmarsh and diverse waterbird communities. Hospital Swamps has retained a more natural wetting and drying pattern. As a result, the swamp’s vegetation community has remained largely unchanged since the 1980s.

Traditional Owner cultural values and uses

The Corangamite CMA works with the Wadawurrung Traditional Owners Aboriginal Corporation (WTOAC) during the development of plans to deliver water for the environment for the lower Barwon wetlands. This is part of an ongoing conversation to respect and incorporate Wadawurrung knowledge and culture in decision-making, with the aim of meeting watering requirements for culturally significant species.

In early 2023, a meeting was held between the Corangamite CMA and WTOAC to discuss the proposed 2023-24 management of environmental flows in the lower Barwon wetlands. WTOAC supports the proposed watering.

WTOAC is a member of the Lower Barwon Community Advisory Committee.

WTOAC released Paleert Tjaara Dja Let’s make Country good together 2020 – 2030 Wadawurrung Country Plan in 2020. Important cultural values and recommendations identified for the lower Barwon wetlands include:

  • culturally significant wetland species such as porronggitj (brolga), toolim (black duck), kunuwarra (black swan), buniya (short-finned eel), tark (common reed) and bal-yan (bull rush)
  • recognition of wetlands as meeting, ceremony and trade places
  • maintaining water holes and refuge pools
  • maintaining access to culturally important story places and ceremonial places
  • protection of artefact sites
  • use of appropriate Wadawurrung language for places of cultural importance
  • increased opportunities for the Wadawurrung to be involved in monitoring and evaluation activities
  • inclusion of the Wadawurrung in all communication about releases of water for the environment and other wetland-related activities.

Paleert Tjaara Dja acknowledges the special place Reedy Lake and Hospital Swamps have in Wadawurrung Dreaming: “The chain of ponds from the Barwon River to Reedy Lake, Hospital Lake, Lake Connewarre and Estuary Bay is connected through water and our Connewarre (Black Swan) Dreaming”.

Social, recreational and economic values and uses

In planning the potential environmental watering actions in Table 3.7.3, the Corangamite CMA consulted widely with stakeholders to ensure it considered shared benefits, including social, economic and recreational values relevant to environmental flows management in the lower Barwon wetlands. Opportunities for social, recreational and economic values and uses are incorporated into planning and watering decisions if they do not compromise environmental outcomes.

Expert advice (such as the 2012 environmental flows study for the lower Barwon wetlands and the 2020 Lower Barwon Review) emphasised that the entire lower Barwon recommended watering regime – providing a fill to the wetlands and allowing water levels to draw down at the right times – would have to be implemented to improve biodiversity and protect the long-term health of the wetlands. This may mean it is not possible to meet some community expectations for shared benefits that don’t maintain or improve environmental outcomes. However, the Corangamite CMA, where possible, manages water levels in the wetlands to meet ecological requirements and also support a range of social, economic and recreational values and uses, including:

  • water-based recreation (such as boating, duck hunting and fishing)
  • wetlands recreation and amenity (such as birdwatching and spending time outdoors)
  • community events and tourism (such as community events and Traditional Owner events)
  • socioeconomic benefits (such as commercial fishing). The Corangamite CMA works with its community advisory group and stakeholders and seeks to accommodate their interests where possible while maintaining the overall health of the wetlands.

Scope of environmental watering

The term ‘environmental watering’ refers to the active delivery of water for the environment to support particular environmental objectives by altering the flow in a river or the water level in a wetland. While other terms are also used to describe the delivery of water for the environment, ‘environmental watering’ is deliberately used here and in seasonal watering statements to ensure consistency in the legal instruments that authorise the use of water for the environment in Victoria.

Table 3.7.3 describes the potential environmental watering actions in 2023-24, their expected watering effect (that is, the intended physical or biological effects of the watering action) and the longer-term environmental objectives they support. Each environmental objective relies on one or more potential environmental watering actions and their associated physical or biological effects.

Table 3.7.3 Potential environmental watering actions, expected watering effects and associated environmental objectives for the lower Barwon wetlands

Potential environmental watering action

Expected watering effects

Environmental objectives

Reedy Lake

Autumn/winter/spring fill (April to November) and top-ups as required (year-round) (targeting 0.8 m AHD)

  • Maintain a mosaic of water depths and resources across the wetland to support waterbird breeding events
  • Inundate fringing wetland vegetation to provide foraging habitat for waterbirds
  • Maintain a sufficient depth of water around wetland vegetation to provide fish breeding habitat
  • Temporarily inundate the outer edges of the wetland to initiate the growth and recruitment of diverse vegetation communities while permanently inundating the inner wetland vegetation communities
  • Allow fish to move between the river, lake and estuary
  • Stimulate waterbug communities to breed for waterbird feeding
  • Dilute soil and surface water salts and initiate the decomposition of organic matter
Fish iconPlant icon  Heron iconInsect iconWater drop iconJigsaw icon
Summer/autumn drawdown (December to May) (targeting 0.3 m AHD)
  • Dry out wetland fringing vegetation to reduce potential waterlogging of saltmarsh communities to support germination
  • Expose mudflats and margins to provide feeding habitat for wading/ migratory waterbirds
  • Manage reed colonisation of low-lying areas by allowing drying and saline groundwater intrusion to reduce reed growth
  • Support a drying phase for vegetation communities that require drying to grow and recruit
  • Restrict carp movement and access to habitat
  • Allow vegetation to decay and soils to oxidise and release nutrients to improve lake productivity and maintain biogeochemical processes
  • Enable surface water/groundwater interaction by allowing saline groundwater to discharge to the wetland bed

Fish iconPlant iconHeron iconJigsaw icon

Hospital Swamps

Autumn/winter/spring fill (April to November) and top up as required (year- round) (targeting 0.5 m AHD)

  • Maintain a mosaic of water depths and resources across the wetland and inundate various vegetation communities and create nesting, breeding and feeding opportunities for waterbirds, fish and waterbugs
  • Increase water levels to trigger fish spawning and waterbird breeding; high water levels will allow fish to access the wetland from the river
  • Increase freshwater to dilute the salt in the soil and surface water over winter
  • Initiate the decomposition of organic matter
  • Inundate the outer edges and margins to initiate the growth and maintain the condition of important wetland vegetation communities

Fish iconPlant iconHeron iconInsect iconWater drop iconJigsaw icon

Summer/autumn drawdown (December to May) (targeting 0.1-0.3 m AHD)

  • Dry out the wetland fringing vegetation and expose mudflats and margins to support the feeding of wading/migratory waterbirds
  • Manage reed colonisation of low-lying areas by allowing drying and saline groundwater intrusion to reduce reed growth
  • Support a drying phase for vegetation communities that require drying to grow and recruit
  • Restrict carp movement and access to habitat
  • Allow vegetation to decay and soils to oxidise and release nutrients to improve lake productivity and maintain biogeochemical processes
  • Enable the interaction of surface water and groundwater by allowing saline groundwater to discharge to the wetland bed

Fish iconPlant iconHeron iconJigsaw icon

Page last updated: 01/07/22