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manage water and water flows

 

Much of the environmental damage in the Hunter River estuary has been due to past practices which have altered water flows across the floodplain. Managing water on the floodplain and protecting threatened species are central to improving the environment at Kooragang Wetlands. While we create freshwater ponds and block flows into or out of some areas that are particularly important for the conservation of threatened species, most of our water and water flow management involves:

 

removing culverts

In a number of tidal creeks on Ash Island, we replaced constricting culverts (pipes) with bridges. This restored tidal flows in the creeks and increased the extent and vigour of mangroves along them. The effect on saltmarsh depended largely on the lie of the land. Where surrounding land was gently sloped away from the creek, saltmarsh increased in area as well. Where the creeks banks were steep, increased flows were not able to reach beyond the creek-line and saltmarsh areas were unable to expand and were sometimes even replaced by mangroves. Fish, benthic (mud dwelling) invertebrates, shorebirds and a number of other species were monitored for two years before and after the culvert removal. Numbers and variety of fish and crustaceans increased following culvert removal, while results for birds were too variable to draw any definite conclusions.


Before: Tidal flows greatly reduced by this culvert. Photo:1993

Before culvert removal: insufficient tidal flows result in very poor saltmarsh. Photo:1993

After: much greater tidal flows possible after culvert replaced . Photo:1995

After culvert removal: increased tidal flows (and cattle removal) result in mangroves & healthy saltmarsh. Photo:2001

 
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opening floodgates

Floodgates built in the Hunter River estuary have effectively stopped tidal exchange and decreased mangrove and saltmarsh vigour and extent. On our Tomago site, this loss of tidal exchange has destroyed an important high tide roost site for migratory shorebirds

Our attempts to restore our Tomago site have focussed on both restoring the migratory shorebird high-tide roost site and enhancing fisheries nursery habitat while maintaining rainwater drainage run-off from neighbouring properties and ensuring that tidal influence is contained within the project boundary.

We are working with the NSW Department of Environmental Conservation in this area. Hydrological modelling and studies have been done; a Review of Environmental Factors completed; neighbouring landholders consulted and written agreements are being sought for floodgate opening to proceed. We hope to complete the opening by June 2006.


Before: Floodgates stop tidal flows into our Tomago site.

Before: Reduced fish and prawn habitat and loss of saltmarsh high tide roost areas for migratory & local shorebirds.

Before: The area of our Tomago site where we wish to reinstate a high tide roost site for shorebirds.  Photo:2005

View of the future?: Spread of tidal waters after a floodgate flap was found open in 2003.

 
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excavating marginal pasture to create intertidal saltmarsh

Coastal saltmarsh is now listed as an endangered ecological community in NSW, and in the Hunter River estuary more than 1400 hectares has been lost in the past 50 years. As saltmarsh is valuable shorebird and fisheries habitat, we are trying to compensate for this loss by creating additional saltmarsh in previously unsuitable areas.

In 2001 we excavated 3 hectares of marginal pasture to the level of a nearby area of saltmarsh. We carefully monitored the depth to ensure the area would only be inundated by 25 percent of the tides – perfect conditions for growing coastal saltmarsh.

In two years the excavated area was almost completely covered with saltmarsh species, including seablite (Suaeda australis) and samphire (Sarcocornia quinqueflora). Most importantly shorebirds including sandpipers and black-necked storks were sighted using this new habitat.

Before: Marginal pasture  Photo: 2001

Survey stakes were used to mark depth of excavation. 

After: Three months after  excavation. Photo: 2002

After: Saltmarsh covers more than 80% of this same area three years after excavation.  Photo: 2004

In late 2003 we excavated a further 7 hectares in the same area. Three viewing mounds and a pathway around the northern edge of the saltmarsh were incorporated into the overall excavation. Monitoring by students from the University of Newcastle has shown that this excavation is also being colonized by saltmarsh species. The Hunter Bird Observers Club recently recorded 24 red-capped plovers and 27 red-necked stints running along the surface, a sure indication of the success of this saltmarsh creation.

Before: Slashed area of marginal pasture prior to excavation. Photo: 2003

Excavation to a level that only allows 1.7metre tides or greater - perfect for satmarsh.

Several ponds like this one on the right were created alongside the main excavation. These only fill with rain and are for frogs. 

Red-capped plover have given their seal of approval to the  new saltmarsh area.

 
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creating inter-tidal lagoons

The Hunter estuary is the most important site for migratory shorebirds in NSW, attracting 8-16,000 annually in the early 1970's. Loss of high tide roosting sites in the estuary is thought to have contributed to their declining numbers in the decades since then.

Sand dredged during the construction of Stockton Bridge in 1971 was called Stockton Sandspit. This later became a popular high tide roosting site for migratory shorebirds. However, by the late 1980s, the sandspit had become overgrown with woody weeds and no longer functioned as a high tide roost site.

In 1995 we removed the woody weeds and reconfigured the sandspit to make a lagoon. A weir was put in place to allow only tides greater than 1.7metres into the lagoon. Under these conditions saltmarsh flourished and many shorebirds including eastern curlew, bar-tailed godwits and red-necked avocets flocked in great numbers to the sandspit at high tide.

Before: Stockton Sandspit overgrown with woody weeds and not functioning as a high tide roosting site in 1985.

Weeds were removed and a lagoon excavated at the sandspit in 1995.

After: Stockton Sandspit attracts thousands of shorebirds at high tide during summer.

Red-necked avocets, bar-tailed godwits and sandpipers at  Stockton Sandspit. Photo: C. Herbert

 
 
  
   
    restore native vegetation