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Draft Proposals Paper - Full - Victorian Environmental Assessment ...

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Levee banks<br />

The third issue is levee banks for flood mitigation.<br />

Throughout the Investigation area there are numerous<br />

levee banks, used to manage or mitigate flooding, mostly<br />

on private land but some also located on public land.<br />

Many, including both those located on private and public<br />

land are in need of major maintenance or upgrade to<br />

remain effective. Many of these levee banks (such as along<br />

the Old Mail Road in the Lindsay–Wallpolla area and in the<br />

lower Goulburn River area) either impede water<br />

movement across the floodplain or are in disrepair. Where<br />

levees are in disrepair, there should be an assessment of<br />

whether the structures are still required or in fact could be<br />

removed or constructed in an alternative manner, thereby<br />

achieving greater spatial coverage during flooding events.<br />

Management of flooding at the boundaries of private and<br />

public land could be managed without levees and<br />

facilitate the greater floodplain connectivity through the<br />

use of special area plans under the Catchment and Land<br />

Protection Act 1994 and environmental overlays under the<br />

Planning and Environment Act 1987.<br />

Salt accumulation on the floodplains<br />

The final issue is salt accumulation in the floodplain soils<br />

where the groundwater is shallow. This salt accumulation<br />

has increased as a result of shallower groundwater levels<br />

from irrigation and native vegetation clearing. Tha salt<br />

levels were kept in check naturally by flooding and rainfall<br />

but with a decline in both the rate of salt accumulation in<br />

the Lindsay-Wallpolla area has led to significant areas of<br />

degraded vegetation. Salt accumulation coupled with lack<br />

of flooding and drought conditions is showing visible signs<br />

progressively up the River Murray.<br />

Summary of environmental water issues<br />

In summary VEAC believes that decision making processes<br />

involved in determining environmental flow events for the<br />

protection of the unique riverine ecosystems should be<br />

undertaken in the context of the following framework.<br />

<strong>Environmental</strong> flow allocations be determined in the<br />

context of clearly stated ecological objectives at a regional<br />

and River Murray scale and be informed by:<br />

• an understanding of the natural water regimes with<br />

respect to volume, seasonality, annual variability and<br />

duration conditions<br />

• ecosystem values and maintenance of those values<br />

rather than the requirements for environmental<br />

restoration works such as flushes for blue-green algae or<br />

salinity management or to support public land resource<br />

utilisation industries.<br />

The arrangements or processes through which these<br />

considerations are addressed should be:<br />

• based on rigorous, transparent and scientifically based<br />

methodology, including water accounting practices that<br />

are freely available to the public<br />

• flexible and adaptable to enable changes to be<br />

introduced when increased information and<br />

understanding becomes available and climate change<br />

impacts require addressing<br />

• based on a delivery system that is compatible with<br />

ecological objectives and attempts to minimise energy<br />

inputs or extensive infrastructure.<br />

RECOMMENDATIONS<br />

<strong>Environmental</strong> water<br />

R10<br />

R11<br />

R12<br />

R13<br />

R14<br />

R15<br />

R16<br />

R17<br />

That the environmental outcomes for the Investigation sought through the public land category system are<br />

dependent on a volume of water in the order of 4000 gigalitres for a floodplain inundation event at least<br />

every five years.<br />

That an Investigation area wide environmental flow strategy be developed with the objective of achieving<br />

an integrated and consistent approach to environmental flows across the River Murray area, its <strong>Victorian</strong><br />

tributaries and the key wetlands of Kerang Lakes, Corop Wetlands, Boort Wetlands and Kanyapella Basin<br />

described in Chapter 3.<br />

That the improvement of the information and knowledge base of the River Red Gum forests and their<br />

ecosystems and wetlands, hydrology and the river as a system, and in particular the use of models to<br />

integrate this information, be given a high priority and for this information and knowledge be readily<br />

available to the community.<br />

That sufficient resources be allocated as a matter of highest priority for the development of a detailed<br />

environmental water accounting system across the entire Investigation area.<br />

That land and water managers develop a suite of non-engineering options to mitigate the causes of<br />

summer flooding in Barmah forest.<br />

That the relevant agency conducts an audit of existing levee banks in the Investigation area and where<br />

appropriate remove those levees in disrepair or seek alternative structures to facilitate greater dispersal of<br />

flood waters across floodplains; and where this is deemed necessary land and water management agencies<br />

undertake an extensive consultation process with private land holders and relevant public land managers.<br />

That where changes to water supply infrastructure are likely to occur in the future then environmental<br />

flows should not be adversely affected and additional costs associated with the provision of environmental<br />

flows be borne by the whole community.<br />

That where potential opportunities exist, special area plans and the statutory planning processes be applied<br />

as management tools to more effectively manage environmental flows for ecological outcomes at the<br />

interface between public and private land.<br />

14 River Red Gum Forests Investigation July 2007

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