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310 River Red Gum Forests Investigation > 2006
AAV Aboriginal Affairs Victoria, a division of theDepartment for Victorian Communities
ABS Australian Bureau of StatisticsAIATSIS Australian Institute of Aboriginal and Torres
Strait Islander StudiesAEMP Asset Environmental Management Plan (for
The Living Murray Icon Sites)ANZECC Australian and New Zealand Environment and
Conservation CouncilARIER Arthur Rylah Institute for Environmental
ResearchATSIC Aboriginal and Torres Strait Islander
CommissionCAR Comprehensive, Adequate and Representative
(conservation reserve systems)CD Census Collection DistrictCFA Country Fire AuthorityCFI Continuous Forest Inventory (forest survey plots)CMA Catchment Management AuthorityCOAG Council of Australian GovernmentsCRG Community Reference Group for the River
Red Gum Forests InvestigationCSIRO Commonwealth Scientific and Industrial
Research OrganisationDBH Diameter at breast heightDCE the former Department of Conservation and
EnvironmentDCFL the former Department of Conservation,
Forests and LandsDCNR the former Department of Conservation and
Natural ResourcesDEH Department of Environment and Heritage
(Federal Government)DHS Department of Human ServicesDIIRD Department of Industry Innovation and
Regional DevelopmentDIPNR Department of Infrastructure, Planning and
Natural Resources (New South Wales)DNRE the former Department of Natural Resources
and Environment recently split into DPI, DSEand DVC
DOI Department of InfrastructureDOJ Department of JusticeDPI Department of Primary IndustriesDSE Department of Sustainability and EnvironmentDVC Department of Victorian CommunitiesDWLBC Department of Water, Land, Biodiversity and
Conservation (South Australia)ECC Environment Conservation CouncilEPA Environment Protection AuthorityESD Ecologically Sustainable DevelopmentEVC Ecological Vegetation ClassEWA Environmental Water AllocationEWG Environmental Watering GroupEWR Environmental Water ReserveFFG Flora and Fauna GuaranteeFMA Forest Management AreaFRB Fuel Reduction BurningFSD First Step DecisionGBCMA Goulburn Broken Catchment Management
Authority
GIS Geographic Information SystemGL GigalitresGMW Goulburn–Murray WaterGMZ General Management Zone in state forestsIPCC Intergovernmental Panel on Climate ChangeIUCN International Union for the Conservation of
Nature and Natural Resources now generallyreferred to as the World Conservation Union
JANIS Joint ANZECC / MCFFA National Forest PolicyStatement Implementation Sub-committee
LCC Land Conservation CouncilLGA Local Government AreaLMEWP Living Murray Environmental Watering PlanMa Millions of yearsMCMA Mallee Catchment Management AuthorityMDB Murray-Darling BasinMDBC Murray-Darling Basin CommissionMDB-IGA Murray-Darling Basin Intergovernmental
AgreementMDBMC Murray-Darling Basin Ministerial CouncilML MegalitresMLDRIN Murray-Lower Darling Rivers Indigenous
NationsMSS Municipal Strategic StatementNAP National Action Plan for Salinity and Water
QualityNCCMA North Central Catchment Management
AuthorityNECMA North East Catchment Management
AuthorityNHT Natural Heritage TrustNNTT Natural Native Title TribunalNSW New South WalesNTSV Native Title Services VictoriaPPA Pest Plant and/or AnimalPV Parks VictoriaQLD QueenslandRCS Regional Catchment StrategyRFA Regional Forest AgreementRMW River Murray WaterRRG River Red GumSA South AustraliaSAMLIV Strategy for Aboriginal Managed Land In
VictoriaSAP Special Area PlanSEA Significant Ecological Asset (under The Living
Murray initiative)SES State Emergency ServiceSFRI State Forests Resource InventorySLA Statistical Local AreaSMZ Special Management Zone in state forestSQ Site Quality (of areas in terms of forest
growth capability)SPZ Special Protection Zone in state forestTLM The Living MurrayTFN Trust For NatureVCMC Victorian Catchment Management CouncilVEAC Victorian Environmental Assessment CouncilWUP Wood Utilisation Plan
ACRONYMS
311Discussion Paper
Adaptive management. Adaptive management is asystematic process of continually improving managementpolicies and practices by learning from the outcomes ofoperational programs by employing managementprograms that are designed to compare selected policiesand practices, by evaluating alternatives about thesystem being managed.
Aeolian. Wind blown sediments such as sand dunes.
Aggradation. Accumulation or raised level of sedimentacross a floodplain, river valley or stream bed.
Alluvial. Deposited by running water.
Anabranch. A secondary channel of a river or streamthat leaves the main stream and re-joins it downstream.
Apiculture. The raising and tending of bees forcommercial or agricultural purposes.
Aquifer. A rock, gravel or sand layer that holds waterand through which water can move.
Aquatard. A rock layer that does not allow the flow ofwater.
Avulsion. A sudden change in a river course or cut-offof a meander, typically during a flood.
Bankfull. The capacity of a channel without spillingonto the surrounding floodplain.
Bank slumping. The falling or slumping of a riverbankinto the river. May occur due to removal of riparianvegetation, erosion or bank destabilisation. The term isoften used in connection with slumping resulting from arapid decrease in river height, in which water drainsmore quickly from the river than it does from the banks,which then collapse under their own weight.
Bar. Well formed ridge or deposit of sand or gravel in astream bed.
Barrage. A construction across the mouth of a riverthat prevents the entry of seawater; freshwater liesupstream of a barrage.
Basalt. Volcanic rock erupted onto the Earth’s surfaceusually from volcanoes. Also known as blue metal whencrushed into pebble or cobble size pieces as aconstruction material.
Baseflow. The sustained flow in a river, not the directresult of runoff from a rainfall event.
Base metals. Minerals extracted for resource use suchas copper, lead and zinc.
Bedload. The soil mineral material transported on thebed of a river, usually during flood events, which maycome from catchment slopes or channel banks.
Bedrock. Well consolidated rocks typically much olderthan overlying sequences. Sometimes also calledbasement.
Bendigo-style gold deposits. Orogenic goldmineralisation linked to the Benambran Orogeny,predominantly deposited along major structures such asthe apex of folds (saddle reefs) and fault planes.
Benthic. Living on or near the bottom of a body ofwater.
Billabong. A backwater channel, often formed by acut-off river bend, that forms an ox bow lake, lagoon orpool when river levels fall.
Biodiversity. The variety of all life: the different plants,animals and micro-organisms; the genes they contain;and the ecosystems they form. Biodiversity is usuallyconsidered at three levels: genetic diversity, speciesdiversity, and ecosystem diversity.
Biodiversity Strategy. Victoria’s Biodiversity Strategyfulfils commitments in the national Strategy for theConservation of Biodiversity and requirements under theVictorian Flora and Fauna Guarantee Act 1988. It detailsstrategic frameworks to prevent further loss of habitat,and a focus for better management of existing habitatsand the continuation of natural ecological processes.
Biomass. The weight of living material in a unit volumeor area at a given time.
Biolinks. See ‘habitat links’.
Bioregion. A region determined by vegetation coverand the earth’s physical features and climate.
Biota. All living things, including micro-organisms,plants and animals.
Blue-green algae. Naturally occurring, microscopic,primitive photosynthetic bacteria. Under certainconditions, including high nutrients, warm still water,strong sunlight into the water, they can bloom into adense and visible growth and may become toxic.
Blue metal. See ‘basalt’.
Buffer (strip). Under the terms of the Code of ForestPractices for Timber Production, a protective margin ofvegetation abutting a stream, spring, wetland, body ofstanding water or swampy ground, which protects itfrom potentially detrimental disturbances in thesurrounding forest. Buffer width is defined as thehorizontal distance from which various harvestingoperations are excluded.
Cap. An upper limit on the amount of water thatmaybe diverted from a river system for human uses. Themost notable being the Cap introduced by the MurrayDarling Basin Ministerial Council in 1995 for the entireMurray-Darling Basin.
CaLP Act. Catchment and Land Protection Act 1994.This Act establishes ten catchment regions andcatchment management authorities across Victoria.Their role is to provide strategic advice on naturalresource management through the development of acommunity based Regional Catchment Strategies.
CAR reserve system. A system of forest reservesestablished by agreement between Commonwealth,State and Territory governments to provide forbiodiversity protection. The system is based on theprinciples of comprehensiveness, adequacy andrepresentativeness.
Catchment. The area of land drained by a river and itstributaries.
Catchment Management Authority (CMA). Regionalstatutory authorities established under the Land andCatchment Protection Act, 1994 and who are
GLOSSARY
312 River Red Gum Forests Investigation > 2006
responsible for the strategic planning and coordinationof natural resources, including land water andbiodiversity within their catchment region. Catchmentmanagement authorities also have floodplainmanagement functions under the Water Act 1989.
Channel capacity. The volume of water that can passalong the river channel at a certain point and timewithout spilling over the tops of the banks.
Chert. Hard, fine-grained silicic sedimentary rock,formed by chemical or biological processes sometimes innodules in other sediments and is known as flint.
Choke or Barmah Choke. A narrow section of theRiver Murray near Barmah, Victoria, that constrains theflow of the River Murray.
Clastic rock. Any rock or sediment that is composed ofparticles (clasts). Particle size is not important—examples include sandstone, mudstone andconglomerate.
Code of Forest Practice. A set of principles andminimum standards adopted by Government for theconduct of timber harvesting and associated works onpublic land in Victoria. The Code aims to ensure thatimpacts on environment and heritage values areminimised.
Commence to flow. Volume at which flow spills into achannel or wetland. For instance, commence to flow fora wetland is the volume at which water enters thewetland.
Competition. In the context of forest growth, thecontest between plants of the same or different speciesfor limited resources, such as water, nutrient and light,producing differential growth.
Connectivity. The extent of connection between theriver and its floodplain and from the floodplain back tothe river by overbank flows or through flood runners.
Confluence. The place where two or more streamsflow together.
Conservation reserve system. The system of reservesbased on public land that are managed primarily fornature conservation. This system aims to represent allvegetation types and land systems in permanentlyprotected reserves via dedicated reserves, informalreserves and protection by prescription. In Victoria, thereserve system is generally considered to consist ofnational, state and wilderness parks, reference areas andnature conservation reserves (including flora, flora andfauna, and non-hunting wildlife reserves).
Conservation status. An assessment of thesusceptibility of a biological entity (usually a species orecological unit such as an ecosystem or vegetation type)to changes in abundance and extinction. In Victoria, theWorld Conservation Union (IUCN 2000) classification isused to describe the conservation status of vertebrates.In order to qualify for a threatened category, a taxonmust meet one or more assessment criteria, based onfeatures such as numbers of individuals and populations,previous or projected declines in numbers or habitat,extent of occurrence, area of occupancy and extremefluctuations in numbers or habitat. The categories, in
descending level of threat are critically endangered,endangered and vulnerable. Other categories areextinct, near-threatened and data deficient (seeAppendices 4 and 5).
Conversion: firewood cubic metres to tonne. 1 m3
of firewood equals about 700 kg (0.7 tonne) oven dryweight (weight would vary with the species and densityof the particular sample of wood).
Conversion: railway sleeper volume. Sleepers usuallymeasure 2.7 m x 25 cm x 13 cm, a volume of about0.09 cubic metres. Eleven sleepers thereby equal aboutone cubic metre of sawn timber. However, conversionof round logs to sleepers produces waste.
Coupe. An area of forest of variable size, shape andorientation from which logs for sawmilling or otherprocessing are harvested.
Coppice (ing). Regrowth (adventitious) stemsoriginating from dormant buds on the stump or the baseof the trunk of a damaged eucalypt; the process ofremoving coppice (usually to reduce the number ofstems on a stump).
‘Country’. Indigenous people regularly refer to theland and natural resources of an area as ‘country’. Theland and waters of Australia have sustained Indigenouspeoples for many thousands of years. This longoccupation has resulted in a profound cultural andspiritual relationship between indigenous people andcountry.
Crossing timbers. Large, 30 cm x15 cm, sections inlengths from 2.7 m up to 8 m, used as sleepers tounderpin converging or diverging rail tracks, such as atstations and passing places.
Crown land. At the time of European settlement, alllands in Victoria were claimed as Crown land. Crownland is a class of public land that includes unreservedland, land temporarily and permanently reserved underthe Crown Land (Reserves) Act 1978, state forest withinthe meaning of the Forests Act 1958 and park, withinthe meaning of the National Parks Act 1975. It ismanaged and held in trust by the Government for thebenefit of the Victorian community. Crown lands maybe licensed or leased or vested. Crown land does notinclude freehold land whether or not owned by a publicauthority.
Cultural heritage value. Historic, scientific, social oraesthetic value for past, present or future generations.
DBH (Diameter at breast height). The diameter of atree trunk at 1.3 m above the ground.
Declared water supply catchment areas. Under theCatchment and Land Protection Act 1994, watercatchments can be declared as ‘special water supplycatchment areas’—a mechanism that identifies theimportance of the area for water supply. ‘Special areaplans’ can be prepared for such areas to guide land use.
Dedicated reserve. A term used in the CAR reservesystem to describe reserves that are equivalent to theIUCN Protected Area Management Categories I, II, III orIV as defined by the International Commission forNational Parks and Protected Areas (IUCN 1994) and
313Discussion Paper
have secure tenure that requires action by a Parliamentto be revoked. In practice such reserves include naturalfeatures reserves (such as bushland reserves and scenicreserves), historic and cultural feature reserves andregional parks, as well as national, state and wildernessparks, reference areas and nature conservation reserves.See also ‘informal reserves’.
Deep leads. A miner’s term for buried river gravelswhere mining is needed to win gold. They occur whereancient gold-bearing gravels are buried by younger rivergravels, or by basalt flows.
Demographic. The description of communities andtheir population’s social, economic and socialcharacteristics.
De-snagging. The removal of fallen trees and deadbranches from a watercourse.
Diversion. Transferral of water from a river, usually intoa storage system or for direct use.
Diversion weir. A structure built across a river toenable water flow to be diverted into a water supplysystem.
Dry Sheep Equivalent (DSE). Level of stock grazingequivalent to a two-year old wether weighing 45kilograms and maintaining its weight.
ECC – Environment Conservation Council. VEAC’spredecessor from 1997 to 2001. See also ‘LandConservation Council (LCC)’.
Ecological Vegetation Classes (EVCs). Componentsof a vegetation classification system derived fromgroupings of vegetation communities based on floristic,structural and ecological features (see Appendix 6).
Ecologically Sustainable Development (ESD).Development which aims to meet the needs ofAustralians today, while conserving our ecosystems forthe benefit of future Australians (see Introductionchapter).
Ecology. The study of the interrelationship betweenliving organisms and their environment.
Ecosystem. A community of naturally co-occurring andinteracting species and their physical environment inwhich they live and with which they also interact.
Ecosystem services. The services or benefits humansderive from the interactions of the elements ofecosystems. This might be in the form of production ofgoods, regeneration of services, stabilising services, life-fulfilling services (e.g., spiritual inspiration) orpreservation of options.
Effluent creek. A creek that leaves a watercourse anddoes not return to it.
Endemic species. Species confined to a particularregion or locality.
Environmental Water Entitlement. A waterentitlement held by the Victorian Minister forEnvironment that permits the use of water in a river orstorage for a purpose that benefits the environment.
Environmental flows. Any managed river flow patternprovided with the intention of maintaining or improving
river health. These flows ensure that the key chemical,geomorphological, and ecological processes necessaryfor healthy river ecosystems are kept functioning.
Environmental value. A particular value or use of theenvironment that is conducive to public welfare, safetyor health.
Environmental Water Allocation. An amount ofwater allocated to the environment under anenvironmental entitlement.
Environmental Water Reserve. The share of waterresources set aside to maintain the environmental valuesof a water supply system and other water services thatare dependent on the environmental condition of thesystem.
Ephemeral stream. A stream that flows for only shortperiods and then dries up.
Eutrophication. Excessive levels of aquatic plantgrowth (including algae) resulting from raised levels ofnutrients and other factors.
Evaporation. The process by which atoms or moleculesin a liquid state gain sufficient energy to enter thegaseous state.
Evapo-transpiration. The process of water beingtranspired by vegetation.
Even-aged stand. A forest stand where all or most ofthe trees are of the same age, that is, they haveregenerated from the same event (e.g. a particular floodor fire).
EVC complex. A vegetation unit where two or moreEVCs are unable to be distinguished in an area but areknown to exist discretely elsewhere.
EVC mosaic. A vegetation unit consisting of two ormore discrete EVCs, which were unable to bedistinguished in mapping processes because of the scaleused.
Exempt Crown land. Crown land which, under theMineral Resources Development Act 1990, is in a publicland-use category in which exploration or mining is notpermitted. Exempt Crown land includes national, stateand wilderness parks, and reference areas. Exceptions toallow mining exist under Section 40 of the NationalParks Act 1975 which provides for the continuance of anexploration or mining licence current at the time theland is declared in one of those public land-usecategories.
Exploration licence. A licence under the MineralResources Development Act 1990, issued by the Ministerfor Energy and Resources, entitling the holder to carryout exploration on the land covered by the licence,subject to satisfying the criteria for commencement ofwork.
Extant. Still existing.
Extraction. In the context of water, is where water istaken from rivers or streams for off-stream use orconsumption.
Facies. The primary characteristic of a sedimentary rock.
Fault. A fracture in the Earth’s crust accompanied by a
314 River Red Gum Forests Investigation > 2006
displacement of one side of the fracture.
Fold belt. A series of rocks formed during a mountainbuilding tectonic episode or orogeny.
Filter strip. Under the terms of the Code of ForestPractices for Timber Production, a narrow strip of groundretained either side of a drainage line or temporarystream. In the strip, trees may be felled subject tocertain conditions and machinery entry is only permittedin certain circumstances.
Fire protection plan. Plans prepared within thecontext of the Code of Practice for Fire Management onPublic Land. They define fire protection strategiesadopted to achieve those objectives. Each FireProtection Plan has four main strategies: wildfireprevention, wildfire preparedness, wildfire suppressionand wildfire recovery.
First Step Decision. A decision announced by theMurray–Darling Basin Ministerial Council in November2003 to address the decline in health of the RiverMurray system.
Fish ladder or fishway. A structure designed to enablefish to move over a physical barrier (dam or weir) in awaterway.
Flood. Flows that are high enough at their peak tooverrun river banks or cause flow through high-levelanabranches, floodrunners or to wetlands.
Flood channel. A natural channel in a floodplain,which carries flowing water only during a flood.
Floodplain. Flat land beside a river that is inundatedwhen the river overflows its banks during a flood.
Flora and Fauna Guarantee (FFG) Action Statement.Documents prepared for selected species, ecologicalcommunities and potentially threatening processes listedunder the Flora and Fauna Guarantee Act 1988.
Flow regimes. The spatial and temporal pattern offlows in the main river bed and the floodplain areassurrounding the river. Natural flows refer to a floodregime unaffected by any form of flow modification.Regulated flow refers to artificial control of dams, weirs,diversions or other structures or practices.
Fluvial. A geomorphic process whereby sediments aretransported and deposited by flowing water.
Forest. Vegetation formation with the tallest stratumcomprising trees which project a foliage cover forgreater than 30 percent of the site (cf. woodland).
Forest management area (FMA) plan. A plandeveloped to address the full range of values and uses instate forest, including nature conservation and timberproduction. There are 14 forest management areas inVictoria, and a plan is produced for each FMA.
Forest structure. The main physical features of theforest—such as the density and height of vegetationlayers (e.g. canopy, shrub layer, ground layer), and sizeand density of trees.
Fresh. A flow pulse in a river which is higher than themedian flow at that time of the year. It may occurnaturally or be the result of a decision to release water
from a reservoir. A fresh can occur at any time of year.Also known as flush.
Fuel reduction burning (FRB). The use of lowintensity fires as a management tool to remove the moreflammable fuel from parts of forests and parks, with thepurpose of reducing flame height, fire intensity andslower spreading patterns of any potential bushfire andmaking firefighting easier.
Geographic Information System (GIS). A systemwhich holds spatially referenced data which can beclassified, overlaid, analysed and presented in map,tabular or graphic form.
Geomorphology. The study of the arrangement andform of the Earth’s crust and of the relationship betweenthese physical features and the geologic structuresbeneath.
Geomorphological. Pertaining to the development ofpresent landforms and the history of changes in theearth’s structure as recorded by surface features.
Gigalitres. A measurement of water equivalent to onebillion litres.
Glauconitic. Sediments containing a greenishmicaceous mineral (glauconite).
Golden Triangle. Area of western and central Victoriaencompassing the rich gold fields between Bendigo,Ballarat and Stawell.
Grey water. Household (including caravan andhouseboat) water which has not been contaminated bytoilet discharge and includes water from bathtubs,dishwashing machines, clothes washing machines andkitchen sinks.
Groundwater. Underground water filling the voids inrocks, often between mineral grains in sedimentaryrocks. Water in the zone of saturation in the Earth’scrust.
Group selection system. An uneven-aged silviculturalsystem, involving the felling of all trees in small patches(or groups) at intervals (generally every 10-15 years) overthe rotation. The gaps created are scattered over thecoupe. Gap size is usually no more than about two treeheights in diameter, so that seedfall from surroundingtrees can be used to regenerate the gap. Deliberateseedbed preparation is generally required, involving soildisturbance or burning of slash.
Geographic Representation Units (GRU).Subdivisions created to help analyse the distribution ofthe reservation system across the region and the degreeto which values are represented in that reserve system.
Gypsum/Gypseous. Mineral derived from evaporationof salty water (CaSO4.2H2O).
Habitat. The place or environment in which anorganism naturally occurs.
Habitat links. Areas of often linear remnant or plantedvegetation that connect two or more patches ofvegetation. These links may be continuous ordiscontinuous strips and patches of vegetation. Oftenreferred to as corridors.
315Discussion Paper
Headwaters. The small streams on the higher groundof a catchment, which flow into a river.
Heavy mineral sands. Sediments that containeconomic concentrations of heavy minerals such asilmenite, rutile and zircon rich in the elements titaniumand zirconium.
Heritage. All those things which we have inheritedfrom previous generations and which we value.Heritage includes places, things (movable objects) andfolklore (customs, songs and sayings).
Heritage River. Rivers or reaches of rivers designatedunder the Heritage Rivers Act 1992, managed primarilyto protect their significant nature conservation,recreation, scenic or cultural heritage values.
Hinterland. The area within the sphere of influence ofa large town, city, river or coastline.
Human settlement and patterns. Where and howpeople live and work in rural areas, towns and cities.
Hydraulic. Refers to the local dynamic aspects of flow,usually measured in terms of shear stress, water depth,flow velocity.
Hydrological system. Includes streams, wetlands,billabongs, floodplains, swamps, ground water rechargeareas, ephemeral lakes, estuaries and the sea.
Hydrology. The science that deals with surface andgroundwaters of the earth; their occurrence, circulationand distribution; their chemical and physical propertiesand their reaction with the environment.
Hydrological system. This includes streams, wetlands,billabongs, floodplains, swamps, groundwater rechargeareas, ephemeral lakes, estuaries and the sea.
Igneous. Rock formed from crystallisation of moltenmagma either slowly at depth (granite) or rapidly at thesurface (basalt, rhyolite).
Indigenous vegetation. Vegetation native to aparticular location.
Industrial minerals. Minerals such as gypsum and claythat are largely used for construction and industrialpurposes.
Informal reserve. A term used in the CAR reservesystem to describe areas clearly identified inmanagement plans suitable for and set aside forconservation purposes. See also ‘dedicated reserves’.
Interpretation. Information, signage, nature trails andguided nature walks, aimed at providing insight andawareness of natural features, ecological systems,cultural heritage, and park management.
Introduced species. Species of plants or animals thatare not native to Australia (also referred to as exotic oralien species).
Indigenous vegetation. Vegetation native to a specificlocation.
Inundation. To cover with water, usually by the processof flooding.
JANIS criteria. Criteria defined by the JointANZECC/MCFFA National Forest Policy Statement
Implementation Sub-committee for the establishment ofthe CAR system of forest reserves (see chapter 10).
Lacustrine. Pertaining to a lake; sediment formed atthe base of a lake; organisms living or growing in a lake.
LCC – Land Conservation Council. VEAC’spredecessor from 1971 to 1997. See also ‘EnvironmentConservation Council (ECC)’.
Levee. A natural levee is a deposit of alluvium, which israised above the general level of the banks of a streamand its floodplain. Man-made levees may beconstructed along the course of a river or stream inorder to contain flood waters.
Lignotuber. A woody swelling, partly or whollyunderground at the base of the stem of many eucalypts.It is composed of food reserves and dormant shoots thatcan emerge for survival if the plant’s aerial parts aredestroyed.
Lithology. A physical characteristic of a rock formationor stratigraphic unit.
Lock. A rectangle chamber of concrete within a riverwith gates each end that enables boats to move fromone water level to another.
Long-term sustainable yield. The theoretical rate ofharvest that can be maintained in perpetuity; i.e. whenthe condition of the available forest is equal to thetheoretical yield of the normal forest. It is a general goalfor forest managers to work towards (cf sustainableyield).
Lunette. Crescent or semicircular shaped aeoliandeposits of fine sediment located on the eastern (or lee)side of lake beds or playas in semi-arid areas.
Marls. A marine sediment consisting of calcareousmudstone.
Mature forest. Forest stands and/or individual treeswhere the tree crowns are well foliated and rounded.Trees have reached maximum height and crowns havereached full lateral development. Branch thickening canoccur. The height and crown development of the treeshas effectively ceased (compared with regrowth) butdecline of the crown (loss of limbs, development ofepicormic growth) has not yet significantly begun (as inthe senescent or over-mature growth stage).
Meander. A curve in the course of a river, alwayspresent in a series.
Megalitre (ML). One million litres (one Olympic sizedswimming pool is approximately 2 ML).
Merchantable. Used to describe trees suitable forprocessing into forest produce and for which a marketexists.
Micaceous. Containing mica minerals.
Mineral sands. See ‘Heavy mineral sands’.
Mining licence. A licence under the Mineral ResourcesDevelopment Act 1990, issued by the Minister forEnergy and Resources, entitling the holder to carry outexploration and mining on the land covered by thelicence, subject to receiving an authority to commencework.
316 River Red Gum Forests Investigation > 2006
National Water Initiative. The Council of AustralianGovernments (29 August 2003) agreed to theestablishment of a National Water Initiative to improvethe security of water entitlements for ecosystem healthand consumptive uses through expanding water tradingpractices, encouraging water conservation in cities, andimprovements in irrigation practices.
Natural flow regime. The likely pattern of water flowbefore European settlement in Australia. Natural flowregime refers to the flow patterns without anyregulation or water extraction.
Oceanic arc. A volcanic arc situated in an oceansetting. Indonesia is a modern example.
Old-growth forest. Forest that contains significantamounts of its oldest growth stage in the upperstratum—usually aging trees—and which has been notbeen disturbed or, only experienced disturbance theeffect of which is now negligible.
Orogeny. A major mountain-building event.
Overmature. See ‘senescent’.
Overwood. Trees left after harvesting that competewith regeneration for light, water and nutrients (mayinclude trees retained for habitat or seed supply andunmerchantable trees).
Peri-urban. Low density development on the edge ofurban areas. It is characterised by a mixture of rural andresidential land uses and may be the location ofcommuters who live in a rural setting while travelling towork in the nearby urban centre.
Phytoplankton. Plant plankton, usually algae.
Planform. A bird’s eye view of a river channel. In otherwords, the shape of a river from the air or as seen on amap.
Playa. A shallow, salty desert lake. May bepredominantly dry and hold water only after prolongedor heavy rain.
Point bar. Deposit of sand or gravel on the inside of ameander or river bend.
POMA – Powerful Owl Management Area.Designated areas containing suitable habitat forpowerful owls based on confirmed records of breedingsites, roosts and sightings.
Pool. A body of water in a river that is relatively deepand slow moving.
Pool-riffle morphology. A type of three dimensionalstream bed morphology characterised by fairly regularly-spaced alternating pool and riffles. Not all streams havethis morphology.
Porphyry. Igneous intrusive rock consisting of a finegrained matrix with larger crystals.
Potentially Threatening Process. A process that hasthe potential to pose a significant threat to flora orfauna and is listed under the Flora and Fauna GuaranteeAct 1988. The Commonwealth equivalent is a KeyThreatening Process.
Precautionary principle. The principle that the lack ofscientific certainty should not be the reason to postponepreventative measures to avert threats of serious orirreversible damage.
Pre-1750 EVC. The extent of an ecological vegetationclass (EVC) prior to the year 1750 as defined by existingvegetation supplemented by predictions and modellingof vegetation that has been cleared since Europeansettlement.
Prior stream. The course of a former streamresponsible for the nearby sediments that did not carrywater other than local drainage. A low ridge built upfrom materials deposited by stream flow along a formerstream channel.
Prospecting. The use of metal detectors, hand tools,pans or simple sluices to search for minerals, such asgold and gemstones.
Protected area. Park or reserve with the primary aim ofbiodiversity conservation.
Public land. Under the Victorian EnvironmentalAssessment Council Act 20001 public land refers to (a)any unalienated land of the Crown, including landtemporarily or permanently reserved under the CrownLand (Reserves) Act 1978; (b) state forest within themeaning of the Forests Act 1958; (c) park, within themeaning of the National Parks Act 1975; (d) land underthe ownership or control of Melbourne Parks andWaterways, established under the Water Industry Act1994; (e) land vested in any public authority, otherthan—(i) a municipal council; or (ii) an Authority underthe Water Act 1989, to the extent that the land vestedin the Authority is within a sewerage district listed incolumn 3 of Schedule 12 of that Act.
Public land use categories. A classification of publiclands into major land-use categories such as parks,nature conservation reserves, state forest and so forth.Each land-use category in essence defines the primarypurpose of the land. For many of the land-usecategories a range of additional purposes are alsodefined. Each land-use category is generally subject toparticular legislation and management arrangements(see chapter 9).
Pugging. The compaction and rutting of soil throughtrampling by hard-hoofed animals, particularly duringwet conditions, leading to reduced water infiltration intosoils and damage to plants.
Rain rejection flows/floods. Water that is ordered butnot used because rain subsequently falls. Currently thiswater is not debited on the water-user’s account.
Ramsar convention. Lists of wetlands of internationalimportance. To be placed on the register a wetland hasto fulfil certain criteria such as being important to thesurvival of migratory birds or endangered animals andplant species.
Ramsar site. A wetland of international significanceunder the Ramsar Convention.
Reach. A relatively homogenous section of a river.
Recharge. Water that infiltrates through the soilsurface to the watertable.
317Discussion Paper
Regeneration (noun). The young regrowth of forestplants following disturbance of the forest such as timberharvesting or fire includes juvenile and sapling stageswhere the tree is very small and the crown exhibitsapical dominance.
Regeneration (verb). The renewal of forest by naturalor artificial means.
Regime. For water, the prevailing pattern of flows.
Regional Forest Agreement (RFA). An agreementbetween the Commonwealth and a State or TerritoryGovernment, for the long-term management and use offorests in a particular region.
Regional water authority. Statutory authorityresponsible for supplying water primarily to urbanconsumers and the disposal of waste-water from towns.
Regrowth. (a) a forest stand regenerated eithernaturally or by seeding following death or removal ofthe forest overstorey; (b) a growth stage of a foreststand or individual tree in which the tree is activelygrowing, has a well developed stem with crown and anarrow conical form of small branches, but is below themaximum height for the stand. Apical dominance isapparent in vigorous trees.
Regulated river/stream. Controlled flows within ariver system resulting from the influence of a regulatingstructure such as weir or dam.
Regulator. Structural works that control water flow.
Residual logs. Produced as a by-product of sawlogharvesting and regrowth management operations.Comprises a log too small to meet sawlog or sleeperspecifications or may meet sawlog specifications for sizebut with greater than 50 percent defect. Includes lowquality logs suitable for conversion into sawn productsor those unsuitable for sawing, such as firewood orpulpwood. Utilised for a variety of products where shortlengths are suitable and the appearance and strength ofthe timber are less important. My be harvested underannual licence or tender from areas not required forproduction of commercial and domestic firewood.
Restricted Crown land. Land owned by the Crownupon which, under the Mineral Resources DevelopmentAct 1990, any exploration or mining requires theconsent of the Minister for Environment; includes natureconservation reserves, regional parks and naturalfeatures reserves.
Retained trees. Trees retained on a coupe duringharvesting operations to provide habitat for wildlife, orto grow on after thinning.
Riffle. A shallow area of a river in which water flowsrapidly over stones or gravel.
Rill erosion. The development of numerous minuteclosely spaced channels resulting from the unevenremoval of surface soil by running water.
Riparian. The area of land along the bank of a river orstream.
Riparian rights. The rights to water use possessed by aperson owning land containing or bordering a watercourse or lake.
Riverine. Relating to a river.
Salinity. A measure of the total soluble salts in a soil.A saline soil is one with an accumulation of free salts atthe soil surface and/or within the profile affecting plantgrowth and/or land use. It is generally attributed tochanges in land use or natural changes in drainage orclimate, which affects the movement of water throughthe landscape. Salinity levels of soil or water can betested using Electrical Conductivity (EC). Theconcentration of various salts dissolved in a volume ofwater or soil.
Sediment load. The mass of sediment transported pasta point in a river over a given time period.
Senescent. A growth stage of a forest stand orindividual tree that is characterised by declining crownleaf area and crown diameter and irregular crown shapedue to the loss of branches and epicormic growth. Thisterm is interchangeable with overmature or veteran intimber-production terms, but from a nature conservationpoint-of-view the tree is regarded as a large old (habitat)tree.
Shales. Sedimentary rocks formed from muds andclays, usually with fine even layers.
Significant ecological asset (SEA). These assets areselected for their regional, national and internationalimportance because of their ecological values, and thebelief that they are at risk of ongoing environmentaldegradation because of changes in water flow regimesbecause of river regulation. The six significantenvironmental assets are: Barmah-Millewa Forest,Gunbower and Koondrook-Perricoota Forests, HattahLakes, Chowilla Floodplain, Murray Mouth, Coorong andLower Lakes and the River Murray Channel.
Siltation. The process of deposition of material whichcan be clay, silt, or sand-sized material on the base of ariver or lake.
Siltstones. Similar to mudstones but composed ofslightly coarser grade of sediment.
Silviculture. The theory and practice of managingforest establishment, composition and growth, toachieve specified objectives (a harvesting andregeneration system).
Silvicultural system. A planned program of forestmanagement that includes tending, harvesting andregeneration.
Site quality. A measure of the growth potential of aforest site (as determined by soils and climate). Oftenexpressed in terms of the dominant height of trees at aparticular age.
Snag. Large woody debris in rivers that impacts onhuman use of rivers. Provides habitat for plants andanimals.
Source bordering dune. Sand and clay rich dunesformed on the downwind side of sandbars or wide riverchannels during dry or low water periods.
Southern 80. An annual high speed water-ski race heldon the River Murray between Torrumbarry and Echuca.
318 River Red Gum Forests Investigation > 2006
Special area plan (SAP). A plan developed under theCatchment and Land Protection Act 1994 that detailsspecific conditions on land-use and land managementpractices. To date most Special Area Plans deal withland-use in declared water supply catchments.
Special Management Zone (in FMA plans).Delineates an area that is managed to maintain specifiedvalues, such as flora and fauna habitat or catchmentvalues, while catering for timber production undercertain conditions.
Special Protection Zone (in FMA plans). Delineatesan area that is managed for the conservation of naturalor cultural values and where timber harvesting isexcluded. It forms part of a network designed to linkand complement conservation reserves. An informalreserve.
Species. A group of similar organisms generally capableof interbreeding only with each other to produce fertileoffspring. For clarity, the term ‘species’ is frequentlyused in this Discussion Paper when, technically, ‘taxon’or ‘taxa’(see below) would more accurate.
Stand. A group of trees in a forest that can bedistinguished from other groups by their age, speciescomposition and condition.
Stand condition. The health, age and size-classdistribution and stocking of a forest stand.
Statistical Local Area. A subdivision of a municipalityused by the Australian Bureau of Statistics for thepurposes of collection and analysis of census data.
Stratification. Distinct layers of water in a dam or weirpool, formed when there is little movement to causeintermixing, usually in summer when deeper layers ofwater become cold and deoxygenated.
Stressed river. An evaluation approach used in theassessment of appropriate management strategies forwater allocation and flow management in uncontrolledstreams. A classification based on environmental andwater-use criteria, hence a stressed river is one that hashigh levels of water diverted and is often associated withdeclining water quality and biodiversity.
Stocking. Density of any given forest stand, usuallyexpressed in terms of the number of trees per hectare.
Surface water. Water on the surface of the land, forexample in rivers, creeks, lakes and dams.
Sustainable yield. Rate of harvest of timber that canbe maintained for a defined period. This figure mayincrease in the future if the condition of the forest isimproved but should not decrease except in the case ofa catastrophic event such as fire (cf long-termsustainable yield).
Swale. A long, narrow trough or depression, oftenbetween sand dunes or ridges. May be a marsh orswamp when the depression carries water.
Taxon (plural: taxa). The named classification unit towhich individuals or sets of species are assigned, such assubspecies, species, genus or family.
Terrane. Sections of rock with different geologicalhistories that come together as a single landmass,
typically during orogenesis as fold belts.
Terrestrial. On land, pertaining to the earth and its dryland.
Timber production. Growing and harvesting of timberfrom native forests.
Thinning. The removal of a proportion of trees from a(usually even-aged) stand, with the aim of increasing thegrowth rate and/or health of the retained trees. Noregeneration is required or implied.
Threatened community. An ecological association ofplants and/or animals interacting within a commonenvironment that is listed as threatened under theVictorian Flora and Fauna Guarantee Act 1988 orCommonwealth Environment Protection and BiodiversityConservation Act 1999.
Threatened species. A term for a plant or animalgenerally listed under the Flora and Fauna GuaranteeAct 1988 or the Commonwealth Environment Protectionand Biodiversity Conservation Act 1999. Species may befurther categorised depending on the level of threat(e.g. critically endangered, endangered, vulnerable).Species may also be classed as near threatened whenthey are close to qualifying for a threatened category, ordata deficient when it is believed a species should be ina threatened category but sufficient data to make anassessment is lacking (see Appendices 4 and 5).
Tributary. A creek or river flowing into a larger river.
Trigger. In relation to water, triggers relate to when aflow of a particular size and duration is likely to initiatepart or all of an ecological response to theenvironmental flow.
Turbidity. A measure of the light scattering propertiesof water, indicating how much silt, algae and othermaterial is suspended in water. Highly turbid waterlooks muddy.
Ultra-mafic (also ultrabasic). Igneous rocks thatconsist mostly of iron, magnesium and chromiumminerals and virtually no quartz or feldspars.
Uneven-aged (forest or stand). Forest or stand whichcontains a continuum of age classes resulting from moreor less continuous regeneration over a number of years.
Unrestricted Crown land. Land owned by the Crownthat, under the Mineral Resources Development Act1990, can generally be prospected, explored or mined,but over which conditions may apply.
Veteran tree. Formerly used to describe a tree more orless at the senescent stage of growth.
Visitor days. Accumulated number of visits to a siteincluding overnight stays.
Volcanogenic. Sediment derived in part from volcanicmaterial.
Wake boarding. A sport similar to water-skiing basedon a down-sized board, similar to a surf board. Therider is towed behind a boat and attempts to do trickssuch as jumps and flips using the wake of the boat.
Water entitlement. The volume of water authorised tobe taken and used by an irrigator or water authority.
319Discussion Paper
Water entitlements include bulk entitlements,environmental entitlements, water rights, sales water,surface water and groundwater licences.
Water right. Rights to water held by irrigators in anirrigation district.
Watertable. The upper surface of a groundwater body.
Weir. A structure that transverses the river to regulatewater flow and provide a relatively constant pool level tofacilitate pumping or gravity feeding for irrigation andwater supply purposes.
Weir pool. The water held back by a weir, forming astill pool.
Wetland. The Ramsar Convention has adopted thefollowing definition of wetlands: areas of marsh, fen,peatland, or water, whether natural or artificial,permanent or temporary, with water that is static orflowing, fresh, brackish or salt, including areas of marinewater at the depth of water at low tide does not exceedsix metres. It includes the community of plants andanimals that lives in it.
World Conservation Union (IUCN). The WorldConservation Union was created in 1948. It is theworld’s largest conservation-related organisation andbrings together 76 states, 111 government agencies aswell as a large number of non-governmentorganisations, and some 10,000 scientists and experts,from 181 countries. Through various programs itsupports the conservation of natural heritage—forinstance the work of the IUCN World Commission onProtected Areas aims to promote the establishment andeffective management of a worldwide, representativenetwork of terrestrial and marine protected areas.
Yorta Yorta Co-operative Management Agreement.A formal agreement between Yorta Yorta NationAboriginal Corporation and the State of Victoria relatingto management of Crown land and waters over a totalarea of approximately 50,000 ha in northern Victoria.
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Millewa Forum Project 2003.13.Wareing, K. and D. Flinn (2003). The Victorian Alpine Fires January-March 2003. Fire Management, Department of
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Whetton, P.H., R. Suppiah, K.L. McInnes, K.J. Hennessy and R.N. Jones (2002). Climate Change in Victoria: highresolution regional assessment of climate change impacts. Department of Natural Resources and Environment,The State of Victoria., Melbourne.
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Williams, R.J., C.-H. Wahren, R.A. Bradstock and W.J. Muller (in press). Alpine grazing reduces blazing: A landscapetest of a widely held hypothesis. Austral Ecology.
Woodgate, P.W., B.D. Peel, J.E. Coram, S.J. Farrell, K.T. Ritman and A. Lewis (1996). Old-growth forest studies inVictoria, Australia concepts and principles. Forest Ecology and Management 85:79-94.
Yang, J.L. and G. Waugh (1996a). Potential of plantation-grown eucalypts for structural sawn products. I. Eucalyptusglobulus Labil. ssp globulus. Australian Forestry 59:90-98.
Yang, J.L. and G. Waugh (1996b). Potential of plantation-grown eucalypts for structural sawn products. II. Eucalyptusnitens Dean & Maiden and E. regnans F. Muell. Australian Forestry 59:99-107.
Yen, A.L. (2003). Invertebrates of coarse woody debris in river red gum forests in southern New South Wales: ascoping study. Unpublished report prepared for the New South Wales Red Gum Industry Strategy - Firewood andLog Residue Working Group Inc.
Yen, A.L., S. Hinkley, P. Lillywhite, J. Wainer and K. Walker (2002). A preliminary survey of the arboreal invertebratefauna of two river red gum trees Eucalyptus camaldulensis near the Murray River. Victorian Naturalist 119:180-185.
Yen, A.L., S.D. Hinkley, P.A. Horne, G.A. Milledge and T.R. New (1996). Development of invertebrate indicators ofremnant grassy-woodland ecosystems. Unpublished report to the Australian Nature Conservation Agency Save theBush Program.
APPENDIX 1: River Red Gum Forests InvestigationCommunity Reference Group
Contact Person Organisation
Ian Lobban Victorian Farmers’ Federation
Louise Anderson Goulburn Valley Environment Group
Paul Madden Victorian Association of Forest Industries
Euan Moore Birds Australia
Faye Ashwin Timber Communities Australia
Trevor Shard Minerals Councils of Australia (Victorian Division)
Kelvin Trickey Barmah Forest Cattlemen’s Association
Stan Vale Barmah Forest Preservation League
Rod Orr Environment Victoria
Nick Roberts Victorian National Parks Association
Nicholas Hunt Tourism Alliance, Victoria
Steve Robertson Federation of Victorian Walking Clubs (VicWalk)
Debbie Warne Horse Riding Clubs Association of Victoria
Peter Ellard1 Australian Motorcycle Trail Riders Association
John Corbett VRFish
Colin Wood Sporting Shooters’ Association of Victoria
Audrey Dickens2 Bush Users’ Group Victoria
Ian Cook Confederation of Australian Motor Sport, Victoria
Zac Powell Four Wheel Drive Victoria
Cr Neville Goulding Gannawarra Shire Council
Cr Tom Crouch Mildura Shire Council
Cr David McKenzie Moira Shire Council
Cr Neil Repacholi Shire of Campaspe
Joe Blake Friends of Nyah Vinifera Forest
Rachel Rogers Country Fire Authority
Wayne Webster Murray Lower Darling Rivers Indigenous Nations
1 until 1 September 20062 until 25 August 2006
River Red Gum Forests Investigation Government Contact Group
336 River Red Gum Forests Investigation > 2006
APPENDIX 2: River Red Gum Forests InvestigationGovernment Contact Group
Contact Person Organisation
Mr Pat Groenhout VicForests
Mr Graeme Davis Parks Victoria
Ms Chris White Tourism Victoria
Ms Sharon MacDonnell VicRoads
Mr Trent Wallis Mallee Catchment Management Authority
Mr Jon Leevers(Ms Emer Campbell) North Central Catchment Management Authority
Mr Keith Ward Goulburn-Broken Catchment Management Authority
Mr Geoff Robinson North-East Catchment Management Authority
Mr Owen Russell Lower Murray Urban & Rural Water Authority
Mr Nigel Binney Grampians Wimmera Mallee Water Authority
Mr Pat Feehan Goulburn-Murray Rural Water
Ms Sally-Anne Mason Coliban Water
Mr Ken Ellis Goulburn Valley Water
Mr Pat Feehan Goulburn-Murray Water
Mr Aleksy Bogusiak North East Water
Mr Brian Walsh Regional Development Victoria, Department of Innovation, Industry & Regional Development
Mr Stewart Simmons Aboriginal Affairs Victoria, Department for Victorian Communities
Dr Tim Cleary Department of Primary Industries
Dr Ian Mansergh Department of Sustainability & Environment
Ms Cathryn Pilioussis Department of Sustainability & Environment
Mr Bernie Young Department of Sustainability & Environment
Mr Mark Riley Department of Sustainability & Environment
Dr Jane Doolan Department of Sustainability & Environment
Mr Ian Miles Department of Sustainability & Environment
Mr David Harvey Department of Sustainability & Environment
Ms Joan Phillips* Department of Sustainability & Environment
Mr Clive Smith Department of Sustainability & Environment
Mr Mark O'Brien Department of Sustainability & Environment
Ms Judy Goode Department for Water, Land & Biodiversity (SA)
Ms Merridie Martin Department of Environment & Heritage (SA)
Mr Michael Davis Department of Infrastructure Planning & Natural Resources (NSW)
Mr Paul Packard
(Michael Penny) Department of Environment & Conservation (NSW)
Mr Mark Siebentritt Murray-Darling Basin Commission (Cwth)
Ms Deb Callister Department of Environment and Heritage (Cwth)
* until June 2006
River Red Gum Forests Investigation Government Contact Group
337Discussion Paper
338 River Red Gum Forests Investigation > 2006
Organisation Contact Sub. No.
Arbuthnot Sawmills Mr Paul Madden 271
Archard Laser & Hydraulics The Manager 41
Australian Conservation Foundation Dr Arlene Buchan 44
Australian Motorcycle Trail Riders Association Mr Peter Ellard 3
Barham Koondrook Garden Club Ms Lyn Smith 503
Barham Koondrook Historical Society Ms Rhonda Frankling 544
Barham Progress Association Inc. Ms Joy Eagle 15
Barmah Forest Cattlemen's Association Inc. Mr Kelvin Trickey 364
Barmah Forest Preservation League Mr Stan Vale 404
Benalla District Environment Group Ms Christine Holmes 98
Bird Observers Club of Australia, Murray-Goulburn Branch Mr Gary Deayton 339
Birds Australia, Victorian Regional Group Mr Euan Moore 13
Bush Users Group, Indigo Region Ms Win Morgan 384
Bush Users Group Victoria Inc. Mr Bob Richardson 373
Central Murray Apiaries Mr Peter Pigdon 14
Cohuna & District Progress Association Inc. Mr Greg Peace 526
Cohuna Joinery & Building Supplies Mr Alan Fletcher 177
Cohuna Trail Riding Club Ms Audrey Dickins 81
Cohuna Uniting Church Shared Ministry Team Ms Hazel Radley 541
Confederation of Australian Motor Sport, Victoria Mr Gary Grant 523
Conservation Council of South Australia Mr Peter Owen 200
Construction Material Processors' Association Mr Grant Phillips 454
Daylesford Anglers Club Mr Dale Whitehouse 524
Department of Infrastructure Mr John Robinson 170
Ecosurveys Pty Ltd Mr Rick Webster 95
Environment Victoria Inc. Ms Sue Phillips 432
Federation of Victorian Walking Clubs (VicWalk) Inc. Mr Steve Robertson 391
Field & Game Australia Inc. Mr Rod Drew 456
Forest Action Trust Ms Lauren Caulfield 428
Four Wheel Drive Victoria Mr Barry Chare 460
Friends of Nyah Vinifera Forest Inc. Mr John O'Bree 434
Friends of the Box-Ironbark Forests, Mount Alexander Region Mr Bernard Slattery 340
Friends of the Earth Mr Jonathon La Nauze 261
Gannawarra Shire Council, Kerang Mr Des Bilske 525
Gondwana Canoe Hire Pty Ltd Ms Lyn O'Brien 267
Goulburn Broken Catchment Management Authority Mr Bill O'Kane 366
Goulburn Valley Environment Group Dr Doug Robinson 199
Happy Horses Hoofcare Ms Audrey Dickins 82
Institute of Foresters of Australia Mr Ross Penny 398
J. & G. Coulter Pty Ltd Ms Jeanette Coulter 389
Kerang & District Assembly of God Church Inc. Ps Allan Jakobi 70
Kerang Environment Study Centre Mr George Hardwick 537
Kingston Conservation & Environment Coalition Inc. Mr Bill Hampel 310
Kyabram Field and Game Mr Graham Jamison 399
Leitchville Bunyip Sporting Club Mr L.J. Taylor 362
Mallee Catchment Management Authority Mr Trent Wallis 435
Melbourne Bushwalkers Inc. Mr Rod Novak 358
APPENDIX 3: List of Submissions received in response to the Notice of Investigation
339Discussion Paper
Organisation Contact Sub. No.
Mid Murray Landcare Network Mr David Ellemor 57
Mid Northern Association of Angling Clubs Inc. Mr Rob Loats 54
Mildura Rural City Council Mr Phil Pearce 506
Minerals Council of Australia, Victorian Division Mr Chris Fraser 314
Minister for Aboriginal Affairs The Hon Mr Gavin Jennings MLC 79
Murrabit Advancement Association Inc. Mr Stephen O'Donoghue 505
Murrabit Riding Club Inc. Ms Jeanette Coulter 388
Murray Darling Association Inc. Mr Adrian Wells 19
Murray Lower Darling Rivers Indigenous Nations Mr Steven Ross 431
Murray River Horse Trails Mr Graeme Padget & Ms Debbie Jackson 216
The Myer Foundation Ms Christine Fraser 430
Nathalia Fire Brigades Group Mr Phil Hawkey 85
National Association of Forest Industries 4711
National Parks Association of New South Wales Ms Jacquie Kelly 421
Nature Conservation Council of NSW Ms Madeline Hourihan 169
New South Wales Forest Products Association 4711
North Central Catchment Management Authority Mr Gavin Hanlon 439
North-Eastern Apiarists' Association Ms Elwyne Papworth 474
Plantations North East Incorporated Mr Bernard Young 443
Prospectors & Miners Association of Victoria Ms Rita Bentley 319
River Country Adventours Mr Rob Asplin 74
River Redgum Furniture Mr Dean Attwell & Mr Wayne Hall 370
Ryan & McNulty Sawmills Mr Greg McNulty 313
Shepparton Adult Riding Club Mr Chris Flynn 392
Shire of Campaspe Mr Wayne Harvey 365
Sporting Shooters' Association of Australia (Victoria) Ltd Mr Philip Brown 320
Sunraysia Bird Observers' Club Ms Pauline Bartels 181
Surveyor-General Victoria Mr David Boyle 24
Swan Hill Rural City Council Cr Bruce Jones 348
The Timber Benders Ms Sue Ewart 419
Timber Communities Australia Mr Ray Hill 180
Timber Communities Australia, Central Murray Red Gum Branch Ms Faye Ashwin 322
Timber Communities Australia, Victorian State Office Ms Kersten Gentle 4711
Trust For Nature (Vic) Dr Chris Williams 385
Victorian Association of Forest Industries Mr Pat Wilson 4711
Victorian Farmers Federation, Nathalia Picola Branch Mr Tom Tinkler 344
Victorian Farmers Federation, St James-Devenish Branch (incorporating Broken Boosey Landholders Group) Ms Kathy Beattie 381
Victorian Forest Health Advisory Committee Mr Ian Smith 451
Victorian National Parks Association Mr Nick Roberts 311
Victorian Piscatorial Council Inc Mr George Hardwick 217
Wangaratta Rural City Council Ms Karen Jones 472
Wangaratta Urban Landcare Group Ms Helen Curtis 16
Waterkeepers Australia Mr Greg Hunt 120
Wildlife Profiles Mr Peter Robertson 4
Yalca-Yielima Rural Fire Brigade The Secretary 407
Yorta Yorta Nation Aboriginal Corporation; Council of Ms Monica Morgan;Elders Yorta Yorta Nation Mr Henry Atkinson 450
1 joint submission
340 River Red Gum Forests Investigation > 2006
Name Sub. No.
Mr Ian Adams 436Mr Leigh Ahern 134M- Chris Allen 420Mr Ron & Mrs Margaret Armstrong 130Mrs M.E. Ash 547Ms Lyndall Ash 208Mr Roger Ashburner 466Ms Faye Ashwin 455Dr Wayne Atkinson 168M- J. Augello 84M- Neylan Aykut 445Mr Max & Mrs Belinda Baker 520Mr Jock & Mrs Lorna Bartram 176Mr John Bat 78Ms Beth Batt 350Mr Matt Batten 467M- M.L. Baxter 349Mr Darren Beattie 542Mr John Bentley 202M- E. Bergmeier 299Mr Geoff Berry 77Ms Linda Bester 437Mr David Beyer 441Ms Julia Bielak 107Ms Laura Billings 263Ms Deanne Bird 111Ms Rhiannon Bogaert 240Ms Annie Bolitho 429Mr Frank Bolton 6Mrs Eleanor Bolza 39Mr Greg & Mrs Kathleen Botterill 461Mr Darcy Botterill 382Ms Laura Botterill 383Mr Mark Boulet 75Mr John Bowen 94Ms Cara Bramich 136Ms Edwina Breitzke 30Mr Owen & family Brew 336Mr Darren & Ms Margie Briggs 63Mr John Brissett 112Mr William Broen 298M- S.C. Brown 191M- V. Brown 194Mr Robert & Mrs Dorothy Brown 453M- P.J. Brown 189M- M.E. Brown 190M- D. Brown 192M- E.S. Brown 193Mr Terry & Jerry Browning 380Ms Ann Buik 55Mr Tony Buiu 246Ms Georgie Burns-Williamson 377
Name Sub. No.
Mr Andrew Butcher 253Ms Sophie Butcher 251Ms Penny Byrne 368Mrs Gwen Calder 521Mr Bruce Calder 530Mr Brad Caldwell 369Ms Helen Caldwell 393Mr Pierre Call 417Mr John Cameron 26Mr Douglas & Mrs Joan Campbell 376Mr Anthony Carroll 214Ms Lisa Carter 515Mr John & Mrs Barbara Caven 329M- J. Chalmers 534Mr Luke Chamberlain 187Mr Michael Chew 295M- Childs 148Mr Wayne Church 514Ms Mary Cilli 418Ms Barbary Clarke 390Ms Nicole Cleary 236Mr Craig & Mr John Cleave 546Mr Steve Collett 491Mrs E.M. Colman 528Ms Elizabeth Cook 301M- E. Coppings 414Mr Walter Cordes 363Ms Rleena Cordes 531Mr David Corke 510Ms Tarryn Corkery-Lavender 219Miss Frances Corry 309Ms Esther Costa 354Ms Brigid Cowling 532Ms Courtney Cox 37Mr Don Crichton 131M- M. Curtis 272Mr Darryl Curwood 164Mr Peter Dale 278Ms Lesley Dalziel 315Mr Geoffrey Davey 495Mr Barry & Mrs Faye Davis 161M- Chris Dawson 463M- J.G. Dawson 233M- Chic Dee 508Ms Julia Dehm 88Mr Jack Delaney 345Mr Frank Di Mascolo 104Mr James Donald 283Ms Tanya Doran 139Mr Malcolm Dow & Ms Elinor Knappert 197Mr Jason Doyle 470M- Duggan 154
Name Sub. No.
M- Duggan 155M- J.M. Duggan 144Ms Jennifer Duke 241Ms Lorna Dunn 10Mr Neil Eagle 195Ms Melissa Eastham 80Mr John Eberbach 427Mr Victor Eddy 101Mr Rodney & Mrs Sandy Edwards 27Mr Peter Ellard 317Mr Michael & Ms Lara English 452M- Falahey 185Mr Robert Fallon 69Dr Mike Faris 269M- K.B. Farley 335Ms Frances Farrall 488Ms Denise Fenwick 287Mr Rob Fisher 535Dr James Fitzsimons 473Mr J. & Mrs A. Flack 117Mr Peter Flanagan 102M- P.F. Flynn 529Miss Trikkelle Flynn 337Mr Owen Flynn 333Mr Ray Foley 462Mr Charles Foster 213Mr Adrian Francis 265Ms Catherine Fraser & Mr Robert Blake 446M- G.F. & H.M. Frostick 361Ms Tanya Galvin 42Mr Miles Geldard 9Mrs B.M. George 122M- D. Gilpin 158Ms Belinda Glass 401Mr Anthony Glass 400Mrs Fay & Mr George Godden 93Mr Gerard Gomes 224M- J. Goss 256Cr Neville Goulding 65Ms Angela Grace 221Ms Ann Grant 62Mr Keith Greenham 49Mr William Hahucke 346Mr George Hall 321Ms June Halls 47Ms Lexie Hancock 481M- B. Hancock 416Ms Kylie Hannel 492Ms Denise Hanson 152Mr Jim Happ 196Mr Brendan Harding 110Ms Celia Hardy-Smith 477Mr Jim Harker 198Ms Susan Harrington 211
Name Sub. No.
Mr Ian Harris 328M- G.C. Harrisen 302Mr Barry & Mrs Heather Harvey 7Mr James Hattam 326Mr John Hay 173Mr Julian Hay 125Ms Ashley & Ms Linda Hazelman 215Mr Jason & Mrs Lorelle Heap 447Mr Gary & Mrs Carole Heap 448Mr Soc Hedditch 91Ms Julia Hempel 296Mr Greg Henry 356M- P. Hense 183Mr Wayne Hester 119Mrs Mavis Hester 126Ms Jacqueline Hibbert 12Mrs Hannah Hicks 83Ms Juanita Hill 482Mr Paul Hiraber 277Mr Neville Holland 331Ms Rebecca Holland 458Ms Isobel Holland 243Mr Keith & Mrs Jeanette Holland 343Ms Mouci Holland 238Mr Robert Hollingworth 109Ms Annette Hollingworth 166Ms Ann Holmes 497Ms Christine Holmes 72Mr Darren Howard 281Mr Peter Hunter 201M- Jeffrey 274Mr Reg Johnson 59Ms Katrina Joiner 5Ms Antonia Jolic 239Mr Carl Justin 288Ms Effie Kene 61Mr Andrew Kennedy 479Ms Wilma Kennedy 413Ms Amanda Keogh 282Mr Stewart Kerr 115Ms Lauren Kerr 500Mr Barry Kidd 533Mr Jim Killmister 522Ms Lucy Klem 499M- K.M. Kloe 300Ms Dawn Kneen 374Mr Roger Knight 518Ms Joy Knight 175M- Alex Knight 174M- L. Koch 143Ms Maree Kratzer 36Ms Ana Kuzmanic 494Mr Geoff Lacey 20Ms Bervene Lake 538
341Discussion Paper
342 River Red Gum Forests Investigation > 2006
Name Sub. No.
Ms Melanie Lambert 444M- N. Lane 285Ms Jennifer Lang & Mr Paul Webb 45Mr Stephen Lavender 38Mr Shaun Lawlor 442Ms Jan Laws 415Mr Michael Lea-Whyte 188M- N. Leoy 235Mr Peter Lewis 347Ms Rachel Liebhaber 469Mr David Lilley 484Ms Holly Livesey 284Mr Len Lock 121Mr Alan Lodge 476Mr Stephen Lodge 459Mr Graham Long 207Ms Ruth Long 325Ms Anne Low 22Mr Les Lubke 424Mr Geoff Lubke 179Mr Ian Lubke 425Mr Andrew Luke & Ms Helen Gargan 35Mr Paul Madden 406Mrs Lyn Madden 405Ms Kaaren Manley 56Mr Tim Mannion 132Mr Niki Marijancevic 504Mr Joe & Mrs Inge Marinac 330Mr Peter Maroudas 291Mr Dudley Marrows 527M- M. Matan 290Mr Ken Mawson 92Mr Robert McBain 87Mr James McCaw 29Mr Cameron McDonald 378Ms Pam & Ms Lyn McDonald 323Mr Peter McDonald 449Mr Ian McDonald 332Ms Raelene McFarlane 286M- S. McGrath 146Mr Daniel McGrath 480Ms Patricia McGrath 184Mrs Eileen McKee 512Ms Laura McKenzie 270M- J. McLeish 318Mr John & Ms Margot McNeil 396Ms Margaret Mikulin 225M- B. Miller 210Mr Jeff Mills 105Dr Lee-Ann Monk 379Mr Max Moor 129Ms Marlene Moor 342Mrs L.M. Morris 203Mr Michael Morrow 60
Name Sub. No.
Mr Philip Moser 334Mr Ian & Mrs Lois Mues 178Ms Judith Muir 52Ms Stella Mulder 140Ms Maureen Murray 409Ms Betty Murtagh 371Mr Colin Myers 316Mr Peter Newman 394Ms Linda Nicholls 395Ms Jackie Nicholson 167Mrs W. Nikolovski 58Mr Daniel Nitsche 501Mr Rod Novak 206Mr Ken O'Brien 516Mr Martin O'Brien 360Ms Joanna O'Brien 464Ms Kylie O'Brien 275M- J.M. O'Callaghan 145M- W.F. O'Callaghan 156Mr Harry & Mrs Margaret O'Connor 86Mr Terry O'Donoghue 352Ms Alison O'Gorman 279Ms Margaret O'Neill 48Mr Chris O'Neill 305Mr Patrick O'Neill 171Mr Grant Palmer 408Ms Lucille Palmer 422M- D.H. Panton 186Mr Rodney Pascoe 517Mr Wolf Passauer 2Mr Ric Pawsey 66Mr Leon & Mrs Brooke Peace 327Mr Stanislaw & Ms Barbara Pelczynski& Pelczynska 108Mr Michael Pellegrino 519M- Miki Perkins 90Ms Kiera Perrott 100Mr John Pettigrew 308Mr Eric Pilkington 25M- J.M. & D.R. Plattfuss 351Ms Ellenie Pond 498Ms Jan Poolsinso 43Ms Eva Popov 124Mr Fabian Postiglioni 485Ms Dorothy Powell 153Mr Rod Power 545Mr David Prest 223Mr Anthony Price 135Mr Bill Probst 11Ms Sandra Pullman 507Dr Frank Purcell 118Mr Neville Quinlan 157Mr Pat & Ms Michelle Quinn 50Mr L. & Mrs H. Radley 540
Name Sub. No.
Dr Victor Radywonik 357Ms Sue Radywonik 402Mr Tony Rae 234Mr River Rain 324Ms Jan Ramage 232Mr Geoffrey Randall 513Ms Gillian Rayner 312Ms Melanie Read-Wishart 502Mr Jack Rees 511Mr David Reid 307Ms Pauline Reilly 34Mr Max Richards 18Mr Peter Richardson & Ms Helen Harley 53Mr David Riis 8Mr David & Mrs Fay Rimmer 438Mr Morgan Roberts 490Mr Nick Roberts 106Mr Ray Roberts 123Mr Hugh Robertson 440Mr Allan Robins 89Mr Chris Robson 244Ms Jane Robson 242Mr Cameron Rodda 475Mr Murray Ross 97Mr Dave Roy 228Ms Sharon Roy 229Ms Karin Ruff 411Ms Josephine Rumsey 151Ms Holly Russ 539Ms Jacqueline Russ 543Mr Colin Russell 423Ms Penni Russon 260Mr Rick Ryan 76Mr Terry Ryder 292Ms Emma Salter 355Mr Luke Sango 245Ms Olympia Sarrunkolaou 231Mr Erwin Sauerwein 1M- K. Saxton 294Ms Julie Schilin 412Mrs Tania Schlemitz-Justin 289Mr James Schrieber 262Mr Brendan Scott 493Mr Lee Seary 23Ms Anne Selmas 293Mr Ken & Mrs Ula Sheather 46Mr Alan Shell 71Mr David Simeveks 486Mr Alex Sislov & Ms Rhonda Chrisanthou 28Ms Lyndall Sleep 359Mr Bruce Smith 338Ms Zoe Smith 259Ms Ellen Smith 237Mr Colin Smith 172
Name Sub. No.
M- R. Smith 303Mr Terry Smith 182Dr Peter Snider 128Ms Tracee Spiby 403Mr Peter Stafford 33Mr Ross Staley 99M- P. Starkey 147Mr Jim Starkey 149Ms Maya Statton 252Mr Bob Steel 113M- B. Stephens 487M- R.R. Stephenson 165Ms Hannah Stewart 230Mr Keith Stockwell 17Ms Marie-Claire Stoller 297Mr Douglas & Mrs Lois Stone 341M- P.R. Sullivan 304Ms Jane Sultana 103Mr Kevin Swan 249Mr Robert Swan 509Mr Trent Swan 250Ms Amanda Swaney 32Ms Jessica Sykes 127Mr Howard Tankey 410Ms Limia Tarr 73Ms Angela Thelen 258Mrs Joan Theyers 51M- J.R. Thomas 137Mr Geoff Thompson 67M- T. Thomson 306Ms Brooke Thomson 387Mr Stuart Trickey 367Mr Neil & Mrs Robyn Trickey 204Mr Enoch Trickey 96Mr Kelvin Trickey 205Mr Paul Turnbull 433Mr Rob Turner 468Ms Maureen Turner 478Mr Ron Turner 141Mr John Turner 257M- B. Turner 142Ms Ann Turner 222Mr Ken Turner 264Mr Chris Tzaros 372Ms Jean Vagg 138Ms Linley Walker 114Ms Tanya Walker 116Ms Justine Ward 31Mr Albert & Mrs Dolly Warild 465Mrs Nancy & Mr Harry Weatherman 160Mr John & Mrs Jan Webb 40Mr Hugh Webb 536Mr Shane Webster 496Ms Raelene West 375
343Discussion Paper
Name Sub. No.
Mr James Westland 247Mr James Wetter 220Ms Bronte Wicker 226Mr Nils Wiebkin 64Mr Craig Williams 489Ms Nicola Williams 386Mr Philip Williamson 353Miss Grace Willoughby 212Miss Jenna Wilson 68Mr James & Ms Shirley Wilson 397Ms Ruth Wilson 483Mr Douglas Wood 133Ms Elizabeth Woodhouse 209Ms Amanda Zame 280
Name incomplete or illegible: 21, 150, 159, 162, 163, 218, 227, 248, 254, 255, 266,268, 273, 276, 426, 457.
344 River Red Gum Forests Investigation > 2006
345Discussion Paper
346 River Red Gum Forests Investigation > 2006
APPENDIX 4: Flora Species Recorded in the River Red Gum Forests Study AreaAs of September 2006, the Department of Sustainability and Environment’s Flora Information System databasecontained records for the following taxa in the River Red Gum Forests study area. The Flora Information System hascomprehensive coverage of all vascular plants, but not lower plants such as mosses, liverworts and algae.
LEGEND:
EPBC: status under Commonwealth EnvironmentProtection and Biodiversity Conservation Act1999, as at December 2004.
C Critically Endangered: A taxon is criticallyendangered when it is facing an extremely highrisk of extinction in the wild in the immediatefuture.
E Endangered: A taxon is endangered when it isnot critically endangered but is facing a very highrisk of extinction in the wild in the near future.
V Vulnerable: A taxon is vulnerable when it isnot critically endangered or endangered but isfacing a high risk of extinction in the wild in themedium-term future.
Vic: conservation status in Victoria, after DSE (2005a).
x Presumed Extinct in Victoria: not recordedfrom Victoria during the past 50 years despitefield searches specifically for the plant, or,alternatively, intensive field searches (since 1950)at all previously known sites have failed to recordthe plant.
e Endangered in Victoria: at risk ofdisappearing from the wild state if present land use and other causal factors continue to operate.
v Vulnerable in Victoria: not presentlyendangered but likely to become so soon due to continued depletion; occurring mainly on siteslikely to experience changes in land-use whichwould threaten the survival of the plant in thewild; or, taxa whose total population is so small
that the likelihood of recovery from disturbance,including localised natural events such asdrought, fire or landslip, is doubtful.
r Rare in Victoria: rare but not consideredotherwise threatened - there are relatively fewknown populations or the taxon is restricted to a relatively small area.
k Poorly Known in Victoria: poorly known andsuspected, but not definitely known, to belong to one of the above categories (x, e, v or r)within Victoria. At present, accurate distributioninformation is inadequate.
FFG: status under the Victorian Flora and FaunaGuarantee Act 1988, as at December 2004. For the most up-to-date listings under the Act,visit: http://www.dse.vic.gov.au
L – listed as threatened.
N – nominated for listing, awaiting recommendation.
X – rejected or ineligible for listing.
“Threatened and near-threatened species” refersto any taxon in this table with an “L” under FFG,or any category under “EPBC” or “Vic” (exceptrare or poorly known).
No.: The number of records of the taxon in the FloraInformation System database as at September2006.
* denotes species exotic to Victoria
# denotes species indigenous to Victoria but notthe study area
Gym
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Upr
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audi
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a33
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lish
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EPB
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GN
o.
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pp.
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lish
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eSc
ien
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ame
EPB
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ual B
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127
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tail*
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443
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173
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Eng
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Nam
eSc
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tifi
c N
ame
EPB
CV
icFF
GN
o.
348 River Red Gum Forests Investigation > 2006
Brus
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rass
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19
Eng
lish
Nam
eSc
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ame
EPB
CV
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GN
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Des
maz
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ibol
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ia a
urea
75G
race
ful S
pear
-gra
ssA
ustr
ostip
a ac
roci
liata
8G
rass
Poac
eae
spp.
13G
rass
(na
tura
lised
)*Po
acea
e sp
p.(n
atur
alis
ed)
6G
reat
Bro
me*
Brom
us d
iand
rus
261
Gre
en P
igeo
n-gr
ass*
Seta
ria v
iridi
s1
Gre
y Tu
ssoc
k-gr
ass
Poa
sieb
eria
na14
Gre
y Tu
ssoc
k-gr
ass
Poa
sieb
eria
na v
ar.
hirt
ella
5G
rey
Tuss
ock-
gras
sPo
a si
eber
iana
var
. si
eber
iana
2H
air
Gra
ss*
Aira
spp
.73
Hai
ry P
anic
Pani
cum
eff
usum
17H
are’
s-ta
il G
rass
*La
guru
s ov
atus
4H
ighl
and
Bent
*A
gros
tis c
apill
aris
var
. ar
ista
ta1
Hill
Wal
laby
-gra
ssA
ustr
odan
thon
ia e
riant
ha34
Italia
n M
illet
*Se
taria
ital
ica
1Ita
lian
Rye-
gras
s*Lo
lium
mul
tiflo
rum
6Je
richo
Wire
-gra
ssA
ristid
a je
richo
ensi
s va
r. s
ubsp
inul
ifera
eL
2Jo
hnso
n G
rass
*So
rghu
m h
alep
ense
6K
anga
roo
Gra
ssTh
emed
a tr
iand
ra48
Ken
tuck
y Bl
ue-g
rass
*Po
a pr
aten
sis
3K
ikuy
u*Pe
nnis
etum
cla
ndes
tinum
20K
need
Spe
ar-g
rass
Aus
tros
tipa
bige
nicu
lata
17K
need
Wal
laby
-gra
ssA
ustr
odan
thon
ia g
enic
ulat
a4
Kno
tted
Bar
ley-
gras
s*H
orde
um s
ecal
inum
4
Eng
lish
Nam
eSc
ien
tifi
c N
ame
EPB
CV
icFF
GN
o.
349Discussion Paper
Kno
tted
Poa
Poa
drum
mon
dian
ar
4K
nott
y Sp
ear-
gras
sA
ustr
ostip
a no
dosa
78K
nott
ybut
t G
rass
Pasp
alid
ium
con
stric
tum
55La
rge
Qua
king
-gra
ss*
Briz
a m
axim
a44
Leaf
y W
alla
by-g
rass
Aus
trod
anth
onia
bip
artit
a s.
l.33
Leaf
y W
alla
by-g
rass
Aus
trod
anth
onia
bip
artit
a s.
s.8
Less
er B
urr-
gras
s*C
ench
rus
ince
rtus
2Le
sser
Can
ary-
gras
s*Ph
alar
is m
inor
78Le
sser
Qua
king
-gra
ss*
Briz
a m
inor
81Li
vers
eed
Gra
ss*
Uro
chlo
a pa
nico
ides
1Lo
bed
Wal
laby
-gra
ssA
ustr
odan
thon
ia a
uric
ulat
a17
Long
Gre
y-be
ard
Gra
ssA
mph
ipog
on c
aric
inus
var
. ca
ricin
us5
Long
-aw
n Sp
ear-
gras
sA
ustr
ostip
a te
nuifo
liav
2Lo
ng-h
air
Plum
e-gr
ass
Dic
hela
chne
crin
ita22
Long
-leaf
Wal
laby
-gra
ssN
otod
anth
onia
long
ifolia
2Lo
ng-n
osed
Sw
amp
Wal
laby
-gra
ssA
mph
ibro
mus
mac
rorh
inus
6Lo
ve G
rass
Erag
rost
is s
pp.
21M
adrid
Bro
me*
Brom
us m
adrit
ensi
s13
Mal
lee
Love
-gra
ssEr
agro
stis
die
lsii
173
Mal
lee
Tuss
ock-
gras
sPo
a lo
wan
ensi
sr
1M
anna
Gra
ss*
Gly
ceria
dec
linat
a3
Mar
sh F
ox-t
ail*
Alo
pecu
rus
geni
cula
tus
51M
at G
rass
Hem
arth
ria u
ncin
ata
var.
unc
inat
a46
Mea
dow
Bro
me*
Brom
us r
acem
osus
sub
sp. c
omm
utat
us4
Med
iterr
anea
n Ba
rley-
gras
s*H
orde
um h
ystr
ix59
Med
iterr
anea
n Br
ome*
Brom
us la
nceo
latu
s22
Mex
ican
Lov
e-gr
ass*
Erag
rost
is m
exic
ana
1N
ativ
e C
ouch
Cyn
odon
dac
tylo
n va
r. p
ulch
ellu
sk
33N
ativ
e M
illet
Pani
cum
dec
ompo
situ
m v
ar.
deco
mpo
situ
m24
Nee
dle
Gra
ssTr
iraph
is m
ollis
r12
Nig
ger-
head
sEn
neap
ogon
nig
rican
s6
Nor
ther
n Ba
rley-
gras
s*H
orde
um g
lauc
um17
5O
at K
anga
roo-
gras
sTh
emed
a av
enac
eak
4O
at*
Ave
na s
ativ
a25
Oat
*A
vena
spp
.21
9O
rang
e Fo
x-ta
il*A
lope
curu
s ae
qual
is13
Pale
Pig
eon-
gras
s*Se
taria
pum
ila s
ubsp
. pu
mila
11Pa
mpa
s G
rass
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orta
deria
spp
.1
Pani
cPa
nicu
m s
pp.
7Pa
nic
Gra
ssPa
spal
idiu
m s
pp.
25Pa
nic
Veld
t-gr
ass*
Ehrh
arta
ere
cta
var.
ere
cta
12Pa
nic*
Pani
cum
gilv
um18
Para
doxi
cal C
anar
y-gr
ass*
Phal
aris
par
adox
a13
7Pa
spal
um*
Pasp
alum
dila
tatu
m15
9
Eng
lish
Nam
eSc
ien
tifi
c N
ame
EPB
CV
icFF
GN
o.
Pasp
alum
*Pa
spal
um s
pp.
8Pe
pper
Gra
ssPa
nicu
m la
evin
ode
v5
Pere
nnia
l Bea
rd-g
rass
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Agr
opog
on li
ttor
alis
1Pe
renn
ial R
ye-g
rass
*Lo
lium
per
enne
194
Pere
nnia
l Vel
dt-g
rass
*Eh
rhar
ta c
alyc
ina
2Pi
geon
Gra
ss*
Seta
ria s
pp.
(nat
ural
ised
)1
Plum
p Sp
ear-
gras
sA
ustr
ostip
a ar
istig
lum
is11
4Po
rcup
ine
Gra
ssTr
iodi
a sc
ario
sa24
Prai
rie G
rass
*Br
omus
cat
hart
icus
52Pr
airie
Gra
ss*
Brom
us c
atha
rtic
us v
ar. c
atha
rtic
us12
Pric
kly
Barn
yard
-gra
ss*
Echi
noch
loa
mur
icat
a va
r. m
icro
stac
hya
2Pr
ickl
y Sp
ear-
gras
sA
ustr
ostip
a pi
lata
v1
Purp
le L
ove-
gras
sEr
agro
stis
lacu
naria
v90
Purp
lish
Wal
laby
-gra
ssA
ustr
odan
thon
ia t
enui
or3
Qui
cksi
lver
Gra
ss*
Aira
cup
ania
na42
Qui
zzic
al S
pear
-gra
ssA
ustr
ostip
a st
upos
a2
Rat’s
-tai
l Fes
cue*
Vulp
ia m
yuro
s75
3Ra
t’s-t
ail F
escu
e*Vu
lpia
myu
ros
f.m
yuro
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tail
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chSp
orob
olus
mitc
helli
i49
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t-ta
il G
rass
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obol
us s
pp.
6Ra
t-ta
il G
rass
*Sp
orob
olus
afr
ican
us5
Red
Brom
e*Br
omus
rub
ens
766
Red
Nat
al-g
rass
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elin
is r
epen
s su
bsp.
rep
ens
1Re
d-le
g G
rass
Both
rioch
loa
mac
ra18
Reed
Ben
t-gr
ass
Dey
euxi
a qu
adris
eta
73Re
ed S
wee
t-gr
ass*
Gly
ceria
max
ima
3Rh
odes
Gra
ss*
Chl
oris
gay
ana
8Ri
ce M
illet
*Pi
ptat
heru
m m
iliac
eum
3Ri
gid
Pani
cW
halle
ya p
rolu
ta22
1Ri
ver
Swam
p W
alla
by-g
rass
Am
phib
rom
us f
luita
nsV
X17
8Ro
ugh
Dog
’s-ta
il*C
ynos
urus
ech
inat
us13
Roug
h Sp
ear-
gras
sA
ustr
ostip
a sc
abra
sub
sp.
falc
ata
471
Roug
h Sp
ear-
gras
sA
ustr
ostip
a sc
abra
203
Roug
h Sp
ear-
gras
sA
ustr
ostip
a sc
abra
sub
sp.
scab
ra15
Roug
h-se
ed W
ire-g
rass
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tida
obsc
ura
eL
2Ry
e Be
etle
-gra
ssTr
ipog
on lo
liifo
rmis
r12
Rye
Gra
ss*
Loliu
m s
pp.
82Sa
lt C
ouch
Spor
obol
us v
irgin
icus
4Sa
nd B
rom
eBr
omus
are
nariu
sr
18Sa
nd W
ire-g
rass
Aris
tida
cont
orta
11Sc
aly
Poa
Poa
fax
r1
Sea
Barle
y-gr
ass*
Hor
deum
mar
inum
282
Serr
ated
Tus
sock
*N
asse
lla t
richo
tom
a2
Shin
y W
alla
by-g
rass
Aus
trod
anth
onia
indu
ta5
Shor
t W
alla
by-g
rass
Aus
trod
anth
onia
car
phoi
des
14
Eng
lish
Nam
eSc
ien
tifi
c N
ame
EPB
CV
icFF
GN
o.
350 River Red Gum Forests Investigation > 2006
Shor
t-aw
ned
Whe
at-g
rass
Elym
us m
ultif
loru
sk
10Sh
ort-
bris
tle W
alla
by-g
rass
Aus
trod
anth
onia
set
acea
var
. bre
vise
tar
1Sh
ort-
crow
n Sp
ear-
gras
sA
ustr
ostip
a cu
rtic
oma
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hair
Plum
e-gr
ass
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hela
chne
sci
urea
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. ag
g.5
Sibe
rian
Wild
-rye
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ymus
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ticau
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le L
ove-
gras
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agro
stis
fal
cata
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y Bl
ue-g
rass
Dic
hant
hium
ser
iceu
m s
ubsp
. se
riceu
m8
Silk
y Br
ownt
opEu
lalia
aur
ea63
Silk
y U
mbr
ella
-gra
ssD
igita
ria a
mm
ophi
lav
19Si
lky-
head
sC
ymbo
pogo
n ob
tect
use
2Si
lver
top
Wal
laby
-gra
ssJo
ycea
pal
lida
6Si
lver
y H
air-
gras
s*A
ira c
aryo
phyl
lea
38Sl
ende
r Ba
rb-g
rass
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raph
olis
str
igos
a3
Slen
der
Love
-gra
ssEr
agro
stis
exi
gua
e7
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der
Pani
cPa
spal
idiu
m g
raci
ler
1Sl
ende
r Pi
geon
Gra
ss*
Seta
ria p
arvi
flora
7Sl
ende
r W
alla
by-g
rass
Aus
trod
anth
onia
rac
emos
a va
r. r
acem
osa
21Sm
all B
urr-
gras
sTr
agus
aus
tral
ianu
sr
3Sm
all H
air-
gras
s*M
olin
erie
lla m
inut
a5
Smal
l-see
d Pl
ume-
gras
sD
iche
lach
ne m
icra
ntha
2Sm
alle
r St
ink-
gras
s*Er
agro
stis
min
or1
Smoo
th W
alla
by-g
rass
Aus
trod
anth
onia
laev
is3
Soft
Bro
me*
Brom
us h
orde
aceu
s su
bsp.
hor
deac
eus
228
Soft
Lov
e-gr
ass*
Erag
rost
is p
ilosa
4So
ft T
usso
ck-g
rass
Poa
mor
risii
2So
uthe
rn C
ane-
gras
sEr
agro
stis
infe
cund
a14
3So
uthe
rn S
wam
p W
alla
by-g
rass
Am
phib
rom
us n
eesi
i4
Spea
r G
rass
Aus
tros
tipa
spp.
301
Spea
r-gr
ass
Aus
tros
tipa
tric
hoph
ylla
r3
Spea
r-gr
ass
Aus
tros
tipa
scab
ragr
oup
4Sp
ider
Gra
ssEn
tero
pogo
n ac
icul
aris
462
Spin
y Bu
rr-g
rass
*C
ench
rus
long
ispi
nus
11Sp
iny
Mud
-gra
ssPs
eudo
raph
is s
pine
scen
s13
2Sp
urre
d Sp
ear-
gras
sA
ustr
ostip
a gi
bbos
a86
Squi
rrel
-tai
l Fes
cue*
Vulp
ia b
rom
oide
s19
7St
erile
Bro
me*
Brom
us s
teril
is20
Ster
ile O
at*
Ave
na s
teril
is3
Ster
ile O
at*
Ave
na s
teril
is s
ubsp
. lu
dovi
cian
a10
Ster
ile O
at*
Ave
na s
teril
is s
ubsp
. st
erili
s2
Stiff
Rye
-gra
ss*
Loliu
m lo
liace
um4
Stin
k G
rass
*Er
agro
stis
cili
anen
sis
21Su
mm
er G
rass
Dig
itaria
spp
.1
Sum
mer
Gra
ss*
Dig
itaria
san
guin
alis
10Su
pple
Spe
ar-g
rass
Aus
tros
tipa
mol
lis9
Eng
lish
Nam
eSc
ien
tifi
c N
ame
EPB
CV
icFF
GN
o.
Swam
p M
illet
Isac
hne
glob
osa
1Sw
amp
Wal
laby
-gra
ssA
mph
ibro
mus
spp
.30
Swee
t Ve
rnal
-gra
ss*
Ant
hoxa
nthu
m o
dora
tum
3Ta
ll C
up-g
rass
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chlo
a cr
ebra
k1
Tall
Fesc
ue*
Fest
uca
arun
dina
cea
4Ta
ll K
eros
ene
Gra
ssA
ristid
a ho
lath
era
var.
hol
athe
rav
6Ta
ll Sp
ear-
gras
sA
ustr
ostip
a pu
bino
dis
2Ta
ll W
heat
-gra
ss*
Loph
opyr
um p
ontic
um12
Teff
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agro
stis
tef
1Ti
ny B
ent
Agr
ostis
aus
tral
iens
isr
1Ti
ny B
ristle
-gra
ss*
Rost
raria
pum
ila40
Toow
oom
ba C
anar
y-gr
ass*
Phal
aris
aqu
atic
a11
7Tu
ssoc
k G
rass
Poa
aust
ralis
spp
. ag
g.2
Tuss
ock
Gra
ssPo
a sp
p.14
Two-
row
Bar
ley*
Hor
deum
dis
ticho
n2
Um
brel
la G
rass
Dig
itaria
div
aric
atis
sim
av
4Va
sey
Gra
ss*
Pasp
alum
urv
illei
2Ve
ldt
Gra
ss*
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arta
spp
.1
Velv
et W
alla
by-g
rass
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trod
anth
onia
pilo
sa7
Vern
al G
rass
*A
ntho
xant
hum
spp
.1
Wal
l Bro
me*
Brom
us t
ecto
rum
5W
all F
escu
e*Vu
lpia
mur
alis
118
Wal
laby
Gra
ssD
anth
onia
s.l.
spp
.11
2W
alla
by G
rass
Aus
trod
anth
onia
spp
.13
4W
alla
by G
rass
Rytid
ospe
rma
spp.
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arre
go S
umm
er-g
rass
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alid
ium
jubi
floru
m44
5W
ater
Cou
ch*
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alum
dis
tichu
m18
3W
eepi
ng G
rass
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rola
ena
stip
oide
s va
r. s
tipoi
des
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eepi
ng L
ove-
gras
sEr
agro
stis
par
viflo
ra23
Wee
ping
Wal
laby
-gra
ssA
ustr
odan
thon
ia p
enic
illat
a1
Wes
tern
Rat
-tai
l Gra
ssSp
orob
olus
cre
ber
v3
Wet
land
Wal
laby
-gra
ssN
otod
anth
onia
sem
iann
ular
is1
Whe
at*
Triti
cum
aes
tivum
8W
hisk
y G
rass
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ndro
pogo
n vi
rgin
icus
1W
hite
-wat
er P
anic
*Pa
nicu
m o
bsep
tum
3W
horle
d Pi
geon
-gra
ss*
Seta
ria v
ertic
illat
a6
Wild
Oat
*A
vena
fat
ua17
7W
imm
era
Rye-
gras
s*Lo
lium
rig
idum
445
Win
dmill
Gra
ssC
hlor
is t
runc
ata
188
Win
dmill
Gra
ssC
hlor
is s
pp.
3W
ire-g
rass
Aris
tida
spp.
1W
itch
Pani
c*Pa
nicu
m h
illm
anii
4Ya
kka
Gra
ssSp
orob
olus
car
oli
r19
York
shire
Fog
*H
olcu
s la
natu
s29
Can
adia
n Po
ndw
eed*
Elod
ea c
anad
ensi
s11
Eng
lish
Nam
eSc
ien
tifi
c N
ame
EPB
CV
icFF
GN
o.
351Discussion Paper
Eel G
rass
Valli
sner
ia a
mer
ican
a va
r. a
mer
ican
a41
Hyd
rilla
Hyd
rilla
ver
ticill
ata
r1
Swam
p Li
lyO
ttel
ia o
valif
olia
sub
sp.
oval
ifolia
13G
olde
n W
eath
er-g
lass
Hyp
oxis
hyg
rom
etric
a1
Hyp
oxis
Hyp
oxis
spp
.7
Tiny
Sta
rH
ypox
is g
labe
lla v
ar.
glab
ella
34Ye
llow
Sta
rH
ypox
is g
labe
lla s
.l.1
Yello
w S
tar
Hyp
oxis
vag
inat
a1
Blue
Pig
root
*Si
syrin
chiu
m ir
idifo
lium
4Bu
lbil
Wat
soni
a*W
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184
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196
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le R
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Nam
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.l.12
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l.1
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lish
Nam
eSc
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tifi
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ame
EPB
CV
icFF
GN
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352 River Red Gum Forests Investigation > 2006
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tifol
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Nam
eSc
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EPB
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.)8
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rev
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Eng
lish
Nam
eSc
ien
tifi
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ame
EPB
CV
icFF
GN
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Day
Lily
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ax L
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35
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Nam
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EPB
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Spre
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naw
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Goo
sefo
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heno
podi
um g
lauc
um13
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bula
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gwee
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ysph
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. gl
omul
ifera
18G
oat
Hea
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ocer
a tr
icor
nis
r11
5G
oose
foot
Che
nopo
dium
spp
.11
Gre
en C
oppe
rbur
rSc
lero
laen
a de
curr
ens
v17
Gre
y Bl
uebu
shM
aire
ana
appr
essa
64G
rey
Cop
perb
urr
Scle
rola
ena
diac
anth
a54
1G
rey
Cop
perb
urr
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rola
ena
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ubby
for
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s su
bsp.
ha
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emoi
des
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Roly
-pol
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lero
laen
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vill
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airy
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agon
a40
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airy
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head
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isso
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arad
oxus
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asta
te O
rach
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trip
lex
pros
trat
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thy
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bush
Mai
rean
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posi
tifol
iar
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edge
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hRh
agod
ia s
pine
scen
s37
6K
eele
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oose
foot
Che
nopo
dium
car
inat
umv
2K
idne
y Sa
ltbus
hA
trip
lex
stip
itata
19
Eng
lish
Nam
eSc
ien
tifi
c N
ame
EPB
CV
icFF
GN
o.
356 River Red Gum Forests Investigation > 2006
Lax
Goo
sefo
otEi
nadi
a tr
igon
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ubsp
. trig
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ss B
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Mai
rean
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k31
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ne C
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lee
Cop
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iple
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mili
o11
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exic
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ea*
Che
nopo
dium
am
bros
ioid
es9
Nat
ive
Ora
che
Atr
iple
x au
stra
lasi
ca3
Nitr
e G
oose
foot
Che
nopo
dium
nitr
aria
ceum
223
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ding
Sal
tbus
hEi
nadi
a nu
tans
sub
sp.
nuta
ns87
8O
ld-m
an S
altb
ush
Atr
iple
x nu
mm
ular
ia94
Old
-man
Sal
tbus
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trip
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mul
aria
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sp.
num
mul
aria
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arl B
lueb
ush
Mai
rean
a se
difo
liar
9Po
inte
d Sa
ltbus
hA
trip
lex
acut
ibra
ctea
r2
Poin
ted
Saltb
ush
Atr
iple
x ac
utib
ract
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ubsp
. kar
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nsis
r4
Pop
Saltb
ush
Atr
iple
x ho
loca
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vL
16Po
vert
y Bu
shSc
lero
laen
a in
tric
ata
v11
Pric
kly
Saltw
ort
Sals
ola
trag
us18
6Pr
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y Sa
ltwor
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a tr
agus
sub
sp. t
ragu
s28
3Ra
dian
t Bl
uebu
shM
aire
ana
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ata
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d-st
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podi
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acro
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Blue
bush
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rean
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38Ro
sy B
lueb
ush
Mai
rean
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iocl
ada
7Ru
by S
altb
ush
Ench
ylae
na t
omen
tosa
var
. to
men
tosa
1096
Sago
Bus
hM
aire
ana
pyra
mid
ata
119
Salo
opEi
nadi
a ha
stat
a32
Salt
Cop
perb
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ena
vent
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ae
L2
Saltb
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Atr
iple
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p.86
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spp
.5
Satin
y Bl
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ana
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a43
Seab
lite
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da s
pp.
15Sh
inin
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lass
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tH
alos
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Shor
t-le
af B
lueb
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Mai
rean
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ort-
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g Sa
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mys
bra
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tera
514
Silv
er S
altb
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Atr
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x rh
agod
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L15
Slen
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ende
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ptoc
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530
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g Bl
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l-lea
f Bl
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aire
ana
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e13
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f G
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foot
Che
nopo
dium
des
erto
rum
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sp.
mic
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Bus
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eoba
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pro
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lora
e2
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bane
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heno
podi
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ural
e37
Eng
lish
Nam
eSc
ien
tifi
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ame
EPB
CV
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GN
o.
Spea
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ar
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a79
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221
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oose
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inki
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foot
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heno
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ulva
ria1
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aked
Cop
perb
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rola
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s33
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ngle
d C
oppe
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varic
ata
k36
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bush
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rean
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ipte
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rnip
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17Tw
in-f
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ingl
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rean
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ides
227
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nicu
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ruit
Blue
bush
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chito
n sc
lero
laen
oide
s20
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ican
Bon
esee
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ubsp
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onili
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nthu
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Ann
ual B
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L15
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ual C
udw
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Euch
iton
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nnua
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ysoc
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23
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ual F
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cio
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us16
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ual N
ew H
olla
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aisy
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ual N
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olla
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aisy
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ervi
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ar.
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Hol
land
Dai
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bcer
vicu
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43A
rtic
hoke
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ynar
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s14
Ast
er-w
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Ast
er s
ubul
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284
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urr*
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110
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pp.
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btus
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lish
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ame
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CV
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GN
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Bran
chin
g G
roun
dsel
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cunn
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cun
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istly
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eed*
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Cas
sini
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Com
mon
Cot
ula
Cot
ula
aust
ralis
128
Com
mon
Cud
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dEu
chito
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volu
crat
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.l.22
Com
mon
Eve
rlast
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Chr
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lum
api
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s.l.
110
Com
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.8
Com
mon
Sne
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tiped
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nnin
gham
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hist
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nthu
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3C
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unra
yTr
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odis
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pygm
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112
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Whi
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unra
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odan
the
florib
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e3
Com
pact
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s.l.
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reep
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dEu
chito
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llinu
s s.
s.27
Eng
lish
Nam
eSc
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EPB
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-leaf
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258
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hysc
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deci
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Fiel
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endu
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p.17
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aisy
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zzy
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Hol
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syV
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cun
eata
241
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mor
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r3
Fuzz
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var
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ar
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ande
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Tara
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eryt
hros
perm
a3
Eng
lish
Nam
eSc
ien
tifi
c N
ame
EPB
CV
icFF
GN
o.
358 River Red Gum Forests Investigation > 2006
Gar
den
Dan
delio
n*Ta
raxa
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Sect
. ha
mat
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lish
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Eng
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360 River Red Gum Forests Investigation > 2006
Whi
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243
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leaf
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156
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Nam
eSc
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EPB
CV
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364 River Red Gum Forests Investigation > 2006
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Eng
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Nam
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EPB
CV
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GN
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365Discussion Paper
Swam
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Eng
lish
Nam
eSc
ien
tifi
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ame
EPB
CV
icFF
GN
o.
366 River Red Gum Forests Investigation > 2006
Gre
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1
Eng
lish
Nam
eSc
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tifi
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ame
EPB
CV
icFF
GN
o.
367Discussion Paper
Hai
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139
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Eng
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Nam
eSc
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EPB
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368 River Red Gum Forests Investigation > 2006
Ann
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Nam
eSc
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tifi
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EPB
CV
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Bask
et W
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lix X
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371Discussion Paper
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372 River Red Gum Forests Investigation > 2006
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APPENDIX 5: Fauna Species Recorded in the River Red Gum Forests Study Area
LEGEND:
EPBC: status under Commonwealth EnvironmentProtection and Biodiversity Conservation Act1999, as at December 2004.EN Endangered: A taxon is endangered when itis not critically endangered but is facing a veryhigh risk of extinction in the wild in the nearfuture.VU Vulnerable: A taxon is vulnerable when it isnot critically endangered or endangered but isfacing a high risk of extinction in the wild in themedium-term future.
Vic: conservation status in Victoria, after DSE (2003a).EX Extinct: when there is no reasonable doubtthat the last individual has died. A taxon ispresumed Extinct when exhaustive surveys inknown and/or expected habitat, at appropriatetimes (diurnal, seasonal, annual), throughout itshistoric range have failed to record an individual.Surveys should be over a time frame appropriateto the taxon’s life cycle and life form. Records ofseveral extinct species that were formerly foundin the study area are not in the DSE databases—they are listed in a separate table following themain table.RX Regionally Extinct: As for Extinct but withina defined region that does not encompass theentire geographic range of the taxon—in thiscase Victoria. A taxon is presumed RegionallyExtinct when exhaustive surveys in known and/orexpected habitat, at appropriate times (diurnal,seasonal, annual), throughout the region havefailed to record an individual. Surveys should beover a time frame appropriate to the taxon’s lifecycle and life form. Records of several regionallyextinct species that were formerly found in thestudy area are not in the DSE databases—theyare listed in a separate table following the maintable.CR Critically Endangered: A taxon is CriticallyEndangered when the best available evidenceindicates that it meets any of the criteria A to Efor Critically Endangered (see Species SurvivalCommission 2001), and it is therefore consideredto be facing an extremely high risk of extinctionin the wild.EN Endangered in Victoria: when the bestavailable evidence indicates that the taxon meetsany of the criteria A to E for Endangered (seeSpecies Survival Commission 2001), and it istherefore considered to be facing a very high riskof extinction in the wild.
VU Vulnerable in Victoria: when the bestavailable evidence indicates that the taxon meetsany of the criteria A to E for Vulnerable (seeSpecies Survival Commission 2001), and it istherefore considered to be facing a high risk ofextinction in the wild.NT Near Threatened: A taxon is NearThreatened when it has been evaluated againstthe criteria but does not qualify for CriticallyEndangered, Endangered, Vulnerable now, but isclose to qualifying for, or is likely to qualify for athreatened category in the near future.DD Data Deficient: A taxon is Data Deficientwhen there is inadequate information to make adirect, or indirect, assessment of its risk ofextinction based on its distribution and/orpopulation status. A taxon in this category maybe well studied, and its biology well known, butappropriate data on abundance and/ordistribution are lacking. Data Deficient istherefore not a category of threat. Listing of taxain this category indicates that more information isrequired and acknowledges the possibility thatfuture research will show that threatenedclassification is appropriate.
FFG: status under the Victorian Flora and FaunaGuarantee Act 1988, as at December 2004. Forthe most up-to-date listings under the Act, visit:http://www.dse.vic.gov.au
L – listed as threatened.
“Threatened and near-threatened species” refers toany taxon in this table with an “L” under FFG, orany category under “EPBC” or “Vic” (exceptData Deficient species).
No.: The number of records of the taxon in the Atlasof Victorian Wildlife and the Aquatic Faunadatabases as at September 2006.
* denotes species exotic to Victoria^ denotes species listed under the JAMBA agreement# denotes spedies listed under the CAMBA agreement(see chapter 5 for details of these agreements)
As of September 2006, the Department of Sustainability and Environment (DSE) Atlas of Victorian Wildlife andAquatic Fauna databases contained records for the following taxa in River Red Gum Forests study area. These twodatabases provide coverage of vertebrate fauna and threatened invertebrate fauna but are still improving theircoverage of other invertebrates. Chapter 5 describes key points relating to species diversity and threatened species.
373Discussion Paper
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2931
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75C
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551
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e86
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569
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1342
Pied
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rius
NT
194
Litt
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lack
Cor
mor
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773
Gre
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8A
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alia
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lican
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1149
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165
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63A
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35Ro
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lish
Nam
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ien
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198
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170
Spot
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NT
42Sw
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Har
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401
Brow
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209
Gre
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Acc
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eV
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1Br
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572
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161
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41Pe
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130
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18A
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Purp
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752
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30Re
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11Pa
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neck
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135
Long
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5Bu
sh S
tone
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566
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133
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8Re
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557
Red-
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283
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Cre
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768
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phic
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9Li
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loss
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lla85
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112
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9Re
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L27
4C
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1587
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us3
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s13
68A
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9Bl
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onne
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113
Swift
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121
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29El
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42Pa
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249
Brus
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115
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328
Mas
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s15
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106
Whi
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Kin
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ae18
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s64
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135
Supe
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Tree
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1140
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2481
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spl
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4Va
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ted
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-wre
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us la
mbe
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188
Eng
lish
Nam
eSc
ien
tifi
c N
ame
EPB
CV
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GN
o.
375Discussion Paper
Whi
te-w
inge
d Fa
iry-w
ren
Mal
urus
leuc
opte
rus
230
Mal
lee
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wre
nSt
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mal
lee
VU
VU
L3
Stria
ted
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ssw
ren
Am
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stria
tus
NT
1Sp
otte
d Pa
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638
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y H
eath
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nH
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a38
Rufo
us F
ield
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alam
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ampe
stris
NT
2Re
dthr
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Pyrr
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bler
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aV
UL
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icro
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bre
viro
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1347
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tern
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ygon
eG
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eryg
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ygon
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Brow
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illA
cant
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195
Inla
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horn
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nthi
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Che
stnu
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cant
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402
Buff
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s41
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Thor
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oa13
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Tho
rnbi
llA
cant
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a80
7St
riate
d Th
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cant
hiza
line
ata
249
Sout
hern
Whi
tefa
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phel
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leuc
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s34
1Re
d W
attle
bird
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hoch
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car
uncu
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684
Litt
le W
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chr
ysop
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9Sp
iny-
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ked
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ter
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ntha
geny
s ru
fogu
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444
Strip
ed H
oney
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ecto
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cha
lanc
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ta12
0N
oisy
Fria
rbird
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mon
cor
nicu
latu
s58
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ttle
Fria
rbird
Phile
mon
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909
Rege
nt H
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Blue
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243
Bell
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42Ye
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Man
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9Ye
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137
Yello
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7Pu
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Yello
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252
Gre
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76Bl
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216
Brow
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Mel
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458
Whi
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103
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lish
Nam
eSc
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Whi
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L14
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9Bl
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Art
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Dus
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amus
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827
Eng
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Nam
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EPB
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376 River Red Gum Forests Investigation > 2006
Litt
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Pied
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9Bl
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term
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1
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EPB
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Boug
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378 River Red Gum Forests Investigation > 2006
Com
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ount
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may
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may
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rd.
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mat
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ay n
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uatic
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perf
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ayfly
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Eng
lish
Nam
eSc
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tifi
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ame
EPB
CV
icFF
GN
o.
379Discussion Paper
Dra
gonf
lyH
emig
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us s
p.4
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phyl
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anar
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en.
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sp.
12
Eng
lish
Nam
eSc
ien
tifi
c N
ame
EPB
CV
icFF
GN
o.
Cra
ne f
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Tipu
lidae
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01
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Cra
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The
tabl
e be
low
list
s fa
una
spec
ies
once
rec
orde
d in
the
stu
dy a
rea
but
now
ext
inct
1an
d ot
her
spec
ies
that
wer
e al
so r
ecor
ded
in t
he s
tudy
are
a bu
t ar
e no
w e
xtin
ct in
Vic
toria
2(a
nd n
ot r
ecor
ded
in t
he A
tlas
ofV
icto
rian
Wild
life)
. Th
ese
spec
ies
are
not
in t
he m
ain
list
of s
peci
es r
ecor
ded
in t
he s
tudy
are
a. A
num
ber
ofot
her
spec
ies
poss
ibly
occ
urre
d in
the
stu
dy a
rea
at t
he t
ime
of E
urop
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380 River Red Gum Forests Investigation > 2006
381Discussion Paper
APPENDIX 6: Reservation Status of EcologicalVegetation Classes (EVCs)
A vegetation community is a collection of co-occurringplant species—it reflects the vegetation’s response toenvironmental influences such as geology, soils,landform and rainfall. Ecological Vegetation Classes(EVCs) are groups of one or more vegetationcommunities which exist under a common regime ofecological processes and which are linked to broadlandscape features. The similarity of environmentalregimes is apparent in comparable life forms, genera andvegetation structure. The communities within an EVCdiffer due to geographical separation rather than majorecological differences.
Once EVCs have been identified, it is possible to maptheir distributions with the aid of maps of sites wherethey are known to occur; aerial photographs; maps ofthe main environmental determinants of vegetationdistribution (such as soils, rainfall, topography); any pre-existing vegetation mapping; and extensive field work toidentify boundaries and ground-check that EVCs doindeed occur where they have been mapped.
As well as the standard EVCs, the process of mappinggenerates two variations of the standard EVCs—mosaicsand complexes. A mosaic consists of two or morediscrete EVCs that cannot be mapped separately due tothe scale of the map. A complex occurs where two ormore EVCs are unable to be distinguished in an area butare known to exist discretely elsewhere. A slash is usedto separate the component EVCs in the name of amosaic or complex. For example, AquaticHerbland/Floodplain Grassy Wetland Mosaic. SomeEVCs occur only in mosaics. The units identified on asingle vegetation map may be communities, EVCs,mosaics or complexes, depending on the resolution atwhich the units were described and mapped. However,for convenience, mapped vegetation units of any ofthese types are referred to simply as ‘EVCs’.
The extent to which vegetation has been depleted—thatis, cleared as a result of European settlement—is a keyconsideration in the establishment of conservationreserve systems (see chapter 10). To assess the extent ofdepletion of each EVC, it is necessary to map the extentof EVCs prior to European settlement, as well as thecurrent distribution of EVCs. The mapping of vegetationprior to European settlement is called ‘pre-1750mapping’; 1750 being a round-number year closely pre-dating European settlement in Australia. Essentially pre-1750 mapping involves predicting, or modelling, thevegetation that was originally cleared from areas which
no longer support indigenous vegetation. It involves asimilar process to mapping the current distribution ofEVCs, but (of course) with little or no assistance fromaerial photographs and ground-checking.
In most regions, the EVC currently found at any givenlocation where native vegetation remains is nearlyalways the same as that which would have been therepre-1750—even if it has been cleared and regrown,most of the fundamental determinants of that EVCremain in place (e.g. slope, soil type, climate) and so thesame EVC should re-establish (although probably in apoorer state). In the River Red Gum Forests study area,one of the most pervasive environmental changes hasbeen the alteration of flood regimes across wetlands andforests. Flood regime is one of the primary determinantsof EVCs in these environments, and so in many instancesthe vegetation present at a site will differ from thatpresent prior to river regulation. One of the best knownexamples of this phenomenon is the invasion of Moiragrass plains (Floodplain Grassy Wetland EVC) by river redgums (probably Riverine Swamp Forest EVC) and giantrush. As a result it is impossible to reliably map all pre-1750 EVCs, and some apparently straightforwardchanges in EVC extent (such as a reduction from pre-1750 extent to current extent) may mask more complexchanges such as a greater total reduction countered by asmaller increase in some areas. Overall, this problemwould generally lead to around 10 percent variation inthe total extent of some EVCs.
The vegetation of the study area is mapped in Map B.Because of the large number of EVCs, and the closelyinterwoven occurrence of EVCs in many areas (e.g. seethe Barmah forest inset in Map B), it is not possible todiscern individual EVCs over much of a map of this scale.Accordingly, EVCs have been grouped for presentation inMap B—with EVCs of similar composition andenvironmental determinants shown in the same colour.Complementing Map B is Appendix 7, which providesdescriptions of each of the main EVCs in the study area.
The EVC mapping on which Map B is based is also thebasis of the Representation Table following. Broadly, thistable lists all the EVCs mapped in the study area, andquantifies their current and pre-1750 extent in the studyarea, as well as their current extent in conservationreserves and other public land. Preceding the table isthe following detailed key for the column headings andsymbols used in the table.
382 River Red Gum Forests Investigation > 2006
KEY
Data in the Representation Table were derived by GISanalysis, that is overlaying, on computer, maps of:
• the pre-1750 extent of EVCs (data used to deriveMap B); that is, the distribution of EVCs as it isthought to have been immediately prior to Europeansettlement;
• current extent of intact native vegetation, based on aseparate mapping exercise to the EVC mapping; and
• current extent of each public land use category.
Many small public land units may not be picked up inthe public land GIS layer. For example, none of thesefigures include roads and roadsides, for which noestimate of extent exists. In addition to theRepresentation Table for the study area as a whole,presented here, VEAC has prepared RepresentationTables for each of the main bioregions which overlapwith the study area. These tables are available on theVEAC website (www.veac.vic.gov.au) or by request fromVEAC.
The total extent of both public land (see Table 10.1) andthe conservation reserve system in the study area isgreater than the figures shown in the RepresentationTable because several thousand hectares of public landthat do not support intact native vegetation are notincluded relevant totals in the Representation Tablebelow.
It is important to understand that the figures in theRepresentation Table are generated by computer-basedspatial analysis, and are not meant to be interpretedwith the level of precision at which they are provided.That is, for example, the table should not be interpretedas saying that the current extent of Alluvial Plains Semi-arid Grassland is exactly 3517 hectares—as opposed to3516, 3518, or indeed 3520 hectares. As general rule,the focus should be on changes to the vegetation moregenerally, or on more extensive EVCs. In addition, allarea figures are rounded to the nearest hectare. As aresult several EVCs have ‘0’ pre-1750 extent in the tablee.g. Sedgy Riverine Forest/Spike-sedge Wetland Mosaic,for which the precise figure is 0.46 hectares.
Column 1: Ecological Vegetation Classes
The names of the 169 EVCs mapped within the RiverRed Gum Forests study area. Here, the term ‘EVCs’ is
used to describe several units of classification: EVCs per se, and complexes and mosaics—see above for definitions of these units and their relationships toeach other. The last row (‘other - natural’) is mostly river bank, sandy beach, and other bare ground.
Column 2: Pre-1750 Extent
The total area in hectares thought to have beenoccupied by each EVC prior to European settlement,corresponding to the mapped extent of EVCs used togenerate Map B.
Column 3: Current Extent (public and private land)
The total area in hectares currently occupied by eachEVC—that is, that part of the pre-1750 distributionwhere intact native vegetation is currently present.
Column 4: Percent Remaining
The current extent (column 3) as a percentage of thepre-1750 extent (column 2), for each EVC.
Column 5: Conservation Status (JANIS)
A simplified version of the status of each EVC in termsof the categories developed by JANIS, and the DSE theBioregional Conservation status (see below). Theassessments refer to the study area as a whole and takeno account of EVC distributions outside the study areaor in bioregions within the study area. The percentremaining (column 4) is a key factor in assigning EVCs toJANIS categories. E = endangered, V = vulnerable, R =rare.
Column 6: Dedicated Reserve System
The total area in hectares of each EVC in existing publicland categories that comprise the conservation reservesystem (see chapter 10).
Column 7: Other Public Land
The total area in hectares of each EVC in all public landcategories outside the dedicated reserve system. Notethat some of these areas will be in informal reservessuch as Special Protection Zones in state forest.
Column 8: Dedicated Reserves as % of Pre-1750Extent
The area of dedicated reserves (column 6) as apercentage of the pre-1750 extent (column 2), for eachEVC.
Status
Presumedextinct
Endangered
Vulnerable
Depleted
Rare
Least concern
Code
X
E
V
D
R
LC
Criteria
Probably no longer present in the Bioregion (the accuracy of this assumption is limitedby the use of remotely sensed 1:100,000 scale woody vegetation cover mapping todetermine depletion – grassland, open woodland and wetland types are particularlyaffected).
Contracted to less than 10% of former range; OR
Less than 10% pre-European extent remains; OR
Combination of depletion, degredation, current threats and rarity is comparable overallto the above:
• 10 to 30% pre-European extent remains and severely degraded over a majority ofthis area; or
• naturally restricted EVC reduced to 30% or less of former range and moderatelydegraded over a majority of this area; or
• rare EVC cleared and/or moderately degraded over a majority of former area.
10 to 30% pre-European extent remains; OR
Combination of depletion, degradation, current threats and rarity is comparable overallto the above:
• greater than 30% and up to 50% pre-European extent remains and moderatelydegraded over a majority of this area; or
• greater than 50% pre-European extent remains and severely degraded over amajority of this area; or
• naturally restricted EVC where greater than 30% pre-European extent remains andmoderately degraded over a majority of this area; or
• rare EVC cleared and/or moderately degraded over a majority of former area.
Greater than 30% and up to 50% pre-European extent remains; OR
Combination of depletion, degradation and current threats is comparable overall to the above and:• greater than 50% pre-European extent remains and moderately degraded over a
majority of this area; or
Rare EVC (as defined by geographic occurrence) but neither depleted, degraded norcurrently threatened to an extent that would qualify as Endangered, Vulnerable orDepleted.
Greater than 50% pre-European extent remains and subject to little to no degradationover a majority of this area.
Source: MDBC (2005b)
Definitions of Bioregional Conservation Status for Ecological Vegetation Classes. Note the differentcategories and definitions used for EVCs compared with the conservation status categories anddefinitions used for flora and fauna species in Appendices 4 and 5.
383Discussion Paper
384 River Red Gum Forests Investigation > 2006
Allu
vial
Pla
ins
Sem
i-arid
Gra
ssla
nd3,
520
3,51
799
.91,
568
1,54
844
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vial
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race
s H
erb-
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dlan
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reek
line
Gra
ssy
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dlan
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osai
c15
961
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05
0.0
Aqu
atic
Her
blan
d13
913
910
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139
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atic
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blan
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Gra
ssy
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land
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aic
5959
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atic
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atic
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st M
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atic
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ll M
arsh
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aic
6868
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land
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rass
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land
467
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6116
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101
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in G
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y W
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iver
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and
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aic
95
54.5
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in G
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all M
arsh
Mos
aic
2121
100.
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in R
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in R
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Woo
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3434
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022
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Eco
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Veg
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1750
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Are
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1750
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12
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Are
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2718
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0
Floo
dpla
in R
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Woo
dlan
d/Ri
verin
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Fore
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osai
c23
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0.0
Floo
dpla
in R
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d/Se
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osai
c20
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.0R
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0
Floo
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in R
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d/Ta
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arsh
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01
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Floo
dpla
in W
etla
nd C
ompl
ex1,
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912
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Floo
dway
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d H
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and
1,16
61,
156
99.2
183
871
15.7
Floo
dway
Pon
d H
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and/
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Swam
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Com
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2,52
32,
523
100.
00
2,51
80.
0
Floo
dway
Pon
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and/
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Swam
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rest
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8932
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and/
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sh M
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hwat
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4,22
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ssy
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and
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1,14
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98.7
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23.5
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55
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ssy
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ssy
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Fore
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8,32
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76.5
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Gra
ssy
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Fore
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p Fo
rest
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6767
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0R
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0.0
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ssy
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rine
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11
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rine
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edgy
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rest
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344
344
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0
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ssy
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st/T
all M
arsh
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0R
02
0.0
Gra
ssy
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dlan
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137
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ssy
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lley
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ssy
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st M
osai
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6E,
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thy
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est
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b-ric
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othi
ll Fo
rest
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0
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rmitt
ent
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py W
oodl
and
9,20
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Bed
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blan
d3,
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3,64
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.81,
850
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um S
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land
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,045
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5,65
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286
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wam
py W
oodl
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69,6
8541
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,016
8.2
Eco
log
ical
Veg
etat
ion
Cla
sses
(EV
Cs)
Pre-
1750
Exte
nt
Ded
icat
ed
Res
erve
Sys
tem
Cu
rren
tEx
ten
t
Perc
ent
Rem
ain
ing
Co
nse
rvat
ion
Stat
us
Oth
er P
ub
licLa
nd
Ded
icat
edR
eser
ves
as%
of
Pre-
1750
Ext
ent
12
34
56
78
Are
a in
ha
Are
a in
ha
385Discussion Paper
386 River Red Gum Forests Investigation > 2006
Lign
um S
wam
py W
oodl
and/
Lake
Bed
Her
blan
d M
osai
c12
564
51.2
R0
350.
0
Lign
um S
wam
py W
oodl
and/
Plai
ns G
rass
land
Mos
aic
12,6
381,
352
10.7
V9
200.
1
Lign
um W
etla
nd51
,420
17,1
0133
.31,
938
2,12
33.
8
Loam
y Sa
nds
Mal
lee
1,39
91,
384
99.0
1,33
610
95.6
Low
Che
nopo
d Sh
rubl
and
40,8
4938
,819
95.0
5,97
25,
443
14.6
Low
Ris
es W
oodl
and
3,02
071
623
.7V,
R54
308
1.8
Low
Ris
es W
oodl
and/
Rive
rine
Swam
py W
oodl
and
Mos
aic
22
100.
0R
02
0.0
Lune
tte
Woo
dlan
d1,
581
131
8.3
E, R
025
0.0
Mos
aic
of A
quat
ic H
erbl
and/
Floo
dway
Pon
d H
erbl
and-
Rive
rine
Swam
p Fo
rest
Com
plex
22
100.
0R
02
0.0
Mos
aic
of A
quat
ic H
erbl
and/
Sedg
y Ri
verin
e Fo
rest
-Riv
erin
e Sw
amp
Fore
st C
ompl
ex0
010
0.0
R0
00.
0
Mos
aic
of D
rain
age-
line
Agg
rega
te/F
lood
way
Pon
d H
erbl
and-
Rive
rine
Swam
p Fo
rest
Com
plex
11
100.
0R
01
0.0
Mos
aic
of D
rain
age-
line
Agg
rega
te/G
rass
y Ri
verin
e Fo
rest
-Riv
erin
e Sw
amp
Fore
st C
ompl
ex14
614
610
0.0
R0
146
0.0
Mos
aic
of D
rain
age-
line
Agg
rega
te/S
edgy
Riv
erin
e Fo
rest
-Riv
erin
e Sw
amp
Fore
st C
ompl
ex67
6799
.8R
019
0.0
Mos
aic
of F
lood
plai
n G
rass
y W
etla
nd/F
lood
way
Pon
d H
erbl
and-
Rive
rine
Swam
p Fo
rest
Com
plex
11
100.
0R
01
0.0
Mos
aic
of F
lood
plai
n G
rass
y W
etla
nd/G
rass
y Ri
verin
e Fo
rest
-Riv
erin
e Sw
amp
Fore
st C
ompl
ex23
2310
0.0
R0
220.
0
Mos
aic
of F
lood
plai
n G
rass
y W
etla
nd/S
edgy
Riv
erin
e Fo
rest
-Riv
erin
e Sw
amp
Fore
st C
ompl
ex2
210
0.0
R0
20.
0
Mos
aic
of F
lood
plai
n Ri
paria
n W
oodl
and/
Sedg
y Ri
verin
e Fo
rest
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erin
e Sw
amp
Fore
st C
ompl
ex0
010
0.0
R0
00.
0
Mos
aic
of F
lood
way
Pon
d H
erbl
and/
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ssy
Rive
rine
Fore
st-R
iver
ine
Swam
p Fo
rest
Com
plex
44
100.
0R
04
0.0
Mos
aic
of F
lood
way
Pon
d H
erbl
and/
Sedg
y Ri
verin
e Fo
rest
-Riv
erin
e Sw
amp
Fore
st C
ompl
ex8
810
0.0
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80.
0
Mos
aic
of G
rass
y Ri
verin
e Fo
rest
-Riv
erin
e Sw
amp
Fore
st C
ompl
ex/R
iver
ine
Swam
p Fo
rest
239
239
100.
0R
023
80.
0
Mos
aic
of G
rass
y Ri
verin
e Fo
rest
/Flo
odw
ay P
ond
Her
blan
d-Ri
verin
e Sw
amp
Fore
st C
ompl
ex37
937
910
0.0
R0
379
0.0
Eco
log
ical
Veg
etat
ion
Cla
sses
(EV
Cs)
Are
a in
ha
Pre-
1750
Exte
nt
Ded
icat
ed
Res
erve
Sys
tem
Cu
rren
tEx
ten
t
Perc
ent
Rem
ain
ing
Co
nse
rvat
ion
Stat
us
Are
a in
ha Oth
er P
ub
licLa
nd
Ded
icat
edR
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ves
as%
of
Pre-
1750
Ext
ent
12
34
56
78
Mos
aic
of G
rass
y Ri
verin
e Fo
rest
/Pla
ins
Gra
ssy
Woo
dlan
d-G
rass
y W
oodl
and
Com
plex
00
100.
0R
00
0.0
Mos
aic
of G
rass
y Ri
verin
e Fo
rest
/Sed
gy R
iver
ine
Fore
st-R
iver
ine
Swam
p Fo
rest
Com
plex
7676
100.
0R
076
0.0
Mos
aic
of R
iver
ine
Gra
ssy
Woo
dlan
d/Fl
oodw
ay P
ond
Her
blan
d-Ri
verin
e Sw
amp
Fore
st C
ompl
ex1
110
0.0
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10.
0
Mos
aic
of R
iver
ine
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p Fo
rest
/Flo
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ay P
ond
Her
blan
d-Ri
verin
e Sw
amp
Fore
st C
ompl
ex88
288
210
0.0
R0
881
0.0
Mos
aic
of R
iver
ine
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py W
oodl
and/
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y Ri
verin
e Fo
rest
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erin
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amp
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st C
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ex32
3210
0.0
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320.
0
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aic
of S
edgy
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erin
e Fo
rest
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erin
e Sw
amp
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st C
ompl
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Floo
dway
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d H
erbl
and-
R65
6510
0.0
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650.
0
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aic
of S
edgy
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erin
e Fo
rest
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erin
e Sw
amp
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st C
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ex/T
all
Mar
sh7
710
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70.
0
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aic
of S
edgy
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erin
e Fo
rest
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odw
ay P
ond
Her
blan
d-Ri
verin
e Sw
amp
Fore
st C
ompl
ex31
3110
0.0
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310.
0
Mos
aic
of S
edgy
Riv
erin
e Fo
rest
/Sed
gy R
iver
ine
Fore
st-R
iver
ine
Swam
p Fo
rest
Com
plex
1,25
31,
231
98.2
01,
135
0.0
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aic
of T
all M
arsh
/Flo
odw
ay P
ond
Her
blan
d-Ri
verin
e Sw
amp
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st
Com
plex
8383
100.
0R
083
0.0
Mou
ntai
n Va
lley
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rian
Woo
dlan
d1,
325
892
67.3
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515
0.0
Plai
ns G
rass
land
251,
131
37,7
8415
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1,96
998
00.
8
Plai
ns G
rass
land
/Pla
ins
Gra
ssy
Woo
dlan
d/G
ilgai
Wet
land
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aic
13,1
881,
391
10.5
V19
192
0.1
Plai
ns G
rass
y W
etla
nd2,
172
645
29.7
V, R
121
235.
6
Plai
ns G
rass
y W
oodl
and
13,8
511,
532
11.1
V3
112
0.0
Plai
ns G
rass
y W
oodl
and/
Cre
eklin
e G
rass
y W
oodl
and/
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dpla
in R
ipar
ian
Woo
dlan
d M
osai
c1,
291
806.
2E,
R0
20.
0
Plai
ns G
rass
y W
oodl
and/
Cre
eklin
e G
rass
y W
oodl
and/
Wet
land
Fo
rmat
ion
Mos
aic
00
96.6
R0
0.0
Plai
ns G
rass
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oodl
and/
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ai W
etla
nd M
osai
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110
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00.
0
Plai
ns G
rass
y W
oodl
and/
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ssy
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dlan
d C
ompl
ex95
3031
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02
0.0
Plai
ns G
rass
y W
oodl
and/
Valle
y G
rass
y Fo
rest
Com
plex
141
3.8
E, R
00
0.0
Plai
ns G
rass
y W
oodl
and/
Valle
y G
rass
y Fo
rest
/Gra
ssy
Woo
dlan
d C
ompl
ex19
415
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04
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Eco
log
ical
Veg
etat
ion
Cla
sses
(EV
Cs)
Pre-
1750
Exte
nt
Ded
icat
ed
Res
erve
Sys
tem
Cu
rren
tEx
ten
t
Perc
ent
Rem
ain
ing
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nse
rvat
ion
Stat
us
Oth
er P
ub
licLa
nd
Ded
icat
edR
eser
ves
as%
of
Pre-
1750
Ext
ent
12
34
56
78
Are
a in
ha
Are
a in
ha
387Discussion Paper
388 River Red Gum Forests Investigation > 2006
Plai
ns S
altm
arsh
Com
plex
298
266
89.3
R3
257
0.9
Plai
ns S
avan
nah
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257
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1
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ns W
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204
22,0
5516
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313
4,82
70.
2
Plai
ns W
oodl
and/
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um W
etla
nd M
osai
c1,
250
137
11.0
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00.
0
Plai
ns W
oodl
and/
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ns G
rass
land
/Gilg
ai W
etla
nd M
osai
c6
227
.3V,
R0
0.0
Plai
ns W
oodl
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Red
Gum
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land
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aic
1,03
416
916
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40.
0
Red
Gum
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land
1,70
61,
600
93.8
451,
350
2.7
Red
Gum
Wet
land
/Pla
ins
Gra
ssy
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land
Mos
aic
718
398
55.4
R1
200
0.2
Ridg
ed P
lain
s M
alle
e1,
825
463
25.4
V, R
112
836.
1
Ripa
rian
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st40
031
979
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024
60.
0
Ripa
rian
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st/S
wam
py R
ipar
ian
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dlan
d M
osai
c42
3480
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01
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rian
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st/S
wam
py R
ipar
ian
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dlan
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paria
n Sh
rubl
and/
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rpm
ent
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0
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rine
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nopo
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and
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361
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5643
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219.
6
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rine
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nopo
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00
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rine
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nopo
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land
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aic
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326
623
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0
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rine
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mer
al W
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110
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0
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rine
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ssla
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061
0.0
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rine
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ssy
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8451
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376
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546.
0
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rine
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ssy
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dlan
d/G
rass
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rest
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amp
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ex0
010
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0
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rine
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ssy
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ains
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dlan
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ompl
ex1,
355
283
20.9
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042
0.0
Rive
rine
Gra
ssy
Woo
dlan
d/Pl
ains
Woo
dlan
d/G
ilgai
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land
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plex
829
146
17.6
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06
0.0
Rive
rine
Gra
ssy
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dlan
d/Pl
ains
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dlan
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verin
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Woo
dlan
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ex1,
131
280
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01
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Rive
rine
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ssy
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dlan
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rine
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ssy
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verin
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st M
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0
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rine
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ssy
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dlan
d/Ri
verin
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dlan
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osai
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1
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rine
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ssy
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dlan
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gy R
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st M
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556
663
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053
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0
Rive
rine
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p Fo
rest
12,6
8712
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94.9
3411
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0.3
Rive
rine
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p Fo
rest
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e Sw
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c55
5510
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0
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log
ical
Veg
etat
ion
Cla
sses
(EV
Cs)
Pre-
1750
Exte
nt
Ded
icat
ed
Res
erve
Sys
tem
Cu
rren
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ten
t
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ent
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ain
ing
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nse
rvat
ion
Stat
us
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er P
ub
licLa
nd
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edR
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ves
as%
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1750
Ext
ent
12
34
56
78
Are
a in
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Are
a in
ha
Rive
rine
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p Fo
rest
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st M
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c47
539
683
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1326
52.
8
Rive
rine
Swam
p Fo
rest
/Sed
gy R
iver
ine
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st-R
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ine
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p Fo
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C
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ex1,
325
1,21
891
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0
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rine
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rest
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ke-s
edge
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land
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aic
66
100.
0R
06
0.0
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rine
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p Fo
rest
/Tal
l Mar
sh M
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c57
357
310
0.0
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Rive
rine
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py W
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and
8,93
86,
182
69.2
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542
0.5
Rive
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py W
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824
2,23
138
.38
210
0.1
Rive
rine
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py W
oodl
and/
Plai
ns G
rass
y W
etla
nd M
osai
c30
830
9.7
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10
0.3
Rive
rine
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py W
oodl
and/
Sedg
y Ri
verin
e Fo
rest
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aic
348
345
99.2
R0
321
0.0
Rock
y O
utcr
op S
hrub
land
141
4330
.4R
01
0.0
Rush
y Ri
verin
e Sw
amp
293
206
70.4
R0
193
0.0
Salin
e La
ke M
osai
c18
218
199
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3514
119
.0
Sam
phire
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ubla
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351
1,26
693
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751
822
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Sand
Rid
ge W
oodl
and
1,84
572
739
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112
40.
1
Sand
ston
e Ri
dge
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blan
d/Lo
w R
ises
Woo
dlan
d M
osai
c14
78
5.3
E, R
00
0.0
Sedg
y Ri
verin
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rest
17,6
1316
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93.9
203
14,1
831.
2
Sedg
y Ri
verin
e Fo
rest
/Riv
erin
e Sw
amp
Fore
st C
ompl
ex3,
876
3,83
198
.80
3,73
70.
0
Sedg
y Ri
verin
e Fo
rest
/Spi
ke-s
edge
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land
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aic
00
100.
0R
00
0.0
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y Ri
verin
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rest
/Tal
l Mar
sh M
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210
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0
Sem
i-arid
Che
nopo
d W
oodl
and
33,4
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60.3
1,97
77,
589
5.9
Sem
i-arid
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illa
Woo
dlan
d1,
839
482
26.2
V, R
1823
31.
0
Sem
i-arid
Woo
dlan
d18
,870
12,3
3765
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137
3,56
737
.8
Shal
low
Fre
shw
ater
Mar
sh61
961
899
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4357
27.
0
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bby
Dry
For
est
98
84.1
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00.
0
Shru
bby
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rine
Woo
dlan
d7,
961
7,95
099
.92,
373
4,91
529
.8
Spik
e-se
dge
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land
795
726
91.3
R78
615
9.8
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e-se
dge
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land
/Tal
l Mar
sh M
osai
c59
5910
0.0
R50
984
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Sub-
salin
e D
epre
ssio
n Sh
rubl
and
1,01
193
292
.1R
113
664
11.2
Swam
py R
ipar
ian
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dlan
d9
337
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01
0.0
Swam
py W
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and
9,93
71,
712
17.2
V0
384
0.0
Eco
log
ical
Veg
etat
ion
Cla
sses
(EV
Cs)
Pre-
1750
Exte
nt
Ded
icat
ed
Res
erve
Sys
tem
Cu
rren
tEx
ten
t
Perc
ent
Rem
ain
ing
Co
nse
rvat
ion
Stat
us
Oth
er P
ub
licLa
nd
Ded
icat
edR
eser
ves
as%
of
Pre-
1750
Ext
ent
12
34
56
78
Are
a in
ha
Are
a in
ha
389Discussion Paper
390 River Red Gum Forests Investigation > 2006
Tall
Mar
sh1,
437
1,41
198
.253
1,29
13.
7
Tall
Mar
sh/A
quat
ic H
erbl
and
Mos
aic
77
100.
0R
07
0.0
Tall
Mar
sh/N
on-V
eget
atio
n M
osai
c16
1610
0.0
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160.
0
Tall
Mar
sh/O
pen
Wat
er M
osai
c18
518
499
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015
60.
0
Tall
Mar
sh/R
iver
ine
Swam
p Fo
rest
Mos
aic
33
100.
0R
03
0.0
Valle
y G
rass
y Fo
rest
1,56
021
413
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R0
280.
0
Valle
y G
rass
y Fo
rest
/Gra
ssy
Dry
For
est
Mos
aic
31
35.7
R0
00.
0
Wet
land
For
mat
ion
11,8
853,
625
30.5
2425
50.
2
Woo
rinen
Mal
lee
2,46
51,
393
56.5
668
486
27.1
Woo
rinen
San
ds M
alle
e2,
672
2,45
091
.72,
265
3384
.8
wat
er b
ody
- na
tura
l or
man
mad
e6,
000
6,64
611
0.8
307
4,84
75.
1
othe
r -
natu
ral
3,83
33,
822
125
2,17
5
Tota
ls:
1,21
5,77
448
3,36
039
.868
,010
179,
926
5.6
Eco
log
ical
Veg
etat
ion
Cla
sses
(EV
Cs)
Pre-
1750
Exte
nt
Ded
icat
ed
Res
erve
Sys
tem
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rren
tEx
ten
t
Perc
ent
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ain
ing
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nse
rvat
ion
Stat
us
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er P
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EVC 806 Alluvial Plains Semi-arid GrasslandDefining characteristics: Grassland (turf) to herblandwith only incidental shrubs. Flood-promoted flora,potentially including a wide range of opportunisticephemeral / annual species.Structure: Grassland / herbland - variable according toseasonal conditions and site-wetness, mostly < 0.2 m.The potential dominant, Red-tail Couch Sporobolusmitchellii, is a species with warm season growth, withvigour and performance flood-promoted, but apparentlynot emergent until after flood recession.Habitat: Low-lying areas within at least previously flood-prone (mostly) higher-level terraces. These can beeffectively shallow lakes when flooded. Also sometimeson flats along creeks of the further north-west, inhabitat akin to that of Floodway Pond Herbland (whichmostly occurs nearer the Murray River). Floristics: While some examples are virtually devoid ofwoody plants, incidental shrubs can include TangledLignum Muehlenbeckia florulenta, Nitre GoosefootChenopodium nitrariaceum, Streaked CopperburrSclerolaena tricuspis and Spiny Lignum Muehlenbeckiahorrida. The floristics are quite variable. In lessdesiccated examples, the vegetation is dominated byRed-tail Couch Sporobolus mitchellii. These habitats canbe relatively species -poor or include a wide a range ofassociated species, mostly annual or ephemeral herbs,many of which are shared with more open versions ofLignum Shrubland (with which Alluvial Plains Semi-aridGrassland appears to intergrade). Pale Beauty-headsCalocephalus sonderi is sometimes co-dominant (or eveneffectively dominant in the absence of emergent growthof Red-tail Couch Sporobolus mitchellii. A range ofother small chenopods (e.g. Bluebush Maireana spp.,Star Bluebush Stelligera endecaspinis) can be present inthe drier north-west. Additional species commonlyrecorded within this mapping unit include Salt Sea-spurrey Spergularia sp. 3, Grass Cushion Isoetopsisgraminifolia, Mouse-tail Myosurus minimus var. australis,Crassula Crassula spp., Rough Raspwort Haloragisaspera, Goodenia spp., Clay Plantain Plantagocunninghamii, River Bluebell Wahlenbergia fluminalis,Hairy Burr-daisy Calotis hispidula, Hard-head DaisyBrachyscome lineariloba, Variable Daisy Brachyscomeciliaris, Rosinweed Cressa cretica, Warty Pepper-cressLepidium papillosum, Slender Groundsel Senecioglossanthus and Desert Spinach Tetragonia eremaea s.l.Distribution: Lindsay Island, Mulcra Island, WalpollaIsland, Kings Billabong. Former distribution possiblyobscured by impacts of land-use and altered hydrologyin other parts of apparent potential range (e.g. Hattah -Kulkyne).Vegetation Quality: While this habitat is capable oftolerating prolonged periods without flooding, it seemsinevitable that, if sustained into the longer-term, theabsence of flooding will result in permanent changes to
the floristic composition (including the invasion ofspecies from non-flooded habitats and loss of speciesdependant on at least occasional flooding). A range ofsignificant flora can occur in this vegetation (includingversions transitional to Lignum Shrubland).
EVC 653 Aquatic HerblandDefining characteristics: Herbland of permanent tosemi-permanent wetlands, dominated by sedges(especially on shallower verges) and/or aquatic herbs.Occurs on fertile paludal soils, typically heavy claysbeneath organic accumulations. Previously widespreadwithin restricted areas of suitable habitat across thestudy area but now greatly reduced through drainingand use for agriculture.Structure: Herbland, floating mat to weakly emergent.Habitat: Permanent to seasonal wetland, in suitablysheltered sites with reliable water supply and soilsstaying moist at depth. Floristics: Indicator species: Water-milfoil Myriophyllumspp., Water-ribbons Triglochin procerum spp. agg. withRunning Mrash-flower Villarsia reniformis / Clove-stripLudwigia peploides subsp. montevidensis, and variouslyWater-lily Nymphaea spp., River Buttercup Ranunculusinundatus, Australian Lilaeopsis Lilaeopsis polyantha andSwamp Crassula Crassula helmsii. Diversity is potentiallyhigher on outer fringes, with a range of small herbs (e.g.Floating Club-sedge Isolepis fluitans, Lobelia spp.,Swamp Goodenia Goodenia humilis, Centella Centellacordifolia and/or Shining Pennywort Hydrocotylesibthorpioides).
EVC 829 Chenopod GrasslandDefining characteristics: Open to sparse shrublandwith a more or less continuous tussock grass swardfound on heavy clay plains fringing the active floodplainsof major watercourses such as the Loddon and Avoca. Structure: Open shrubland to 1 m with an inter-shrubsward of perennial caespitose grasses to 1 m. Short-lived perennial chenopod herbs and annual forbsvariously and seasonally dominate the field layer.Habitat: Occurs on relict alluvial plains and low risesassociated with clay lunettes. The soils are commonlygrey to red brown clays. Not normally subject toinundation as a consequence of overbank flows frommajor rivers but poorly drained settings may result inprotracted pooling of water in winter months due toheavy rainfall. Typically found in ‘inlying’ slightly raisedparts of the lower reaches of river systems. Floristics: No remnants of this distinctive and oncewidespread vegetation formation remain in asubstantially intact state in Victoria. As a consequence,detailed floristics cannot be specified. It is thought thatdivaricately branched chenopod shrubs such as LeaflessBluebush Maireana aphylla, Rohrlach’s BluebushMaireana rohrlachii, Nitre-bush Nitraria billardierei andHedge Saltbush Rhagodia spinescens once dominated
APPENDIX 7: Descriptions of the Main EVCs in the River Red Gum Forests Study AreaAppendix 6 provides definitions of vegetation communities, EVCs, mosaics and complexes. The following pages provide descriptions of the main 34 EVCs in the study area.
391Discussion Paper
392 River Red Gum Forests Investigation > 2006
this formation. Tangled Lignum Muehlenbeckiaflorulenta and the tall cane grass Southern Cane-grassEragrostis infecunda may also be occasional co-dominants in localised depressions or gilgai. The inter-shrub spaces are typically dominated by medium to largecaespitose grasses, particularly Rigid Panic Whalleyaproluta, Spider Grass Enteropogon acicularis, PlumpSpear-grass Austrostipa aristiglumis, Copper-awnedWallaby-grass Austrodanthonia fulva, and Brown-backWallaby-grass Austrodanthonia duttoniana. Othercommon perennials include Black Roly-poly Sclerolaenamuricata, Short-wing Saltbush Sclerochlamysbrachyptera, Tangled Copperburr Sclerolaena divaricata,Bush Minuria Minuria cunninghamii, Woolly ButtonsLeiocarpa panaetioides, Berry Saltbush Atriplexsemibaccata, Rosinweed Cressa australis and TwiggyLignum Muehlenbeckia diclina. The seasonal flora ofthis EVC would once have been very rich in annuals andgeophytes including Sunray Hyalosperma spp. SunrayRhodanthe spp. and Swainson Pea Swainsona spp.Distribution: Highly modified and widely cleared, thisEVC once occurred widely in the south and south-eastern riverine plains.
EVC 168 Drainage-line AggregateDefining characteristics: Eucalypt-dominatedwoodland with occasional scattered shrub layer over amostly grassy/sedgy to herbaceous ground-layer. Occurson low-gradient ephemeral to intermittent drainagelines, typically on fertile colluvial/alluvial soils, on a widerange of suitably fertile geological substrates. Structure: Varies from grassy wetland to low openherbland or sedgeland, and can develop to a Red GumSwamp in places.Habitat: Ephemeral wetlands and floodways alongdefined drainage-lines on the riverine floodplain. Floristics: River Red-gum Eucalyptus camaldulensis,Spiny Mud-grass Pseudoraphis spinescens, River SwampWallaby-grass Amphibromus fluitans, Common Spike-sedge Eleocharis acuta, Love Grass Eragrostis spp., smallannuals such as Button Rush Lipocarpha microcephala,Fringe Sedge Fimbristylis spp., and various Sedge Carexspp. Potentially diverse range of associated species,variously including Water Ribbons Triglochin procera s.l.,Upright Water-milfoil Myriophyllum crispatum, SwampLily Ottelia ovalifolia subsp ovalifolia, Floating PondweedPotamogeton tricarinatus, Common SneezeweedCentipeda cunninghamii, Yellow Twin-heads Ecliptaplatyglossa, Knotweed Persicaria spp., Dock Rumex spp.,Hypsela Hypsela tridens, Poison Pratia Lobelia concolor,Matted Starwort Stellaria caespitosa, and River BluebellWahlenbergia fluminalis. Total species richness can behigh due to the complexity of microhabitats.
EVC 809 Floodplain Grassy WetlandDefining characteristics: Wetland dominated byfloating aquatic grasses (which persist to some extent asturf during drier periods), occurring in the most flood-prone riverine areas. Typically treeless, but sometimeswith thickets of saplings or scattered more maturespecimens of River Red-gum Eucalyptus camaldulensis.Structure: Floating emergent aquatic grassland or turf-like grassland sward, according to prevailing conditions (inparticular the relevant stage of flood cycles). Typically <15
cm emergent, but stoloniferous aquatic growth mayexceed two metres, persisting as thick mats until grazedor cut back by frosts following flood recession. Habitat: Temporary shallow lakes in the most flood-proneareas. This vegetation type also occurs as a narrowintermediate band around floodway ponds - between theouter zone dominated by Common Spike-sedgeEleocharis acuta and the Floodway Pond Herblandtypically dominated by Sneezeweed Centipeda spp. andSmall Knotweed Polygonum plebium (or sometimesCommon Blown-grass Lachnagrostis filiformis, particularlyduring dry periods).Floristics: Typically dominated by Spiny Mud-grassPseudoraphis spinescens, sometimes with associatedspecies including Common Spike-sedge Eleocharis acuta,Creeping Knotweed Persicaria prostrata, Common Blown-grass Lachnagrostis filiformis, Native Couch Cynodondactylon var. pulchellus, Rat-tail Couch Sporobolusmitchellii and Sneezeweed Centipeda spp. Furtherupstream (e.g. Barmah), River Swamp Wallaby-grassAmphibromus fluitans (often with open Giant RushJuncus ingens) can also locally dominate or co-dominatevegetation of similar character. Ranges (both spatially andtemporally) from virtually monospecific (at optimumdevelopment) to diverse with opportunistic species.Distribution: Rare, small areas dispersed localities.Vegetation Quality: While a naturally very restrictedvegetation type within the study area, Floodplain GrassyWetland can be presumed to have become even rarer asa consequence of reduced flooding. Introduced speciesare opportunistic in this habitat during dry phases only.
EVC 56 Floodplain Riparian WoodlandDefining characteristics: An open woodlanddominated by River Red-gum Eucalyptus camaldulensisover a medium to tall shrub layer with a ground layerconsisting of amphibious and aquatic herbs and sedges. Habitat: Occurs along the banks and floodplains of thelarger meandering rivers and major creeks, often inconjunction with one or more floodplain wetlandcommunities. Elevation and rainfall are relatively lowand soils are fertile alluviums subject to periodic floodingand inundation.Floristics: River Red-gum Eucalyptus camaldulensis is thetypical dominant overstorey species. The occasionalspecimen of Manna Gum E. viminalis and MountainSwamp Gum E. camphora or Swamp Gum E. ovata mayoccur in the upper reaches of the Ovens, King andKiewa Rivers in transition to other EVCs such as RiparianForest or Swampy Woodland. Shrubs are predominantlySilver Wattle Acacia dealbata, and Tree VioletHymenanthra dentata. The ground cover on the drier,elevated banks consists mainly of Common TussockGrass Poa labillardierei with other species such as Bent-grass Deyeuxia spp. On the wetter, lower banks TallSedge Carex appressa, Common Reed Phragmitesaustralis, Silky Browntop Eulalia aurea, and various RushJuncus spp. and Sedge Cyperaceae spp. occur. Spike-sedge Eleocharis sphaecalata, Knotweed Persicaria spp.and other aquatic species are found in the low-lyingwetland areas with a range of herbs occupying theseasonally exposed soil.Comments: Floodplain Riparian Woodland represents a
mosaic of terraces, active floodways and formerchannels, and as such is not readily amenable to simplefloristic description. In many instances, streamregulation has diminished the extent of flooding.
EVC 172 Floodplain Wetland AggregateCollective label for the various zones of vegetationassociated with wetlands of riparian floodplains, bestdeveloped in association with Floodplain RiparianWoodland. Potentially includes mosaics ofscrub/shrubland, reedbed, sedgeland, rushland,grassland and/or herbland zones. The followingcomponents are variously recognisable within FloodplainWetland Aggregate: Aquatic Herbland, AquaticSedgeland, Tall Marsh, Floodway Pond Herbland andDwarf Floating Aquatic Herbland. Billabong Wetland isalso an aggregate EVC including many of thesecomponents.
EVC 810 Floodway Pond HerblandDefining characteristics: Low herbland on the dryingmud of floors of ponds on floodway systems (mainlyriverine floodplains).Structure: Low herbland, treeless (or virtually so),usually with a high content of ephemeral species.Habitat: Drying mud within ponds on floodplains. It canalso occur as a temporal component within somevariants of Billabong Wetland Aggregate, in associationwith other wetland types.Floristics: The floristics can be quite variable (bothspatially and temporally), according to the traits of therelevant individual pond. The following generalisedfloristic variations are noted. The floristics also vary intemporal cycles and probably between seasons at somelocations.• Common Sneezeweed Centipeda cunninghamii –
Matted Starwort Stellaria caespitosa (Riverine : mainlyBarmah - Tocumwal, but extending upstream alongtributaries - e.g. Loddon River at Lanacoorie)
• Knotweed Persicaria spp. (widespread, mainly south ofdivide, but also e.g. eastern end Barmah Forest)
• Globular Pigweed Dysphania glomulifera subsp.glomulifera – Fringe Sedge Fimbystylis spp. (rare andinadequately known, on sandy substrates - e.g. DeadRiver at Ulupna Island, Tarma at Barmah Forest)
• Mallee Floodway Pond Herbland : SneezeweedCentipeda spp., Small Knotweed Polygonum plebium(Carpet Weed Glinus spp., Creeping KnotweedPersicaria prostrata, Globular Pigweed Dysphaniaglomulifera subsp. glomulifera, Joyweed Alternantheraspp., Common Blown-grass Lachnagrostis filiformis;with narrow fringes of Spiny Mud-grass Pseudoraphisspinescens, Common Spike-sedge Eleocharis acuta andsometimes Fen Sedge Carex gaudichaudiana). Semi-arid versions can include an increased component ofspecies shared with the lacustrine habitat (notablySouthern Liquorice Glycyrrhiza acanthocarpa,Heliotrope Heliotropium spp. and Small Mud-matGlossostigma elatinoides). On rare occasions canoccur in fine-scale mosaic with Floodplain GrassyWetland. The association of Sneezeweed Centipedaspp. and Small Knotweed Polygonum plebium (oftenwith Carpet Weed Glinus spp.) appears to be rareoutside of Murray Mallee, e.g. Yarra River floodplainwhere apparently very rare and Ulupna Island) - the
distinction between this and the Dysphania -Fimbristylis variant may be somewhat arbitrary.
Distribution: Widely dispersed along major riparianfloodplains, but variable within restricted habitat andselectively depleted. Poorly known outside of MurrayRiver and tributaries.Vegetation Quality: In the Murray Mallee, subject toinvasion by River Red-gum Eucalyptus camaldulensisseedlings under reduced frequency and depth offlooding. In general often grazed and vulnerable tohydrological modification and nutrient run-off inagricultural areas.
EVC 945 Floodway Pond Herbland/Riverine SwampForest ComplexDefining characteristics: Ground layer dominated byherbaceous species largely shared with floodway ponds(Floodway Pond Herbland/Aquatic Herbland), or virtuallyabsent (due to thick accumulations of forest litter orpersistence of black water, or sometimes excluded bydense thickets of young River Red-gum Eucalyptuscamaldulensis regeneration).Structure: Tall woodland or open forest (20 to 40+ m)with low herbaceous ground layer, to a mosaic ofherbland (to 0.8 m, but mostly less than 0.2 m) withregeneration thickets of saplings (to c. 20 m).Habitat: Occurs along floodway systems on low-lyingterraces. Some occurrences appear to be a reflection ofconditions naturally intermediate between the habitatsof the respective EVCs, while others are within areassubject to ecological process, including ecologicalchange due to decreased flooding.Floristics: Major species vary between the two areaswhere the complex is documented.• Murray Mallee – River Red-gum Eucalyptus
camaldulensis with Common Blown-grassLachnagrostis filiformis, Common SneezeweedCentipeda cunninghamii, Joyweed Alternanthera spp.and Knotweed Persicaria spp. - especially CreepingKnotweed P. prostrata ( sparse Common Spike-sedgeEleocharis acuta or Spiny Mud-grass Pseudoraphisspinescens; variously Indian Cudweed Gnaphaliumpolycaulon, Couch Cynodon dactylon var. pulchellus,Spreading Sneezeweed Centipeda minima s.s. andYellow Twin-heads Eclipta platyglossa).
• Mid-Murray (e.g. Barmah) – River Red-gum Eucalyptuscamaldulensis with Common Blown-grassLachnagrostis filiformis and Lachnagrostis filiformis var.2, Matted Starwort Stellaria caespitosa, SneezeweedCentipeda spp., especially Common Sneezeweed C.cunninghamii, Lesser Joyweed Alternantheradenticulata, Knotweed Persicaria spp. (CreepingKnotweed P. prostrata, Slender Knotweed P. decipiens,Water Pepper P. hydropiper), Upright Water-milfoilMyriophyllum crispatum, Common Spike-sedgeEleocharis acuta (sometimes with a component ofGiant Rush Juncus ingens, Flecked Flat-sedge Cyperusgunnii subsp. gunnii or Bulrush Typha spp.).
The abundance of annual species can be highly variablebetween seasons (and equivalent seasons in differentyears). Distribution: Widely dispersed, but within restrictedhabitat along the Murray River and major tributaries. Vegetation Quality: Sites supporting Floodway PondHerbland / Riverine Swamp Forest Complex are typically
393Discussion Paper
undergoing floristic change as a consequence ofchanged hydrology (reduced flooding, and in parts ofBarmah Forest, increased incidence of minor summerflooding).
EVC 106 Grassy Riverine Forest Defining characteristics: Open eucalypt forest (towoodland) with grassy understorey, dominated byspecies indicative of at least occasional flooding, but alsotolerant of sustained dry periods.Structure: Open forest to tall open forest or tallwoodland, with (tufted) grassy understorey.Habitat: More elevated flood-prone river terraces (orotherwise free-draining if in locations subject to deeperor more frequent inundation).Floristics: River Red-gum Eucalyptus camaldulensis withWarrego Summer-grass Paspalidium jubiflorum dominantin the groundlayer (associated species include CommonSneezeweed Centipeda cunninghamii, WoodlandSwamp-daisy Brachyscome basaltica var. gracilis, RiverBluebell Wahlenbergia fluminalis, Flat SpurgeChamaesyce drummondii, Cotton Fireweed Senecioquadridentatus, Slender Dock Rumex brownii and NativeCouch Cynodon dactylon var. pulchellus; with CommonSpike-sedge Eleocharis acuta relatively minor if present).Distribution: Widespread along Murray River, in mostareas within restricted habitat (lower terraces), rare in farnorth-west.Vegetation Quality: While a number of introducedspecies are often present in the vegetation, WarregoSummer-grass Paspalidium jubiflorum tends to retaindominance in the absence of other major forms ofdisturbance. This vegetation type occurs within a zonethat mostly still receives some flooding. While indicativeof flood-prone areas and only producing vigorousgrowth in warm weather following flooding, tussocks ofWarrego Summer-grass Paspalidium jubiflorum are ableto persist over a number of seasons without flood.
EVC 812 Grassy Riverine Forest/Riverine SwampForest ComplexDefining characteristics: Eucalypt forest of flood-proneareas, where the understorey dominants (e.g. CommonSpike-sedge Eleocharis acuta and/or Spiny Mud-grassPseudoraphis spinescens) of Riverine Swamp Forest areconspicuous in association or fine-scale mosaic with thelarger tussock species (Warrego Summer-grassPaspalidium jubiflorum) characteristic of Grassy RiverineForest.Structure: Usually a tall open forest to open forest(sometimes woodland), with a grassy-herbaceousground-layer (to c. 1 m).Habitat: Grassy Riverine Forest/Riverine Swamp ForestComplex occurs in flood-prone areas, where inundationis regular but mostly shallower or less frequent/sustainedrelative to sites supporting Riverine Swamp Forest.These include broad shallow floodways and low-lyingriver terraces prone to reasonably regular flooding.Floristics: River Red-gum Eucalyptus camaldulensis, withWarrego Summer-grass Paspalidium jubiflorum, inassociation or mosaic with Common Spike-sedgeEleocharis acuta and/or Spiny Mud-grass Pseudoraphisspinescens (other conspicuous species variously includeKnotweed Persicaria spp. - in particular CreepingKnotweed P. prostrata, Native Couch Cynodon dactylon
var. pulchellus, Common Sneezeweed Centipedacunninghamii, Yellow Twin-heads Eclipta platyglossa,Riverina Bitter-cress Cardamine moirensis, LesserJoyweed Alternanthera denticulata s.l., Common Blown-grass Lachnagrostis filiformis, Spreading SneezeweedCentipeda minima subsp. minima s.s. and River BluebellWahlenbergia fluminalis).Distribution: Scattered distribution along river, but veryrestricted outside of Barmah Forest.
EVC 813 Intermittent Swampy WoodlandDefining characteristics: Eucalypt (Acacia) woodlandwith (variously shrubby) rhizomatous sedgy - turf grassunderstorey, at best development dominated by floodstimulated species in association with flora tolerant ofinundation.Structure: Woodland with (variously shrubby)rhizomatous grassy - sedgy (to herbaceous) ground-layer.Habitat: Floristics are indicative of flooding which isunreliable but extensive when it happens and usuallyalso traces of salinity. Low elevation areas on riverterraces (mostly at the rear of point-bar deposits oradjacent to major floodways) and lacustrine verges(where sometimes localised to narrow transitionalbands). Soils often have a shallow sand layer over heavyand frequently slightly brackish soils.Floristics: River Red-gum Eucalyptus camaldulensis withEumong Acacia stenophylla (+/- Black Box Eucalyptuslargiflorens and relatively open Tangled LignumMuehlenbeckia florulenta). Floristics is variable andoften appears skewed by disturbance. Major speciesinclude Rat-tail Couch Sporobolus mitchellii, Spiny Flat-sedge Cyperus gymnocaulos, Rosinweed Cressa australis,Rough Raspwort Haloragis aspera, CommonSneezeweed Centipeda cunninghamii, Spreading Nut-heads Sphaeromorphaea australis, Blue Rod Stemmodiaflorulenta, Common Blown-grass Lachnagrostis filiformis,River Bluebell Wahlenbergia fluminalis and Pale Beauty-heads Calocephalus sonderi, with Warrego Summer-grass Paspalidium jubiflorum typically a very minorspecies present. On flood-prone sandy terracesconnected to the river or major floodway creeks, Love-grass Eragrostis spp. and Native Couch Cynodondactylon var. pulchellus can be locally dominant - thisvariant is transitional towards Riverine Swamp Forest.The relevant habitat is extremely restricted, and thesandy terraces variant is very rare - small areas areknown from Belsar Island and Barmah Forest.Distribution: In further North-West Victoria,Intermittent Swampy Woodland is of scattereddistribution along Murray River, mostly downstream ofRobinvale but extending to near the Murrumbidgee Riverconfluence (e.g. Lake Walla Walla and Lindsay Island,Kings Billabong, Kulkyne Forest and presumed formerlyextensive along the Chalka Creek system at HattahLakes). Vegetation Quality: The relevant vegetation isextensively invaded by *Fog-fruit Phyla canescens atKings Billabong, and in general floristically alteredthrough desiccation and grazing (extremely so atHattah). The EVC is quite variable, and may haveincluded a number of communities, but the originalfloristic patterns are often obscured by the impacts ofdisturbance (grazing and desiccation).
River Red Gum Forests Investigation > 2006394
EVC 107 Lake Bed HerblandDefining characteristics: Herbland dominated byspecies adapted to drying mud within lake beds. Someevade periods of prolonged inundation as seed, othersas dormant tuber-like rootstocks.Structure: Herbland, varying from very low to mediumheight (0.02 -) 0.1- 0.5 (- 1.0 m), sometime with lowopen shrubland component to 0.5 m. Subject toinvasion by River Red-gum Eucalyptus camaldulensisseedlings under reduced frequency and depth offlooding - sometimes with regeneration thickets ofyoung trees.Habitat: Drying deep-cracking mud of lakes onfloodplains. While flooding events are mostlyintermittent, lakes can retain water for several or moreseasons. Actively growing at the drying mud stage.Typically heavy clay soils. This vegetation can be intemporal phase with the open water / bare mud‘unvegetated’ unit.Floristics: Can vary seasonally, depending on when andhow much water has been available / other seasonalconditions. The main native species include SouthernLiquorice Glycyrrhiza acanthocarpa, Australian HollyhockMalva australiana s.l., Clammy Goosefoot Chenopodiumpumilio, Heliotrope Heliotropium spp. and Small Mud-mat Glossostigma elatinoides. Oondoroo Solanum simileis also reported as being abundant on occasions at somesites. Other species that are present at some sitesinclude Mallee Cucumber Mukia micrantha, GlaucousGoosefoot Chenopodium glaucum, HeliotropeHeliotropium spp. and Hairy Carpet-weed Glinuslotoides. In sites where inundation periods are not tooextended (and grazing pressure has not eliminated thespecies), the low shrub Spiny Lignum Muehlenbeckiahorrida can also be locally conspicuous.Distribution: Very localised habitat, mainly at HattahLakes, Lake Walla Walla and Lake Bael Bael.Vegetation Quality: Annual or other opportunisticspecies may colonise or invade during dry phases,especially in lakes that are now rarely filled. In theextreme, a low open chenopod shrubland can develop,in which species including Ruby Saltbush Enchylaenatomentosa var. tomentosa, Nodding Saltbush Einadianutans subsp. nutans, Flat-top Saltbush Atriplex lindleyiand a range of introduced annuals predominate,sometimes along with sparse drought-stressedindividuals of indicator species such as SouthernLicquorice Glycyrrhiza acanthocarpa. While thevegetation is typically treeless, thickets of saplings ofRiver Red-gum Eucalyptus camaldulensis can be presenton the outer verges (or across the beds of less frequentlyinundated shallow lakes), indicative of a process ofcontraction of the vegetation type due to decreasedflooding.Comments: Some wetlands of depressions on higherterraces in the north-west may have supportedvegetation referrable to this EVC. The EVC is alsopresumed to have had additional limited occurrenceswithin shallow lakes in the general vicinity of Mildura, inhabitats now extremely altered by saline discharges.
EVC 808 Lignum ShrublandDefining characteristics: Relatively open shrubland ofspecies of divaricate growth form. The ground-layer is
typically herbaceous or a turf grassland, rich inannual/ephemeral herbs and small chenopods. Theshrubs are of more open and even distribution and ofrelatively small stature in comparison to the denserthickets of robust lignum with patchy open areasincluded in Lignum Swamp. Species diversity is typicallymuch higher (and consistent through the vegetation) inLignum Shrubland, whereas most of the species diversityin Lignum Swamp occurs within gaps in the thicket.Structure: Shrubland/open shrubland, with ground-layerherbaceous or a turf grassland, rich in annual/ephemeralherbs and small chenopods.Habitat: Heavy soil plains along Murray River, low-lyingareas on higher-level (but still potentially flood-prone)terraces. Flooding is mostly now rare due to reducedpeak river flows.Floristics: Tangled Lignum Muehlenbeckia florulentaand/or Nitre Goosefoot Chenopodium nitrariaceum(sometimes Cane Grass Eragrostis australasica) withdiverse ground-layer small chenopods and annual herbs.Two structural variants are noted - these may eachinclude more than one floristic variant.1) Riverine Lignum ShrublandTangled Lignum Muehlenbeckia florulenta and/or NitreGoosefoot Chenopodium nitrariaceum (or sometimesCane Grass Eragrostis australasica); +/- WarregoSummer-grass Paspalidium jubiflorum and StreakedCooperburr Sclerolaena tricuspis (common speciesinclude Short-wing Saltbush Sclerochlamys brachyptera,Clay Plantain Plantago cunninghamii, Goodenia spp.,Leek Lily Bulbine semibarbata, Hard-head DaisyBrachsycome lineariloba, Fringed BrachylomaBrachyscome ciliatum, Grass Cushion Isoetopsisgraminifolia, Paper Sunray Rhodanthe corymbiflora,Slender Groundsel Senecio glossanthus, Desert SpinachTetragonia eremaea s.l, Slender-fruit Saltbush Atriplexleptocarpa, Hairy Burr-daisy Calotis hispidula, PaleBeauty-heads Calocephalus sonderi and Rat-tail CouchSporobolus mitchellii).2) Tall Cane Grass Lignum ShrublandCane Grass Eragrostis australasica is rare and localised innorth-western Victoria, but potentially locally dominantwithin small areas of suitable habitat. In the furthernorth-west, associated species include Common Blown-grass Lachnagrostis filiformis, Twin-leaf BedstrawAsperula gemella, Nitre Goosefoot Chenopodiumnitrariaceum, Pale Spike-sedge Eleocharis pallens and TallFireweed Senecio runcinifolius. These occurrences arehere considered a variant of Lignum Shrubland, at leastin the case of the far north-western examples.Distribution: Dicot shrub (riverine) communities:Murray River in further north-west, downstream fromBelsar Island, also including Walpolla Island, MulcraIsland, Lindsay Island, Lake Walla Walla, and presumablyformerly Hattah - Kulkyne. Cane Grass communities:Rare and localised in Victoria - e.g. with floristic variantsin the far north-west (south of Lindsay and WalpollaIslands).Vegetation Quality: Riverine Community - While thecomponent species are tolerant of prolonged periodswithout flooding, this vegetation type appearsvulnerable to floristic changes (possibly including loss ofthe structural dominants) in the longer-term, due toreduced river flows. Annual grasses and medics can be
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very prevalent in the vegetation, particularly in moreopen variants and where grazing has been more intense.Nevertheless, a high diversity of native herbs is oftendetectable in relatively intact examples. The relativeabundance of Sporobolus and Eragrostis spp. is difficultto reliably assess under conditions of desiccation.
EVC 104 Lignum SwampDefining characteristics: Typically treeless, with denseand robust (but sometimes patchy) growth of lignum.Gaps in the denser vegetation may occur in associationwith lower-lying areas where water persists longer -these may support cane-grass, sedgeland and / orephemeral herbs. The character of the vegetation ofthese gaps varies with time since flooding anddisturbance history.Structure: Shrubland to closed scrub, to 3-4 m. Usuallyherbland or sedgeland in gaps, mostly <0.5m.Habitat: Backplains and shallow depressions onfloodplains. Commonly associated with other low-lyingareas such as insipient drainage lines, relict lakebeds andfloodways. Soils are typically heavy cracking grey orblack clays. It is tolerant of prolonged inter-flood phases- up to 8 years - and extended periods – up to 3 months- of shallow inundationFloristics: Tangled Lignum Muehlenbeckia florulenta,with associated species including Common Spike-sedgeEleocharis acuta, Pale Beauty-heads Calocephalussonderi, Tall Fireweed Senecio runcinifolius, Twin-leafBedstraw Asperula gemella, Common Nardoo Marsileadrummondii and sometimes Southern Cane-grassEragrostis infecunda. Denser patches may comprise avirtually mono-specific inter-woven tangle of TangledLignum Muehlenbeckia florulenta. Some examples mayhave included Cane Grass Eragrostis australasica,however most instances where the latter is presentappear to be best referred to the more open andspecies-rich, less robust shrublands of Lignum Shrubland.In the further north-west, a range of chenopods can bepresent, notably Streaked Copperburr Sclerolaenatricuspis and Flat-top Saltbush Atriplex lindleyi, howeverNitre Goosefoot Chenopodium nitrariaceum ischaracteristically absent from well-developed examplesof Lignum Swamp.Distribution: Loddon River floodplain south of Kerang,and scattered downstream of Mitchell Lagoons,including Hattah-Kulkyne (where degraded). Particularlyrobust examples occur at Mulcra Island. A more openvegetation dominated by Tangled LignumMuehlenbeckia florulenta at Lake Walla Walla hassubstantial floristic differences (see relevant commentswithin the description of Lignum Shrubland). Vegetation Quality: In the further north-west, a rangeof chenopods is present, notably Streaked CopperburrSclerolaena tricuspis. While some floristic differences inthe vegetation of the further north-west can beattributed to inherent environmental factors, there isstrong evidence of invasion of a range of species fromthe adjacent Riverine Chenopod Woodland as aconsequence of reduced flooding. Tangled LignumMuehlenbeckia florulenta can be displaced by acombination of desiccation and grazing such as occursat Hattah. A particularly extensive example of LignumSwamp is believed to have formerly occurred at Karadoc
Swamp, but the prior vegetation has been eliminated bysalinisation. It is considered that Lignum Swamp hascontracted in extent (e.g. from floodway systems onhigher terraces at Walpolla Island and Lindsay Island) asa consequence of reduced frequency and amplitude offlooding.
EVC 823 Lignum Swampy WoodlandDefining characteristics: Understorey dominated byTangled Lignum Muehlenbeckia florulenta, typically ofrobust character and relatively dense (at least inpatches), in association with a low Eucalypt and/orAcacia woodland. The ground layer includes acomponent of obligate wetland flora that is able topersist even if dormant over dry periods.Structure: Woodland or open woodland to c. 10 (-15)m, with well-developed shrub layer to c. 2 - 3 m, residueof understorey mostly < 1m.Habitat: Shallow wetland associated with floodwaysystems on (relatively) higher terraces. Soils are heavyand water-retentive.Floristics: The tallest stratum is dominated by EumongAcacia stenophylla and Black Box Eucalyptus largiflorens,with River Red-gum Eucalyptus camaldulensis sometimesalso present. A shrub layer of Tangled LignumMuehlenbeckia florulenta is conspicuous. Commonassociated species variously include Southern Cane-grassEragrostis infecunda, Common Nardoo Marsileadrummondii, Twin-leaf Bedstraw Asperula gemella,Variable Daisy Brachyscome ciliaris, Pale Beauty-headsCalocephalus sonderi, Nodding Saltbush Einadia nutanssubsp. nutans, Slender Groundsel Senecio glossanthus,Warrego Summer-grass Paspalidium jubiflorum, Flat-topSaltbush Atriplex lindleyi, Slender-fruit Saltbush Atriplexleptocarpa, Native Peppercress Lepidiumpseudohyssopifolium, Tall Fireweed Senecio runcinifolius,Salt Sea-spurrey Spergularia sp. 3, Annual CudweedEuchiton sphaericus, Rat-tail Couch Sporobolus mitchelliiand Common Spike-sedge Eleocharis acuta. NitreGoosefoot Chenopodium nitrariaceum ischaracteristically rare if at all present. Similarly absentare the range of other shrubs (e.g. Wattle Acacia spp.,Emu-bush Eremophila spp., Weeping PittosporumPittosporum angustifolium) which are characteristic ofrelatively intact Riverine Chenopod Woodland.Distribution: Scattered on Murray River floodplaingenerally west of Nathalia.Vegetation Quality: This vegetation is vulnerable todesiccation from prolonged reduced flooding - localsevere die back of the major structural dominants wasobserved in places (notably on Walpolla Island). Manyexamples include a conspicuous component of shrubbychenopods (notably Enchylaena tomentosa andSclerolaena tricuspis), particularly in the further north-west. It is considered likely that these species haveinvaded or at least substantially increased as a reflectionof reduced flooding. Muehlenbeckia florulenta isvulnerable to prolonged desiccation and heavy grazing.
EVC 102 Low Chenopod ShrublandDefining characteristics: Low chenopod – dominated,largely treeless shrublands occupying the highestterraces on the floodplain of the Murray River and othermajor river systems such as the Loddon. Also found innarrow bands fringing raak and saline lakes such as Lake
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Tyrell and on relict lakebed surfaces such as Pine Plains. Structure: Open shrubland to 1 m (but typically less),with a field layer variously and seasonally dominated byshort lived perennial chenopod herbs, caespitose grasses,annual forbs and prostrate succulent herbsHabitat: Occurs in areas with a distinctly semi-aridclimate on relict alluvial plains and abandoned streamstructures typically lightly mantled with parna. Theseplains are rarely flooded but are poorly drained and maybe subject to periods of inundation following heavyrains. The soils are commonly grey to brown clays andduplex soils with loamy clays and loams above clay sub-soils. Occupies plains – formed by recent alluvialprocesses with insignificant topographic relief. Notsubject to inundation as a consequence of overbankflows from major rivers but poorly drained settings mayresult in protracted pooling of water in winter monthsdue to heavy rainfall. The climate can be described assemi-arid to arid with low but highly variable rainfall.Soils are typically clays with minor or shallow depositionof aeolian materials at the surface. Surface soils are red-brown sandy clay loams and sandy clays giving way toheavier textured brown-grey clay soils within 50 cm ofthe surface. The soils are sub-saline (sodic) withcomparatively high EC (generally above 2 dS/m and upto 9 dS/m) at depth and high pH (generally above 8) ator near the surface, due to the proximity of salinegroundwater and the shallow surface deposition ofreworked Woorinen sediments respectively. Floristics: Trees are virtually absent from this EVC due tosummer drought stress in the heavy textured soils –occasional Umbrella Wattle Acacia oswaldii or Cattle-bush Alectryon oleifolius subsp. canescens may bepresent on slightly deeper drifts of coarser soils. Tworelatively distinct floristic entities are here described. The shrub layer is variously dominated by BladderSaltbush Atriplex vesicaria, Desert Glasswort Pachycorniatriandra, Nitre-bush Nitraria billardierei and otherperennial woody chenopods such as Kidney SaltbushAtriplex stipitata, Thorny Lawrencia Lawrencia squamata,Twin-flower Saltbush Dissocarpus biflorus var. biflorusand depending on the degree to which salinegroundwater affects the site various Sea Heath Frankeniaspecies. A range of Copperburr Sclerolaena species mayalso be prevalent – becoming more so following heavygrazing episodes, protracted dry spells or flooding –including Tangled Copperburr S. divaricata, LimestoneCopperburr S. obliquicuspis, Grey Copperburr S.diacantha and Streaked Copperburr S. tricuspis. Old-man Saltbush Atriplex nummularia is occasional in areasreceiving local runoff. The ground layer is highly variableand composition responds readily to the vagaries of theprevailing weather. In particular, the season of significantrainfall events may promote a significantly different suiteof annual taxa. Some common species include RoundedNoon-flower Disphyma crassifolium subsp. clavellatum,Pale Beauty-heads Calocephalus sonderi, Desert Spear-grass Austrostipa eremophila, Yakka Grass Sporoboluscaroli, Bristly Wallaby-grass Austrodanthonia setacea,Rough Spear-grass Austrostipa scabra, Windmill GrassChloris truncata, Pink Bindweed Convolvulus erubescenss.l., Hairy Bluebush Maireana pentagona, Goat HeadMalacocera tricornis, Babbagia Osteocarpum acropterumvar. diminuta, Woolly-fruit Bluebush Eriochiton
sclerolaenoides Short-wing Saltbush Sclerochlamysbrachyptera, Shrubby Twin-leaf Zygophyllumaurantiacum subsp. aurantiacum, Bristly Love-grassEragrostis setifolia, Hairy Bluebush Maireana pentagona,and Flat-top Saltbush Atriplex lindleyi, Frankenia spp.,Common White Sunray Rhodanthe floribunda, WartyPepper-cress Lepidium papillosum, Small PodolepisPodolepis muelleri, and Yellow Tails Ptilotus nobilis var.nobilis. In temporarily wet depressions, Cane GrassEragrostis australasica maybe locally common todominant and on localised areas of saline clay SlenderGlasswort Sclerostegia tenuis becomes an important andoften dominant component of the vegetation. Distribution: Large relatively intact remnants of thenorthern floristic variant of this EVC persist on the raisedtertiary terraces of the Murray river floodplaindownstream of Mildura – the soils generally being tooheavy and the climate too dry for cropping. The fringesof the major discharge basins throughout the study areaincluding the Sunset Raak Plains, Rocket Lake, LakeTyrrell, and deflations in the Morkalla and Murrayvillearea. This EVC has proved to be sensitive to the impactsof grazing and historic records show that saltbush plainswere once scattered throughout the study area as farsouth as Pine Plains in Wyperfeld National Park. Comments: The EVC is quite variable, and may haveincluded a number of communities, but the originalfloristic patterns are often obscured by the impacts ofdisturbance (grazing and desiccation).
EVC 66 Low Rises WoodlandDefining characteristics: Eucalypt woodlands onelevated plains, and low rises with a diverse shrubunderstorey and grassy field layer. Habitat: Occurs in a range of environmental settingsthat have resulted in well-drained surface soils mantlingclay sub-soils. Within the study area, it typically occurson deep fans of weathered Parilla sandstone on themargins and crests of broad or subdued sandstoneridges and residuals but may also occur on source-bordering sand deposits such as lunettes. The duplexsoils are typically well-drained, brown sandy clay-loamsurface soils above heavy to medium clay sub-soils. Thisrather abrupt textural change usually occurs at 20-60cm. The climate across the range of this EVC is variable but isgenerally high – in comparison with most of the studyarea. The average annual precipitation is calculated tobe 435 mm with a median annual rainfall of 367 mm. Structure: Woodland to 20 m with an open tall shrubstratum to 3 m. Smaller shrubs are common above agenerally grassy field layer of tussock and sward grasses. Floristics: Across most of its range within the study areathe characteristic overstorey trees are BulokeAllocasuarina luehmanni, Yellow Gum Eucalyptusleucoxylon (typically Waxy Yellow Gum Eucalyptusleucoxylon subsp. pruinosa) and Slender Cypress-pineCallitris gracilis subsp. murrayensis. A storied shrub layer is usually well developed in lessdisturbed remnants of this EVC. Commonlyencountered species include Hooked Needlewood Hakeatephrosperma, Sweet Bursaria Bursaria spinosa subsp.spinosa, Golden Wattle Acacia pycnantha, MoonahMelaleuca lanceolata subsp. lanceolata, Sweet
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Quandong Santalum acuminatum, Leafless BallartExocarpos aphyllus, Sugarwood Myoporum playtcarpum,Weeping Pittosporum Pittosporum angustifolium,Wedge-leaf Hop-bush Dodonaea viscosa subsp. cuneata,Gold-dust Wattle Acacia acinacea s.l., Grey Mulga Acaciabrachybotrya, Common Eutaxia Eutaxia microphylla var.microphylla, Pimelea Daisy-bush Olearia pimeleoides andRuby Saltbush Enchylaena tomentosa var. tomentosa.The field layer across the range of this broad EVC isvariable. It is typically dominated by a sward ofcaespitose grasses such as Common Wallaby-grassAustrodanthonia caespitosa, Bristly Wallaby-grassAustrodanthonia setacea, Spider Grass Enteropogonacicularis, Grey Tussock-grass Poa sieberiana var.sieberiana and Common Wheat-grass Elymus scaber var.scaber. Common inter-tussock herbs and semi-shrubsinclude Mallee Flax-lily Dianella sp. aff. revoluta (Mallee),Wingless Bluebush Maireana enchylaenoides, FrostedGoosefoot Chenopodium desertorum, Sticky Sword-sedge Lepidosperma viscidum, Fuzzy New Holland DaisyVittadinia cuneata, Lemon Beauty-heads Calocephaluscitreus, Grassland Wood-sorrel Oxalis perennans, MullaMulla Ptilotus exaltatus, Variable Sida Sida corrugata,Scented Mat-rush Lomandra effusa, Nodding SaltbushEinadia nutans subsp. nutans and Cut-leaf GoodeniaGoodenia pinnatifida. Distribution: Scattered on riverine plains between SwanHill and Cobram. Widely cleared for cereal cropping.
EVC 132 Plains GrasslandDefining characteristics: Tussock grassland, rich in awide variety of (mostly perennial) forbs, particularlyAsteraceae, geophytes and small chenopods. Woodyplants are absent.Habitat: Moderately poorly drained quaternary alluvialand paleo-lacustrine clay deposits in areas with less than500mm/pa rainfall. Poor drainage characteristics of thesubstrates are attributed as the principal reason for theabsence of trees and larger shrubs.Floristics: As so few examples remain, it is difficult toassemble the true floristic nature of this EVC. Remnantsare often dominated by Rough Spear-grass Austrostipascabra and/or Common Wallaby-grass Austrodanthoniacaespitosa, although a number of other dominants maybe encountered, and there is little confidence that theabove species are the true dominants of pre-Europeanvegetation. On the heaviest soils, often demonstrating a ‘gilgai’nature, Plump Spear-grass Austrostipa aristiglumis andBrown-back Wallaby-grass Austrodanthonia duttonianaare the dominant tussocks. Rigid Panic Whalleya prolutaand Common Tussock-grass Poa labillardierei may alsobe present (the latter less so). A range of forbs adaptedto an edaphic environment which may experience bothseasonal waterlogging and summer moisture deficitoccur in the inter-tussock spaces. Such forbs includeRosinweed Cressa australis, Pale Beauty-headsCalocephalus sonderi, Milky Beauty-heads Calocephaluslacteus, Paper Sunray Rhodanthe corymbiflora, JoyweedAlternanthera spp., Rough Burr-daisy Calotisscabiosifolia, Woodland Swamp-daisy Brachyscomebasaltica var. gracilis Prickly Woodruff Asperulascoparia, Poison Pratia Lobelia concolor, Broughton PeaSwainsona procumbens, Prickfoot Eryngium vesiculosum,
and Long Eringyum Eryngium paludosum.In areas experiencing less waterlogging, the originaldominants are thought to be (variously) Kangaroo GrassThemeda triandra or Spider Grass Enteropogonacicularis, with the latter dominating in slightly wetterareas. Geophytes are prevalent in this vegetation andinclude lilies such as Bulbine Lily Bulbine bulbosa,Milkmaids Burchardia umbellata, Blue Grass-lily Caesiacalliantha, Small Vanilla-lily Arthropodium minus,Chocolate Lily Arthropodium strictm s.l, Common EarlyNancy Wurmbea dioica and Yellow Star Hypoxis glabellas.l.. Other forbs include Grassland Wood-sorrel Oxalisperennans, Blushing Bindweed Convolvulusangustissimus, Lemon Beauty-heads Calocephaluscitreus, Cut-leaf Burr-daisy Calotis anthemoides, BlueDevil Eryngium ovinum, Cut-leaf Goodenia Goodeniapinnatifida, Variable Sida Sida corrugata, FrostedGoosefoot Chenopodium desertorum, WinglessBluebush Maireana enchylaenoides, Bottle BluebushMaireana excavata, Hairy Bluebush Maireana pentagona,Black Cotton-bush Maireana decalvans, Yam DaisyMicroseris scapigera spp.agg., Woolly New Holland DaisyVittadinia gracilis, Nodding Saltbush Einadia nutanssubsp. nutans, Berry Saltbush Atriplex semibaccata, andMulla Mulla Ptilotus exaltatus..Distribution: Formerly on heavy soil plains west ofEchuca in the Victorian Riverina such as the Patho Plains.
EVC 55 Plains Grassy WoodlandDefining characteristics: An open, eucalypt woodlandoccurring on a number of geologies and soil types.Occupies poorly drained, fertile soils on flat or gentlyundulating plains at low elevations. The understoreyconsists of a few sparse shrubs over a species-rich grassyand herbaceous ground layer. Structure: An open woodland with an understorey ofscattered shrubs and a high species diversity of grasses,sedges, lilies, orchids and herbs.Floristics: Dominanted by River Red-gum Eucalyptuscamaldulensis and often Grey Box Eucalyptusmicrocarpa. The shrub layer includes Gold-Dust WattleAcacia acinacea, Hedge Wattle Acacia paradoxa, DwarfBush-pea Pimelea humilis, Guinea-flower Hibbertia spp,Sweet Bursaria Bursaria spinosa and occasionally Acaciawilliamsonii Whirrakee Wattle near creeks aroundBroadford. Black Wattle Acacia mearnsii may also occurin the south west of the study area. The ground layerincludes: a dense layer of Kangaroo Grass Themedatriandra, Spear grasses Stipa spp., and Common Wheat-grass Elymus scaber var. scaber. Typical forbs includeBlue Devil Eryngium ovinum, Common Everlasting,Chrysocephalum apiculatum s.l., Lemon Beauty-headsCalocephalus citreus, Pale Sundew Drosera peltata, PinkBindweed Convolvulus erubescens, Scaly ButtonsLeptorhyncos squamatus, Chocolate Lily Arthropodiumstrictum s.l., Early Nancy Wurmbea diocea, Yellow Rush-lily Tricoryne elatior, Bulbine Lily Bulbine bulbosa,Common Onion-orchid Microtis unifolia and MilkmaidsBurchardia umbellata. Sedges and rushes present includeCommon Bog-sedge Schoenus apogon, Club SedgeIsolepis spp., Sedge Carex spp. and Rush Juncus spp.Distribution: Formerly an extensive distribution acrossthe southern and eastern Victorian Riverina in areas ofhigher effective rainfall than Plains Woodland.
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EVC 803 Plains WoodlandDefining characteristics: Grassy woodland, rich insmall chenopods and annual or geophytic forbs,occurring on non-riverine alluvial deposits. Outside ofincluded small seasonal wetlands or associated gilgaidepressions lacking flood dependant species in theground-layer.Structure: Woodland (sometimes including areas oftussock grassland). In most remnants, shrubs are aminor component, but it is considered that theabundance and diversity of the shrub layer has generallybeen reduced in diversity by grazing.Habitat : Low-lying areas within former drainagesystems on heavy soils plains. The habitat is not subjectto flooding, though can include low-lying seasonallywater-logged areas. Clay alluvial soils, sometimes withshallow sandy overlay, at elevations of c. 70 - 130 m.Floristics: The overstorey comprises Black BoxEucalyptus largiflorens (sometimes with other boxeucalypts, e.g. Grey Box Eucalyptus microcarpa, YellowBox Eucalyptus melliodora) and/or Buloke Allocasuarinaluehmannii, with sometimes scattered Gold-dust WattleAcacia acinacea s.l. in the understorey. Other rarelyencountered shrubs include Umbrella Wattle Acaciaoswaldii, Golden Wattle Acacia pycnantha, Small Hop-bush Dodonaea bursariifolia, Silver Needlewood Hakealeucoptera subsp. leucoptera, Weeping PittosporumPittosporum angustifolium, Pale-fruit Ballart Exocarposstrictus, Water Bush Myoporum montanum, SugarwoodMyoporum platycarpum subsp. platycarpum, CommonEutaxia Eutaxia microphylla, Cranberry heath Astrolomahumifusum and Peach Heath Lissanthe strigosa subsp.subulata. A grassy ground layer is dominated by speciesof Wallaby-grass Austrodanthonia and Spear-grassAustrostipa and a diversity of small chenopod (saltbush)species. Main dominants in the ground layer includeBristly Wallaby-grass Austrodanthonia setacea, RoughSpear-grass Austrostipa scabra subsp. falcata, KneedWallaby-grass Austrodanthonia geniculata, CommonWheat-grass Elymus scaber var. scaber, Grey Tussock-grass Poa sieberiana and Nigger-heads Enneapogonnigricans or with associated species including MalleeLove-grass Eragrostis dielsii, Spider Grass Enteropogonacicicularis and a diverse range of small chenopods,mainly Bluebush Maireana spp. (Wingless BluebushMaireana enchylaenoides, Black Cotton-bush Maireanadecalvans), Saltbush Atriplex spp. (Berry Saltbush Atriplexsemibaccata, Small Saltbush Atriplex eardleyae, MealySaltbush Atriplex pseudocampanulata, Flat-top SaltbushAtriplex lindleyi), Ruby Saltbush Enchylaena tomentosavar. tomentosa and Nodding Saltbush Einadia nutanssubsp. nutans. In relatively intact sites, a range of forbsand sedges can be found such as Sheep’s Burr Acaenaechinata, Blushing Bindweed Convolvulus angustissimus,Smooth Solenogyne Solenogyne dominii, Common EarlyNancy Wurmbea dioica, Common Bog-sedge Schoenusapogon, Twining Fringe-lily Thysanotus patersonii, RubySaltbush Enchylaena tomentosa var. tomentosa, andLemon Beauty-heads Calocephalus citreus. Smallephemeral depressions support Common SwampWallaby-grass Amphibromus nervosus and Spike-sedgeEleocharis spp. with a range of small herbs indicative ofephemeral wetland within gilgai terrain, or otherwiseseasonally waterlogged soils, broader-scale wetland and
species indicative of more sustained or deeperinundation are absent. Distribution: Scattered in heavy soil areas of drier partsof the Northern Plains but principally around the fringesof the Murray River and Loddon River floodplains, buthabitat now largely modified and few relatively intactremnants persist.
EVC 18 Riparian ForestDefining characteristics: A tall forest along river banksand associated alluvial terraces with occasionaloccurrences in the heads of gullies leading into creeksand rivers.Habitat: Confined to river flats, alluvial terraces andperennial streams on Quaternary alluviums derived froma variety of parent geologies.Structure: A tall eucalypt forest over an open tosecondary tree layer of wattles and scattered densepatches of shrubs, ferns, grasses and herbs.Floristics: The overstorey is dominated by Manna GumEucalyptus viminalis though a range of other eucalyptsmay be present including Narrow-leaf PeppermintEucalyptus radiata s.l. and Eurabbie Eucalyptus globulussubsp. bicostata. The EVC has a well-developedsecondary tree layer with Blackwood Acacia melanoxylonand Silver Wattle Acacia dealbata being common. A diversity of tall shrubs, also common to Wet or DampForest, form a major component in the understoreyincluding Hazel Pomaderris Pomaderris aspera, TreeLomatia Lomatia fraseri and Prickly Currant-bushCoprosma quadrifida.The ground layer is generally diverse in both species andlife forms. Due to the constant supply of water and, inmany cases shade, ground ferns form a majorcomponent of Riparian Forest, often lining the stream-banks and are dispersed across the flats in moister sites.Common ferns include Fishbone Water-fern Blechnumnudum,, Soft Water-fern Blechnum minus, MotherShield-fern Polystichum proliferum and Soft Tree-fernDicksonia antarctica. Tall Sedge Carex appressa oftendominates stream banks and the more open areas.The most common forbs are Ivy-leaf Violet Violahederacea, Bidgee Widgee Acaena nova-zelandiae,Creeping Cudweed Euchiton involucratus s.l. and Small-leaf Bramble Rubus parvifolius. Common grasses includeWeeping Grass Microlaena stipoidse var. stipoides,Common Hedgehog-grass Echinopogon ovatus andYorkshire Fog *Holcus lanatus in disturbed sites. Thecommon and seriously invasive weeds of this EVC areWillow *Salix spp,, .Blackberry *Rubus fruticosus spp.agg., Cat’s Ear *Hypochoeris radicata, Self Heal*Prunella vulgaris, Yorkshire Fog *Holcus lanatus, MuskMonkey Flower *Mimulus moschatus and White Clover*Trifolium repens.
EVC 103 Riverine Chenopod Woodland Defining characteristics: Eucalypt woodland of mostelevated riverine terraces, intact examples with a diverseshrubby-grassy understorey. Formerly prone to irregularshallow flooding.Habitat: Heavy clay soils on higher level terraces withinor on the margins of riverine floodplains (or formerfloodplains), naturally subject to only extremelyinfrequent incidental shallow flooding from majorevents if at all flooded.
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Structure: Woodland, mostly, < c. 15 m but to c. 25 min mature examples. In relatively intact examples theunderstorey is shrubby-grassy and can be rich in annualspecies. Where present the shrub component is to 2 (-5)m, with the grassy-herbaceous component typicallymostly < 0.2 (-0.5) m) - depending on current grazingpressure.Floristics: Dominated by an overstorey of Black BoxEucalyptus largiflorens (and in some areas Grey BoxEucalyptus microcarpa) with a characteristic salt-bushdominated understorey. Common species includeNodding Saltbush Einadia nutans subsp. nutans, andRuby Saltbush Enchylaena tomentosa var. tomentosa.Other less common species are Prickly Saltwort Salsolatragus, Slender-fruit Saltbush Atriplex leptocarpa, SmallSaltbush Atriplex eardleyae, Black Cotton-bush Maireanadecalvans, Grey Roly-poly Sclerolaena muricata varvillosa, Hedge Saltbush Rhagodia spinescens, BerrySaltbush Atriplex semibaccata, Sprawling SaltbushAtripex suberecta, Old-man Saltbush Atriplexnummularia, Mealy Saltbush Atripexpseudocampanulata, Flat-top Saltbush Atriplex lindleyi,Beaded Glasswort Sarcocornia quinqueflora, LeaflessBluebush Maireana aphylla, Rounded Noon-flowerDisphyma crassifolium subsp. clavellatum, Saloop Einadiahastata, Cottony Saltbush Chenopodium curvispicatum,Nitre Goosefoot Chenopodium nitrariaceum and TangledLignum Muehlenbeckia florulenta. A number of shrubs can also be present, including Emu-bush Eremophila spp. – Bignonia Emu-bush Eremophilabignoniiflora, Spotted Emu-bush Eremophila maculatavar. maculata and Spreading Emu-bush Eremophiladivaricata subsp. divaricata; also Wattle Acacia spp. -variously including Eumong Acacia stenophylla, HakeaWattle Acacia hakeoides and Willow Wattle Acaciasalicina. Small locally elevated areas can have a mixtureof Black Box Eucalyptus largiflorens and MoonahMelaleuca lanceolata subsp. lanceolata - these representa transition towards Semi-arid Woodland and aredelineated below as Black Box - Moonah Woodland.Similarly, the woody species Cattle Bush Alectryonoleifolius subsp. canescens and Slender Cypress-pineCallitris gracilis subsp. murrayensis can be sparselypresent in some drier sites. Many areas are severelydisturbed by grazing and have a high proportion ofintroduced grasses. Common introduced grasses include *Perennial Rye-grass Lolium perenne, *Soft Brome Bromus hordeaceussubsp. hordeaceus, *Sterile Brome Bromus sterilis,*Rat’s-tail Fescue Vulpia myuros, *Squirrel-tail FescueVulpia bromoides, *Spider Grass Enteropogon acicularisand *Barley-grass Hordeum murinum s.l. In contrastBristly Wallaby-grass Austrodanthonia setacea andWarrego Summer-grass Paspalidium jubiflorum are theonly common native grass species although RoughSpear-grass Austrostipa scabra subsp. falcata may bepresent. A diverse range of ephemeral/annual herbs and semi-shrubs include Hairy Burr-daisy Calotis hispidula, SandSpurrey Spergularia sp. 3, Slender-fruit Saltbush Atriplexleptocarpa, Variable Daisy Brachyscome ciliaris, Leek LilyBulbine semibarbata, Pale Beauty-heads Calocephalussonderi, Crassula Crassula spp., Nodding SaltbushEinadia nutans subsp. nutans, Peppercress Lepidium
spp., Clay Plantain Plantago cunninghamii, Variable SidaSida corrugata, Common Nardoo Marsilea drummondii,Slender Groundsel Senecio glossanthus, Goodenia spp..The following variations are noted:Distribution: Widespread along Murray Riverdownstream from Gunbower and major Wimmeradrainage lines and Loddon River floodplains. Vegetation Quality: Relatively intact remnants ofRiverine Chenopod Woodland are extremely rare due tomodification through grazing and reduced incidence andextent of flooding. Large Saltbush Atriplex spp., notablyOld-man Saltbush Atriplex nummularia have declinedgreatly as a consequence of grazing in most formerhabitats. Remnants of the habitat (e.g. around smalllakes) can also be vulnerable to salinization. Thesemodifications include reduction of diversity, notably lossof shrubby species, increases in abundance of speciesfrom drier habitats and reduction in the vigour of thestructural dominant. In some areas grazing anddesiccation have resulted in woodland vegetation with agrassy understorey, typically dominated by BristlyWallaby-grass Austrodanthonia setacea (or sometimesRough Spear-grass Austrostipa scabra subsp. falcata) andintroduced annuals. In such situations a component ofmore resilient chenopod species is usually present. Insome localities, notably at Hattah, extension of wind-blown sand into former Riverine Chenopod Woodlandhas resulted in major floristic changes, with colonisationof species indicative of adjacent non-riverine vegetation(e.g. Tangled Burr-daisy Calotis erinacea, Poached-eggsDaisy Polycalymma stuartii, Velvet Tobacco Nicotianavelutina, Cushion Knawel Scleranthus minisculus,Purslane Calandrinia spp.). This change appears to bepermanent and ultimately at the EVC level, with futurerecruitment of Black Box Eucalyptus largiflorens in theseareas now appearing ecologically impossible.Comments: Riverine Chenopod Woodland is potentiallysubject to only incidental shallow flooding from themost extreme inundation events (e.g. once in a hundredyear floods) and would generally not be considered asfunctionally representing wetland. Due to the droughtconditions of 2002 when the survey was carried out,herbaceous species were rare but Paper SunrayRhodanthe corymbiflora and Woolly Buttons Leiocarpapanaetioides may be more common after spring rains.A variable component of associated shrubby chenopods(e.g. Ruby Saltbush Enchylaena tomentosa var.tomentosa, Streaked Copperburr Sclerolaena tricuspis,Hedge Saltbush Rhagodia spinescens) reflects bothinherent site factors and disturbance history.
EVC 295 Riverine Grassy WoodlandDefining characteristics: Eucalypt woodland ofrelatively elevated sections of floodplain, understoreygrassy (to lightly shrubby), dominated by species notecologically reliant on flooding (but tolerant of relativelybrief and superficial inundation).Structure: Woodland to c. 25 m, often lower. Theunderstorey is generally dominated by tussock grasses,sometimes lightly shrubby or with chenopod semi-shrubs. The ground-layer is typically grazed bykangaroos to <0.1 m height.Habitat: Prone to high-level flooding only and thusoccupies the least flooded red gum environment andoccasionally grades into mixtures with Black Box
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Eucalyptus largiflorens and Grey Box Eucalyptusmicrocarpa. This is reflected in reduced tree height,frequently severe crown die-back and an open woodlandformation that includes many of the low shrubs thatoccur scattered in the Black Box and Grey Boxwoodlands. It occupies higher ground throughout theforest and along the river levees. The understorey isdominated by species that respond to winter and springrains and do not depend upon flooding. Soils are oftensandy to silty.Floristics: Overstorey of River Red-gum Eucalyptuscamaldulensis, variously with a component of Black BoxEucalyptus largiflorens. There is generally a sparsescattering of low shrubs frequently including NoddingSaltbush Einadia nutans subsp. nutans but Berry SaltbushAtriplex semibaccata, Small Saltbush Atriplex eardleyae,Grey Roly-poly Sclerolaena muricata var. villosa, RubySaltbush Enychlaena tomentosa var. tomentosa, BlackCotton-bush Maireana decalvans, Cottony SaltbushChenopodium curvispicatum and Prickly Saltwort Salsolatragus occasionally occur at different times.The ground-layer is grassy and potentially herb-rich inrelatively intact vegetation. The dominant ground-layerspecies are Bristly Wallaby-grass Austrodanthonia setaceaand Rough Spear-grass Austrostipa scabra. Thedominant native grass Bristly Wallaby-grassAustrodanthonia setacea is one of the few able topersist under grazing pressure. Other native grassesrarely recorded include Common Wallaby-grassAustrodanthonia caespitosa, Velvet Wallaby-grassAustrodanthonia pilosa and Rough Spear-grassAustrostipa scabra. Other persistent species in theground-layer include Nodding Saltbush Einadia nutanssubsp. nutans, River Bluebell Wahlenbergia fluminalis,Knob Sedge Carex inversa, Grassland Wood-sorrel Oxalisperennans, Finger Rush Juncus subsecundus, SlenderDock Rumex brownii, Cotton Fireweed Senecioquadridentatus, Cranesbill Geranium sp., Variable SidaSida corrugata, Fuzzy New Holland Daisy Vittadiniacuneata, Woolly New Holland Daisy Vittadinia gracilisand Black Roly-poly Sclerolaena muricata. Dominantweeds include *Soft Brome Bromus hordeaceus subsp.hordeaceus, *Red Brome Bromus rubens and *Barley-grass Hordeum murinum s.l. Distribution: Once common along Murray Riverfloodplain downstream from Lake Hume to Echuca andin small, localised patches downstream of Echuca.Vegetation Quality: Typically it has been heavilyovergrazed in Gunbower State Forest. Less flood-proneareas along river banks are prone to degradation andweed invasion as a consequence of intensive recreationaluse (and at least elsewhere concentration of herbivoresduring flood events).
EVC 814 Riverine Swamp ForestDefining characteristics: Tall open eucalypt forest (towoodland), to 30 - 40 m or more in height withunderstorey dominated by obligate wetland species (oropportunistic annuals during sustained dry periods). Structure: Tall open forest (to woodland). The ground-layer can range from +/- low closed sedgeland orherbland to grassy-herbaceous (mostly < O.3 memergent) or extremely sparse and with cover primarilyleaf-litter, black water or exposed alluvium.
Habitat: Low-lying areas subject to reasonably regularflooding, typically flood-prone lower river terraces andlow-lying areas adjacent to floodways through or withinriverine forest, recorded from elevation of c. 95 - 135 m.Floristics: River Red-gum Eucalyptus camaldulensis withspecies-poor ground-layer dominated by Spiny Mud-grass Pseudoraphis spinescens and/or Common Spike-sedge Eleocharis acuta, (locally) River Swamp Wallaby-grass Amphibromus fluitans, or sometimes bare (leaf-litter/mud). Where present, associated species variouslyinclude Common Blown-grass Lachnagrostis filiformis,Riverina Bitter-cress Cardamine moirensis, Ferny Small-flower Buttercup Ranunculus pumilio, Water RibbonsTriglochin procera s.l. and Common SneezeweedCentipeda cunninghamii).[On localised areas of flood-prone sandy terraces,connected to the river or major floodway creeks, Love-grass Eragrostis spp. and Native Couch Cynodondactylon var. pulchellus can be locally dominant.Distribution: Restricted, by far the most extensiveoccurrences at Barmah.Vegetation Quality : Often subject to modification dueto changed river flows. Grazed by cattle (and brumbies)at Barmah, and subject to intense pugging. Feral pigscan also create considerable soil disturbance within therelevant habitat.
EVC 815 Riverine Swampy WoodlandDefining characteristics: Eucalypt woodland to openwoodland, ground-layer grassy to sedgy - herbaceous,with species indicative of periodic water-logging (andwith floristic affinities with Plains Grassy Wetland).Structure: Seasonally wet herbland, grassland or openwoodland (to woodland), sometimes with treeless grassy/sedgy areas; ground-layer grassy to sedgy – herbaceous.Habitat: Areas subject to shallow inundation only fromhigher-level flooding. Soils are typically heavy, crackingmottled grey-brown clays/clay-loams and water-retentive,often with a gilgai profile which can be wet duringwinter. Site range in elevation from c. 95 - 150 m.Floristics: River Red-gum Eucalyptus camaldulensis(sometimes with scattered Black Box E. largiflorens), withspecies including Brown-back Wallaby-grassAustrodanthonia duttoniana, Common Swamp Wallaby-grass Amphibromus nervosus, Common Spike-sedgeEleocharis acuta, Small Spike-sedge Eleocharis pusilla,Poison Pratia Lobelia concolor, River BluebellWahlenbergia fluminalis, Goodenia spp., Burr-daisyCalotis spp., Nardoo Marsilea spp. and WoodlandSwamp-daisy Brachyscome basaltica var. gracilis. Sparsetussocks of Poong’ort Carex tereticaulis or WarregoSummer-grass Paspalidium jubiflorum can also bepresent.Distribution: Mostly Murray River system upstream ofWakool Junction. Depleted and rare, most extensive atBarmah and upstream to Lake Hume. Grey BoxEucalyptus microcarpa dominated variant occurs inseasonally wet sites in the central area of the riverineplains, e.g. Echuca and Shepparton districtsVegetation Quality: Distribution of remnants requiresfurther investigation. Much of the former extent iscleared and heavily modifed by agricultural use. Theformer habitat of the Grey Box dominated variant inparticular is mainly in private ownership. Most remnantsare grazed.
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EVC 264 Sand Ridge WoodlandDefining characteristics: Open pine-box woodlandwith a small or medium shrub layer of variable densityand including a range of annual herbs, grasses andgeophytes, in the dense ground layer. Occupiesdistinctive sandy rises (or sand mounts) adjacent tomajor rivers and wetlands. Very sandy, deep, free-draining, moderately fertile soil, developed on sandblown up by wind action from a prior stream bed. Habitat: Source-bordering dunes composed of deepsandy soils support this vegetation. These soils types aredeveloped on sand blown up by wind action from theprior stream bed. Structure: A woodland to low open forest. Theunderstorey appears to be dominated by grasses at thesites in Victoria, however less disturbed remnants inN.S.W. have a moderately dense shrub layer.Floristics: The overstorey is often dominated by WhiteCypress-pine Callitris glaucophylla with Yellow BoxEucalyptus melliodora and Drooping SheokeAllocasuarina verticillata. Sites adjacent to the riverineenvironment may also support River Red-gum Eucalyptuscamaldulensis. Shrubs recorded from a range of sitesinclude: Common Fringe-myrtle Calytrix tetragona, GreyMulga Acacia brachybotrya, Lightwood Acacia implexa,Golden Wattle Acacia pycnantha, Mallee Wattle Acaciamontana, Gold-dust Wattle Acacia acinacea, WeepingPittosporum Pittosporum angustifolium, Sweet BursariaBursaria spinosa, and Drooping Cassinia Cassiniaarcuata. The few native ground layer species detected inVictoria provide an indication of the distinctive andunusual flora. Grasses are Jericho Wire-grass Aristidajerichoensis var. subspinulifera and Purple Wire-GrassAristida personata, Summer Grass Digitaria spp., HairyPanic Panicium effusum, Nigger-heads Enneapogonnigricans, Common Wheat-grass Elymus scaber var.scaber and Spear Grasses Austrostipa spp. including (yetto be confirmed) Balcarra Spear-grass Austrostipa nitida.Herbs include Blue-bush, Maireana spp., Small Scurf-peaCullen parvum, and Smooth Minuria Minuriaintegerrima.Historical records indicate a number of species whichonce occurred on sandy ridges : Silver Banksia Banksiamarginata, Yarran Wattle Acacia omalophylla, andHooked Needlewood Hakea tephrosperma. Sand ridgesadjacent to rivers may also have supported RiverBottlebrush Callistemon sieberi on the fringe. NorthernSandalwood Santalum lanceolatum once occurred onsandy rises near creeks and the Murray River.Distribution: Within close proximity to the Murrayupstream of Echuca and lower Goulburn floodplain.
EVC 816 Sedgy Riverine ForestDefining characteristics: Eucalypt forest (to woodland)with understorey dominated by larger sedges (to sedgy-herbaceous), floristics with some affinities to Red GumSwamp.Structure: Open forest to woodland - at Barmah, mostlyc. 20 - 35 m in height, sometimes with taller emergentveteran trees.Habitat: Typically on heavy clay/clay-loam soils in areasprone to only shallow (but more than occasional andoriginally reasonably regular) flooding. The habitat caninclude billabongs, floodways and old anabranches.
Floristics : River Red-gum Eucalyptus camaldulensis withPoong’ort Carex tereticaulis, with understorey rangingfrom closed-tussock sedgeland (e.g. at Barmah whereincluding with Marsh Club-sedge Bolboschoenusmedianus) to more open sedgy-grassy with WarregoSummer-grass Paspalidium jubiflorum also present.Other common species include Common Spike-sedgeEleocharis acuta, Hollow Rush Juncus amabilis, PoisonPratia Lobelia concolor, Brachyscome basalticavar.gracilis, Common Swamp Wallaby-grassAmphibromus nervosus, Common Blown-grassLachnagrostis filiformis and Burr-daisy Calotis spp., withSmall Spike-sedge Eleocharis pusilla on drier margins).Where not grazed out of the vegetation, otherassociated species can include Swamp Starwort Stellariaangustifolia, Common Reed Phragmites australis andSwamp Billy-buttons Craspedia paludicola. Obligatewetland species such as Common Spike-sedge Eleocharisacuta and Common Nardoo Marsilea drummondii maybe prevalent in inter-tussock gaps, but are not dominantover sustained areas - if so, then the vegetationrepresents a complex with Riverine Swamp Forest.Distribution: Widespread (within restricted floodplainhabitat) in less arid riverine areas, but absent fromfurther north-west of State (Murray River and majortributaries, downstream to Murphy Island near theMurrumbidgee junction).Vegetation Quality: Remaining areas of Sedgy RiverineForest are mostly subject to disturbance (variously fromtimber harvesting, recreational vehicles and/or grazing).Within the Wimmera and outside of larger tracts ofriverine forests, substantially reduced by clearing (forgrazing land and irrigation farming). Disturbed areaslacking regular flooding are vulnerable to weed invasion,notably by *Fog-fruit Phyla canescens along the MurrayRiver (e.g. at Nyah and Vinifera Forests, where theoriginal floristics of this vegetation are almost obscured).
EVC 817 Sedgy Riverine Forest/Riverine SwampForest ComplexDefining characteristics: Understorey dominants ofRiverine Swamp Forest conspicuous in association orfine-scale mosaic with larger tussock or rhizomatousspecies characteristic of Sedgy Riverine Forest.Structure: Eucalypt forest (to tall open forest) with opensedgy-herbaceous ground-layer.Habitat: Flood-prone areas, where inundation isreasonably regular and reasonably sustained butshallower and typically less frequent or sustained relativeto sites supporting Riverine Swamp Forest. Recordedfrom elevations of c. 80 - 110 m, on mottled heavyclay/clay-loam soils.Floristics: River Red-gum Eucalyptus camaldulensis, withPoong’ort Carex tereticaulis and, variously Marsh Club-sedge Bolboschoenus medianus, Common ReedPhragmites australis and Warrego Summer-grassPaspalidium jubiflorum in association or mosaic withCommon Spike-sedge Eleocharis acuta and/or SpinyMud-grass Pseudoraphis spinescens (also CommonSwamp Wallaby-grass Amphibromus nervosus,Knotweed Persicaria spp. - in particular CreepingKnotweed P. prostrata, Common Sneezeweed Centipedacunninghamii, Yellow Twin-heads Eclipta platyglossa andPoison Pratia Lobelia concolor.
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Distribution: Low-lying river terraces prone toreasonably regular flooding, most extensive at Barmah.Vegetation Quality: In the north-west part of its range,Sedgy Riverine Forest is heavily invaded and largelydominated by the introduced *Fog-fruit Phyla canescens.In some areas, particularly where the floodplain isrestricted to narrow terraces, the respective habitat issubject to extensive disturbance due to recreationalpressure. The respective habitats (of Sedgy RiverineForest) at Barmah Forest are within areas subject tocattle grazing. However the denser variants of SedgyRiverine Forest vegetation are mostly of lower interest tocattle, which prefer the more open grassy types ofground-layer. Consequently, while the habitat may becrossed by a network of cattle (and brumby) tracks, itstill provides some refugia for a range of relativelygrazing-sensitive species. In general it is considered thatthese species would mostly have been more abundant inother habitats, but have been eliminated either byselective grazing or vulnerability to the deep puggingcaused by stock when the soil is wet.
EVC 818 Shrubby Riverine WoodlandDefining characteristics: Eucalypt woodland (to openforest) of less flood-prone (riverine) watercourse fringes,principally on levees and higher sections of point-bardeposits. Understorey includes a range of species sharedwith drier floodplain habitats (e.g. those supportingBlack Box Eucalyptus largiflorens), with a sparse shrubcomponent, ground-layer patchily dominated by variousgrowth-forms. A range of large dicot herbs (mostlyherbaceous perennial, several with a growth-formapproaching that of small shrub) are conspicuous,notably daisies and peas) are conspicuous in relativelyintact vegetation.Structure: Woodland (to open forest), mostly c. 15- 25m, but sometimes taller with veteran trees. The ground-layer is primarily grassy - herbaceous to c. 1 m. A sparsecomponent of shrubs to 2m or small trees is typicallypresent.Habitat: River verges (and also along major anabranchcreeks), on more elevated portions of lower terraces.Flooding is infrequent, and the habitat is free-drainingfollowing recession of floodwaters. The alluvial soilsoften have a conspicuous sandy component.Floristics: River Red-gum Eucalyptus camaldulensis (+/-Black Box Eucalyptus largiflorens, Eumong Acaciastenophylla), with open Warrego Summer-grassPaspalidium jubiflorum and scattered shrubs includingNitre Goosefoot Chenopodium nitrariaceum, TangledLignum Muehlenbeckia florulenta, Ruby SaltbushEnchylaena tomentosa var. tomentosa and HedgeSaltbush Rhagodia spinescens. Dicot herbs includeBranching Groundsel Senecio cunninghamii var.cunninghamii, Variable Groundsel Senecio pinnatifolius,Golden Everlasting Xerochrysum bracteatum, Squat PicrisPicris squarrosa, Grey Germander Teucrium racemosums.l., Austral Trefoil Lotus australis, Blue Burr-daisy Calotiscuneifolia and (very localised) Hairy Darling-peaSwainsona greyana.Distribution: Murray River, best developed (both interms of floristics and extent) at Lindsay Island, MulcraIsland and Walpolla Island (far north-west), but moremarginal examples are scattered upstream at least tonear the junction with the Wakool River.
Vegetation Quality: Many examples are subject torecreational disturbance due to their proximity towatercourses. In general, weeds appear relatively minor(at least under drought conditions), and vegetationquality is high in areas not subject to major recreationalpressure.
EVC 819 Spike-sedge WetlandDefining characteristics: Low sedgy vegetation ofspecies-poor seasonal or intermittent wetlands,dominated by spike-sedges.Structure: Sedgeland (typically closed), mostly c. 0.2 -0.5 m at maximum culm growth, with dead culmsforming a dense prostrate mat during drier periods.Habitat: Mostly confined to a narrow ring around theupper margins of floodway ponds. Soils are typicallyheavy clays (e.g. mottled yellow-grey clay, grey loamyclay), occasionally silty near the surface. The elevationsof quadrat samples range from c. 60 - 130 m but can bepresumed to occur over a somewhat wider elevationrange. The relevant floristic balance appears to bedetermined by a subtle combination ofreliability/variability, timing and depth of inundation, inassociation with soil characteristics (such that CommonSpike-sedge Eleocharis acuta is able to form acompetitive sward within stages of very shallow springto early summer inundation). In some riverine sites,annual inundation is not reliable and the rhizomicrootstocks of Common Spike-sedge Eleocharis acutaappear capable of surviving at least occasional periods oflonger dormancy.Floristics: Common Spike-sedge Eleocharis acuta (andat some Barmah locations, with Small Spike-sedgeEleocharis pusilla). The vegetation is often virtuallymonospecific, but can be richer in drier or peripheralsites. Typically treeless, but sometimes with thickets ofsaplings or scattered more mature specimens of RiverRed-gum Eucalyptus camaldulensis. Shallow seasonalwetlands in flood-prone areas, dominated by low sedgesthat are tolerant of inundation. In its flooded and dryingphase, some of the following may be present, WaterRibbons Triglochin procera s.l., Upright Water-milfoilMyriophyllum crispatum, Common Nardoo Marsileadrummondii, Ludwigia peploides subsp. montevidensis,Poison Pratia Lobelia concolor, Drain Flat-sedge*Cyperuseragrostis, Matted Water-starwort Callitriche sonderi,and Western Water-starwort Callitriche cyclocarpa. In adrier phase, Creeping Knotweed Persicaria prostrata,Common Blown-grass Lachnagrostis filiformis may bethe most common associated species. Often densestands of Cotton Fireweed Senecio quadridentatus occuron the margins of this community. Similar vegetation,occurs along many of the deeper creek channels. Wherethese receive irrigation effluent, some may remainperpetually wet and Water Couch*Paspalum distichummay be prolific, replacing the Common Spike-sedgeEleocharis acuta and Common Sneezeweed Centipedacunninghamii. In wet but unsaturated locations, densestands of Tall Flat-sedge Cyperus exaltatus sometimesoccur. Distribution: Scattered distribution on the Riverinafloodplain (eg. Benwell Swamp and Guttram Swampnear Levee Track in Gunbower State Forest) Vegetation Quality: Spike-sedge Wetland ischaracteristically species-poor, except around the verges.
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However, the species-richness of the relevant systemscan be further reduced by grazing of cattle (throughselective grazing, pugging and trampling). Whilereasonably resilient to longer dry periods, deteriorationand contraction of riverine floodplain occurrences can beanticipated as a consequence of reduced flooding of theMurray River. When disturbed, Spike-sedge Wetland canbe invaded by weeds such as Curled Dock *Rumexcrispus, *Sagittaria spp., Water Plantain *Alismalanceolata, Water Couch*Paspalum distichum andLilaea*Lilaea scillioides.
EVC 820 Sub-saline Depression ShrublandDefining characteristics: Low open shrubland/herblandof the highest terraces of the former (i.e. pre-1750)Murray River floodplain in far north-west, dominated bychenopods and succulents, occupying semi-salinetreeless pans within the Black Box - ChenopodWoodland zone.Structure: Low open shrubland/herbland, dominated bychenopods and succulents, mostly < 0.5 - 1 m in height.Habitat: Low-lying areas with very heavy and mildlysaline clay soils. On higher terraces, and presumably nolonger subject to occasional shallow flooding. Recordedfrom elevations within the range of c. 30 - 50 m.Floristics: The major species include StreakedCopperburr Sclerolaena tricuspis, Goat Head Malacoceratricornis and Rounded Noon-flower Disphymacrassifolium subsp. clavellatum, variously with HairyBluebush Maireana pentagona and Rosinweed Cressacretica/Sea Heath Frankenia spp./Sarcocornia spp.South of Lindsay River: Streaked Copperburr Sclerolaenatricuspis, Goat Head Malacocera tricornis, RosinweedCressa cretica, Rounded Noon-flower Disphymacrassifolium subsp. clavellatum, Flat-top Saltbush Atriplexlindleyi, Hairy Bluebush Maireana pentagona, Short-wingSaltbush Sclerochlamys brachyptera, Slender GroundselSenecio glossanthus, Salt Sea-spurrey Spergularia sp. 3,Goodenia spp. and Daisy Brachyscome spp.Lambert Island: Sarcocornia spp. and Sea-heathFrankenia spp. in association with Streaked CopperburrSclerolaena tricuspis.Distribution: Very localised in far north-west, mostextensive in the vicinity of Lindsay Island, with smallerexamples at Walpolla Island and Lambert Island - originalextent difficult to ascertain due to habitat degradation.Vegetation Quality: The former floristics of higher-levelfloodway depressions are poorly understood due to theimpacts of grazing and virtual cessation of higher-levelflooding.
EVC 937 Swampy WoodlandDefining characteristics: Open eucalypt woodland withground-layer dominated by tussock grasses and/orsedges and often rich in herbs. Occurs on poorlydrained, seasonally waterlogged heavy soils, primarily onswamp deposits but extending to suitable substrateswithin some landscapes of sedimentary origin. Once a common vegetation type along broad drainagelines with slight gradients and on lower slopes nearstreams or larger rivers, Swampy Riparian Woodland hasbeen largely altered particularly by drainage foragriculture. It may be found growing on lower slopesnear streams and less commonly in gentle basins onvalley slopes in association with permanent soaks or
springs, not necessarily associated with permanentstreams. Rainfall is in the range of 900-1500 mm peryear and the elevation range is between 300 and 800 m.The soils are generally Quaternary alluviums in streamenvironments derived from a broad range of parentgeologies which are mostly Cambrian and Ordovicianmarine sediments and metamorphosed sediments. The woodland overstorey often forms mosaics withwetter treeless areas dominated by sedges, rushes andmany other plants associated with riparianenvironments. Mountain Swamp Gum Eucalyptuscamphora is the dominant overstorey species. A widerange of other eucalypts can be present, mainly asadventive species from the surrounding drier forests,The understorey shrubs consist of Blackwood Acaciamelanoxylon (as it rarely reaches tree-form in thiscommunity) and Prickly Currant-bush Coprosmaquadrifida. Common Cassinia Cassinia aculeata andSilver Wattle Acacia dealbata are also sporadicallypresent as adventive species from the surrounding driervegetation. Ovens Wattle Acacia pravissima, Prickly Tea-tree Leptospermum continentale may also be present.The ground stratum is the most characteristic feature ofthis EVC and is normally dense with sedges such asLeafy Flat-sedge Cyperus lucidus and Tall Sedge Carexappressa competing for space with ferns like FishboneWater-fern Blechnum nudum, Soft Water-fern Blechnumminus and Mother Shield-fern Polystichum proliferum. There are many other plants which also occur in RiparianForest which compete for space between the inter-tussock gaps of sedges and ferns such as Bidgee WidgeeAcaena novae-zelandiae, Kidney-weed Dichondrarepens, Cinquefoil Cranesbill Geranium potentilloides,Austral Brooklime Gratiola peruviana, and HairyPennywort Hydrocotyle hirta.
EVC 821 Tall MarshDefining characteristics: Wetland dominated by tallemergent graminoids, typically in thick species-poorswards. Competitive exclusion in core wetland habitat -of optimum growing conditions for species tolerant ofsustained shallow inundation.Structure: Rushland, sedgeland or reedbed. Usuallydense vegetation, varying from locally closed to inassociation or fine-scale mosaic with Aquatic Herbland(e.g. along floodway lagoons). Mostly within (1-) 2- 4 mheight range.Habitat: Wetlands (usually associated with anabranchcreeks) and spontaneous along irrigation drains. Also inaltered habitat where high water levels associated withlocks create wet terraces, especially on small islands andin areas not subject to grazing by domestic stock. Soilsare almost permanently moist. Dominant species aretolerant of relatively deep and sustained inundation, butnot total immersion for any sustained period.Floristics: Sparse specimens of Eucalyptus camaldulensiscan be present (or form an overhanging canopy alongnarrow floodways), but well developed examples of thisvegetation type are typically treeless or virtually so. Inthe far north-west, Bulrush Typha spp. (mainly Narrow-leaf Cumbungi Typha domingensis but tentatively alsoBroad-leaf Cumbungi Typha orientalis) are the usualdominant species, sometimes in association or mosaicwith River Club-sedge Schoenoplectus tabernaemontani.Common Reed Phragmites australis sometimes occurs as
River Red Gum Forests Investigation > 2006404
a thin riparian verge, but mostly below map scale.Other graminoids that can be present include RushJuncus spp. such as Giant Rush Juncus ingens#andSedge Cyperus spp. A range of aquatic andopportunistic herbaceous species is present in moreopen areas supporting Bulrush Typha spp. (e.g. withinfloodway channels). Common associated species includeSlender Knotweed Persicaria decipiens, Pale KnotweedPersicaria lapathifolia, Small Loosestrife Lythrumhyssopifolia, Pacific Azolla Azolla filiculoides, RobustWater-milfoil Myriophyllum papillosum, Wavy MarshwortNymphoides crenata, Common Spike-sedge Eleocharisacuta, Water Ribbons Triglochin procera s.l., FloatingPondweed Potamogeton tricarinatus s.l., Clove-stripLudwigia peploides subsp. montevidensis and SpinyMud-grass Pseudoraphis spinescens. Under drierconditions Common Sneezeweed Centipedacunninghamii, Lesser Joyweed Alternanthera denticulatas.l. and Common Blown-grass Lachnagrostis filiformismay be present. Introduced herbaceous species (e.g.Marsh Yellow-cress*Rorippa palustris, Dock *Rumexspp., Sow-thistle *Sonchus spp. and Lettuce *Lactucaspp.) and the grass Annual Beard-grass *Polypogonmonspeliensis can also be conspicuous, especially duringdrier periods. In many areas the community has beeninvaded by Grey Sallow *Salix cinerea. This Willow iswell established along Gunbower Creek. Distribution: Scattered, mostly as thin strips anddisjunct small patches on the riverine floodplain such ason the southern verges of Kings Billabong.Vegetation Quality: Smaller occurrences are typicallyhighly modified by changed hydrology and weedinvasions. Artificial habitats maintained by irrigationwater can be colonised by tall emergent graminoids,
notably Narrow-leaf Cumbungi Typha domingensis. Thiscommunity occupies all the semi permanent waterbodies of Gunbower Forest and has probablyexperienced a considerable decline with river regulationeg. this vegetation was probably well represented inBlack Swamp before the installation of the regulator onGunbower Creek. Traces of the community can be seenin some of the swamps within Gunbower Forest wherethey still receive irrigation waters eg. Batemans Lagoon.Comments: Generally occupies deep water adjacent tothe flooded Sedgy Riverine Forest/Riverine Swamp Forest.Tall Marsh can be adventive in Floodplain GrassyWetland and Floodway Pond Herbland, (and relatedcomplexes and mosaics).Ginat Rush #Juncus ingens occupies areas within theforest whose frequency and duration of floodingexceeds the tolerance of forest. Under natural floodingregimes, these low areas may remain flooded into thesummer months when air temperatures are high. Thisfeature, when combined with the dense resilient foliagehas attracted colonies of breeding water birds in thepast. The late spring/early summer flood recessionresults in high water temperatures and poor soil aerationduring the growing season, causing tree death butwhich can be tolerated by Giant Rush Juncus ingens.This species is also capable of withstanding periods ofdrought provided these are infrequent and of shortduration. It is probable that this community hascontracted greatly at Gunbower Forest as a result of thehydrological changes that have occurred since floodcontrol and it formerly would have been associated withmost of the semi-permanent swamps within the forest.This contraction is still evident at the Reed Beds inGuttram State Forest.
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APPENDIX 8: Potentially Threatening Processesin the River Red Gum Forests study area
Potentially Threatening Process Act
Alteration to the natural flow regimes of rivers and streams FFG
Alteration to the natural temperature regimes of rivers and streams FFG
Collection of native orchids FFG
Degradation of native riparian vegetation along Victorian rivers and streams FFG
Habitat fragmentation as a threatening process for fauna in Victoria FFG
High frequency fire resulting in disruption of life cycle processes in plants and animals and loss of vegetation structure and composition FFG
Inappropriate fire regimes causing disruption to sustainable ecosystem processes and resultant loss of biodiversity FFG
Increase in sediment input into Victorian rivers and streams due to human activities FFG
Input of toxic substances into Victorian rivers and streams FFG
Introduction of live fish into waters outside their natural range within a Victorian river catchment after 1770 FFG
Invasion of native vegetation by ‘environmental weeds’ FFG
Loss of coarse woody debris from Victorian native forests and woodlands FFG
Loss of hollow-bearing trees from Victorian native forests FFG
Loss of terrestrial climatic habitat caused by anthropogenic emissions of greenhouse gases. FFG
Predation of native wildlife by the cat, Felis catus FFG
Predation of native wildlife by the introduced Red Fox Vulpes vulpes FFG
Prevention of passage of aquatic biota as a result of the presence of instream structures FFG
Reduction in biomass and biodiversity of native vegetation through grazing by the Rabbit Oryctolagus cuniculus FFG
Removal of wood debris from Victorian streams FFG
The introduction and spread of the Large Earth Bumblebee Bombus terrestris into Victorian terrestrial environments FFG
Threats to native flora and fauna arising from the use by the feral honeybee Apis mellifera of nesting hollows and floral resources FFG
Use of lead shot in cartridges for the hunting of waterfowl FFG
Wetland loss and degradation as a result of change in water regime, dredging, draining, filling and grazing FFG
Invasion of native vegetation by Blackberry Rubus fruticosus L. agg. FFG
Competition and land degradation by feral Goats EPBC
Competition and land degradation by feral Rabbits EPBC
Infection of amphibians with chytrid fungus resulting in chytridiomycosis EPBC
Land clearance EPBC
Loss of climatic habitat caused by anthropogenic emissions of greenhouse gases EPBC
Predation by feral Cats EPBC
Predation by the European Red Fox (Vulpes vulpes) EPBC
Predation, Habitat Degradation, Competition and Disease Transmission by Feral Pigs EPBC
Psittacine Circoviral (beak and feather) Disease affecting endangered psittacine species EPBC
Potentially threatening processes expected to occur in or have impacts within the River Red Gum Forestsstudy area listed under the Flora and Fauna Guarantee Act 1988 (FFG) or the Environment Protection andBiodiversity Conservation Act 1999 (EPBC).
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Preamble1. Yorta Yorta Nation Aboriginal Corporation represents
the Yorta Yorta People who assert culturalconnection, based on ancestry and tradition, to theDesignated Areas (described in Schedule 2).
2. The State of Victoria recognises the culturalconnection of the Yorta Yorta People to theDesignated Areas.
3. Accordingly, the State has agreed to recommend tothe Minister responsible for the Conservation, Forestsand Lands Act 1987 (Vic) the establishment of acommittee pursuant to section 12 of that Act.
4. The committee will be known as the Yorta Yorta JointBody.
5. In establishing the Yorta Yorta Joint Body the Ministeror the Secretary intends to refer the matters describedin this Agreement to it for consideration.
6. The Yorta Yorta Joint Body will formalise the YortaYorta People's involvement in the management of theDesignated Areas and facilitate the development of asustainable partnership based on recognition, mutualrespect and agreed goals .
7. The State will adopt a flexible and learning approachto working with and meeting the aspirations of theYorta Yorta People. The Yorta Yorta People will adopta flexible and learning approach to state landmanagement policies and processes.
8. The Yorta Yorta People and the State recognise thatSchedule 2 of the Conservation, Forests and LandsAct has effect on committees established pursuant tosection 12 of that Act.
9. The purpose of this Agreement is to set out the termsand conditions reached between the State and theYorta Yorta People, including the Terms of Referenceof the Yorta Yorta Joint Body (Schedule 3) that theState will recommend to the Minister.
10. This Agreement successfully completes negotiationsfor the co-operative management of the DesignatedAreas between the State and the Yorta Yorta People,consistent with the signed Negotiating Principles.
Acknowledgment11. The State recognises:
• the right of the Yorta Yorta People to retain their identity and intellectual property; and
• the Yorta Yorta People’s role in management decision making within the Designated Areasrelating to the protection, maintenance andsustainable of cultural and environmentalvalues.
12. The Yorta Yorta People recognise the State as therepresentative of all Victorians, and its established andon-going responsibilities for the sustainablemanagement of the Designated Areas.
Objectives13. The objectives of this Agreement are to facilitate:
13.1 the active and resourced (in accordance withSchedule 4) involvement of the Yorta YortaPeople in decisions about the management ofthe Designated Areas including the integrationof Yorta Yorta knowledge, internal decision-making processes and perspectives intomanagement planning and works programming;
13.2 the development of mutual recognition and trust between the Yorta Yorta Peopleand the State; and
13.3 the identification and promotion ofemployment, training and economicdevelopment opportunities for the YortaYorta People.
Designated Areas14. The Agreement will apply to the Designated Areas, as
defined in Schedule 2.
Relationships
Relationship of the Yorta Yorta Joint Body with landmanagement bodies
15. The State shall assist and to the extent possiblerequire other organisations responsible for managingand/or providing advice regarding the management ofthe Designated Areas to develop communicationprotocols and working relationships with the YortaYorta Joint Body.
Relationship of the Yorta Yorta Joint Body with theMinister and Secretary
16. In the process of making a decision regarding themanagement of the Designated Areas, the Minister orthe Secretary will take into account relevant adviceand recommendations he or she has received from:
16.1 the Yorta Yorta Joint Body in accordancewith this Agreement; and
16.2 the organisations responsible for managingand/or providing advice regarding themanagement of the Designated Areas.
17. If there is conflicting advice prior to making adecision regarding the management of the DesignatedAreas, the Minister or Secretary, as applicable, willtake into account advice from the Yorta Yorta JointBody in relation to that conflicting advice.
18. If the Minister or the Secretary, as applicable, inmaking a decision in relation to a matter on whichthe Yorta Yorta Joint Body has provided advice or arecommendation, decides to act otherwise than inaccordance with that advice or recommendation, theMinister or Secretary, as applicable, may provide theYorta Yorta Joint Body with written reasons for thedecision.
APPENDIX 9: Extract of the Co-operative ManagementAgreement between Yorta Yorta Nation AboriginalCorporation and The State of VictoriaNote: the agreement, map and a factsheet are available at the following website:http://www.dse.vic.gov.au/dse/nrenlwm.nsf/LinkView/7FA349BEAE0F5A3FCA256E8D00210309A4AD52AC7C448F1A4A256DEA0024EDD2
Discussion Paper 407
Affect of this Agreement on rights andobligations19. To be clear, nothing in this Agreement:
19.1 compromises the legal rights or politicalaspirations of the Yorta Yorta Peoplerelative to any of their other social, culturaland economic goals;
19.2 affects any rights that the Yorta YortaPeople may have to their intellectual andcultural property;
19.3 limits the State’s prerogatives under anyrelevant laws and policies;
19.4 limits the powers of the Minister or theSecretary in relation to any matter, in particular, the powers of the Minister unders12 of the Conservation, Forests and LandsAct 1987 (Vic) to deal with the Yorta YortaJoint Body;
19.5 affects any rights, duties or obligations arisingfrom the operation of the Archaeological andAboriginal Relics Preservation Act 1972 (Victoria)or the Aboriginal and Torres Strait IslanderHeritage Protection Act 1984 (Commonwealth);
19.6 limits the capacity of organisationsresponsible for managing the DesignatedAreas to continue to perform theirestablished functions including, asapplicable, in relation to the managementof lands or waters and the provision ofindependent advice; or
19.7 affects the valid rights of parties, bothIndigenous and non-Indigenous.
Review20. The role and structure of the Yorta Yorta Joint Body
will be subject to ongoing internal review.21. The Minister may review the structure and role of the
Yorta Yorta Joint Body, at the end of the first 2-yearperiod from the date of its establishment.21.1 The review period shall be 30 days.21.2 In conducting a review, the Minister or the
Secretary may take into account any AnnualReport prepared by the Yorta Yorta Joint Body.
21.3 At the end of the review period, the Ministeror the Secretary shall discuss with the YortaYorta Joint Body any changes that the Ministeror the Secretary wishes to make to thestructure, role or terms of reference of the
Yorta Yorta Joint Body.
Resources22. The Yorta Yorta Joint Body will be resourced, as
detailed in Schedule 4.
Termination by the Yorta Yorta People23. The Yorta Yorta People may at any time, and in their
sole discretion, provide a written request to theMinister or the Secretary to abolish the Yorta YortaJoint Body.
Schedule 1List of Definitions“Convenor” means the person referred to in Clause 17 ofSchedule 3.
“Cultural Heritage Officer” means the person referred bythis name in Schedule 4.
“Designated Areas” means the areas set out in Schedule 2.
“Elders” according to Yorta Yorta traditional law and custommeans a mature, capable, wise and respected adult YortaYorta person who has knowledge of Yorta Yorta culture andis recognised and respected by the Yorta Yorta People ingeneral as having such knowledge.
“Elders Council” means a group of Yorta Yorta Elders, eachnominated by their respective family groups, who are theguardians of the objects of YYNAC.
“Executive Officer” means the person referred to by thisname in Schedule 4.
“Funding Agreement” means the Funding Agreementbetween the State and the YYNAC.
“Minister” means the Minister for Environment and delegates.
“Negotiation Principles” means the signed principles ofnegotiation approved by Cabinet in May 2002.
“Secretary” means the Secretary of the Department ofSustainability and Environment.
“Specialist Officer” means the person referred to by thisname in Schedule 4.
“State” means the State of Victoria.
“VEAC” means the Victorian Environmental AssessmentCouncil.
“Yorta Yorta Joint Body” means the Committee establishedunder s12 of the Conservation Forests and Lands Act 1987(Vic).
“Yorta Yorta People” means the Indigenous peoples who areeligible to be members of the YYNAC.
“YYJB” means the Yorta Yorta Joint Body.
“YYNAC” means Yorta Yorta Nation Aboriginal Corporation,a body corporate incorporated under the Aboriginal Councilsand Associations Act 1976 (Cth) on 27 November 1998 torepresent the Yorta Yorta People.
Schedule 2Designated Areas1. “Designated Areas” means (using the same land and
water identification numbers (ID) referred to in theYorta Yorta Proceedings) the following areas:
(a) Barmah State Park (IDs 58; 63); Barmah StateForest (IDs 56; 118); The Ranch (ID 134); Top IslandReference Area (ID 68); Top End Reference Area (ID64); Murray River State Reserved Forest (IDS 46;919); Murray River Reserve (ID 908) to andincluding Ulupna Creek Reserve (ID 909);
(b) Kow Swamp Water Supply Reserve (ID 82) ; and
(c) Goulburn River State Forest (IDs 145; 221);Kanyapella Timber Reserve (ID 159) ; KanyapellaState Forest (ID 160); Redgum Swamp State Forest(ID 176); Monroes Reserved Forest (ID 181) ; LochGary Wildlife Reserve (ID901); Reedy SwampWildlife Reserve (ID 203) ; Youngs Bend State Forest(ID 213) ; Gemmill Swamp Wildlife Reserve (ID 216);Goulburn River Reserved Forest (IDs 237; 240);Goulburn River Reserve (ID 912); and MurchisonNorth Crown Land (ID 913).
2. A legal plan reflecting the Designated Areas will bedrawn up within six months of the execution of thisAgreement.
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APPENDIX 10: Nature Conservation Reserves
Name ofReserve
Area(ha)
LCC rec CurrentReservation Status
Date ofcreation
Comments (see also information sourcesprovided below)
Boort FloraReserve
43 G2(a) Not currentlyreserved
– Scrub community of dumosa mallee and yellowgum woodland.
Cannie FloraReserve
16 G69(c) Not currentlyreserved
– Relatively undisturbed buloke woodland andassociated grassland growing on calcareous clays.Very little of this vegetation and soil type remainas public land in the southern Mallee.
DartagookWildlifeReserve
746 D9 andadditionD15(c)
Not currentlyreserved
– Nature Conservation Status pending reservation.The forest of black box, river red gum andlignum is part of the floodplain at the junction ofthe Loddon River and Sheepwash Creek.
Duck LakeWildlifeReserve
413 D27(c) Not currentlyreserved
– Reservation as a wildlife reserve (no hunting)pending. This saline wetland has wide muddyshores frequented by wading birds.
FlanneryWildlifeReserve
51 C12(a) Reserved for themanagement ofwildlife under theCrown Land(Reserves) Act 1978,and the Wildlife Act1975
1986 Wetland of lignum with some black box anddead trees.
GemmillSwampWildlifeReserve
213 C17(a) Reserved for themanagement ofwildlife under theCrown Land(Reserves) Act 1978,and the Wildlife Act1975
1986 Also known as ‘Youngs Bend’. Semi-permanentfresh-water wetland comprising rushes and reedswith a river red gum forest and some yellow boxwoodland to the north.
Karadoc Flora Reserve
111 G56(c) Not currentlyreserved
– A reasonably intact remnant of the higher riverterrace carrying alluvial-plain shrublands togetherwith the black box and river red gum terracesdescending to the River Murray afford this areasignificant botanical variety. The climbing herbtwining purlane and the subshrub twin-flowersaltbush, both being rare plants usuallyassociated with saline shrublands, are foundhere.
KingsBillabongWildlifeReserve
2135 D1(c) Reserved for themanagement ofwildlife under theCrown Land(Reserves) Act 1978
1979 Contains a mosaic of wet and dryland habitatson the Murray River floodplain. It has a largewaterfowl population. A Proposed ManagementPlan was implemented in 1991.
Kotta NatureConservationReserve
226 No LCCrec (landpurchase)
Temporarily reservedfor the preservationof an area ofecologicalsignificance underthe Crown Land(Reserves) Act 1978
2004 Purchased through the National Reserve SystemProgram. A management statement (2005) is inplace. Contains a diverse example ofendangered Northern Plains Grasslands with anumber of threatened flora species. Provideshabitat for plains-wanderer, barking marsh frogand fat-tailed dunnart. Adjoins Trust for Nature-owned Glassons Grassland and conservationcovenant-protected grasslands. (2) (4)
Discussion Paper 409
Name ofReserve
Area(ha)
LCC rec CurrentReservation Status
Date ofcreation
Comments (see also information sourcesprovided below)
LakeMoodemereNatureConservationReserve
12 No LCCrec (landpurchase)
Part temporarilyreserved for theconservation of anarea of naturalinterest and parttemporarily reservedfor the preservationof an area ofecologicalsignificance underthe Crown Land(Reserves) Act 1978
2001 Purchased through the National ReserveSystem Program. A management statement(2005) is in place. Significant areas ofthreatened grey box-buloke woodland occuron the site and the vulnerable buloke mistletoeis also present. Adjoins Lake Moodemere LakeReserve. (1) (5)
Lakes Powelland CarpulWildlifeReserve
683 D2 andadditionof D14(c)
Reserved for themanagement ofwildlife andpreservation ofwildlife habitat underthe Crown Land(Reserves) Act 1978,and the Wildlife Act1975
1979 Lakes surrounded by river red gum and blackbox woodlands filled when the Murray Riverfloods.
MullarooCreekWildlifeReserve
1142 D17(c) Not currentlyreserved
- A range of values including broad grasslands,river red gum forests, blackbox-chenopodwoodlands, and alluvial plain shrubland..
LambertIsland FloraReserve
948 G55(c) Not currentlyreserved
1990 Extensive black box—chenopod woodlandsand small stands of cypress-pine and river redgum, notable species include the flood-dependent herb jerry-jerry and a large colonyof the endangered herb yellow tails. Currentlyhas apiary sites.
LeaghurWildlifeReserve
176 D33(c) Not currentlyreserved
1990 Nature Conservation Status pendingreservation. Portion of a braided stream.Lignum wetland, with common wetlandgrasses and herbs and relatively low weedcover. Moderately high native species diversity.Significant species are pale spike-sedge, bluishraspwort form glauca, and swamp buttercup(all vulnerable in Victoria).
One TreeSwampNatureConservationReserve
676 No LCCrec (landpurchase)
Reserved for thepreservation of anarea of ecologicalsignificance underthe Crown Land(Reserves) Act 1978,small area currently aWater Reserve.
2003 Purchased through the National ReserveSystem Program. Large Cane Grass Wetlandwith small areas of Northern Plains Grasslandand Plains Woodland. Important brolgabreeding habitat. Adjoins Two Tree SwampWildlife Reserve to the north. (2)
Ovens RiverFlora Reserve(Peechelba)
220 G8(a) Reserved for thepreservation ofspecies of nativeplants under theCrown Land(Reserves) Act 1978
1986 Also known as ‘Peechelba Flora Reserve’. Riverred gum forest on the Ovens River with ashrub understorey of river bottlebrush, silverwattle, and swamp paperbark. The occurrenceof this melaleuca here is unique in the areaand of conservation significance. The OvensHeritage River is an overlay.
River Red Gum Forests Investigation > 2006410
Name ofReserve
Area(ha)
LCC rec CurrentReservation Status
Date ofcreation
Comments (see also information sourcesprovided below)
PassageCamp FloraReserve
21 G65(c) Reserved underForests Act 1958
1990 River red gum forest grows on an island bendof the River Murray with a large population ofthe grass silky browntop.
Patho WildlifeReserve
75 C14(c) Reserved for themanagement ofwildlife under theCrown Land(Reserves) Act 1978,and the Wildlife Act1975
1986 Permanent and semi-permanent wetland andlagoon system with river red gum open forestand black box open forest-woodland.
Pelican LakeWildlifeReserve
38 D29(c) Not currentlyreserved
– Nature Conservation Status pendingreservation. A brackish wetland, anddegrading; it is used by large numbers ofwaterfowl.
Pine GroveNatureConservationReserve
38 No LCCrec (landpurchase)
Temporarily reservedfor the preservationof an area ofecologicalsignificance underthe Crown Land(Reserves) Act 1978
2001 Purchased through the National ReserveSystem Program. Management Statement inplace (2005). Contains endangered NorthernPlains Grasslands and habitat for plains-wanderer. Gilgais and drainage lines are stillpresent, while the cracks in the heavier greysoils provide habitat for reptiles and fat-taileddunnarts. (1) (6)
Red GumSwampWildlifeReserve(Gannawarra)
148 C8(a) Reserved for themanagement ofwildlife under theCrown Land(Reserves) Act 1978,and the Wildlife Act1975
1986 Wetland containing saltbush, lignum, andnumerous dead river red gum trees.
RoslynmeadFlora Reserve
574 G4(a) plusadditionofpurchasedland
Partly reserved forthe preservation ofspecies of nativeplants, partlytemporarily reservedfor the conservationof an area of naturalinterest, partlytemporarily reservedfor public purposes,and partlytemporarily reservedfor the preservationof an area ofecologicalsignificance underthe Crown Land(Reserves) Act 1978
1986,2001
Mostly purchased through the NationalReserve System Program to be combined withTurrumberry North Flora Reserve asRoslynmead Nature Conservation Reserve.Management Statement in place (2005).Contains endangered Northern PlainsGrasslands and habitat for plains-wanderer. Sixthreatened plant species have been recordedon the site and there is a high level of diversityand complexity in the habitats found acrossthe site due to small changes in relief andvarying soil types. (1) (7)
RowlandWildlifeReserve
126 C11(a) Reserved for themanagement ofwildlife under theCrown Land(Reserves) Act 1978,and the Wildlife Act1975
1986 Heathy wetland of saltbush with some blackbox and dead trees.
Discussion Paper 411
Name ofReserve
Area(ha)
LCC rec CurrentReservation Status
Date ofcreation
Comments (see also information sourcesprovided below)
Ryans LagoonWildlifeReserve
151 C5(b) Reserved for PublicPurposes (RegionalParklands) under theCrown Land(Reserves) Act 1978
1987 Nature Conservation Status pendingreservation. Managed as part of the Albury-Wodonga Regional Parklands. Shallow fresh-water swamp with floodways, lagoons, andgrasslands. This reserve supports a breedingrookery of Australian white ibis, nankeennight herons, egrets, and other waterfowl.
SheppartonFlora andFauna Reserve
21 No LCCrec
Reserved for thepreservation ofnative flora andfauna under theCrown Land(Reserves) Act 1978
1972 Former township land excluded from LCCinvestigations.
Terrick TerrickEast NatureConservationReserve
212 No LCCrec (landpurchase)
Temporarily reservedfor the conservationof an area of naturalinterest under theCrown Land(Reserves) Act 1978
2000 Purchased through the National ReserveSystem Program. Management Statement inplace (2005). Contains endangered NorthernPlains Grasslands community and habitat forplains wanderer. Contains populations of twonationally threatened plants: chariot wheelsand slender darling-pea, as well as a numberof species of state and regional significance.(1) (8)
TomaraGilgais NatureConservationReserve
336 No LCCrec (landpurchase)
Temporarily reservedfor the preservationof an area ofecologicalsignificance underthe Crown Land(Reserves) Act 1978
2005 Purchased through the National ReserveSystem Program. Contains endangeredNorthern Plains Grasslands and habitat forplains-wanderer. Significant flora includeslong eryngium, pin sida, umbrella wattle,spiny lignum and yakka grass. Brolgas havebeen recorded using the wetland area. (3)
TowaninnyFlora Reserve
21 G70(c) Not currentlyreserved
– Relatively undisturbed grassland again occurson calcareous clays, very little of whichremains as public land in the southernMallee.
TowaninnySouth FloraReserve
81 G71(c) Not currentlyreserved
– Relatively undisturbed grassland again occurson calcareous clays, very little of whichremains as public land in the southernMallee.
TragowelSwampWildlifeReserve
274 C4(a) Partly reserved forthe management ofwildlife, publicpurposes forrecreation and publicamenity under theCrown Land(Reserves) Act 1978,and the Wildlife Act1975
1986 Grassy, fresh-water wetland with scatteredblack box. An ibis breeding area.
Two TreeSwampWildlifeReserve
167 C11(a) Deemed reserved for the managementof wildlife andpreservation ofwildlife habitat underthe Crown Land(Reserves) Act 1978,and the Wildlife Act1975
1982 Cane grass wetland. Adjoins One TreeSwamp Nature Conservation Reserve to thesouth.
River Red Gum Forests Investigation > 2006412
Name ofReserve
Area(ha)
LCC rec CurrentReservation Status
Date ofcreation
Comments (see also informationsources provided below)
Wandella Floraand FaunaReserve
981 G38(c) Not currentlyreserved
– Black box with an understorey of lignum,grasses and herbs and excellent waterbirdhabitat.
WanurpNatureConservationReserve
120 No LCC rec(landpurchase)
Temporarily reservedfor the preservationof an area ofecologicalsignificance underthe Crown Land(Reserves) Act 1978
2003 Purchased through the National ReserveSystem Program. Management Statementin place (2005). Contains endangeredNorthern Plains Grasslands and grassywoodlands, rare and threatened flora andknown habitat for Bush stone-curlew. (3)(9)
WinlatonNatureConservationReserve
91 No LCC rec(landpurchase)
Part temporarilyreserved for theconservation of anarea of naturalinterest and partreserved for thepreservation of anarea of ecologicalsignificance underthe Crown Land(Reserves) Act 1978
2004 Main block purchased through the DSEConservation Land Purchase Program withaddition of small Crown land parcel.Contains Riverine Chenopod ShrublandEVC with a number of rare or threatenedflora species. Adjoins land containingnative vegetation protected by aconservation covenant. (3)
YassomSwamp Floraand FaunaReserve
362 G51(c) Not currentlyreserved
– Important breeding and feeding area forwaterbirds and the grassland to the southis growing on red duplex soils of the higheralluvial plains of the Avoca River system.The grasslands are also the habitat of theendangered plains-wanderer.
QuambatookFlora & FaunaReserve.
67 G33(c) Not currentlyreserved
–
Notes:
Nature Conservation Reserves includes the following reserves: Flora, Flora and Fauna, Nature Conservation, Wildlife Area (nohunting). All Nature Conservation Reserves are managed by Parks Victoria.
Although some of these areas are not formally reserved (i.e. LCC recommendation have not been implemented) or are temporarilyreserved as Nature Conservation Reserves, all are managed as if they were so reserved.
LCC recommendations as follows: (a) Murray Valley (1985); (b) North-East (BUM) (1986); (c) Mallee Review (1989).
Source:
(1) Fitzsimons and Ashe (2003)
(2) Fitzsimons et al. (2004)
(3) Fitzsimons et al. (2006)
(4) Robertson & Fitzsimons (2005a)
(5) Robertson & Fitzsimons (2005b)
(6) Robertson & Fitzsimons (2005c)
(7) Robertson & Fitzsimons (2005d)
(8) Robertson & Fitzsimons (2005e)
(9) Robertson & Fitzsimons (2005f)
Discussion Paper 413
APPENDIX 11: Natural Features Reserves
NATURAL FEATURES
Murray River Reserve 16,061 Murray Valley (1985); Mallee Review (1989)
PUBLIC LAND WATER FRONTAGES
various public land water frontages 16,708 various various
BUSHLAND RESERVES
Barrakee Bushland Reserve 9 I162 Wimmera (1986) 1987
Barwo Bushland Reserve 10 H20 Murray Valley (1985) 1986
Barwo Bushland Reserve 6 H22 Murray Valley (1985) 1986
Bockie Bushland Reserve 5 I16 Mallee Review (1989) –
Bonegilla Bushland Reserve 6 I97 North-eastern Area (Benalla-Upper Murray) Review (1986) 1987
Bonegilla Station Bushland Reserve 4 I98 North-eastern Area (Benalla-Upper Murray) Review (1986) 1987
Boosey Bushland Reserve 18 H42 Murray Valley (1985), H8 Box-Ironbark Investigation (2001) 1986
Bumbang Bushland Reserve 27 I261 Mallee Review (1989) 2005
Carlyle Bushland Reserve 5 H115 Murray Valley (1985) 1986
Carwarp Natural Features Reserve 6 No LCC Rec 1989
Chiltern West Bushland Reserve 4 H126 Murray Valley (1985) –
Echuca South Bushland Reserve 28 H12 Murray Valley (1985) (also known as Nanneella 1902Bushland Reserve)
Gunbower Bushland Reserve 7 H4 Murray Valley (1985) 1986
Gunbower Bushland Reserve 9 H5 Murray Valley (1985) 1986
Kaarimba Bushland Reserve 32 H24 Murray Valley (1985) 1986
Kotta (Torrumbarry) Bushland 19 H9 Murray Valley (1985); proposed Little Kotta NatureReserve Conservation Reserve
Kotupna Bushland Reserve 4 H21 Murray Valley (1985) 1986
Kotupna Bushland Reserve 3 H23 Murray Valley (1985) 1986
Lockington Public Purposes Reserve 3 H9A Murray Valley Area 2002
Milloo Bushland Reserve 12 H8 Murray Valley (1985) then H8 Box-Ironbark 1986Investigation (2001)
Moira Bushland Reserve 8 H13 Murray Valley (1985) then H8 Box-Ironbark Investigation 1986(2001)
Moira Bushland Reserve 1 H14 Murray Valley (1985) 1986
Moira Bushland Reserve 2 H15 Murray Valley (1985) 1986
Mologa Bushland Reserve 3 H7 Murray Valley (1985) 1986
Murrabit Bushland Reserve 7 H3 Murray Valley (1985) 1986
Mystic Park Bushland Reserve 646 I291 Mallee Review (1989) 1990
Narioka Bushland Reserve 2 H16 Murray Valley (1985) 1986
Ninyeunook Bushland Reserve 8 I205 Mallee Review (1989) 1979
Nyah Bushland Reserve 150 I164 Mallee Review (1989) 1979
Piangil Bushland Reserve 1 I272 Mallee Review (1989) 1990
Quambatook Bushland Reserve 9 D8 Mallee Review (1989) 1979
Rushworth-Colbinabbin rail line 4 H114 Box-Ironbark Investigation (2001) 2002Bushland Reserve
Shepparton Bushland Reserve 4 H48 Murray Valley (1985) 1986
Strathmerton Bushland Reserve 4 H29 Murray Valley (1985), then H8 Box-Ironbark Investigation 1986(2001)
Name ofReserve
Area (ha)
LCC/ECCrecommendations
Date of creation
River Red Gum Forests Investigation > 2006414
Strathmerton Bushland Reserve 5 H30 Murray Valley (1985), then H8 Box-Ironbark Investigation 1986(2001)
Strathmerton Bushland Reserve 26 H31 Murray Valley (1985), then H8 Box-Ironbark Investigation 1986(2001)
Tallygaroopna Bushland Reserve 7 H25 Murray Valley (1985) –
Terrapee Bushland Reserve 40 I183 North Central (1981) 1983
Towaninny Bushland Reserve 40 I203 Mallee Review (1989) 1979
Turrumberry North Bushland Reserve 7 H10 Murray Valley (1985) 1986
Undera Bushland Reserve 1 H24 Murray Valley (1985) 1990
Wharparilla Bushland Reserve 2 H11 Murray Valley (1985) 1986
Wodonga Bushland Reserve 5 I95 North-eastern Area (Benalla-Upper Murray) Review (1986) 1987
Wyuna Bushland Reserve 201 H113 Box-Ironbark Investigation (2001) 2002
HIGHWAY PARKS
Ballendella (Campaspe River) Northern 21 L9 Murray Valley (1985) 1986Highway Park
Runnymede Highway Park 12 L12 North Central (1981), then H137 Box-Ironbark 1982Investigation (2001)
LAKE RESERVES
Cranes Lake 34 U1 Mallee Review (1989)
Lake Boort Lake Reserve 597 N2 Murray Valley (1985) 1986
Lake Marmal Lake Reserve 151 N1 Murray Valley (1985) 1986
Lake Meering Lake Reserve 205 T7 Mallee Review (1989) 1990
Lake Moodemere Lake Reserve 265 N3 Murray Valley (1985) 1986
SCENIC RESERVES
Red Cliffs Scenic Reserve 23 M1 Mallee Review (1989) 1979
Roslynmead Natural Features Reserve 26 G4 Murray Valley (1985) –
STREAMSIDE RESERVES
Arcadia Streamside Reserve 143 K17 Murray Valley (1985), then H4 Box-Ironbark 1986Investigation (2001)
Campaspe River Streamside Reserve 20 K3 North Central Study (1981), H4 Box-Ironbark Investigation 1982(2001)
Dargalong Streamside Reserve 1 K48 North Central Study (1981) 1875
Deep Creek Streamside Reserve 5 K7 Murray Valley (1985) 1986
Englishs Bridge Streamside Area 14 H4 Box-Ironbark Investigation (2001) 1979
Eurobin Streamside Reserve 2 D5 North-eastern Victoria Oven Softwood Plantation Zone –Special Investigation (1981) but not accepted by Government
Goulburn River Streamside Reserve 24 H4 Box-Ironbark Investigation (2001) –
Goulburn River Streamside Reserve 3 K49 North Central Study (1981), then H4 Box-Ironbark 1982Investigation (2001)
Goulburn River Streamside Reserve 218 K50 North Central Study (1981), then H4 Box-Ironbark 1982Investigation (2001)
Goulburn River, McCoys Bridge 135 K6 Murray Valley (1985) 1986Streamside Reserve
Goulburn River, Yambuna Bridge 44 K5 Murray Valley (1985) 1986Streamside Reserve
Hayanmi Streamside Reserve 17 K30 North Central Study (1981), then H4 Box-Ironbark Investigation (2001) 1982
Kergunyah Streamside Reserve 2 K10 North-eastern Area (Benalla-Upper Murray) Review (1986) 1981
Murray River Streamside Reserve 11 K15 Murray Valley (1985), then H4 Box-Ironbark Investigation 1986(2001)
Murray River Streamside Reserve 14 K16 Murray Valley (1985) 1986
Ovens River Streamside Reserve 12 J5 North-eastern 3,4,5 (1977) 1979
Name ofReserve
Area (ha)
LCC/ECCrecommendations
Date of creation
Discussion Paper 415
Ovens River Streamside Reserve 13 K15 North-eastern Area (Benalla-Upper Murray) Review (1986) 1987
Ovens River Streamside Reserve 11 K16 North-eastern Area (Benalla-Upper Murray) Review (1986) 1987
Oxley Streamside Reserve 1 J4 North-eastern 3,4,5 (1977), then H4 Box-Ironbark Investigation (2001) 1979
Pompapiel Watering Purpose Reserve 17 North Central (1981) (frontage to Bullock Creek) –
Skeleton Creek Streamside Reserve 100 K8 Murray Valley (1985) 1986
Wahring Streamside Reserve 3 No LCC recommendation –
various unnamed streamside reserves 219 various various
WILDLIFE RESERVES (HUNTING ALLOWED)
Baillieu (Richardsons) Lagoon Wildlife 191 C15 Murray Valley (1985) 1986Reserve
Big Reedy Lagoon Wildlife Reserve 274 C30 Murray Valley (1985) 1986
Cemetery Forest Wildlife Reserve 163 C3 Murray Valley (1985) 1986
Corop Wildlife Reserve 2 H1 Box Ironbark (2001)
Cullens Lake Wildlife Reserve 749 D25 Mallee Review (1989) 1990
Gaynor Swamp Wildlife Reserve 452 C10 North Central Study (1981) 1982
Great Spectacle, Little Spectacle, 150 D32 Mallee Review (1989) 1990Round Lake, Tobacco Lake, Little Lake Meran Wildlife Reserve
Heywood Lake Wildlife Reserve 567 D18 Mallee Review (1989) 1990
Hird Swamp Wildlife Reserve 449 C10 Murray Valley (1985) 1986
Johnson Swamp Wildlife Reserve 465 C9 Murray Valley (1985) 1986
Kanyapella State Wildlife Reserve 9 No LCC Rec
Koorangie (The Marshes & Avoca 3255 D8 Mallee Review (1989) and D16 Mallee Review (1989) 1979Floodway) Wildlife Reserve (also known as Koorangie State Game Reserve)
Lake Elizabeth Wildlife Reserve 121 D28 Mallee Review (1989) 1990
Lake Lyndger Wildlife Reserve 332 C2 Murray Valley (1985) 1986
Lake Mannaor Wildlife Reserve 87 D23 Mallee Review (1989) 1990
Lake Murphy Wildlife Reserve 222 D11 Mallee Review (1989) 1979
Lake Tutchewop Wildlife Reserve 515 D24 Mallee Review (1989) 1990
Lake Wandella Wildlife Reserve 62 D30 Mallee Review (1989) 1990
Lake Yando Wildlife Reserve 87 D12 Mallee Review (1989) 1979
Little Lake Charm Wildlife Reserve 61 D26 Mallee Review (1989) 1990
Mansfield Swamp Wildlife Reserve 490 C13 North Central Study (1981) 1982
McDonald Swamp Wildlife Reserve 215 C7 Murray Valley (1985) 1986
Mooroopna Sand Reserve 3 C12 Murray Valley (1985) (to be added to Gemmels Swamp)
Murchison Lagoon Wildlife Reserve 6 C18 North Central Study (1981), then H1 Box-Ironbark 1982Investigation (2001)
Murphy Swamp Wildlife Reserve 85 C16 Murray Valley (1985) 1986
Reedy Swamp Wildlife Reserve 263 C18 Murray Valley (1985) 1986
Stevenson Swamp Wildlife Reserve 93 D10 Mallee Review (1989) 1979
Tang Tang Swamp Wildlife Reserve 129 C9 North Central Study (1981) 1982
The Meadows Wildlife Reserve 50 C13 Murray Valley (1985) 1986
Thunder Swamp Wildlife Reserve 90 C8 North Central Study (1981) 1982
Two Mile Swamp Wildlife Reserve 134 C5 Murray Valley (1985) 1986
Wallenjoe Swamp Wildlife Reserve 425 C12 North Central Study (1981) 1982
Westblades Swamp Wildlife Reserve 70 C6 Murray Valley (1985) 1986
Woolshed Swamp (Boort) Wildlife 472 C1 Murray Valley (1985) 1986Reserve
Name ofReserve
Area (ha)
LCC/ECCrecommendations
Date of creation
River Red Gum Forests Investigation > 2006416
APPENDIX 12: Sites of Geological and GeomorphologicalSignificance in and near the study area
INTERNATIONAL SIGNIFICANCE
BN 079 Murchison Meteorite fall site, MurchisonEast
MD 009 Raak Plain boinka, 16 km NW of Hattah
SH 002 Lake Boga granite quarry mineral typelocality, Lake Boga
NATIONAL SIGNIFICANCE
BD 001 Kow Swamp lake and lunette, 3 km S ofLeitchville
BD 003 Barmah forest alluvial fan and anabranchnetwork, Barmah forest
BN 053 Bama-Goulburn drainage complex,Murray / Goulburn confluence area,Echuca
MD 001 Hattah Lakes overflow land andanabranch system, Hattah
MD 007 Lindsay Island floodplain, scroll bars,active and abandoned channel complex,15 km N of Meringur North
STATE SIGNIFICANCE
BD 003.4 Moira and Barmah Lakes digitate deltaand silt jetty, Barmah forest
BD 003.7 Barmah Choke River Murray constriction,Picnic Point to Barmah
BD 006 Ulupna Creek and Ulupna Islandfloodplain complex, N of Strathmerton
BD 009 Bumbang Bend recent meander cut-off(avulsion), Robinvale
BD 013 Wakool Junction abandoned channels andplains, near Kenley
BN 052 Palaeolake Kanyapella area, E of EchucaVillage
BN 053.3 Murray and Goulburn rivers confluencearea, Echuca
BN 057 Cadell Fault southern trace, KanyapellaSouth
BN 081 Lake Cooper quarry mineral locality,Colbinabbin
BN 086 Shepparton Formation type-section, KiallaWest
MD 007.2 Websters Lagoon and Websters IslandReference Area disrupted drainage andscroll plain
Note: site numbering follows the conventions of GSA Heritage subcommittee- Mapsheets: BD Balranald andDeniliquin; BN Bendigo; SH Swan Hill; SR St Arnaud; MD Mildura; TL Tallangatta; and WN Wangarattaincluding part of Jerilderie.
MD 011 Kings Billabong and the floodplainbetween Butlers and Psyche Bends
MD 018 Olney Bore Eocene to Miocene OlneyFormation type-section, SW of PollardIsland.
MD 019 Wallpolla Island and Creek anabranch andfloodplain, W of Mildura
MD 022 Cowanna Bend neck meander andpotential avulsion site, Redgrove
SH 006 Kerang ground-water discharge area,Kerang to Lake Boga
TL 139 Tawonga Fault, Kiewa Valley Highway
WN 042 Wodonga quarry outwash fans, 6 km Wof Huon Hill
REGIONAL SIGNIFICANCE
BD 002 Murray River cliffs, Robinvale, betweenWemen Cliffs and Euston Lock
BD 003.3 Old Barmah palaeolake area, Barmahforest
BD 003.5 Barmah forest Grass Plains (Long Plain,Duck Hole Plain, Hut Lake Grass Plain,War Plain, and Top Lake)
BD 003.8 Buck's Ridge sand hill, Barmah forest
BD 004 Gunbower Island and Creek, Koondrookto Gunbower
BD 004.3 Little Reedy Lagoon plains area,Gunbower
BD 005 Gunbower Reach of the Murray River,Kate Malone's Bend
BD 006.3 Paddy Hennessy's Cutting, Ulupna Island
BD 007 Murray and Murrumbidgee riversconfluence, near Narrung
BD 010 River Murray floodplain accretion, BelsarIsland, ~15 km SE of Robinvale
BD 012 Haywood Lake, 11 km SE of BoundaryBend
BD014 Murray River channel and concave beach,Boundary Bend
BN 006 Rochester Shire quarry, Rochester
BN 052.2 Bama Sandhill, ~16 km E of Echuca.
BN 053.1 Barmah palaeochannel complex, Barmahforest
SiteNumber
Site Nameand Location
SiteNumber
Site Nameand Location
Discussion Paper 417
BN 054 Kotupna gravel pit, Kotupna
BN 060 Lake Cooper and lunettes, E of theHeathcote
BN 074 Mt. Terrick Terrick, Mitiamo
MD 001.1 Chalka Creek, Yerring Crossing
MD 001.2 Red sand dune, Yerring Track
MD 004 Boundary Point, near state bordersbetween SA, NSW and Victoria
MD 005 Merbein Cliffs, River Murray, Merbein
MD 006 Red Cliffs Murray River, Red Cliffs
MD 007.1 Mullaroo Ck, and floodplain south of theCreek
MD 011.1 Psyche Bend, Murray River
MD 012 Nangiloc cliffs Murray River, at Nangiloc
MD 015 Lake Wallawalla and lunette, 14 km W ofNeds Corner homestead
MD 019.1 grass plain
MD 021 Yelta cliff exposures, Yelta
MD 024 Patterwallkagee Creek, Neds CornerHomestead
SH 003 Lake Tutchewop, Lake Charm
SH 005 Lake Boga and lunette, Lake Boga
SH 006.10 Kangaroo Lake and 3 lunettes, LakeCharm
SH 006.12 Lake Wandella and lunettes, Lake Charm
SH 006.7 Lake Bael Bael and lunette, Lake Charm
SH 013 Meering Lake (Meran Lake) andassociated lakes and lunettes, 13 km SWof Kerang
SH 014 Tragowel Swamp, Two Mile Swamp,Kerang
SH 015 Avoca River terminus area, Lalbert-KerangRoad, Kerang
SH 016 Tyntynder palaeolake, Tyntynder
SH 016.1 Tyntynder choke, Vinifera
SR 001 Gredgwin Ridge quarry, 7 km south ofBoort
SR 013.1 Tyrrell Marsh, Nineunook
SR 027 Loddon River distributary channel system,Serpentine to Kerang
SR 030 Parilla Sand exposure in Woollen Risesquarry, Narrewillock
SR 031 Barrakee Creek - Lake Marmal terminalsystem, Boort-Charlton road, NE ofCharlton
SR 032 Boral hornfels quarry, 5 km E of Charlton
TL 058 Hume Weir quarry and racing circuit, 2.5km SE of Bonegilla
TL 059 Yackandandah Granite and RubyviewGneiss exposures, Kookaburra Point, nearBonegilla
WN 002 Yackandandah and Mudgegonga granitesand metamorphic aureole- crescenticvalley and pinnacles, 11 km SE ofMyrtleford
WN 005 Mitta Junction red clay dune/ ridgelandform, Bonegilla
WN 026 Ordovician-Silurian Barnawartha GneissicGranodiorite and pegmatite dykes, HuonHill De Kerilleau Quarry, Wodonga
WN 063 Shepparton Formation DongawarraTerrace landform, Bonegilla
WN 073 Oxley Flats avulsion channel, Tea GardensCreek
WN 076 Buckland River and terraces, Buffalo River
WN 076.1 Buffalo River incision and Palaeozoicexposures, Osborne’s Bridge,
WN 077 Confluence Ovens and King rivers,Wangaratta
WN 078 Boorhaman East 1 bore, 21 km N ofWangaratta
WN 079 Confluence Ovens- Murray rivers, Brimin
WN 081 Golf Course Bend, 4.5 km S of Corowa
WN 082 Source-bordering dunes Cobram toCobram East
WN 082.1 Source-bordering dune, Dick's Bend, eastCobram
WN 084 Ovens River floodplain, NW of Wangaratta
WN 085 Yarrawonga Reach River Murray andfloodplain, Bruce's Bend.
WN 087 Upstream Ulupna Creek, junction RiverMurray, Eastern end of Ulupna Island (partof BD 006)
WN 088 Horseshoe Lagoon, Ulupna Island (see BD006)
LOCAL SIGNIFICANCE
BD 001.1 Mt. Hope Creek, 4 km S of Leitchville
BD 001.2 Bullock Creek palaeo-drainage, 5 km S ofLeitchville
BD 002.1 Happy Valley cliffs, Robinvale
BD 002.2 Euston Lock 15 cliffs, Robinvale
BD 002.3 Wemen cliffs, Wemen
BD 003.1 Tullah Creek, Double Crossing
BD 003.2 Barmah Borrow Pit, Barmah
SiteNumber
Site Nameand Location
SiteNumber
Site Nameand Location
River Red Gum Forests Investigation > 2006418
BD 003.6 Punt Paddock Lagoon
BD 004.1 Reedy Lagoon, Gunbower
BD 004.2 Sandpit, Near the Spence Bridge ScoutCamp
BD 006.1 Dead River Lagoon, Ulupna Island
BD 006.2 ‘The Junction’, the downstream end ofUlupna Creek, Ulupna Island
BD 008 Haysdale palaeolake, Haysdale
BD 011 Narrung Bend, Narrung
BN 040 Goulburn Weir, Nagambie
BN 044 Reedy Lake, Nagambie
BN 051 Barmah sand pit, Barmah
BN 052.1 Kanyapella lake sediment, Echuca
BN 053.2 Goulburn River and lake sediments,Echuca
BN 055 Tallygaroopna Prior Stream, Tallygaroopna
BN 056 Little Lake Kanyapella and lunette, ~13km E of Echuca
BN 056.1 Kanyapella prior stream, E of Echuca
BN 059 Goulburn River floodplain at McCoysBridge, ~ 4 km SW of Kotupna
BN 083 Goulburn River ancestral point bars, N ofShepparton
BN 084 Loch Garry, Bunbartha
BN 085 Ancestral River Point Bars, near Yambuna
MD 010 Karadoc Swamp and lunette, ~10 km eastof Yatpool
MD 013 Berribee Tank dry lake and lunette,Berribee Tank
MD 014 Horseshoe Bend and lagoon, Merbein
MD 016 Lake Hawthorn, Lake Ranfurley, Mildura
MD 017 Lake Iraak and lunette, Iraak
MD 023 Lake Cullulleraine, Lake Cullulleraine
SH 005.1 Round Lake and lunette, Lake Boga
SH 005.2 Long Lake and lunette, Lake Boga
SH 006.1 Pelican Lake and lunette, Lake Charm
SH 006.11 Third Lake and lunette, Lake Charm
SH 006.2 Reedy Lake and lunette, Lake Charm
SH 006.3 Lake Elizabeth and lunette, Lake Charm
SH 006.4 Duck Lake and lunette, Lake Charm
SH 006.5 Lake Cullen and lunette, Lake Charm
SH 006.6 The Marsh and lunette, Lake Charm
SH 006.8 Middle Lake and lunettes, Lake Charm
SH 006.9 Lake Charm and lunette, Lake Charm
SH 012 Foster Swamp, Nine-Mile Creek
SH 016.2 River bank exposure, Tyntynder Central
SH 017 Little Murray River, Near Lake Boga
SR 013 Avoca River mid-system floodout,Glenloth Road / Avoca River bridge
SR 026 Boort lake and lunette system, Boort
WN 013 Pliocene gravel beds exposure in railwaycutting, Bonegilla
WN 076.2 Pool-and-riffle stream forms at McGuffie'sBridge, Buffalo River
WN 082.2 Source-bordering dune landform, E ofCobram
WN 082.3 Source-bordering dune landform, ~5 km Sof Tocumwal
WN 083 King River lagoonal floodplain,Wangaratta
WN 086 Torgannah Lagoon, Mays Bridge
SiteNumber
Site Nameand Location
SiteNumber
Site Nameand Location
Discussion Paper 419
APPENDIX 13: Planning hierarchy for timberharvesting in Victorian state forests
COUPE PLANDetailed management requirements for coupes and
post harvesting monitoring, including:• all coupe boundaries
• location of all excluded areas• location of filter strips and buffers
• habitat tree requirements• trees for retention or tress for removal
• assessing stocking and need for regeneration works• post-harvest monitoring and regeneration
Independent environmental audit(Under the Environment Protection Act 1970)
Federal legislative and policy contextState
land and natural resource legislative and policy context
Code of Forest Practices for Timber Production
Management Procedures
Forest ManagementPlan
Timber Release PlanFive-year plan, for areas allocated to
VicForests, detailing wood production interms of areas scheduled for harvest, wood
volumes, product types, silviculturaloperations and associated roading
(for commercial timber production operations)
Wood Utilisation PlanAnnual plan, for land managed by DSE,detailing wood production in terms of
areas scheduled for harvest, woodvolumes, product types, silviculturaloperations and associated roading
(for all timber production operations)
River Red Gum Forests Investigation > 2006420
APPENDIX 14: Tree diameter distribution in Barmahforest
0.0
2.0
4.0
6.0
8.0
10.0
12.0
3545
5565
7585
95105
115
125
135
145
150+
1961
1995
Dia
met
er C
lass
(cm
)
Stems per Hectare
Sour
ce:
DN
RE (
2002
a)
Not
e: D
iam
eter
-cla
ss d
istr
ibut
ion
of m
erch
anta
ble
and
pote
ntia
lly m
erch
anta
ble
stem
s sh
owin
g th
e in
crea
se o
ver
time
of t
he n
umbe
r of
larg
er t
rees
in t
he f
ores
t an
d a
redu
ctio
n in
the
num
ber
of t
rees
in t
he s
mal
ler
size
-cla
sses
.
Discussion Paper 421
APPENDIX 15: River red gum log grades
Three grades of river red gum log are applied, determined by size (diameter and length) and the amount ofdefect. Where the proportion of defect exceeds the maximum allowable, the log is consigned to a lowergrade; the allowable proportion of defect increasing with the size of the log.
Red gum sawlog (RGSA)
Logs from which a higher proportion of the highest-quality timber can be expected.
Minimum dimensions: • 40 cm small-end diameter
• 2.1 m length.
Allowable defect:• 25% for RGSA with a centre diameter underbark less
than or equal to 45 cm.
• 30% for RGSA with a CDUB greater than 45 cm.
Allowable sweep:
The maximum allowable sweep is 1/5 of the centrediameter underbark, measured over a minimum 2.1 mof log length.
Red gum standard log (RGSB)
Logs that are expected to produce mostly landscape andutility grade timbers, although some railway sleepers andhigh-quality timber may be produced.
Minimum dimensions:• 30 cm small-end diameter
• 2.1 m length
Allowable defect:• 20% for RGSB with a centre diameter underbark less
than or equal to 35 cm
• 35% for RGSB with a centre diameter underbarkbetween 36 cm and 50 cm (inclusive)
• 50% for RGSB with a centre diameter underbarkgreater than 50 cm.
Allowable sweep:
The maximum allowable sweep is 1/5 of the centrediameter underbark, measured over a minimum 2.1 mof log length.
Red gum residual log (RGRL)
Logs that are not expected to produce sawn timber, butwill produce fuel wood. The purchaser, however, maybe able to extract some sawn material, depending onhow it is processed.
Minimum dimensions:• 10 cm small-end diameter
• 1.8 m length.
Allowable defect and sweep:
No minimum is specified for defect or sweep.
Source: DSE (2005f)
River Red Gum Forests Investigation > 2006422
APPENDIX 16: Timber productivity related to waterand forest management strategies
Present FloodFrequency
10 years out of 10
7–8 years out of 10
4–5 years out of 10
≤2 years out of 10
Timber Productivity (m3/ha/yr)
Scenario 1: current forestmanagement, stand
structure, environmentalprescriptions
Source: Maunsell Australia Pty Ltd (2003)
Timber productivity averaged for all river red gum site qualities (SQ I, SQ II & SQ III) in the Barmah Forest under various forest andwater management strategies.
Scenario 2: timber production asprimary aim but full cognisance of
active water management, silviculturetreatment and environmental
prescriptions and conservation areas
Scenario 3: timberproduction as primary aim
sawlogs
1.48
0.78
0.22
negligible to negative
otherproducts
1.10
0.57
0.16
sawlogs
2.12
1.35
0.43
0.04
other products
1.57
1.00
0.32
0.02
sawlogs
2.50
1.87
0.75
0.15
otherproducts
1.85
1.39
0.56
0.11
Explanatory notesValues are for timber productivity averaged across all sitequalities for each forest management scenario underpresent/predicted and managed flood frequencies.
Level of management input:1. Present forest management for timber production under
present stand structure, current environmental prescriptions,forest flooding and water management policy.
2. Forest management in zones specified for sustainabletimber production as a primary aim and in fullcognisance of:
• active water management in accordance with the Murray-Darling Basin Commission’s approved WaterManagement Strategy for the Barmah–Millewa Forest
• silvicultural treatment facilitating full stocking andsubsequent progressive selective thinning over therotation
• environmental prescriptions that meet the Code ofForest Practice and ensure a high level of flora andfauna conservation
• forest management takes account of significant areasset aside where environmental conservation is theprimary aim to the exclusion of timber production.
3. Forest management for sustainable timber production asthe primary aim.
Flood frequency:
10 years out of 10 – annual flooding.
Except in severe drought years, annual flooding may occuron small sections of forest, wetlands and low-lying plainsfed from major flood runners via on-river regulators. Theseareas flood at low river flows below Yarrawonga/Tocumwal(6500–15,000 ML/day) and are the areas generally mostprone to unseasonable flooding, particularly as a result ofrain rejections in summer and early autumn.
7–8 years out of 10 – pre-river regulation flood frequency(1891–1934)
Only on very rare occasions were there three consecutiveyears without a flood and few occasions, usually widelyspaced, when there were two consecutive years withoutsome flooding over 75–80% of the forest and wetlands.Consequently, the forest did not experience severecumulative drought stress. This situation is reflected inforest productivity described by Jacobs (1955).
4–5 years out of 10 - present flood frequency on 25–50%of the forest and wetlands as a result of actual Murray Riverflows below Yarrawonga/Tocumwal since 1955.
Cumulative drought stress results in a cessation of growthand recovery to pre-stressed levels takes several seasons.Flood duration, apart from 2–3 years each decade, is oftenless (up to 2 months) than that under natural (pre-regulation) flooding conditions. The shorter duration offlooding and season of flooding are considerably less thanoptimal for many biological processes including tree growthand overall vitality for flora and fauna (viz: moira grass,frogs and water bird breeding).
Equal to or less than 2 years out of 10 –present/predicted flood frequencies on up to 75% of theforest area as a consequence of MDBC and NSW andVictoria state land and water management policy decisions.
Tree vitality and growth are very significantly reduced.Cumulative drought stress is much more evident particularlyas the frequency of two or more consecutive years withouta flood is a regular occurrence. Biological activity, includingtree growth, is also more dependent on general seasonalconditions and duration of any flooding. As rainfalldecreases from east (700 mm per annum) to west ( lessthan 200 mm), the lack of flooding results in severecumulative drought stress as evidenced by recent surveys(Brett Lane & Associates Pty Ltd 2005).
Discussion Paper 423