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North East Coast3 North East Coast ....................................................... 2
3.1 Introduction ........................................................ 2
3.2 Key information .................................................. 3
3.3 Description of the region .................................... 4
3.3.1 Physiographic characteristics.................. 6
3.3.2 Elevation ................................................. 7
3.3.3 Slopes .................................................... 8
3.3.4 Soil types ................................................ 9
3.3.5 Land use ............................................. 11
3.3.6 Population distribution .......................... 12
3.3.7 Rainfall zones ....................................... 13
3.3.8 Rainfall deficit ....................................... 14
3.4 Landscape water flows ................................... 15
3.4.1 Rainfall .................................................. 16
3.4.2 Evapotranspiration ................................ 19
3.4.3 Landscape water yield ......................... 22
3.5 Surface water and groundwater ....................... 25
3.5.1 Rivers ................................................... 25
3.5.2 Streamflow volumes ............................. 27
3.5.3 Streamflow salinity ................................ 27
3.5.4 Flooding ............................................... 30
3.5.5 Storage systems ................................... 32
3.5.6 Wetlands ............................................. 34
3.5.7 Hydrogeology ....................................... 40
3.5.8 Watertable salinity ................................. 40
3.5.9 Groundwater management units ........... 40
3.5.10 Groundwater status of
selected aquifers .................................. 44
3.6 Water for cities and towns ................................ 48
3.6.1 Urban centres ....................................... 48
3.6.2 Sources of water supply ....................... 50
3.6.3 Southeast Queensland ......................... 50
3.7 Water for agriculture ......................................... 58
3.7.1 Soil moisture ......................................... 58
3.7.2 Irrigation water ...................................... 59
3.7.3 Irrigation areas ...................................... 59
3.7.4 Burdekin River Irrigation Area ................ 62
North East Coast
2 Australian Water Resources Assessment 2012
3 North East Coast3.1 Introduction
ThischapterexamineswaterresourcesintheNorthEastCoastregionin2011–12andoverrecentdecades.Itstartswithsummaryinformationonthestatusofwaterflows,storesanduse.Thisisfollowedbydescriptiveinformationincludingthephysiographiccharacteristics,soiltypes,population,landuseandclimateoftheregion.
Spatialandtemporalpatternsinlandscapewaterflowsarepresented,andsurfaceandgroundwaterresourcesexamined.Thechapterconcludeswithareviewofthewatersituationforurbancentresandirrigationareas.TheTechnicalSupplementdetailsthesourcesandmethodsusedindevelopingthediagramsandmaps.
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3.2 Keyinformation
Table3.1givesanoverviewofthekeycomponentsofthedataandinformationinthischapter.
Table 3.1 Key information on water flows, stores and use in the North East Coast region
Landscape water flows
Evapo-transpiration
Landscapewater yield
Rainfall
Regionaverage Differencefrom1911–2012long-termannual
mean
Decilerankingwithrespecttothe1911–2012record
1,041mm +22% 9th—aboveaverage
814mm +18% 9th—aboveaverage
223mm +42% 9th—aboveaverage
Streamflow (at selected gauges)
Annualtotalflow: Predominantlyaveragetoaboveaverageflowthroughouttheregion
Salinity: Annualmedianelectricalconductivitypredominantlybelow1,000μS/cmthroughouttheregion
Flooding: Majorfloodsinmanypartsoftheregion
Surface water storage (comprising about 92% of the region’s total capacity of all major storages)
Totalaccessiblecapacity
30June2012 30June2011 Change
accessiblevolume
%oftotalcapacity
accessiblevolume
%oftotalcapacity
accessiblevolume
%oftotalcapacity
9,516GL 9,301GL 98% 9,135GL 96% +166GL +2%
Wetlands inflow patterns (for selected wetlands)
BowlingGreenBay: Averageflowsthroughouttheyear,butverymuchaboveaverageflowsinMarch
FitzroyRiverfloodplain: VerymuchaboveaverageflowsduringFebruaryandMarch2012
GreatSandyStrait: VerymuchaboveaverageflowsovertheJanuarytoMarch2012period
MoretonBay: VerymuchaboveaverageflowsinJanuaryandMarch2012
Groundwater (in selected aquifers)
Levels: Predominantlyrisingtrendsintheselectedwatertableaquifersoverthe2007–08to2011–12period
Salinity: Scatteredareasofsalinegroundwater(≥3,000mg/L)throughouttheregion
Urban water use (Brisbane and Gold Coast)
Totalusein2011–12 Totalusein2010–11 Change Restrictions
176GL 180GL –4GL(–2%) PermanentWaterConservationMeasures
Annual mean soil moisture (model estimates)
Spatialpatterns: Predominantlyaboveaverageannualmeansoilmoisturewithlargeinlandareasofverymuchaboveaveragesoilmoisture
Temporalpatternsinregionalaverage:
Aboveaveragetoverymuchaboveaveragesoilmoisturethroughouttheyear
North East Coast
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Tropical landscape with tree ferns and rain forest, Queensland Tablelands | Dirk Ercken, Dreamstime
3.3 Descriptionoftheregion
TheNorthEastCoastregionisa451,000km²areainQueenslandsurroundedbytheGreatDividingRangeinthewest,theCoralSeaintheeast,TorresStraitinthenorthandtheQueensland–NewSouthWalesborderinthesouth.
Riverbasinsintheregionvaryinsizefrom400–143,000km².MajorriverbasinsincludetheBurdekin,Fitzroy,Burnett,Brisbane,MaryandJohnstone,Mulgrave,Barron,Daintree,BloomfieldandNormanby.
ThelargestriverbasinsaretheBurdekinandtheFitzroy(Figure3.1),whichtogethercomprise64%oftheGreatBarrierReefcatchmentareaandimpactupontheoffshorereef’secosystemsthroughdischargesofsedimentsandnutrients.
TheregionincludessomeofthemosttopographicallydiverseterraininAustralia,includinghighaltitudesassociatedwithcoastalrangesandtablelandsandaretreatingescarpmentwithoutcropsonthecoastalalluvialplains.ThehighestmountainsinQueenslandandthehighestrainfallareasinAustraliaarenorthofInnisfail.Subsections3.3.1–3.3.4givemoredetailonthephysicalcharacteristicsoftheregion.
Withapopulationinexcessof4millionpeopletheregionishometojustover19%ofallAustraliansand92%ofallQueenslandresidents(AustralianBureauofStatistics[ABS]2011b).MajorpopulationcentreswithintheregionincludeBrisbane,theGold
CoastandtheSunshineCoastaswellastheregionalcentresofHerveyBay,Bundaberg,Gladstone,Rockhampton,Mackay,TownsvilleandCairns(Figure3.1).Furtherdiscussionoftheregion’spopulationdistributionandurbancentrescanbefoundinsubsection3.3.6andsection3.6respectively.
Mostoftheregionoutsidetheurbancentresisusedforgrazing.Inthenorththisoccursonnativerangelandswithfewermanagementinputsandpastureimprovementthanoccurinthesouthernriverbasins.Drylandandirrigatedagricultureaccountsforapproximately0.4%ofthelanduseofthearea.Areasofintensivelandusesuchasinurbanareasaccountfor0.2%ofthearea.Section3.7hasmoreinformationonagriculturalactivities.
Theregion’sclimateissubtropicaltotropicalwithhot,wetsummersandcooler,drywinters.Themonsoonalsummerrainfallismorepredictableinthenorththaninthesouth.Subsections3.3.7and3.3.8provideinformationontherainfallpatternsacrosstheregion.
Alargeareaofoutcroppingfracturedbasementrockdominatesthehydrogeologyoftheregion.Thegroundwatersystemsinfracturedrocktypicallyofferrestrictedlow-volumegroundwaterresources.Incontrast,largegroundwaterresourcesarelocalisedinalluvialvalleysystemsandcoastalsanddeposits.Thestatusofsurfacewaterandgroundwaterispresentedinsection3.5.
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Figure 3.1 The North East Coast region
North East Coast
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Figure 3.2 Physiographic provinces of the North East Coast region
3.3.1 Physiographiccharacteristics
Figure3.2isaphysiographicmapindicatingareaswithsimilarlandformevolutionaryhistories(Painetal.2011).Thesearerelatedtosimilargeologyandclimaticimpactsdefiningtheextentoferosionprocesses.
Theareashavedistinctphysicalcharacteristicsthatinfluencehydrologicalprocesses.
TheNorthEastCoastregionhasfourphysiographicprovinces.Thesearedescribedinthefollowinglistwiththeproportionoftheregiontheycovershowninbrackets.
• BurdekinUplands(21%):mixtureofhills,plateausandplainswiththehighlandschieflyongraniteandmetamorphicrockswithsomeyoungbasalticplateaus;
• FitzroyUplands(43%):mixtureofhills,plateausandplainswithhighlandsofsandstone,basalt,graniteandmetamorphicrocks;
• NewEngland–MoretonUplands(23%):sandstoneandigneoushighlandswithsedimentaryandmetamorphiclowlands;and
• PeninsularUplands(13%):mixtureofhills,plateausandplainswithhighlandsofsandstoneaswellasvolcanic,graniticandmetamorphicrocks.
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Figure 3.3 Ground surface elevations in the North East Coast region
3.3.2 Elevation
Figure3.3presentsgroundsurfaceelevationsintheNorthEastCoastregion.InformationwasobtainedfromtheGeoscienceAustraliawebsite(www.ga.gov.au/topographic-mapping/digital-elevation-data.html).
TheNorthEastCoastregionhasaverydiversetopographyandincludeshighaltitudesassociatedwithcoastalrangesandtablelands,andaretreatingescarpmentwithresidualoutliersonthecoastalalluvialplains.
TheregioncontainsmanymountainsfrompartoftheGreatDividingRange.Italsocontainslargeplateausandlow-lyingcoastalareas.
ThehighestmountainsintheregioncanbefoundsouthofCairns,withpeaksreachingaltitudesof1,600mabovesealevel.
Furthersouth,thepeaksofvariouscoastalmountainrangesformwaterdividesbetweenthesmallercoastalriverbasinsandthefewinlandriverbasins.
ThecrestoftheGreatDividingRangeformsthewesternborderoftheregion.Altitudesonthisboundaryvaryfromlessthan200mtomorethan1,200m.
North East Coast
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Figure 3.4 Surface slopes in the North East Coast region
3.3.3 Slopes
Table3.2summarisestheproportionsofslopeclassesfortheregionwhileFigure3.4showsthespatialdistributionofthesurfaceslopes.Areaswithsteepslopesprovidehigherrun-offgeneratingpotentialthanflatareas.TheNorthEastCoastregionhashighslopevariabilitywithlargerexpansesofsteeperslopesthanmostotherpartsofAustralia.Theslopeswerederivedfromtheelevationinformationusedintheprevioussection.
Table 3.2 Proportions of slope classes for the region
Slopeclass(%) 0–0.5 0.5–1 1–5 >5
Proportionofregion(%) 19.0 16.4 43.8 20.8
Slopesareparticularlysteepalongthecoastalescarpment.Riversinboththenorthandsouthoftheregionoftenhaveflashfloodingunderhighintensityrainfall.TheJanuary2011floodintheBrisbaneRiverandMarch2012floodintheHaughtonRiverareexamplesofsuchevents.
Furtherinland,slopesarerathergentle(Figure3.4).Atsomelocationslargelakeshaveformed,bothnaturallyaswellasthroughtheconstructionofdamsforwatersupply.
Intheflattercoastalareasmanylargerriversformextensivefloodplains.Theseareoftenidentifiedaswetlandareasofconservationsignificance.
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Figure 3.5 Soil types in the North East Coast region
3.3.4 Soiltypes
Soilsplayanimportantroleinthehydrologicalcyclebydistributingwaterthatreachestheground.Watercanbetransportedtoriversandlakesviathesoilsurfaceasrun-offorenterthesoilandprovidewaterforplantgrowthaswellascontributingtogroundwaterrecharge.
Thenatureofthesehydrologicalpathwaysandthesuitabilityofthesoilsforagriculturalpurposesareinfluencedbysoiltypesandtheircharacteristics.
SoiltypeinformationwasobtainedfromtheAustralianSoilResourceSystemwebsite(www.asris.csiro.au).
Figures3.5–3.6showthedistributionofsoiltypeswithintheNorthEastCoastregion.About80%ofthelandsurfaceiscoveredbyfivesoiltypes,namelysodosols,kandosols,kertosols,tenosolsandchromosols.Withtheexceptionofvertosols,thesesoilsarewidespreadacrosstheregion,arelowinfertilityandaremostlyusedforgrazing,drylandagriculture,horticultureandforestry.
Soiltypeswithcleartexturecontrastsinthisregionaresodosolsandchromosols.Thesesoilscanhaveapropensitytobecomewaterlogged.
Sodosolshaveimpermeable,sodicsubsoilduetoelevatedsodiumconcentrations.Theyaresusceptibletodrylandsalinityaswellaserosionifvegetationisremoved.Chromosolsalsohaveanimpermeablesubsoilthatisnotstronglysodicoracidic.
Vertosols,onlydistributedthroughthemiddlepartoftheregion,aresoilswithahighclaycontent.Thesearebrown,greyorblacksoilswithlargewater-holdingcapacity,butcandeveloplargecrackswhendrying.Theyarehighlyfertileandself-mulching.
Soilswithlittleornochangesinsoiltextureintheregionarekandosolsandtenosols.Kandosolsareusuallyred,yellowandgreymassiveearthysoilswithalowwater-holdingcapacity;however,awiderangeofcropscanbegrownonthemwhererainfallishighorirrigationisavailable.Similarly,tenosolshaveaweakprofiledevelopment.Theiragriculturaluseislimitedduetotheirlowwater-holdingcapacityandtheiroftenshalloworstonymaterial.Soiltypeswithsmallareacoverageintheregionarerudosols,dermosols,ferrosols,hydrosols,kurosols,andpodosols(1–6%).
North East Coast
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Figure 3.6 Soil type distribution in the North East Coast region
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Figure 3.7 Land use distribution in the North East Coast
Figure 3.8 Land use in the North East Coast region
3.3.5 Landuse
MostoftheNorthEastCoastregionisusedforgrazing.Inthenorththisoccursonnativerangelandswithfewermanagementinputsandpastureimprovementsthaninsouthernriverbasins.
Figure3.7presentslanduseintheregion.Drylandandirrigatedagricultureaccountforapproximately
4%oflanduse,whileintensivelandusessuchasthatofurbanareasaccountfor1%oftheregion(informationfromdata.daff.gov.au/anrdl/metadata_files/pa_luav4g9abl07811a00.xml).
AsseeninFigure3.8natureconservationareas,suchasthoseonCapeYorkareanimportantpartofthelandcoverinthenorth,wherethelargestareasofunspoiltrainforestsinAustraliacanbefound.
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Figure 3.9 Population density and distribution in the North East Coast region
3.3.6 Populationdistribution
Figure3.9showsthepopulationdensityanddistributionintheNorthEastCoastregion.Urbanareasaccountforlessthan1%ofthetotallandareaofthisregion.SouthEastQueensland,whichincludesBrisbane,GoldCoast,andtheSunshineCoast,isthemostheavilyurbanisedandpopulatedareaandconstitutesover65%oftheregion'stotalpopulation.
Agriculture,fishing,miningandtourismarethemajordriversforthemanypopulationcentresinthe
northandlargelyalongthecoastalfringes,estuariesandalluvialplainsoftheregion.CoalminingintheBowenbasininthecentraleasternpartoftheregionhasbeenamajordriverformanysmallinlandtownsaswellasthelargercoastalregionalcitiesthatlieonoradjacenttoitseasternboundary(Gladstone,RockhamptonandMackay).
Furthernorth,thecoastalcitiesofTownsvilleandCairnsprovidethefocalpointsforthemajorpopulationconcentrationsoftheregion’snorthernpopulation.
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Figure 3.10 Rainfall zones in the North East Coast region
3.3.7 Rainfallzones
Figure3.10representsmedianrainfallzonesintheNorthEastCoastregion,whichhasasubtropicaltotropicalclimateandreceivesmostofitsrainfallinsummer.Medianrainfallexceeds350mmthroughouttheregion.
Thenorthernhalfoftheregionreceivessummerdominantrainfallwithamarkedwetsummeranddrywinteraswellmedianrainfalldecreasingwestwards
fromover1,200mmperannumalongthecoasttobetween350mmand650mminland.
Thesouthernpartoftheregionhasasummerrainfallseason(wetsummerandlowwinterrainfall)withlocalisedareasalongthecoastnorthofBrisbanehavingaverageannualrainfallsofover1,200mm.Formoreinformationonthisandotherclimateclassifications,visittheBureauofMeteorology's(theBureau's)climatewebsite:www.bom.gov.au/jsp/ncc/climate_averages/climate-classifications
North East Coast
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Figure 3.11 Rainfall deficit distribution in the North East Coast region
3.3.8 Rainfalldeficit
Therainfalldeficitindicator,thatis,rainfallminuspotentialevapotranspiration,givesageneralimpressionaboutwhichpartsoftheregionarelikelytoexperiencemoisturedeficitsovertheperiodofayear.TheNorthEastCoasthasadistinctrainfalldeficitpattern.
AsshowninFigure3.11,seriousdeficitscanbeexpectedinlargepartsoftheinlandareaswherethemajorlanduseisgrazing.
Alongthecoast,someareasexperienceabundantwaterovertheyear.RiverscarrythiswatertotheCoralSeaandareanimportantsourceoffreshwaterformanyestuarinewetlands.
Formoreinformationonrainfallandevapotranspiration,seetheBureau’smapsofaverageconditions:www.bom.gov.au/climate/averages/maps.shtml
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Figure 3.12 Landscape water flows in 2011–12 compared with the long-term record (July 1911– June 2012) for the North East Coast region
3.4 Landscapewaterflows
Thissectionpresentsanalysesofthespatialandtemporalvariationoflandscapewaterflows(rainfall,evapotranspirationandlandscapewateryield)acrosstheNorthEastCoastregionin2011–12.Nationalrainfallgridsweregeneratedusingdatafromanetworkofpersistent,high-qualityrainfallstationsmanagedbytheBureau.
Figure3.12showstheregionhasahighlyseasonalrainfallpatternwithawetperiodfromDecember–MarchandaparticularlydryperiodfromJuly–September.Evapotranspirationinthedryperiodgenerallyexceedsrainfall.Afterthewetperiodthesoilsnormallycontainmoisturethatisavailableforevapotranspiration.
Themonthlylandscapewateryieldhistoryfortheregionshowsastablepatternofverylowyieldinthedryperiod.Itgraduallyincreasesduringsummermonthsandsubsidesduringautumn.
The2011–12yearwasrelativelywet,particularlybetweenDecember2011andMarch2012,whenrainfallwasmuchgreaterthanthehistoricmedian.AnactivemonsooninthenorthoftheregioncontributedtoparticularlyhighrainfalltotalsforMarch2012.
Withwetsoilconditionspresentatthestartoftheyear,evapotranspirationrateswerehigherthanrainfallratesforthefirstfivemonthsof2011–12.WiththeexceptionofJanuary2012,evapotranspirationratesremainedabovethe75thpercentilefortherestoftheyearasaresultofthehigherthanusualrainfallinmostpartsoftheregion.
Thelandscapewateryieldfor2011–12closelyfollowedthehistoricpatternwiththeexceptionofMarch2012,whenveryhighrainfallgeneratedamuchhigherlandscapewateryieldthanthehistoricaverage.
North East Coast
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Figure 3.13 Spatial distribution of (a) annual rainfall in 2011–12, and (b) their decile rankings over the 1911–2012 period for the North East Coast region
3.4.1 Rainfall
RainfallfortheNorthEastCoastregionfor2011–12isestimatedtobe1,041mm.Thisis22%abovetheregion’slong-termaverage(July1911–June2012)of853mm.Figure3.13ashowsthatthehighestrainfalloccurredalongthecoastalareaswithannualtotalsexceeding2,400mminmanyareasfor2011–12.Themajorityoftheinlandareashadrainfallrangingfrom600–900mmfor2011–12.However,insomeareasalongthewesternborder,rainfallexceeded900mm.
Rainfalldecilesfor2011–12indicateaveragetoaboveaveragerainfallfortheentireregion(Figure3.13b).Mostoftheinlandpartsoftheregionreceivedaboveaveragerainfallwithsomepartsinthewestreceivingverymuchaboveaveragerainfall.ThesoutherncoastalareanorthofBrisbane,includingFraserIsland,alsoreceivedverymuchaboveaveragerainfall.
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Figure 3.14 Time-series of (a) annual rainfall, and (b) five-year retrospective moving averages for the summer (November–April) and winter (May–October) periods for the North East Coast region
Rainfall variability in the recent past
Figure3.14ashowsannualrainfallfortheregionfromJuly1980onwards.Overthis32-yearperiodtheannualaveragewas851mm,varyingfrom551mm(1992–93)to1,586mm(2010–11).Temporalvariabilityandseasonalpatternssince1980arepresentedinFigure3.14b.Thegraphsindicatethepresenceofcyclicalpatternstypicaloftheregion’sannualrainfalloverthese32years,whichare
particularlynoticeableinthesummerperiod.ThispatterniscloselylinkedtotheoccurrenceofElNiñoandLaNiñaperiodsandcorrelateswellwiththeSouthernOscillationIndex(seeNationalOverviewchapter).
AstrongLaNiñaperiodtypicallydeliversaboveaveragerainfalltothisregion,whichisclearlyhighlightedbytherecent2010–11LaNiñaperiod.
North East Coast
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Figure 3.15 Spatial distribution of (a) trends in annual rainfall from 1980– 2012, and (b) their statistical significance at 90% (weak) and 95% (strong) confidence levels for the North East Coast region
Recent trends in rainfall
Figure3.15apresentsthespatialdistributionofthetrendsinannualrainfallforJuly1980–June2012.Thesearederivedfromlinearregressionanalysesonthetime-seriesofeachmodelgridcell.ThestatisticalsignificanceofthetrendsisprovidedinFigure3.15b.
Figure3.15ashowsthatsince1980astrongincreaseinrainfallhasoccurredinlargepartsoftheregion
particularlytowardsthenorth.Thesetrendsarestronglysignificantin22%oftheregion(Figure3.15b).
ThetrendsarelargelyaresultofthecyclicrainfallpatternshowninFigure3.14andtheparticularlyhighrainfallofthepasttwoyears.
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Figure 3.16 Spatial distribution of (a) modelled annual evapotranspiration in 2011–12, and (b) their decile rankings over the 1911–2012 period for the North East Coast region
3.4.2 Evapotranspiration
ModelledannualevapotranspirationfortheNorthEastCoastregionfor2011–12isestimatedtobe814mm.Thisis18%abovetheregion’slong-term(July1911–June2012)averageof692mm.
Figure3.16ashowsthatspatialdistributionofannualevapotranspirationin2011–12issimilartothatofrainfallFigure3.13a.Evapotranspirationratesarehighestalongthecoastwithannualtotals
exceeding1,200mminsomeareasfor2011–12.Evapotranspirationaveragedaround750mmfortheinlandpartsoftheregion.
Figure3.16bshowsthatevapotranspirationdecilesfor2011–12indicateaboveaverageorverymuchaboveaveragetotalsacrossmostoftheregion.Thiscoincideswiththeverymuchaboveaveragerainfallobservedlargelyalongthewesternborder(Figure3.15b).Mostcoastalareasareestimatedtohavehadaverageevapotranspiration.
North East Coast
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Figure 3.17 Time-series of (a) annual evapotranspiration, and (b) five-year retrospective moving averages for the summer (November–April) and winter (May–October) periods for the North East Coast region
Evapotranspiration variability in the recent past
Figure3.17ashowsannualevapotranspirationfortheregionfromJuly1980onwards.Overthis32-yearperiodtheannualevapotranspirationaveragewas682mm,varyingfrom477mm(1992–93)to1,054mm(2010–11).Temporalvariabilityandseasonalpatternssince1980arepresentedinFigure3.17b.
Summerperiodsshowedconsistentlyhigherevapotranspirationratesthanthewinterperiod.
Thehighertemperaturesandthehigherrainfallamountsduringtheseperiodscontributetothis.Comparedwiththeseasonalrainfall(Figure3.14b),thecyclicaltime-seriesofseasonalevapotranspirationislesspronounced(Figure3.17b).
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Figure 3.18 Spatial distribution of (a) trends in annual evapotranspiration from 1980–2012, and (b) their statistical significance at 90% (weak) and 95% (strong) confidence levels for the North East Coast region
Recent trends in evapotranspiration
Figure3.18apresentsthespatialdistributionofthetrendsinmodelledannualevapotranspirationfor1980–2012.Thesearederivedfromlinearregressionanalysesonthetime-seriesofeachmodelgridcell.ThestatisticalsignificanceofthetrendsisprovidedinFigure3.18b.
Figure3.18ashowsthatsince1980trendsaremostlyrisinginthecentralnorthernpartoftheregion.Inthesouth,thetrendsaremoreneutraltoweaklyfalling.
AsshowninFigure3.18b,thetrendsaregenerallyonlystatisticallysignificantinsomeinlandpartsoftheregion.Inthesouthoftheregionthefallingtrendshavenostatisticalsignificance.
Asevapotranspirationisdrivenbytheavailabilityofmoisture,thetrendsarerelatedtothecyclicpatternintherainfallshowninFigure3.14andtheparticularlyhighrainfallof2010–11and2011–12.
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Figure 3.19 Spatial distribution of (a) modelled annual landscape water yield in 2011–12, and (b) their decile rankings over the 1911–2012 period for the North East Coast region
3.4.3 Landscapewateryield
ModelledlandscapewateryieldfortheNorthEastCoastregionfor2011–12isestimatedtobe223mm.Thisis42%abovetheregion’slong-term(July1911–June2012)averageof157mm.
Figure3.19ashowsthespatialdistributionoflandscapewateryieldfor2011–12,whichissimilartothatshowninFigure3.14a,annualrainfalldistribution.Thisisaresultofrainfallintensityandvolumebeingthedominantdriversforgeneratinglandscapewateryield.
Thehighestlandscapewateryieldsin2011–12areobservedinareasalongthemid-northandsouthcoast,locallyexceeding1,200mm.Fortherestoftheregion,thelandscapewateryielddidnotexceed400mm.
Figure3.19bisthedecile-rankingmapfor2011–12andshowsaveragetoverymuchaboveaveragelandscapewateryields.
Aboveaveragewateryieldsarefoundacrossmuchoftheinlandareas,withverymuchaboveaverageyieldsalongthewesternborder,aswellasalongthesoutherncoast.
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Figure 3.20 Time-series of (a) annual landscape water yield, and (b) five-year retrospective moving averages for the summer (November–April) and winter (May–October) periods for the North East Coast region
Landscape water yield variability in the recent past
Figure3.20ashowsannuallandscapewateryieldfortheNorthEastCoastregionfromJuly1980onwards.Overthis32-yearperiod,annuallandscapewateryieldwas162mm,varyingfrom58mm(2001–02)to481mm(2010–11).
Temporalvariabilityandseasonalpatternssince1980arepresentedinFigure3.20b.
AsshowninFigure3.20b,landscapewateryieldisconsistentlyhigherduringthesummerperiodcomparedtothewinterperiod.
Thesummerperiod’saveragealsoexhibitsagreaterinter-annualandcyclicalvariabilitydrivenbytheregion’srainfalldynamics.
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Figure 3.21 Spatial distribution of (a) trends in annual landscape water yield from 1980– 2012, and (b) their statistical significance at 90% (weak) and 95% (strong) confidence levels for the North East Coast region
Recent trends in landscape water yield
Figure3.21apresentsthespatialdistributionofthetrendsinmodelledannuallandscapewateryieldfor1980–2012.Thesearederivedfromlinearregressionanalysesonthetime-seriesofeachmodelgridcell.ThestatisticalsignificanceofthetrendsisprovidedinFigure3.21b.
Figure3.21ashowsthatsince1980risingtrendsoccuralongthecoast,particularlyinareaswhere
annualrainfallnormallyexceeds1,200mm.Intheinlandpartoftheregion,weakerrisingtrendsoccur.
Figure3.21bshowsstronglysignificanttrendsoccurmainlyintheinlandpartsoftheregion.Thehighlandscapewateryieldsbetween2007–08and2011–12(Figure3.20a)contributedappreciablytotheserisingtrends.
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The Fitzroy River, east of Rockhampton | John Casey, Dreamstime
3.5 Surfacewaterandgroundwater
ThissectionexaminessurfacewaterandgroundwaterresourcesintheNorthEastCoastregionin2011–12.Ananalysisofrivers,wetlandsandwaterstoragesarediscussedtoillustratethestateoftheregion’ssurfacewaterresources.Theregion’swatertableaquifersandsalinityaredescribedandthegroundwaterstatusisillustratedbyshowingchangesingroundwaterlevelsatselectedsites.
3.5.1 Rivers
AlltheriversinthisregiondraintotheCoralSeawithmanyoftherivershavingoutflowsthatcanimpactontheGreatBarrierReef.
Figure3.22showsthe45riverbasinsintheregion,whichvaryinsizefrom400–143,000km2.
Manyoftherivershavehighsummerflowswithrelativelylongperiodsofloworzeroflowsinwinter,especiallytothemid-northoftheregion.Streamsinthesoutheastoftheregiongenerallyflowallyearroundbutstillshowdistinctseasonalvariation.
TheBurdekinandtheFitzroyriversareamongstthelargestAustralianriversintermsoftheirtotalflowvolumes.TheBurdekinRiverisasouth-flowingephemeralriverwhichoftendriestojustaseriesofdisconnectedwaterholes,andrunsover300kmbeforeturningeasttothesea.
ThelowerreachesoftheFitzroyRiverareperennialbutalargeproportionofthetributariesinthecatchmentareephemeral.
ThelowerBurdekin,NogoaandMackenzieriversrunthroughhighlymodifiedcatchments.TheBurnettRiverbasinisthethirdlargestbasinintheregion.
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Figure 3.22 Rivers and catchments in the North East Coast region
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3.5.2 Streamflowvolumes
Figure3.23presentsananalysisofflowsat46monitoringsitesduring2011–12relativetoannualflowsfortheperiodfromJuly1980–July2012.Monitoringsiteswithrelativelylongrecordsacross20geographicallyrepresentativeriverswereselected(seeTechnicalSupplementfordetails).
Theannualflowsfor2011–12arecolour-codedaccordingtothedecilerankateachsiteoverthe1980–2012period.TheflowsgenerallyreflectthemostlyaveragetoaboveaveragemodelledlandscapewateryieldresultsshowninFigure3.19b.
Highrun-off,generatedintheupstreamreachesoftherivers,causedaboveaveragetoverymuchaboveaverageflowsinmanyriversinthecentralpartoftheNorthEastCoastregion.
Verymuchaboveaverageflowswereobservedatfivemonitoringsiteslocatedonriversinthewest:thenorthJohnstoneRiverinthecentralnorthandtheGregoryRiverinthesoutheastoftheregion.
Aboveaveragetotalflowswererecordedat23monitoringsites.Theseweremainlylocatedontheriverstothesouth,somecentrallylocatedrivers,andinsomeriverbasinstothecentralnorthoftheregion.
Averageflowsoccurredat17sitesintheregionthatwereontheriversinthesouthwestandfarsouthoftheregion,andamongriverbasinsinthecentralnorthandfarnorthoftheregion.
Therewasonlyonebelowaverageflowrecordedforthe46monitoringsitesexaminedacrosstheregion.ThiswasontheNormanbyRiverinthenorth.
AsshowninFigure3.23,decilesinthesummer(November2011–April2012)wereverysimilartototalannualflowsfor2011–12.Thisisnotsurprisinggiventhatthegreatestvolumeofflowsintheregion,particularlyinthecentralnorth,occurredoverthesummermonths.Thereareafewmonitoringsitesthatdidnotshowthispattern,suchastherelativelylowflowsobservedinthesummerperiodontheStewartRiverinthefarnorthoftheregion.
3.5.3 Streamflowsalinity
Figure3.24showsananalysisofstreamflowsalinityfor2011–12at79monitoringsitesthroughouttheNorthEastCoastregion.Monitoringsiteswithatleastafive-yeardatarecordwereselectedforanalysis.Theresultsareshownaselectricalconductivity(EC,μS/cm).ThisisacommonlyusedsurrogateforthemeasurementofwatersalinityinAustralia.StandardEClevelsfordifferentapplications,suchasfordrinkingwaterortypesofirrigationareprovidedintheTechnicalSupplement.ThemedianannualECvaluesareshownascolouredcircles.ThecirclesizedepictsthevariabilityinannualEC,shownasthecoefficientofvariation(CV),beingthestandarddeviationdividedbythemean.
ThemedianECvaluesformostoftheselectedmonitoringsitesfallintherange0–1,000μS/cm,anamountthatissuitableformostirrigationuses.SomeresultsforsmallriversandcreeksintheFitzroyRiverbasinandtheLoganRiverbasinfalloutsidethisrange(seeFigure3.24).Ofthe79monitoringsites,53%hadmedianECvaluesbelow500μS/cmand33%werebetween500–1,000μS/cm.Only14%ofthemonitoringsiteshadamedianECabove1,500μS/cm.
Riverswithhigher(>1,000μS/cm)mediansalinitiesalloccurinthesouthernhalfoftheregion.Theyaretypicallyassociatedwithlowannualflows.Medianstreamsalinitywasabove2,000μS/cmatthreeofthe79monitoringsites.ThesewerefromonemonitoringsiteontheDeeRiverthatisatributaryoftheDawsonRiver,andtwocreeksintheFitzroyRiverbasin.HighsalinityintheDeeRiverisinfluencedbythedecommissionedMountMorgangoldmine,fromwhichleachatesentertheDeeRiver.
ThesalinityCVvaluesvarywidelyacrosstheNorthEastCoastregion.TheCVishighatafewmonitoringsitesinthesouthandnorthwest,andintheDeeRiverintheeast.Incontrast,theCVisrelativelylowformostriversinthesouth,northeast,andcentralpartsoftheregion.TheCVofsalinityistypicallyrelatedtothevariabilityinannualflowatthemonitoringsite.
North East Coast
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Figure 3.23 Average annual and summer period flow volumes of selected gauges for 2011–12 and their decile rankings over the 1980–2012 period in the North East Coast region
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Figure 3.24 Salinity as electrical conductivity and its associated coefficient of variation for 2011–12 in the North East Coast region
North East Coast
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Ofthe79monitoringsites,27%hadacoefficientofvariationbelow20%;67%ofthesiteshadCVbetween20%and60%;andonly6%ofthesiteshadCVabove60%.ThesewereontheSuttorRiverintheBurdekinRiverbasininthecentreoftheregion,DeeRiverinthecentraleastandPurgaCreekintheBrisbaneRiverbasininthesouthoftheregion.
Streamsalinityvariationwasabove80%atoneofthe79monitoringsites.ThiswasontheSuttorRiverintheBurdekinRiverbasininthecentreoftheregion.
3.5.4 Flooding
FloodsintheNorthEastCoastregionaremainlycausedbytworainfalltypes.Thesearelocalisedhighintensityrainfall(forexample,thunderstorms)orprolongedperiodsofrainfall(forexample,frontalrainfall,monsoon,tropicalstorms).Whilethefirstrainfalltypeoftenresultsinlocalisedflashflooding,theprolongedrainfallcancausesustainedfloodsoverlargeareas.
Theregionhasaseasonalpatternofrainfall,withmostrainfalloccurringinsummer,inwhichbothrainfalltypesoccurfrequently.
Figure3.25showsthelocationswheretheBureaumonitorsriverlevelsintheregionaspartofitsfloodforecastingservices.Thehighestfloodlevels
experiencedduring2011–12areshownintermsofthefloodclassificationlevelsestablishedinconsultationwithemergencymanagementandlocalagenciestodescribefloodimpactsateachlocation(seeTechnicalSupplement).
Alargenumberofmajorfloodsoccurredin2011–12(Figure3.25).InlargeriverstothecentralwestoftheregionmajorfloodswereobservedduringJanuaryandFebruary2012.TheprolongedrainfallinthelastweekofJanuaryresultedinhighwaterlevelsinthesoutherntributariesoftheBurdekinRiverandmostoftheupstreamtributariesoftheFitzroyRiver.
TheprolongedJanuaryrainfallalsoimpactedtheriversaroundBrisbaneinthesouthernpartoftheregion.AlthoughnotassevereastheJanuary2011floods,someareasintheBrisbaneandLoganriverbasinsexperiencedmajorflooding;howevertheimpactsinsuburbanBrisbaneandsurroundswerelessseverewithonlyminortomoderateflooding.
InMarch,themonsooninthenorthernpartoftheregiondeliveredlargeamountsofrainfalltothecoastalareasofnorthQueensland.Majorfloodingoccurredinmanysmallrivers.FloodingalsooccurredfurthersouthinsomeriversbetweenBrisbaneandRockhampton,whererainfallforthismonthwasupto400mm.
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Figure 3.25 Flood occurrence in 2011–12 for the North East Coast region, with each dot representing a river level monitoring station and the colour of the dot representing the highest flood class measured
North East Coast
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Table 3.3 Major public storage systems in the region as identified in the Bureau’s water storage website (August 2012), with ‘non-allocated’ accounting for the storages not allocated to a particular system
System name System type System capacity Accessible volume at 30 June 2011 Accessible volume 30 June 2012
Brisbane urban 2,220GL 1,882GL—85% 2,093GL—94%
BurdekinHaughton rural 1,868GL 1,866GL—100% 1,868GL—100%
NagoaMackenzie rural 1,305GL 1,296GL—99% 1,297GL—99%
Bundaberg rural 909GL 908GL—100% 906GL—100%
Proserpine rural 490GL 490GL—100% 480GL—100%
MareebaDimbulah rural 438GL 433GL—99% 437GL—99%
BoyneTarong rural 196GL 195GL—100% 196GL—100%
UpperBurnett rural 187GL 182GL—97% 182GL—97%
Callide rural 148GL 140GL—95% 105GL—71%
Pioneer rural 147GL 146GL—99% 146GL—99%
BarkerBarambah rural 134GL 134GL—100% 134GL—100%
BowenBroken rural 116GL 115GL—99% 116GL—100%
ThreeMoonCreek rural 88GL 88GL—100% 88GL—100%
Warrillvalley rural 86GL 83GL—97% 82GL—95%
Eton rural 62GL 61GL—98% 62GL—100%
Maryriver rural 56GL 56GL—100% 56GL—100%
Loganriver rural 44GL 44GL—100% 44GL—100%
Non-allocated — 1,022GL 1,016GL—99% 1,009GL—99%
Total 9,516 GL 9,135 GL—96% 9,301 GL—98%
3.5.5 Storagesystems
Thereareover100major,publicly-ownedwaterstoragesintheNorthEastCoastregionwithatotalaccessiblecapacityinexcessof10,400GL.
TheBureau’swaterstorageinformation(asatAugust2012)coversapproximately92%oftheregion’spubliclyownedstoragecapacity.Storagessupply17irrigationareasaswellasthecityofBrisbane.
Table3.3givesasummaryofthemajorstoragesystemstogetherwithanoverviewofthestoragelevelsattheendof2010–11andtheendof2011–12.ThelocationofallthesystemsandassociatedstoragesareshowninFigure3.26.
Totalaccessiblestorageintheregionforthe2011–12yearincreasedmarginally,withmoststoragesclosetofullcapacity.ThemajorincreasewasintheBrisbanesystem,wherevolumeswentupfrom85to94%.TheonlysubstantialdropinstoragelevelswasintheCallidesystem.
MoredetailsontheBrisbaneandBurdekinHaughtonsystemsisprovidedinthe‘Waterforcitesandtowns’and‘Waterforagriculture'sectionsinthischapter.
FurtherinformationonthepastandpresentvolumesofthestoragesystemsandtheindividualstoragescanbefoundontheBureau’swaterstoragewebsite:water.bom.gov.au/waterstorage/awris/
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Figure 3.26 Storage systems in the North East Coast region (information extracted from the Bureau of Meteorology's water storage website in August 2012)
North East Coast
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Woodhouse Lagoon | NQ Dry Topics
3.5.6 Wetlands
Important wetlands
AsseeninFigure3.27,therearealargenumberofwetlandsofnationalandinternationalimportanceintheNorthEastCoastregionthatencompassawidediversityofwetlandtypes,fromcoastalfloodplainstohigheraltitudefreshwaterstreamsandwaterfalls.ThewetlandscreateamosaicoftemporallyandspatiallydynamichabitatswithinthispartofAustralia.Themostspatiallyextensivewetlandtypesintheregionareartificialfreshwaterstoragesandthemarine-influencedcoastalflatsandmangroves.
Theartificialwetlands,despitebeingconstructedfromdammedwatercoursesforurbanandruralwatersupplyandfloodretardationpurposes,providerecreationalandecosystemvaluessuchasaquatichabitatforanumberofimportantfloraandfaunaspecies.Thebrackishtosalinecoastalwetlandsinthisregionprovideecosystemservicessuchasmangroveandsalt-marshhabitataswellasactingasfiltersreducingsedimentdischargestotheGreatBarrierReef.
Inflows to selected wetlands
Thestateofthebiodiversityinawetlandislinkedtothewaywaterisstoredwithintheareaandthetemporalvariabilityofinflows.Ananalysisofhistoricandrecentinflowsintowetlandsformsaninformativepictureofpotentialchanges.
Threeinternationally-recognisedRamsarwetlandsites(BowlingGreenBay,GreatSandyStraitandMoretonBay)andonenationally-listedfreshwaterwetland(theSouthernFitzroyRiverwetlandcomplex)wereselectedforhydrologicalanalysisofmajorinflows.Moreinformationabouttheregion'swetlandsisavailablefromtheAustralian Directory of Important Wetlands(www.environment.gov.au/water/topics/wetlands/database/diwa.html)
Sevenupstreammonitoringgaugeswereselectedtoenabletheanalysesandinterpretationofinflowstothesefourwetlands.Thegaugesusedintheanalysesaretheclosestupstreamgaugesthathavelargelycontinuousdischargerecordssince1980.
Thoughtheanalysesdonotcapturethetotalinflows,theyareindicativeofthetemporalpatternsoffreshwatersurfaceflowstothesewetlands.
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Figure 3.27 Location of important wetlands in the North East Coast region
North East Coast
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Bowling Green Bay
WetlandscentredonBowlingGreenBay,southofTownsville,formoneoftropicalAustralia’slargestandmostdiversecoastalwetlands.Thewetlandsaremostlycoastalplainscoveredintidalmudflats,mangroveforestandsaltmarshes.Riverchannelsandfreshwatermarshesalsoformpartofthislargewetlandcomplex.
DailydischargedataforthemonitoringgaugesontheHaughtonRiveratPowerlineandontheBarrattaCreekatNorthcotehavebeencombinedtoprovideatemporalpatternoffreshwaterinflowsintoBowlingGreenBay(Figure3.28).
Figure3.29presentsanoverviewofthedistributionofdailystreamflowdecilerankingsfortheperiodbetween1980and2012.Thedataisfairlysparseuntil1987.ThereafteronecanseeapatternofwetperiodsinblueofvaryinglengthusuallybetweenNovemberandMay.From2008–09therehasbeenanincreaseinthelengthoftheperiodofverymuchaboveaverageflows.
Figure3.30comparesmonthlydischargesfrom2011–12withtheflowstatisticsfrom1980onwards.TheMarch2012flowswellexceededtheninthdecileofthe32-yearrecordandcontributedasubstantialamountoffreshwatertoBowlingGreenBay.
Figure 3.28 Location of the monitoring sites in relation to Bowling Green Bay
Figure 3.29 Daily flows of the Haughton River at Powerline and on the Barratta Creek at Northcote between 1980 and 2012, ranked in decile classes
Figure 3.30 Combined monthly flows at Haughton River and Barratta Creek from 2011–12 compared with the 1980–2012 decile rankings
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Southern Fitzroy River floodplain complex
TheFitzroycatchmentisthesecondlargestintheregion,atnearly150,000km2,andisdominatedbyagricultureandminingincludingcoalmining.Inter-tidalwetlandsarepresentparticularlyaroundthelowerreachesoftheriverandsouthofthemouth.Thesewetlandstypicallyconsistofextensivesaltpansfringedbymangroves.
DailydischargedataforthemonitoringgaugeontheFitzroyRiveratTheGapprovidesatemporalpatternoffreshwaterinflowsintothesouthernFitzroyRiverfloodplaincomplex(Figure3.31).
Figure3.32presentsanoverviewofthedistributionofdailystreamflowdecilerankingsfortheperiodbetween1980and2012.From1994onwards,flowsweregenerallyverymuchbelowaverageduringthedryperiod,exceptforthelasttwoyears.Additionally,therewereextendedperiodsofverymuchaboveaverageflowsduringthewetmonthsof2009–10to2011–12.
Figure3.33comparesmonthlydischargesfrom2011–12withtheflowstatisticsfrom1980onwards.TheFebruaryandMarch2012flowscontributedasubstantialamountoffreshwatertothefloodplaincomplex.
Figure 3.32 Daily flows of the Fitzroy River at The Gap between 1980 and 2012, ranked in decile classes
Figure 3.31 Location of the monitoring site in relation to the southern Fitzroy River floodplain complex
Figure 3.33 Monthly flows at the Fitzroy River monitoring site at The Gap from 2011–12 compared with its 1980–2012 decile rankings.
North East Coast
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Great Sandy Strait
TheGreatSandyStraitisenclosedbetweentheAustralianmainlandandFraserIsland.TheMaryRiverentersthestraitatRiverHeads.TheStraitisacomplexlandscapeofmangroves,sandbanks,inter-tidalsand,mudislands,saltmarshesandseagrassbeds.Itformsanimportanthabitatforbreedingfish,crustaceans,dugongs,dolphinsandmarineturtles.
DailydischargedataforthemonitoringgaugeontheMaryRiveratMiva(seeFigure3.34)provideatemporalpatternoffreshwaterinflowsintotheGreatSandyStrait.
Figure3.35presentsanoverviewofthedistributionofdailystreamflowdecilerankingsfortheperiodbetween1980and2012.Anirregularpatternofhighandlowflowsoccursthroughoutmostyears.Therewereextendedperiodsofverymuchaboveaverageflowsduringthewetmonthsof2010–2012.Extendedperiodsofverymuchbelowaverageflowsoccurredduring2002–03to2006–07.
Figure3.36comparesmonthlydischargesfrom2011–12withtheflowstatisticsfrom1980onwards.TheJanuary–March2012flowswellexceededtheninthdecileofthe32-yearrecordandcontributedasubstantialamountoffreshwatertothewetland.
Figure 3.36 Monthly flows at the Mary River monitoring site at Miva from 2011–12 compared with its 1980–2012 decile rankings
Figure 3.34 Location of the monitoring site in relation to the Great Sandy Strait
Figure 3.35 Daily flows of the Mary River at Miva between 1980 and 2012, ranked in decile classes
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Moreton Bay
Becauseoftheexistenceofaseriesofoff-shorebarrierislandsthatrestricttheflowofoceanicwater,MoretonBayactssimilartoalagoon.Thewetlandsinthebayrangefromperchedfreshwaterlakesandsedgeswampsontheoffshoresandislands,tointer-tidalmudflats,marshes,sandflatsandmangrovesontheshoresofthebay’sislandsandthemainland.ThemajorriversflowingintothebaypassthroughBrisbane.
DailydischargedataforthemonitoringgaugesontheBrisbane,LoganandNerangrivers(Figure3.37)havebeencombinedtoprovideatemporalpatternoffreshwaterinflowsintoMoretonBay.
Figure3.38presentsanoverviewofthedistributionofdailystreamflowdecilerankingsfortheperiodbetween1980and2012,rankedindecileclasses.TheWivenhoeDamintheBrisbaneRiverwascompletedin1985andfromthenonwardsflowsintheriverbecameincreasinglyregulated.Prolongedperiodsofverymuchbelowaverageinflowstothebayoccurredbetween2006–07and2010–11.TheBrisbanefloodsofDecember2010brokethispattern.
Figure3.39comparesmonthlydischargesfromJune2011–March2012withtheflowfrom1980onwards.DatawasnotavailablebeyondMarch2012.TheMarch2012flowscontributedasubstantialamountoffreshwatertothewetland.
Figure 3.37 Location of the monitoring sites in relation to Moreton Bay
Figure 3.38 Combined daily flows of Brisbane, Logan and Nerang rivers between 1980 and 2012, ranked in decile classes
Figure 3.39 Combined monthly flows of Brisbane, Logan and Nerang rivers from 2011–12 compared with the 1980–2012 decile rankings
North East Coast
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3.5.7 Hydrogeology
AsseeninFigure3.40,theNorthEastCoastregionisdominatedbyfracturedrockgroundwatersystemsthatprovidealow-volumegroundwaterresource.Greaterresourcepotentialisassociatedwiththefollowingaquifergroups:
• Surficialsedimentaquifer(porousmedia—unconsolidated);
• Tertiarybasaltaquifer(fracturedrock);and• Mesozoicsedimentaquifer
(porousmedia—consolidated).
Figure3.40showsthatsedimentsoftheGreatArtesianBasin,whichisoneofAustralia’slargestandmostsignificantgroundwaterbasins,arepresentalongthewesternborderoftheregion;however,thesesedimentsarenotextensiveintheNorthEastCoastregion.
3.5.8 Watertablesalinity
Figure3.41showstheclassificationofwatertableaquifersasfresh(totaldissolvedsolids(TDS)<3,000mg/L)orsaline(TDS≥3,000mg/L).Thesalinitywasinterpolatedfromboreslessthan40mdeepusingthelong-termaveragegroundwatersalinityforallbores.Mostpartsoftheregionhavefreshgroundwater.Saltygroundwateroccursinlocalisedareasinthecentralhighlandsandthecoast.
3.5.9 Groundwatermanagementunits
InQueensland,anumberofgroundwaterareashavebeenestablishedbytheStategovernmenttoprotectundergroundwaterresources.
AgroundwaterareainQueenslandisanareaidentifiedintheWaterRegulation2002asawaterresourceplanorawildriverdeclaration.Withintheseareasauthorisationisrequiredtoaccessgroundwaterorconstructworkstotakegroundwaterforcertainpurposes.
ThegroundwatermanagementunitswithintheregionarepresentedinFigure3.42.ThisdatasetisextractedfromtheBureau’sInterimGroundwaterGeodatabaseascompiledin2009(currentlyunderrevision).
Mostgroundwatermanagementunitsarerelativelysmallinarea.Inlargeareas,groundwaterresourcesareusedoutsideofgroundwatermanagementunits(unincorporatedareas).Thispatternofgroundwaterusereflectsthehydrogeologyintheregion,whichisdominatedbyalargeareaofoutcroppingfracturedbasementrocktypicallyofferingrestrictedlow-volumegroundwaterresources.
Incontrast,significantgroundwaterresourcesarelocalisedinalluvialvalleysystemsandcoastalsanddeposits.
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Figure 3.40 Watertable aquifers of the North East Coast region, data extracted from the Groundwater Cartography of the Australian Hydrological Geospatial Fabric (Bureau of Meteorology 2012)
North East Coast
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Figure 3.41 Watertable salinity classes in the North East Coast region; data extracted from the Groundwater Cartography of the Australian Hydrological Geospatial Fabric (Bureau of Meteorology 2012)
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Figure 3.42 Groundwater management units in the North East Coast region, data extracted from the National Groundwater Information System (Bureau of Meteorology 2013)
North East Coast
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3.5.10Groundwaterstatusofselectedaquifers
ThestatusofgroundwaterlevelsisanalysedateachborethroughouttheNorthEastCoastregion.Thisassessmentevaluatestrendsingroundwaterlevelsoverthefive-yearperiod2007–08to2011–12.
Thetrendsingroundwaterlevelsoverthefiveyearsareinvestigatedusinga5kmx5kmgridacrossdatarichareasusuallyassociatedwiththemajorgroundwatermanagementunits(seeFigure3.42).Thisscalereflectsthemostlylocaltointermediateflowsystemofthealluvialandtertiarybasaltsaquifersintheregion.
Thelineartrendingroundwaterlevelsforagridcellisassessedas:
• decreasing(wheremorethan60%oftheboreshaveanegativetrendinlevelslowerthan–0.1m/year);
• stable(wheremorethan60%oftheboreshaveatrendlowerthan0.1m/yearandhigherthan–0.1m/year);
• increasing(wheremorethan60%oftheboreshaveapositivetrendinlevelshigherthan0.1m/year);and
• variable(wherethereisnodominanttrendingroundwaterlevelsamongsttheboreswithinagridcell).
Exampleborehydrographsarepresentedforeachsub-regionovertheentirerecordlengthandtrendsarediscussedwithafocusonthe2007–08to2011–12period.Theselectedborehydrographsrepresentmostlyboreswithhighdatadensitythatwereusedinthe2010Assessment.
Northern aquifers
ThemapinFigure3.43illustratesthespatialandtemporaltrendsingroundwaterlevelsinthemajoralluvialaquifersalongthecoast(showninbrown)andinthemaininlandbasaltaquifer(showninpink),overthe2007–08to2011–12period,inthenorthoftheregion.Manyofthegridcellsshowarisingtrendwithaminorityofcellsshowingastabletrend.
SelectedBore1showsastabletrendwhilebores2and3showarisingtrendingroundwaterlevelsoverthelastfiveyears.Thisreflectsthelocalgroundwateruseandtherisingtrendinrainfallforthenorthernpartoftheregion.IrrigationintheBurdekinirrigationareamayalsobeaffectinggroundwaterlevelsinBore2.Groundwaterlevelsinthelastfiveyearsarewithintheshallowestlevelsonrecord.
Central aquifers
ThemapinFigure3.44illustratesthespatialandtemporaltrendsingroundwaterlevelsinthemajoralluvial(showninbrown)andbasaltaquifers(showninpink),overthe2007–08to2011–12period,inthecentralareaoftheregion.Manyofthegridcellsshoweitherarisingorstabletrend.
SelectedBore4showsarisingtrendingroundwaterlevelsovertheanalysisperiod.TheBore4hydrographissimilarinnaturetothebehaviourofgroundwaterlevelsinthenortherncoastalaquifers.Bores5and6,locatedintheinlandalluviumoftheCallidegroundwatermanagementunit,showanincreaseingroundwaterlevelfromend2010toearly2011incontrasttothelong-termdecliningtrendsuggestingrecenthighrechargetogroundwater.Thisreflectsthehighrainfallandfloodingthatoccurredsince2010.
Southern aquifers
ThemapinFigure3.45illustratesthespatialandtemporaltrendsingroundwaterlevelsinthemajoralluvial(showninbrown)andbasalt(showninpink)aquifersinlandandalongthecoast,overthe2007–08to2011–12period.Manyofthegridcellsshowarisingtrendwithaminorityofcellsshowingastabletrend.
Selectedbores7,8and9showarisingtrendingroundwaterlevelsovertheanalysisperiod,especiallyinBore9,representingtheLockyervalleyalluviumaquifer;thisisincontrasttothelong-termdecliningtrend.Itsuggestsrecenthighrechargetogroundwater,reflectingthehighrainfallandfloodingsince2010.
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Figure 3.43 Spatial distribution of trends in groundwater levels for the surficial sediments and tertiary basalt aquifers in the northern North East Coast region for 2007–08 to 2011–12 with selected hydrographs showing groundwater levels
North East Coast
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Figure 3.44 Spatial distribution of trends in groundwater levels for the surficial sediments and tertiary basalt aquifers in the central North East Coast region for 2007–08 to 2011–12 with selected hydrographs showing groundwater levels
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Figure 3.45 Spatial distribution of trends in groundwater levels for the surficial sediments and tertiary basalt aquifers in the southern North East Coast region for 2007–08 to 2011–12 with selected hydrographs showing groundwater levels
North East Coast
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3.6 Waterforcitiesandtowns
ThissectionexaminesurbanwaterintheNorthEastCoastregionin2011–12.Thelargeurbancentresintheregion,theirwatersupplysystemsandwaterstoragesituationsarebrieflydescribed.Themainurbanisedarea,southeastQueensland,isaddressedinmoredetailandthehistoryofwaterrestrictionsoverrecentyearsisdiscussed.AbreakdownisprovidedforwaterobtainedforanddeliveredtoBrisbaneandtheGoldCoast.
3.6.1 Urbancentres
StraddlingtheBrisbaneRiver,thecityofBrisbaneisthelargestcityintheregionandwithapopulationofover1.8millionpeopleitisthethirdlargestinAustralia.TheSunshineCoastandGoldCoast,totherespectivenorthandsouthofBrisbane,arehometoafurther743,000people.
Outsideoftheheavilypopulatedsoutheastcoast,theregionhasalargenumberofurbancentresandtowns.Inparticular,anumberofcoastalcitiesthatsupportadjoiningareaswithintheregion.
Cairnsisthenorthernmostandsecondlargestofthesecities.FromnorthtosouthbetweenCairnsandBrisbanethesecitiesincludeTownsville,thelargestregionalcityoutsideofsoutheastQueensland,Mackay,Rockhampton,GladstoneandBundaburg.Thesecities,alongwithBrisbane,TheGoldCoastandtheSunshineCoastareshowninFigure3.46inconjunctionwiththeirpopulationranges.
Table3.4summarisesthemajorurbancentresoftheregionwithpopulationsofover25,000peopleandprovidesinformationonthepopulation,surroundingriverbasinandsignificantwaterstoragesforeachof
themajorurbancentres.
Table 3.4 Cities and their water supply sources in the North East Coast region
City Population1 River basin Major supply sources
Brisbane 1,874,000 BrisbaneRiver Wivenhoe,SomersetandNorthPinereservoirs(partofSEQWaterGrid)
TheGoldCoast 534,000 SouthCoast Hinzereservoir(partofSEQWaterGrid)
TheSunshineCoast 209,000 MaryRiver LakeMacdonald,BaroonPocket,EwenMaddock,CooloolabinandWappareservoirs
Townsville 158,000 RossRiver RossRiverandPalumareservoirs
Cairns 134,000 Mulgrave–RussellRivers
TinarooFallsandCopperlodereservoirs
Mackay 74,000 PioneerRiver TeemburraandKinchantreservoirs
Rockhampton 62,000 FitzroyRiver FitzroyRiverBarrageandEdenBannWeir
Bundaberg 50,000 BurnettRiver BenAndersonBarrage,NedChurchwardWeir,ParadiseandFredHaighreservoirs
HerveyBay 49,000 MaryRiver LakeLenthall
Gladstone 32,000 CalliopeRiver AwoongaReservoir
1 Australian Bureau of Statistics (2011b)
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Figure 3.46 Population range of major urban centres in the North East Coast region
North East Coast
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3.6.2 Sourcesofwatersupply
Surfacewateristhemajorsourceofsupplyforthecitiesandtownsoftheregion.Ithasover70majorwaterstorages,eachwithacapacityofover1GL,thatsupplyacombinationofurban,agricultural,industrialandminingdemands.
SupplyingBrisbaneandsurroundingpopulations,Wivenhoeisarguablythemostwellknownsurfacewaterstorageintheregion;however,withrespecttosizeitranksthirdbehindFairbairnandBurdekinFalls.Thelatter,beingthelargestsurfacewaterstorageintheregion,suppliesbothirrigationandurbandemands,includingthoseoftheCityofTownsville.
Figure3.47showsmajorsurfacewaterstoragesintheregion,includingWivenhoeandBurdekinFalls,thatarepartlyinuseforurbanwatersupply.
Inadditiontosurfacewaterstoragestheregionutilisesdirectriverextractions(includingextractionsofupstreamstoragereleases),groundwater,desalination,recycledwater,andharvestedstormandrainwatertosupplyitsurbandemands.
3.6.3 SoutheastQueensland
SoutheastQueensland(SEQ)isservicedbywhatisarguablythemostcomplexwatersupplysysteminAustralia.KnownastheSEQWaterGrid,thesupplyareaitcoversisabout22,000km2,extending240kmfromtheShireofNoosainthenorthtotheGoldCoastandtheNewSouthWalesborderinthesouth.ItencompassesthetenlocalgovernmentareasofBrisbane,theGoldCoast,Ipswich,LockyerValley,Logan,MoretonBay,Redland,ScenicRim,SomersetandtheSunshineCoast.
Newinstitutionalarrangementsforthemanagementandoperationoftheregion’swaterservicescameintoeffecton1January2013.SevenseparateauthoritiesandutilitiesarecollectivelyresponsiblefortheSEQWaterGridandarecomprisedofabulkwaterauthority(Seqwater),anetworkcontrollerforbulksupplies(LinkWater)awatergridoperator(SEQWaterGridManager),anoperatorfortheregion’sdesalinationandrecycledwaterplants(SecureWater),andthreeretailsuppliers(UnityWater,QueenslandUrbanUtilitiesandAllconnexWater).
Seqwaterisresponsibleforthecollectionandstorageofsurfacewater,extractionofgroundwater,operationofthedesalinationfacilitiesandthearea’sWesternCorridorRecycledWaterScheme.Inaddition,Seqwateristhecatchmentmanagerforthearea'ssurfacewaterandgroundwatersupplycatchments.
LinkWateroperatesandmaintainsthebulkwatersupplynetworkandisresponsibleforthetransportationofwatersuppliestotreatmentplantsandbetweenstorages.
AstheownerofurbanwaterentitlementsintheSEQregiontheSEQWaterGridManageroperatestheSEQWaterGridtosupplythecouncil-ownedretailauthoritiesandindustrywithpotablewater.
SecureWateroperatestheGoldCoastdesalinationplantandtheWesternCorridorRecycledWaterScheme.
Theregion'surbanwaterutilitiesareUnityWater(MoretonBayandSunshineCoast),QueenslandUrbanUtilities(Brisbane,ScenicRim,Ipswich,SomersetandtheLockyerValley)andAllconnexWater(GoldCoast,LoganandRedland).Inadditiontotheprovisionofwatersupplyservicestheseutilitiesareresponsibleforthecollectionandtreatmentofwastewater.
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Figure 3.47 Urban supply storages in the North East Coast region
North East Coast
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Supply system
Theregion'swatersuppliesaredrawnfromacomplexnetworkofsurfacewaterstorages,watertreatmentplants,groundwaterborefieldsandrecycledanddesalinatedwaterplants.
Overtenmajorsurfacewaterstorages,includingWivenhoe,SomersetandNorthPine,aseriesofsmallstoragesandweirs,theStradbrokeIslandandBribieIslandborefields,theTugandesalinationplant,theWesternCorridorRecycledWaterSchemeandacomplexnetworkofpipes,servicereservoirs,pumpstationsandtreatmentplantsmakeuptheSEQWaterGrid.
Figure3.48outlinesthemajorwaterinfrastructureinsoutheastQueenslandandillustratesurbanflowpathwaysbetweenlocalgovernmentandothermaincustomers.
Somewaterisexportedtocostumersbeyondthissystem,thelargestbeingtheTarongPowerStation.
Storage volumes
Incombination,theWivenhoe,Hinze,SomersetandNorthPinestoragesprovideover90%ofthetotalaccessiblesurfacewaterstorageforSEQ,withWivenhoecontributingoverhalfofthistotal.
Figure3.49presentsthetotalaccessiblevolumeheldinthesestoragesoverthepast18years(1984–2012)andclearlyillustratestheimpactsofthemillenniumdroughtwithstorageslevelsreachingcriticallylowlevelsin2008.Ashiftinclimaticconditionsin2009andaseriesofwetteryears,includingAustralia’swettesttwo-yearperiodonrecordin2010and2011,sawstoragelevelsrecoverfromtheirhistoriclows.Continuedgoodrainfallintheregion'scatchmentshasseenstoragelevelsmaintainedatornearcapacitythroughout2011–12.
TheobservedstepchangeintheaccessiblevolumesoftheHinzestorageisexplainedbyanincreaseinthestorage’stotalcapacity.ComingintoeffectinDecember2011,theHinzeDamwasraisedtoincreasethetotalaccessiblestoragefrom161GLto311GL.
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Figure 3.48 Water supply schematic for southeast Queensland
North East Coast
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Figure 3.49 Variation in the amount of water held in storage over recent years (light blue) and over 2011–12 (dark blue) for the Hinze, Wivenhoe, Somerset and North Pine storages, as well as total accessible storage capacity (dashed line)
Gold Coast (Hinze)
Brisbane (Wivenhoe)
Brisbane (Somerset)
Brisbane (North Pine)
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Water restrictions
Followingitsformationon1January2013,SeqwaterhastakenoverthewatersecurityandefficiencyresponsibilitiespreviouslyperformedbytheQueenslandWaterCommission.
Waterrestrictionshavebeeninplacesince2005,andappliedthroughoutSEQ,excludingRedland,SunshineCoastCouncilandToowoombauntilDecember2009.TheyareshownwiththecombinedstoragelevelsinFigure3.50.
Between2005and2008combinedstoragelevelssteadilydecreasedresultingintheintroductionofmorestringentwaterrestrictions.
Permanentwaterconservationmeasures(PWCM)wereintroducedinDecember2009acrosssoutheastQueenslandincludingtheSunshineCoast.Althoughthecombinedstoragelevelremainedabove80%during2011–12,PWCMremainedinplace.Thesemeasuresencouragedtheuseofamaximumof200litresperpersonperday.
Figure 3.50 Urban water restriction levels across southeast Queensland since 2005 shown against the combined accessible water volume of Wivenhoe, Somerset and North Pine storages
North East Coast
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Sources of water obtained
BecauseofdatalimitationsthefollowingdiscussionofsourcesofwaterobtainedpertainsonlytotheBrisbane,LoganandGoldCoastCityCouncilareas.Forthepurposesofthisandthefollowingsectionsthissupplyareaisreferredtoasthe‘combinedarea’andrepresentsthecentralandsouthernextentsoftheSEQWaterGrid.
Figure3.51showsthetotalvolumeofwatersourcedfromsurfacewaterextractions,groundwater,recycling,andbulkwatertransferstothecombinedareaforthelasteightyears(2005–06to2011–12).
FollowingchangestothemanagementofbulkwaterresourcesinSEQwiththecreationoftheSEQWaterGridin2008,reporteddatanolongerdistinguishes
betweenlocallysourcedsurfacewaterandsurfacewaterimportedtothearea.
Theobserveddownwardtrendinthetotalvolumeofwatersourcedforurbansupplyisattributabletodemandmanagementandwaterconservationmeasuresputinplaceinresponsetodwindlingsurfacewaterstoragelevels.
Ashiftinclimaticconditionsin2009andaseriesofwetteryearshasseenstoragesinSEQrecovertoatornearfullsupplylevelsandresultedinaneasingofwaterrestrictions.Theseconditionshaveseenagradualincreaseinthetotalamountofwatersourcedforurbansupplytotheareaandareductioninthevolumeofrecycledwaterusedtomeettheareasdemand.
Figure 3.51 Total urban water sourced for the combined area from 2005–06 to 2011–12
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Categories of water delivered
Asinthepreviousdiscussionthissectionreportsonwaterusageforthe‘combinedarea’comprisingBrisbane,LoganandGoldcoastcouncils.
Figure3.52showsthetotalvolumeofwaterdeliveredtoresidential,commercial,municipal,industrial,andotherconsumers,suchasnurseries,parks,gardensandcemetaries,inthecombinedarea.
Totalwatersuppliedwas220GLin2005–06thatthendecreasedfortwoconsecutiveyearsduetowaterrestrictions.Between2007–08and2009–10,
totalwatersuppliedincreasedslightlyduetotheeasingofwaterrestrictionsandthereintroductionofoutdoorwatering.Thetotalvolumeofwatersuppliedtourbancustomersin2011–12was176GL.Recentwateruseislowcomparedtothatin2005–06.
Averagetotalresidentialwaterconsumptionofthecombinedareain2011–12was297ML/dor158litresperpersonperday(L/p/d).Theresidentialsectoraccountedfor62%oftotalpotablewaterconsumption(similartothepreviousyearwhenresidentialconsumptionwasestimatedtobe59%).Thecommercial,municipalandindustrialsectorsaccountedfor26%ofurbanwaterconsumption.
Figure 3.52 Total urban water supplied to the combined area from 2005–06 to 2011–12
North East Coast
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3.7 Waterforagriculture
ThissectiondescribesthewatersituationforagricultureintheNorthEastCoastregionduringthe2011–12yearcomparedwiththepast.Soilmoistureconditionsarepresentedandimportantirrigationareasareidentified.TheBurdekinirrigationareaisdescribedinmoredetailandinformationisprovidedregardingsurfacewaterstorageandgroundwater.
3.7.1 Soilmoisture
Sincemodelestimatesofsoilmoisturestoragevolumesarebasedonasimpleconceptualrepresentationofsoilwaterstorageandtransferprocessesaveragedovera5kmx5kmgridcell,theyarenotsuitableforcomparisonwithlocallymeasuredsoilmoisturevolumes.Thisanalysis,therefore,presentsarelativecomparisononly,identifyinghowmodelledsoilmoisturevolumesof2011–12relatetomodelledsoilmoisturevolumesofthe1911–2012period,expressedindecilerankings.
Figure3.53givesanoverviewofthedecilerankingofmodelledannualaveragesoilmoisturefor2011–12withrespecttothe1911–2012period.Itshowsthatthemajorityoftheregionhadaboveaverageorverymuchaboveaveragesoilmoistureconditions.Thelatterconditionsweremoreprominentinthewesternpastoralandcroppingareasoftheregionwhereverymuchaboveaveragerainfallsoccurredinthatperiod.
AboveaveragesoilmoistureconditionsintheregionweredominantinthewetmonthsofNovember2011–March2012(Figure3.54).Soilmoistureremainedverymuchaboveaverageinallothermonthsoftheyear.Itcreatedbeneficialwaterconditionsfordrylandcroppingacrosstheinlandandwesternpartsoftheregionwhicharenormallydrier.
Figure 3.53 Deciles rankings of annual average soil moisture for 2011–12 with respect to the 1911–2012 period for the North East Coast region
Figure 3.54 Decile ranking of the monthly soil moisture conditions during the 2011–12 period with respect to the 1911–2012 period in the North East Coast region
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3.7.2 Irrigationwater
TheDepartmentofEnergyandWaterSupply,establishedinApril2012,providespolicyandregulationforthedeliveryofwatertoQueensland.
SunWaterisagovernment-ownedcorporation,whichisthemainsupplierofbulkwater,bulkwaterstorageanddeliveryofservicesforregionalQueensland.Inthesoutheast,Seqwaterprovidesbulkwatersupplyandservicestoaround1,000ruralcommunitiesinfivewatersupplyschemesintheUpperMary,Logan,CentralBrisbane,WarrillvalleyandLockyervalleyareas.
Acomparisonofwateruseinirrigatedcatchmentsbynaturalresourcemanagement(NRM)regionsintheregionovertheperiod2005–06to2010–11isshowninFigure3.55.Figure3.56showsthemapofthewateruseperNRMregionin2010–11.
AswiththepreviousyearsBurdekinhadthehighestirrigationwaterconsumptionamongotherNRM
regions,butthewateruseduringthe2010–11inallregionshaddroppedduetoincreasedavailabilityofwaterthroughrainfall.Atthetimeofwritingthereportdatawasnotavailablefor2011–12.
TheBurdekinRiverIrrigationAreaisdescribedinmoredetailinsubsection3.7.4
3.7.3 Irrigationareas
MostoftheNorthEastCoastregionisusedforgrazing.Drylandandirrigatedagricultureaccountforonly0.4%ofthelanduseoftheregion.Thegreatestareaofdrylandagriculture,1.8millionhectares,islocatedintheFitzroyRiverbasin.
AsshowninFigure3.57,thelargestirrigationareasarelocatedintheBrisbane,Mary,Burnett,BurrumandKolanriverbasinsinthesouth;theFitzroy,PlaneCreekandPioneerriverbasinsinthecentreoftheregion;andtheHaughtonandBurdekinriverbasinsinthenorth.
Figure 3.55 Total annual irrigation water use for 2005–06 to 2010–11 for natural resource management regions in the North East Coast region (ABS 2006–2010; 2011a)
North East Coast
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Figure 3.56 Annual irrigation water use (GL) per natural resource management region for 2010–11 in the North East Coast region (ABS 2011a)
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Figure 3.57 Irrigation areas in the North East Coast region
North East Coast
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3.7.4 BurdekinRiverIrrigationArea
TheBurdekinRiverbasinislocatedinthedrytropicsontheNorthEastCoastregion,coveringatotalcatchmentareaofapproximately133,000km2.
Thebasin’sassetsincludewater,biodiversity,nationalparks,grazing,fertilesoilandcrops(Figure3.58).
TheLowerBurdekininthebasinisthelargestirrigationareainnorthernAustralia,predominantlygrowingsugarcane.Thispartoftheregioncanreceivemorethan300daysofsunshineeachyear,whichisaprimaryreasonforthehighlyproductiveagriculturalsector.Thiscanbetempered,however,bythetraditionalwetseason,whichrunsfromNovember–MarcheachyearwiththewettestmonthstypicallybeingJanuaryandFebruary.
LowerBurdekincomprisestwoschemes:theBurdekinRiverDelta,andtheBurdekin–HaughtonWaterSupplyScheme.
TheBurdekinDeltadownstreamoftheBurdekinRiverisagroundwater-dominatedscheme,with
morethan35,000haofirrigatedsugarcaneandothercrops.Thissystemoverliesmajorgroundwatersupplies.
TheBurdekin–HaughtonWaterSupplySchemeissurfacewaterdominatedandreceivessignificantvolumesofwaterfromBurdekinFallsstorage.Groundwatersuppliessupplementirrigation.
BurdekinFallsontheBurdekinRiverisoneofthelargestsurfacewaterstoragesinQueenslandcovering22,000haandissuppliedbyanupstreamcatchmentareaofapproximately120,000km2.ThetotalaccessiblestoragecapacityofBurdekinFallsis1,850GL.
TotalwaterdeliveryintheBurdekin–Haughtonschemein2011–12was455GL,whichwas41percentofthewateravailabletothescheme(SunWater2012).
Forthepurposeofthisreport,theBurdekinRiverIrrigationAreawasselectedasanexampleofgroundwateruseforirrigationintheNorthEastCoastregion.
Figure 3.58 Burdekin River Irrigation Area
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Surface water storage inflows
Thehighlyseasonalrainfallpatternoftheregion,whichischaracteristicofthetropicsofnorthernAustralia,ishighlightedbythehistoricalstreamflowdischargerecordsofgaugingstationsontheSuttorRiveratStAnns,CapeRiveratTaemasandBurdekinRiveratSellheim(Figure3.59).
TheseasonalrainfallpatternislinkedtotheElNiñoSouthernOscillation,tropicalcyclonesandmonsoonalactivity.
ThemajorityoftherecordeddischargeinthethreecatchmentsupstreamofBurdekinFallsfortheperiod1980–2012occurredduringthemonthsofJanuarythroughtotheendofMarch,whichisthewetseasonintheregion.
Thedischargehydrographsof2011–12showalaginpeakflowcomparedwiththehistoricalpatterns.Thisisconsistentwiththeoverallpatternofrainfallintheregion;showinggradualascentwithapeakinMarchthatsubsidesafterwards.
Figure 3.59 Monthly inflows to Burdekin Falls for 2011–12 with respect to the 1980–2012 decile rankings
North East Coast
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Surface water storage volumes
DespitethelargestoragecapacityofBurdekinFalls,thesignificantseasonaldischargefromtheupstreamcatchmentshasresultedinanalmostperiodicspillingofthedameverywetseasonsinceconstruction(Figure3.60).Inwetyears,thespillingcancontinueformonths.In2011–12,thedamoverflowedfromJanuary2012andcontinuedtospillinJune2012.
BetweenJanuaryandJune2012,morethan29,000MLofwaterpassedoverthespillway.Thefullstorageandwetweatherconditionsensured100%ofwaterallocationswereavailabletolocalirrigators.
Local hydrogeology
IrrigationareasintheBurdekinRiverDeltaareunderlainbyarelativelyshallowwatertable.LowerBurdekinWatermanagesagroundwater-dominatedirrigationsystemdownstreamandeastofMountKelly(Figure3.61).Morethan1,400groundwaterpumpsareinoperationapplying10–40ML/ha/yrtocrops(McMahonetal.2002).Thisisequivalentto1,000–4,000mm/year.
Thewatersourceusedforirrigation(groundwaterorsurfacewater)dependsonproximitytotheriverorirrigationchannelsandongroundwatersalinityandyield.
Thecoastalfloodplainismostlyunconfinedandhasupto100mofsedimentsoverlyingthebasement.TheshallowgroundwaterinthissystemisindirecthydraulicconnectionwiththeBurdekinRiver.
Typically,duringthedryseason,groundwaterelevationishigherthansurfacewaterlevelsintheriverupstreamoftheRocksweirallowinggroundwaterdischargeintotheriver.Duringoccasionalhighflowsinthewetseason,thedirectionofflowisreversedallowingsurfacewatertorechargegroundwater(LenahanandBristow2010).Thisactivityindicatesahighconnectivitybetweensurfacewaterandgroundwater.
Lateralgroundwaterflowisnortherlytowardsthecoast.However,groundwaterpumpingcauseslargefluctuationsingroundwaterlevelsthatcanchangethelocalgroundwaterflowdirection.
Figure 3.60 Variation in the amount of water held in storage over recent years (light blue) and over 2011–12 (dark blue) for Burdekin Falls storage, as well as total accessible storage capacity (dashed line)
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Figure 3.61 The Burdekin River Irrigation Area showing the location of groundwater bore sites, river gauge and rain gauge
North East Coast
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Influences on shallow groundwater
Figure3.62showsthefluctuationsinshallowgroundwaterlevelsatselectedsites.From2003groundwaterlevelsshowarisingtrend.
Figure3.62alsoillustratesthedriversofthegroundwaterlevelbycomparingfluctuationinshallowgroundwaterlevelswiththemonthlycumulativerainfallresidualatAyrandthemonthlydischargeoftheBurdekinRiveratClare(Figure3.62).ThelocationofgaugesandboresisshowninFigure3.61.
Periodsinwhichthecumulativerainfallresidualcurverisesindicatewetterthanaverageconditions.Periodswithafallingtrendindicatedrierthanaverageconditions.
Figure3.62bshowsadrierthanaverageperiodupto2007,followedbyawetterthanaverageperiod.
Bothrainfallandstreamflowappeartobedriversforgroundwaterlevels.Peaksinstreamflowandintherainfallresidualcurvecorrespondtopeaksingroundwater.Thereare,however,someinconsistenciesbetweentherainfallandgroundwaterlevelcycles.Forexample,groundwaterlevelsstartrisingin1995and2003eventhoughtherainfallresidualmasscurveisstillfalling.
Figure 3.62 Comparison of shallow groundwater levels recorded at nested bore sites with rainfall and streamflow in the Burdekin River Irrigation Area to June 2012, showing (a) top panel: Bore 11910262 pipe D (red), Bore 12000202 pipe D (blue), Bore 11900162 pipe D (yellow); (b) cumulative rainfall residual mass at Ayr, Station 33002; and (c) lower panel: Burdekin River discharge at Clare, Station 120006B)
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Groundwater level
Groundwaterlevelmeasurementisanimportantsourceofinformationabouthydrologicalandanthropogenicinfluencesonthegroundwaterinanarea,includingrecharge.
Figure3.63presentsgroundwaterlevelsrecordedinboresofdifferentdepthatthesamesite,anestedboresite,intheLowerBurdekinarea.Groundwaterlevelfluctuationsaresimilaratalldepthsindicatingthatdeeperandshallowergroundwaterishydraulicallyconnected.Verticalgroundwatergradientsaremostlydownwardindicatingpossibilityofflowfromthewatertabletothedeepestpartoftheaquifer.
Figure3.64(a)showsthemediangroundwaterdepthsintheuppergroundwateraquiferintheBurdekinRiverDeltain2011–12;Figure3.64(b)
showsthedecileranksof2011–12mediangroundwaterlevelscomparedtoannualmediangroundwaterlevelsinthelast22years(1990–2012).
Ingeneral,intheupperaquifer,groundwaterlevelsvaryfromquiteshallownearthecoasttodeeperthan10mfurtherinland.Mediangroundwaterdepthsintheupperaquiferin2011–12aremostlyabovetheaverageofrecordedlevelswithintheirrigationareaandareamixofaboveaverageandbelowaveragenortheastoftheirrigationareas.
AsshowninFigure3.65(a),groundwaterlevelsintheloweraquiferaregenerallybetweenoneandfivemetersbelowthesurface.Mediangroundwaterlevelsintheloweraquiferin2011–12aremostlyabovetheaverageofrecordedlevelsofthelast22yearsFigure3.65(b).
Figure 3.63 Groundwater levels between 2007 and 2012 recorded at selected nested bore sites in the Lower Burdekin area, depth of the screen interval increases from pipe D (shallow) to pipe A (deep)
North East Coast
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Figure 3.64 (a) Upper aquifer median groundwater depths for the Burdekin River Delta in 2011–12, and (b) decile ranks of depth in 2011–12 compared to the 1990–2012 period. Deciles 1–3 are shown as below average (greater depth below surface), deciles 4–7 as average and deciles 8–10 as above average
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Figure 3.65 (a) Lower aquifer median groundwater depths for the Burdekin River Delta in 2011–12, and (b) decile ranks of depth in 2011–12 compared to the 1990–2012 period. Deciles 1–3 are shown as below average (greater depth below surface), deciles 4–7 as average and deciles 8–10 as above
North East Coast
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Groundwater salinity
Sincethe1960s,whentheQueenslandGovernmentcommencedregularmonitoringofgroundwaterquality,anincreaseinsalinityhasbeenreportedatmanysites.TwomainissueslinkedtodegradinggroundwaterqualityhighlightedbyLenahanandBristow(2010)are:
• anincreaseingroundwatersalinitybeyondirrigatedcroptolerancelevelreducingthegroundwaterresourcevolumeavailableforirrigation;and
• ecosystemsindeclineduetogreaterinfluxofsolutesfromtheaquifersintothesurfacewaterandultimatelyintotheGreatBarrierReef.
Increasinggroundwatersalinityatsomelocationsiscausedbyinfluencesonthehydrologicalcycle,suchaslandclearingandirrigation,whichmobilisesubsurfacesolutestores.
Increasesingroundwaterpumpingcanresultinseawaterintrusionorupwardmovementofdeepersaltygroundwater.Incontrast,decreasinggroundwatersalinitiesintheshallowsystemcanresultfromdilutionbyirrigationdrainageorleakagefromtheriver.
Figure3.66showsgroundwatersalinity,expressedinunitsofelectricalconductivity,atfourdepthsforeachofthreenestedboresitesinthelowerBurdekinRiverDelta(forborelocations,seeFigure3.61).
Groundwatersalinityinthedeepboresisusuallyveryhighcomparedtotheshallowbores.Atthesenestedsites,theshallowgroundwatersalinityismorethananorderofmagnitudelowerthansalinityindeeperbores.
Figure3.66alsoshowsthatgroundwatersalinityatthesesiteshasbeenrelativelystablesince2007.Ingeneralgroundwatersalinityisslowtochange.
Figure3.67andFigure3.68showthemediangroundwatersalinitiesintheupperandlowergroundwateraquifersin2011–12andtherankingofthesesalinitiescomparedto22-yearannualaveragesforthe1990–2012period.
TheBurdekinRiverDeltagroundwaterintheupperaquiferissaltierinthenorth,inthesoutheastnearthecoastandclosetothebedrockoutcropsinthesouth.Mediangroundwatersalinitiesintheupperaquiferin2011–12donotshowanyconsistenttrendfromthelong-termaverages.
Intheloweraquifer,saltygroundwaterappearstodefinethedistancefromthecoastwhereseawaterintrusionmayhaveoccurred.Mediangroundwatersalinitiesintheloweraquiferin2011–12againdonotshowanyconsistenttrendfromthelong-termaverage.
Figure 3.66 Groundwater salinity recorded at selected nested bore sites in the lower Burdekin area between 2007 and 2012, with depth of the screen increasing from pipe D (shallow) to pipe A (deep)
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Figure 3.67 (a) Upper aquifer median groundwater salinity for the Burdekin River Delta in 2011–12, and (b) groundwater salinity in 2011–12 compared to the 1990–2012 period. Deciles 1–3 are shown as below average (greater depth below surface), 4–7 as average and deciles 8–10 as above average
North East Coast
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Figure 3.68 (a) Lower aquifer median groundwater salinity for the Burdekin River Delta in 2011–12, and (b) groundwater salinity in 2011–12 compared to the 1990–2012 period. Deciles 1–3 are shown as below average (greater depth below surface), deciles 4–7 as average and deciles 8–10 as above average