35 41 Dalgety Street Oakleigh - City of Monash · 2018-06-22 · For the purpose of this report,...

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Arboricultural Impact Assessment 35 - 41 Dalgety Street Oakleigh Prepared for: Rod Quince Prepared by: Matt James (Grad Cert Arb – completing) (Dip. Arb) Submitted: 21.12.17

Transcript of 35 41 Dalgety Street Oakleigh - City of Monash · 2018-06-22 · For the purpose of this report,...

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ArboriculturalImpactAssessment

35 - 41 DalgetyStreet Oakleigh

Preparedfor:RodQuince

Preparedby:MattJames

(GradCertArb–completing)(Dip.Arb)

Submitted:21.12.17

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ExecutiveSummary MelbourneTreeCarewas requestedbyRodQuince toproduce an impact assessmentreportinregardstoaproposeddevelopmentandthepotentialimpactsontreeslocatedinCaloolaReserve to thenorthof thesubjectsite,andstreet trees locatedadjacent tothesubjectsite.Theimpactassessmenthasdeterminedthatthereisminorencroachment(<10%)intotheTreeProtectionZonesoftwo(2)treeslocatedinCaloolaReserve,one(1)streettreelocated on Atkinson Street, and one (1) street tree located on Dalgety Street. It isconsidered that as these encroachments are minor, and the trees can remain viableduringandafterconstruction.Theimpactassessmentalsodeterminedthatthereismajorencroachment(>10%)intotheTreeProtectionZones(TPZ)ofthree(3)streettreeslocatedonDalgetyStreet.TheStructuralRootZones(SRZ)ofthesetreeswerecalculatedtodetermineifanystructuralrootswouldbeimpactedbytheproposeddevelopmentwhereitwasfoundthatthereisnoencroachment intoSRZof these treesby theproposeddevelopment. It is expectedthat the trees can remain viable, as the encroachment into the TPZ of these trees is<20%.The removal of all vegetation within the subject site is required to facilitate theproposeddevelopment.A Tree Protection Management Plan (TPMP) and tree protection measures are alsoincluded in this report. It is recommended all measures be followed tominimise theimpact of the proposed development on trees on adjoining properties and the naturestripdirectlyadjacenttothesubjectsite.

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TableofContentsExecutiveSummary........................................................................................................................2Methodology.....................................................................................................................................4Aimofreport.....................................................................................................................................4Documentsreviewed......................................................................................................................4Observations.....................................................................................................................................5Photographs...................................................................................................................................10TreeProtectionZones................................................................................................................11ImpactAssessment......................................................................................................................13Recommendations.......................................................................................................................16AppendixB:TreeProtectionMeasures................................................................................18AppendixC:GlossaryofTerms................................................................................................21AppendixD:References.............................................................................................................24AppendixE:QualificationsandExperience.........................................................................24AppendixF:ReportLimitationsandConstraints..............................................................25AppendixG:Disclaimer..............................................................................................................25

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Methodology

• MattJamesattendedsiteonthe5thofDecember2017.• DataacquiredisbasedonaVisualTreeInspection(VTA)fromtheground.• DBH(DiameteratBreastHeight)wasmeasuredat1.4metresusingadiameter

tape.• Heightandspreadareestimates.• DatawasrecordedusinganiPad.• Photographsweretakenusingadigitalcamera.

AimofreportTheintentionofthisreportisto:

• Assesstreeswithinthesubjectsite,treeslocatedonthenaturestripadjacenttothesite,andtreeslocatedinthereservetothenorthofthesitethatarewithin5metresofthesiteboundaries.

• Collect data detailing the current size (DBH, crown spread, height), condition(healthandstructure),andULE(usefullifeexpectancy).

• Assesspotentialconstructionimpactsonthetreesassessed.• ProvidedaTreeProtectionManagementPlan(TPMP).

Documentsreviewed

• Drawing:SK01.00Basement2• Drawing:SK01.01Basement1• Drawing:SK01.02GroundPlan• Drawing:SK01.03Level1• Drawing:SK01.04Level2• Drawing:SK01.05Level3• Drawing:SK01.06Level4• Drawing:SK01.07Level5• Drawing:SK01.08Level6• Drawing:SK01.09Level7

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ObservationsForthepurposeofthisreport,treeswithinthesubjectsite,treeslocatedonthenaturestrip, and trees within five (5) metres of the site located in Caloola Reserve wereassessed.Trees that are less than five (5)metres inheightwerenot assessed for thisreport.SeeTable1belowtreedata,andfigure1fortreelocations.The subject site is located in Monash Council Commercial 1 Zone – (C1Z). Planningoverlayspresent:

• DesignandDevelopmentOverlay–Schedule10(DDO10)• EnvironmentalAuditOverlay–(EAO)

35-41DalgetyStreetThe subject site comprises of a brick and claddingwarehouse and offices. There is aconcretecarparktothesouthwestofthesiteandaconcretedrivewaytothenortheastofthesite.Thetreeswithinthesubjectsiteconsistofthree(3)semimatureLophostemonconfertus(Queensland Brush Box) and two (2)matureLophostemon confertus.The trees are ingood to fair health with a good to fair structure. The trees are growing in a narrowconcrete gardenbed, and two (2) trees are impedingon the structure of the adjacentproperty.Thetreesareassessedashavingashortuseful lifeexpectancy(ULE)astheyhaveoutgrownthespace(figure2).CaloolaReserveA total of sixteen (16) trees are located within five (5) metres of the subject site inCaloolaReserve.Thetreesvaryintheirhealthandstructure,withmosttreesdisplayingstructuraldefects (figure3)andpoorhealth.Trees4,12,13,15,and16overhang thesubjectsitebytwo(2)metres(figure4).StreetTreesThree(3)treesarelocatedadjacenttothesubjectsiteonAtkinsonStreet,andfour(4)treesare locatedadjacent to thesubjectsiteonDalgetyStreet.Thegeneralhealthandstructure of the trees is assessed as fair. Tree 19 overhangs the subject site two (2)metres(figure5).

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Figure1.Treelocations

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SeeAppendixBfordescriptors

No Species CommonName Origin DBH

(mm)Height(m)

Spread(m) Health Structure ULE Age Comment

1 Eucalyptusviminalis MannaGum Native 464 10 7x9 Fair Poor Short Semimature Includedcodominantstems

2 Eucalyptusviminalis MannaGum Native 195

199 9 5x6 Fair Poor Short Semimature Includedcodominantstems

3 Acaciamelanoxylon Blackwood Native 165 6 4x3 Good Fair Medium Semimature

4 Eucalyptusviminalis MannaGum Native 222 6 6x4 Fair Fair Medium Semimature Overhangsboundaryby2m.

Rubbingonbuilding.

5 Acaciamelanoxylon Blackwood Native 163

125 5 5x4 Fair Poor Short Semimature Includedcodominantstems

6 Eucalyptusmelliodora YellowBox Native 329 13 5x5 Fair Poor Short Semimature Includedcodominantstems.

Psyllid

7 Acaciamelanoxylon Blackwood Native 248 8 5x5 Good Poor Short Semimature Includedcodominantstems.Borer

8 Eucalyptusspp. Gum Native 145

151 6 5x4 Poor Poor Short Semimature Possumgrazed

9 Angophoracostata

Smooth-barkedApple Native 174

176 8 5x4 Fair Fair Medium Semimature

10 Eucalyptusmelliodora YellowBox Native 209

221 10 5x5 Fair Poor Short Semimature Includedcodominantstems

11 Eucalyptusmelliodora YellowBox Native

177230228

10 6x5 Fair Poor Short Semimature Includedcodominantstems

12 Eucalyptusspp. Gum Native 150 5 6x5 Fair Fair Short Semimature Leaningtree.Overhangboundary

by2m.Rubbingonbuilding.

13 Eucalyptusviminalis MannaGum Native 295 10 5x5 Poor Fair Medium Semimature Leaningtree.Overhangboundary

by2m.Rubbingonbuilding.

Table1–TreeData

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No Species CommonName Origin DBH

(mm)Height(m)

Spread(m) Health Structure ULE Age Comment

14 Corymbiamaculata SpottedGum Native 346 13 6x6 Good Fair Medium Semimature

15 Eucalyptusleucoxylon YellowGum Native 925 14 12x10 Poor Fair Short Mature

Possumgrazing.Leafblisters.Basalshoots.Overhangsboundary

by2m

16 Eucalyptusdealbata SilverWattle Native 431

298 10 12x9 Fair Poor Short Mature Overhangsboundaryby2m

17Platanusorientalis'Digitata'

PlaneTree Exotic 65 5 3x3 Good Good Medium Semimature

18Platanusorientalis'Digitata'

PlaneTree Exotic 118 7 5x4 Good Fair Medium Semimature

19 Platanusxacerifolia LondonPlane Exotic 447 12 12x10 Good Fair Medium Mature Overhangssiteby2m

20 Quercusrobur EnglishOak Exotic 687 10 10x9 Good Fair Medium Mature 21 Quercusrobur EnglishOak Exotic 800 12 14x10 Good Fair Medium Mature 22 Quercusrobur EnglishOak Exotic 615 9 12x8 Good Fair Medium Mature 23 Quercusrobur EnglishOak Exotic 637 9 10x10 Good Fair Medium Mature 24 Lophostemon

confertusQueenslandBrushBox Native 269 9 5x5 Fair Fair Short Semimature Outgrownnarrowgardenbed

25 Lophostemonconfertus

QueenslandBrushBox Native

190110170208160

8 4x5 Fair Fair Short Semimature Outgrownnarrowgardenbed

26 Lophostemonconfertus

QueenslandBrushBox Native

132165

185887 4x4 Fair Fair Short Semimature Outgrownnarrowgardenbed

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No Species CommonName Origin DBH

(mm)Height(m)

Spread(m) Health Structure ULE Age Comment

27 Lophostemonconfertus

QueenslandBrushBox Native 238

258 10 5x6 Good Fair Short Mature Outgrownnarrowgardenbed

28 Lophostemonconfertus

QueenslandBrushBox Native 355 12 6x4 Good Fair Short Mature Outgrownnarrowgardenbed

DBH–DiameteratBreastHeightM–Metre

MM-millimetre

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Photographs

Figure2.Tree26hasoutgrownthespace

Figure5.Tree19overhangsthesubjectsiteby2metres

Figure3.Tree1haspoorstructureasaresultofthecodominantstems

withincludedbark

Figure4.Tree16overhangsthesubjectsiteby2metres

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TreeProtectionZones

A Tree Protection Zone (TPZ), as stated by the Australian Standard AS4970: 2009,Protectionoftreesondevelopmentsites,istheprincipalmeansofprotectionoftreesondevelopmentsite.TheTPZ isacombinationof therootareaandcrownarearequiringprotection.Itisanareaisolatedfromconstructiondisturbance,sothatthetreeremainsviable.TheAustralianStandardAS4970:2009 isbeingused inassessing theprotectionareasforeachtreeasitdescribesthebestpracticesfortheplanningandprotectionoftreesondevelopmentsites.IncalculatingtheradiusfortheTreeProtectionZones(TPZ),theDBH,measuredat1.4mfromtheground,ismultipliedby12.TheTPZrequirementsareasfollows:

• If the TPZ is encroached by less than 10%, the Australian Standard AS4970:2009states:detailedrootinvestigationsshouldnotberequired.

• If the TPZ is encroached bymore than 10%, the Australian Standard AS4970:2009states:theprojectArboristmustdemonstratethatthetree(s)wouldremainviable. The area lost to this encroachment should be compensated for elsewhereandcontiguouswiththeTPZ(figure6).

The Structural Root Zone (SRZ) is the area around the base of the tree required forstabilityintheground.Theserootsarefundamentalforthetreesstructureandhealth.Thestandardstates:

“Theareaaroundthebaseofatreerequiredforthetree’sstabilityintheground.Thewoodyrootgrowthandsoilcohesioninthisareaarenecessarytoholdthetree

Figure6.Examplesofencroachment(AS4970:

2009)

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upright.TheSRZisnominallycircularwiththetrunkatitscentreandisexpressedbyitsradiusinmetres.Thiszoneconsidersatree’sstructuralstabilityonly,nottherootzonerequiredforatree’svigourandlong-termviability,whichwillusuallybeamuchlargerarea.”(AS4970)

TocalculatetheSRZ, theequation is(D×50)^0.42×0.64,whereD is theDiameteratBase(DAB).Theeffectsofrootlossordamagebyanymeanscouldinclude:

• Lossofstabilityifstructuralwoodyrootsorevenlowerorderwoodyrootsarecut

• Reductioninwaterandnutrientuptake• Aneventuallossofleaves,reducedphotosynthesisandthussugarproduction• Decayasaresultofwounding• Predispositiontosoilbornepathogens

Table2.TreeProtectionZonesofretainedtrees

No DBH(mm)

TPZradius(m)

DB(m) SRZradius(m)

1 464 5.57 559 2.592 195199 3.36 377 2.203 165 1.98 228 1.784 222 2.66 280 1.945 163125 2.52 249 1.856 329 3.95 405 2.267 248 2.98 303 2.008 145151 2.25 245 1.839 174176 3.00 190223 1.9710 209221 3.60 344 2.1111 177230

2284.44 390 2.23

12 150 1.80 220 1.7513 295 3.54 343 2.1114 346 4.15 458 2.3815 925 11.10 832 3.0616 431298 6.24 520 2.5117 65 2.00 140 1.4518 118 1.42 178 1.6019 447 5.36 553 2.5820 687 8.24 810 3.0321 800 9.60 855 3.1022 615 7.38 715 2.8723 637 7.64 755 2.94

DBH–DiameteratBreastHeight.DB–DiameteratBase.M–Metre.MM-Millimetre

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ImpactAssessmentTheproposeddevelopmentwill require thedemolitionof the currentbuildingandallvegetation within the site, including Trees 24-28. The subsequent construction is tocomprise of a multi story apartment complex and two (2) basement levels. Newlandscapingisalsoproposedacrossthesite.Figure7andTable3belowdemonstratestheimpactsoftreeswithinthesubjectsiteandtreeslocatedonadjoiningproperties.

No TPZradius(m) Encroachment SRZradius(m) Encroachment1 5.57 0 2.59 02 3.36 0 2.20 03 1.98 0 1.78 04 2.66 0 1.94 05 2.52 0 1.85 06 3.95 0 2.26 07 2.98 0 2.00 08 2.25 0 1.83 09 3.00 0 1.97 010 3.60 0 2.11 011 4.44 0 2.23 012 1.80 0 1.75 013 3.54 0 2.11 014 4.15 0 2.38 015 11.10 7.57% 3.06 016 6.24 1.19% 2.51 017 2.00 0 1.45 018 1.42 0 1.60 019 5.36 5.74% 2.58 020 8.24 12.86% 3.03 021 9.60 16.78% 3.10 022 7.38 10.49% 2.87 023 7.64 6.19% 2.94 0

Table3.Individualencroachmentpercentages

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Figure7.IndividualTreeProtectionZonesand

constructionencroachments

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Minorencroachment

• Tree 15 – TPZ encroached by 7.57%. This is a minor encroachment as perAS4970, and as such, the tree is expected to remain viable during and afterconstruction.

• Tree 16 – TPZ encroached by 1.18%. This is a minor encroachment as perAS4970, and as such, the tree is expected to remain viable during and afterconstruction.

• Tree 19 - TPZ encroached by 5.74%. This is a minor encroachment as per

AS4970, and as such, the tree is expected to remain viable during and afterconstruction.Thecanopyofthetreeoverhangsthesubjectsiteby2metres,andmayrequireminorpruningtoensurethereisnotdamagetothecanopyduringconstruction.

• Tree 23 - TPZ encroached by 6.19%. This is a minor encroachment as per

AS4970, and as such, the tree is expected to remain viable during and afterconstruction.

MajorEncroachment

• Tree 20 – TPZ encroached by 12.86%. This is a major encroachment as perAS4970, therefore the SRZwas calculated to determine if any structural rootswould be impacted upon by the proposed development. There is no SRZencroachment,andwhiletheTPZencroachmentismajor,itisexpectedthetreecanremainviableduringandafterconstruction.

• Tree 21 –TPZ encroached by 16.78%. This is a major encroachment as per

AS4970, therefore the SRZwas calculated to determine if any structural rootswould be impacted upon by the proposed development. There is no SRZencroachment,andwhiletheTPZencroachmentismajor,itisexpectedthetreecanremainviableduringandafterconstruction.

• Tree 22 – TPZ encroached by 10.49% This is a major encroachment as per

AS4970, therefore the SRZwas calculated to determine if any structural rootswould be impacted upon by the proposed development. There is no SRZencroachment,andwhiletheTPZencroachmentismajor,itisexpectedthetreecanremainviableduringandafterconstruction.

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Recommendations

• Trees 24-28 are recommended for removal to facilitate the proposeddevelopment.Thetreesaregrowinginanarrowgardenbedandhaveoutgrownthespace.Theproposedlandscapingissufficienttooffsettheirremoval.

• Pruning of trees 4, 12, 13, 15, 16, and 19 is recommended to prevent canopydamageduringconstruction.

• ImplementtheTreeProtectionManagementPlanandTreeProtectionMeasuresasoutlinedinAppendixAandAppendixBofthisreport.

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AppendixA:TreeProtectionManagementPlanThisplaniscompiledwithreferencetotheAustralianStandardforProtectionOfTrees

OnDevelopmentSites;AS4970-2009.

Stage Objectives Description Actionby

Preliminary

ArboriculturalReport-

Aid to develop design

layoutEvaluatetreessuitableforretentionandmarkonplan

withindicativeTPZs.ProjectArborist

Arboricultural Impact

Assessment-Minimize impact on

retainedtreesWorkwiththedesignteamtoidentifytreescapableof

viable retention. Recommend measures necessary to

protectthetreesthroughouttheconstructionprocess.

ProjectArborist

Removalandpruningof

approvedvegetationRemoval and pruning of all

trees not cited on plan for

retention (in accordance

withAS4373)

SubmitManagementplantoCouncil.Seekpermission

to remove trees. Carry out approved removals.Grind

stumpsremovingdebris.

Project Arborist,

Council,

Arboricultural

contractors

Pre-construction

meetingEducate construction

managersAttendancerequiredbySiteSupervisor toexplain the

purpose and importance of TPZs and the

consequencesofignoringthem.

Project Arborist /

SiteSupervisor

Installation of TPZ

fencing and protection

measures

Use fencing, mulch and

other measures to protect

trees.

Apply forest mulch and install protection measuresdescribedinArboriculturalImpactAssessment.

Site Supervisor and

ProjectArborist

Encroaching on TPZ (if

required)Maintain the integrity of

TPZfencingAny breach of TPZ fencing to be ratified by the Site

SupervisorandsupervisedbytheProjectArborist.Site Supervisor and

ProjectArborist

Practical completion of

theprojectRemove protective

measuresPracticalcompletionoftheproject. Site Supervisor and

ProjectArborist

Meeting with

LandscapeSupervisorObserve and record details

ofadherencetoTPMPEducate andexplain consequencesof damaging trees

duringworks.Discussmattersthatarose.Project Arborist &

Landscape

Contractors

Finalcertification Assess condition of trees

afterconstructionA statement specifying that the completed works

carried out were in compliance with the approved

plans, and/or details of any deviations, and their

impactsonthetrees.

ProjectArborist

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AppendixB:TreeProtectionMeasures• SignsidentifyingtheTPZshouldbeplacedaroundtheedgeoftheTPZandbevisible

fromwithinthedevelopmentsite.• Fencingshouldbeerectedbeforeanymachineryormaterialsarebroughtontothe

site and before the commencement of works including demolition. Once erected,protectivefencingmustnotberemovedoralteredwithoutapprovalbytheprojectarborist.TheTPZshouldbesecuredtorestrictaccess.

Figure9.Exampleoffencing(AS4970:2009)

• IftheTPZistobeencroachedbyconstruction,manualexcavationoftherootsistobecarriedoutunderthesupervisionoftheprojectarboristtoidentifyrootscriticaltotreestability.

• Norootsgreaterthan25mmaretobecutunlesssupervisedbytheprojectarborist.• Rootsshouldbeprunedwithsharptoolssuchassecateurs,handsawsorchainsaws.

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• No roots within the TPZ are to be cut with machinery such as backhoes orexcavators.

• Whererootsareexposed,temporaryrootprotectionshouldbeinstalledtopreventthemdryingout.Hessiansheetingasmultiplelayersonexposedrootswouldreducethelossofmoisture.

• All services should be routed outside the TPZ. If underground services are to beroutedthroughtheTPZ,theyshouldbeinstalledbydirectionaldrillingormanuallyexcavatedtrenches.Directionalboringshouldbeatleast600mmdeep.

• If temporary access for machinery is required within the TPZ ground protectionmeasures will be required. The purpose of ground protection is to prevent rootdamage and soil compaction within the TPZ. Measures may include a permeablemembranesuchasgeotextilefabricbeneathalayerofmulchorcrushedrockbelowrumbleboard.

• ActivitiesgenerallyexcludedfromtheTPZincludebutarenotlimitedto:

o Machineexcavationincludingtrenchingo Excavationforsiltfencingo Storageo Preparationofchemicals,includingpreparationofcementproductso Parkingofvehiclesandplant

Figure10.GroundProtection(AS4970:2009)

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o Refuelingo Dumpingofwasteo Washdownandcleaningofequipmento Placementoffillo Lightingoffireso Soillevelchangeso Temporaryorpermanentinstallationofutilitiesandsignso Physicaldamagetothetree

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AppendixC:GlossaryofTermsAGE

Juvenile Juvenileorrecentlyplantedapproximately1-7years.SemiMature Treeactivelygrowing.Mature Treehasreachedexpectedsizeinsituation.Senescent Treeisovermatureandhasstartedtodecline.

USEFULLIFEEXPECTANCY–ULETheusefullifeofatreeisanestimateofhowlongatreeislikelytoremaininthelandscapebasedonhealth,amenityandrisk.LongULE Trees that appear to be retainable with an acceptable level of risk for

morethan40years.1. Structurally sound trees located in positions that can accommodate

futuregrowth.2. Storm damaged or defective trees that could be made suitable for

retentioninthelongtermbyremedialtreesurgery.3. Trees of special significance for historical, commemorative or rarity

reasons thatwouldwarrant extraordinary efforts to secure their long-termretention.

MediumULE Treesthatappeartoberetainablewithanacceptablelevelofriskfor15to40years.

1. Treesthatmayonlylivebetween15and40years.2. Trees that may live formore than 40 years but would be removed to

allowthesafedevelopmentofmoresuitableindividuals.3. Treesthatmayliveformorethan40yearsbutwouldberemovedduring

thecourseofnormalmanagementforsafetyandnuisancereasons.4. Stormdamageordefectivetreesthatcanbemadesuitableforretention

inthemediumtermbyremedialwork.

ShortULE Treesthatappeartoberetainablewithanacceptablelevelofriskfor5to15years.

1. Treesthatmaylivefor5to15years.2. Trees that may live formore than 15 years but would be removed to

allowthesafedevelopmentofmoresuitableindividuals.3. Treesthatmayliveformorethan15yearsbutwouldberemovedduring

thecourseofnormalmanagementforsafetyandnuisancereasons.

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4. Stormdamagedordefectivetreesthatrequiresubstantialremedialworktomakesafeandareonlysuitableforretentionintheshortterm.

Remove Treeswithahighlevelofriskthatwouldneedremovalwithinthenext5years.

1. Deadtrees.2. Dyingorsuppressedanddecliningtreesthroughdiseaseorinhospitable

conditions.3. Dangeroustreesthroughinstabilityorrecentlossofadjacenttrees.4. Dangerous trees through structural defects including cavities, decay,

includedbark,woundsorpoorform.5. Damagedtreesthatareconsideredunsafetoretain.6. Trees that will become dangerous after removal of other trees for the

abovereasons.CONDITIONThis is a combined indicator of ‘health’ and ‘structure’ based on the followingdescriptors:HEALTH

Good Foliage of tree is entire, with good colour, very little sign ofpathogens and of good density. Growth indicators are good ie.Extension growth of twigs and wound wood development.Minimalornocanopydieback(deadwood).

Fair Treeisshowingoneormoreofthefollowingsymptoms;<25%

deadwood,minor canopydie back, foliage generallywith goodcolour though some imperfections may be present. Minorpathogen damage present, with growth indicators such as leafsize, canopy density and twig extension growth typical for thespeciesinthislocation.

Poor Tree is showingoneormoreof the followingsymptomsof tree

decline; > 25% deadwood, canopy die back is observable,discoloured or distorted leaves. Pathogens present, stresssymptomsareobservableasreducedleafsize,extensiongrowthandcanopydensity.

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Deadordying Tree is in severe decline; > 55% deadwood, very little foliage,possiblyepicormicshoots,minimalextensiongrowth.

STRUCTURE

Good Trunk and scaffold branches show good taper and attachmentwithminorornostructuraldefects.Treeisagoodexampleofthespecies with a well-developed form showing no obvious rootproblemsorpestsanddiseases.

Fair Tree shows someminor structural defects orminor damage to

trunkeg.barkmissing, therecouldbecavitiespresent.Minimaldamagetostructuralroots.Treecouldbeseenastypicalforthisspecies.

Poor There are major structural defects, damage to trunk or bark

missing. Co-dominant stems couldbepresent orpoor structurewith likelypointsof failure.Girdlingordamaged rootsobvious.Treeisstructurallyproblematic.

RetentionValue

• High • Atreethatisingood-fairhealthandstructurewithalongULE• Atreethathascultural,botanical,orlandscapesignificance• A tree that is not located within the subject site i.e. nature strip,

adjoiningproperties.• Medium

• AtreethatisinfairhealthandstructurewithamediumULE

• Low • AtreethatisinpoorhealthandstructurewithashortULE.• Weedspecies.

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AppendixD:References

• StandardsAustralia2009SAIGlobal-AS4970ProtectionOfTreesOnDevelopmentSites

AppendixE:QualificationsandExperience

MattJameshasthefollowingqualificationsandexperience:GraduateCertificateinArboriculture(completing)-2017DiplomaArboricultureQTRA(QuantifiedRiskAssessment)registereduser.ArboricultureAustraliaNationalConference:2016TreeAnatomyWorkshop(MarkHartley)2016CertNutritionFarming201510Yearsindustryexperience

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AppendixF:ReportLimitationsandConstraints

• Thereportislimitedtothetimeofinspection.• Thereportreflectsthetreesasfoundonthedaysofinspection.Anychangesto

siteconditionsorsurroundings,suchasconstructionworksorlandscapeworksmayalterthefindingsofthereportsubjecttoconditionsandrecommendationsassetoutwithinthereport.

• Thereport isbasedon the inspectionand thematerialavailableat the timeofinspectionorthatinformationfurthertotheinspectionfoundwithinthereport.

• Nosoilsamplesweretakenforlaboratoryanalysis.• Treerootswerenot inspectedbelowgroundexceptwherepreviouslyexposed

and/orwhereotherwisestatedwithinthereport.• Measurementsmaybeapproximatesonlyandgenerallynottoscale.• All imagessuppliedare interpretationsonlyandshouldnotbetakenastrueat

timeof inspectionorindicativeoftreeconditionorstatusattimeof inspectionortimeofreportrelease,inclusiveofGoogleimagesifapplicable

AppendixG:DisclaimerAlthoughMELBOUNRETREECAREP.L.usesallduecareandskill inprovidingyoutheinformationmadeavailableinthisreport,totheextentpermittedbylawMELBOURNETREE CARE P.L. otherwise excludes all warranties of any kind, either expressed orimplied.Totheextentpermittedbylaw,youagreethatMELBOURNETREECAREP.L.isnotliabletoyouoranyotherpersonorentityforanylossordamagecausedorallegedto have been caused (including loss or damage resulting from negligence), eitherdirectly or indirectly, by your use of the information (including by way of example,Arboricultural advice) made available to you in this report. Without limiting thisdisclaimer, innoeventwillMELBOURNETREECAREP.L.be liable toyou forany lostrevenueorprofits,orforspecial,indirect,consequentialorincidentaldamage(howevercausedandregardlessofthetheoryof liability)arisingoutoforrelatedtoyouruseofthat information, even if MELBOURNE TREE CARE P.L. has been advised of thepossibilityofsuchlossordamage.