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Summary of the Environmental Impact Statement

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CÔTÉ GOLD PROJECT Chester and Neville Townships, Ontario ENVIRONMENTAL IMPACT STATEMENT / DRAFT ENVIRONMENTAL ASSESSMENT REPORT EXECUTIVE SUMMARY Submitted to: IAMGOLD Corporation 401 Bay Street, Suite 3200 Toronto, Ontario M5H 2Y4 Submitted by: AMEC Environment & Infrastructure, a Division of AMEC Americas Limited 160 Traders Blvd., Suite 110 Mississauga, Ontario L4Z 3K7 May 2014 TC121522
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  • CT GOLD PROJECT Chester and Neville Townships, Ontario

    ENVIRONMENTAL IMPACT STATEMENT /

    DRAFT ENVIRONMENTAL ASSESSMENT REPORT EXECUTIVE SUMMARY

    Submitted to: IAMGOLD Corporation

    401 Bay Street, Suite 3200 Toronto, Ontario

    M5H 2Y4

    Submitted by: AMEC Environment & Infrastructure, a Division of AMEC Americas Limited

    160 Traders Blvd., Suite 110 Mississauga, Ontario

    L4Z 3K7

    May 2014

    TC121522

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES1

    INTRODUCTIONANDENVIRONMENTALASSESSMENTCONTEXTIAMGOLD Corporation (IAMGOLD) is a leading midtier goldproducerheadquartered inToronto,Ontario. IAMGOLD is listedon the Toronto Stock Exchangemain board under the symbol"IMG". IAMGOLD currently owns six mines in Canada andabroad, and is in the process of developing four additionalprojects,includingtheCtGoldProject(theProject).

    IAMGOLD acquired Trelawney Mining and Exploration Inc.(Trelawney) in2012.Trelawneyhadbeen exploring theProjectpropertysince2009,withtheobjectiveofdevelopinganopenpitgoldmineandprocessplant.AsofDecember31,2012,theCtGold drill hole database contained results of 293 diamond drillholesforatotalof158,047m.IAMGOLDhasalsoundertakenorcommissioned environmental, hydrogeological, geotechnical,mineralogical, engineering, logistics and economic studiesrelatedtothepotentialdevelopmentoftheproperty.

    ProjectName: CtGoldProject

    Proponent: IAMGOLDCorporation

    PrimaryContact: IAMGOLDCorporation:StevenWoolfenden,Manager,CorporateEnvironmentalAssessmentsandApprovals401BayStreet,Suite3200Toronto,Ontario,[email protected]:4165942884

    IAMGOLDhasbeenworkingcloselywiththeProvincialandFederalregulatoryagenciestoharmonizethe Federal and Provincial Environmental Assessment (EA) processes applicable to the Ct GoldProject(theProject)and,wherepossible,toalignpublicconsultationperiodstomeetbothFederalandProvincialrequirements,minimizingduplicationofeffort.

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES2

    IAMGOLD submitted aProjectDescription to theCanadianEnvironmentalAssessmentAgency (theAgency)onMarch15,2013.BasedontheProjectDescription, theAgencydeterminedthataFederalEA, pursuant to theCanadianEnvironmentalAssessmentAct 2012 (CEAA 2012),was required.TheAgencythenissueddraftEISGuidelinesonMay13,2013todeterminethescopeoftheEArequiredfortheProject.OnJuly9,2013,IAMGOLDwasinformedthataStandardAssessmentwouldberequiredfortheCtGoldProjectandfinalEISGuidelineswere issuedbytheAgency,therequirementsofwhichthisEAReportisintendedtofulfil.

    IAMGOLD initiated the Provincial EA process, through the submission of aDraft ToR, to facilitateongoingpublicconsultationontheProject.ADraftToRwasissuedfora30daypublicreviewcommentperiodbetweenMay 10,2013 and June9, 2013.TheDraftToRwas subsequently revised,basedoncommentson thedocumentand resultsofopenhouses,andwas reissuedas theProposedToR foranother30daypubliccommentreviewperiod fromJuly19,2013andAugust19,2013.TheProposedToRwasapprovedbytheOntarioMinisteroftheEnvironmentonJanuary14,2014.

    This EA report has been prepared to provide Federal and Provincial authorities with informationregarding the proposed Ct Gold Project in order to assist with decisionmaking by the FederalMinisteroftheEnvironmentregardingtheapplicabilityoftheCEAA2012.Itisalsointendedtoprovidesufficient informationfortheOntarioMinisteroftheEnvironmenttoapprovetheProjectpursuanttotheOntario EnvironmentalAssessmentAct. The Federal andProvincial government authorities haveagreedthatasingleEAreportwillbeusedforthecoordinatedEAprocess.

    PROJECTOVERVIEWThe Project is located in theChester and Neville Townshipsin the District of Sudbury,northeastern Ontario. It isapproximately 20kilometres(km) southwest of Gogama,130km southwest of Timmins,and 200km northwest ofSudbury,seeFigureES1.

    IAMGOLD proposes toconstruct, operate andeventually rehabilitate a new

    openpitgoldmine,and iscurrentlyconductingengineeringstudiestofurtherconfirmanddeterminethetechnicalandeconomicaspectsoftheProject.

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES3

    Thepreliminarysite layout (seeFigureES2)proposes toplace the requiredminerelated facilities incloseproximitytotheopenpit,totheextentpracticable,onlandsthatareleasedand/or,onpatentedlands held fully and/or jointly by IAMGOLD. Open pit mining operations will occur at a rate ofapproximately60,000tonnesoforeperday.Overburden,minerockandlowgradeoreextractedfromtheopenpitwillbestockpiledinanearbyminerockarea(MRA).

    Oreprocessingwillbecarriedoutbyconventionalmethods,usingacombinationofgravityseparationandcyanidationforgoldrecovery,followedbyinplantcyaniderecycleanddestruction.Tailingswillbestored ina constructed tailingsmanagement facility (TMF).Ahighproportionof theoreprocessingplant water requirement will derive from water recycled from the TMF, augmented by open pitdewatering,aswellasrunoffcollectedfromthevariousstockpileareas,withaseasonalneedforfreshwatermakeup(fromMesomikendaLake).ExcesssitewaterwillbedischargedtoBagsverdCreekviaapolishing pond and/or additionalwater treatment, if required. Such dischargewillmeet applicableFederalandProvincialeffluentdischargerequirementsandwillbeprotectiveofreceivingwateraquaticlife.

    Miningoperationswillbesupportedbythedevelopmentofanexplosivesmanufacturingandstoragefacility.Amaintenancegarage,warehouseandadministrationcomplexwillbedevelopedadjacenttotheoreprocessingplant.

    Anonsiteaccommodationscomplexwillalsobedevelopedatthestartofconstructionwithacapacitytohost1,500workers.Thiscomplexwillprovideaccommodation fortheconstructionandoperationsworkforce.SomeProjectpersonnelmaycommutefromGogamaandfromtheMattagamiFirstNationreserve. Potable water will be extracted primarily from groundwater resources. Nonhazardousdomesticsolidwasteswilllikelybedepositedinanonsitelandfill,unlessasuitableoffsitelandfillwithsufficientcapacityisidentified.IAMGOLDisplanningoncontinuingandexpandingitsexistingrecyclingprogramwith theaim tominimize solidwastes.Domestic sewagewillbe treatedusingapackagedsewage treatment plant or equivalent. Hazardous solid and liquidwastewill be hauled off site bylicensed contractors to licensed storage facilities. Opportunities to recycle some of the hazardouswaste,suchasusedoil,willbeinvestigated.

    InitialconstructionpowerwillbeprovidedbytheexistingtransmissionlineconnectiontotheProvincialelectricalgrid,supportedbydieselpowergenerator(s)(lessthan5MWrequired).Permanentpowerwillbeprovided throughadedicatedconnectiontoaproposednew230kVtransmission line,originatingfromasubstationlocatedwithintheCityofTimmins.

    Aspartoftheproposeddevelopmentoftheopenpit,CtLakewillneedtobedrained.Itisexpectedthat portions of Three Duck Lakes, Chester Lake, Clam Lake and theMollie River system will bedammedand/orwillrequirerealignmenttoallowforthesafedevelopmentandoperationoftheopenpit.ItiscurrentlyplannedthatBagsverdCreekwillalsoberealignedtoallowdevelopmentoftheTMF.

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES4

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    CITY OF TIMMINS

    GOGAMA

    CITY OF GREATER SUDBURY

    PROJECTSITE

    FLYING POST IR. 73

    MATACHEWAN IR. 72

    MATTAGAMI IR. 71MOUNTBATTEN IR. 76A

    WAHNAPITAE IR. 11

    WHITEFISH LAKE IR. 6

    SAGAMOK IR

    POINT GRONDINE IR. 3WHITEFISH RIVER IR. 4SERPENT RIVER IR. 7

    MISSISSAGI RIVER IR. 6

    NightHawkLake

    MinisinakwaLake

    WanapiteiLake

    Lake Huron

    RushLake

    HorwoodLake

    Hwy 101

    Hwy 101

    Hwy 14

    4

    Hwy 560

    Hwy 560Hwy 144

    Hwy 810 Hwy 17

    Hwy 64Hwy 637

    Hwy 17

    Hwy 108

    Hwy 17

    Hwy 546

    District of CochraneDistrict of Timiskaming

    District of TimiskamingDistrict of Sudbury

    District of SudburyDistrict of Algoma

    FRENCH RIVER IR. 13

    DUCK LAKE IR. 76B Englehart

    ElliotLakeSudbury

    KirklandLake

    Timmins

    350000 400000 450000 500000 550000

    510000

    0515

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    520000

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    CT GOLD PROJECT

    SCALE:PROJECT No: TC121522

    DATE: April 2014FIGURE: ES-1

    1:1,450,000

    Project Location

    Area Enlarged

    NOTES:- All base data on this map was extacted from Land Information Ontario, MNDM, OBM Ontario Digital Geospatial Database and Ontario Road Network Database._ Project Site Location !. Regional Communities

    Major RoadsRailwayLower Tier MunicipalityBoundaryUpper Tier MunicipalityBoundary

    First Nation ReserveConservation Reserve (Regulated)Provincial ParkWaterbody / Large WatercourseWooded Area

    500 Km

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES6

  • E

    E

    E

    E

    E

    EE E E

    E

    EE

    E

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    E

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    Open Pit

    Realignment connectLittle Clam Lake to Bagsverd Lake (South Arm)

    Realignment connect Clam lake and LittleClam Lake

    Realignment Chester Lake to Clam Lake

    Proposed WasteDisposal Site

    AggregatePit #1

    Shining Tree 230 kV Transmission Line AlignmentEmulsionPlant

    Fresh Water LineBagsverd Creek toWeeduckLakeRealignment

    Realignment connect Weeduck Lake and Three Ducks Lake (upper)

    Mine Water Pond AreaProcessing Plant

    Tailings andReclaim Pipeline

    BagsverdCreekRealignment

    Camp Site

    SecurityOffice

    Fuel Bay

    Low-grade Ore Stockpile

    AggregatePit #3

    MainAccessRoad

    MNR Landfill

    Cross-Country 230 kV Transmission Line Alignment

    PolishingPond Area

    MRA

    TMF

    MesomikendaLakeSubwatershed

    Mollie RiverSubwatershed

    UnnamedLake #1UnnamedLake #2

    Inlet

    BerniceCreek

    NevilleLake

    WolfLake

    Upper St.Louis LakeLoucksLake

    SusanneLake

    BagsverdLakeErringtonLake

    MooreLake

    WeeduckLake

    BenneweisLakeThree DuckLakes(Upper) BerniceLake

    ClamLake

    ThreeDuck Lakes(Middle)LorryLakeChainLake

    AttachLakeOctaveLake

    SawpeterLakeRoundLakeGeorgeLake

    Three DuckLakes(Lower)

    SchistLake

    ChesterLake

    SchouLake

    UnnamedPond

    Errington Creek

    St. Louis

    Creek

    Bagsverd Creek

    Mollie River

    Bagsv erdCreek

    Clam Cree k

    Hwy 144

    426000 428000 430000 432000 434000 436000 438000

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    CT GOLD PROJECT

    SCALE:PROJECT No: TC121522

    DATE: April 2014FIGURE: ES-2

    1:70,000

    Preliminary Site Plan

    Existing Intermittent WatercourseExisting Permanent WatercourseExisting WaterbodiesHighwayLocal RoadSubwatershed BoundaryWooded Area

    Open PitPotential Discharge LocationsFacilitiesDamMain Access RoadAccess RoadCross-Country 230 kVTransmission Line AlignmentShining Tree 230 kV Transmission Line AlignmentTailings and Reclaim Pipeline

    Fresh WaterWatercourse Realignment

    E Proposed WaterFlow DirectionProposed Lake AreaPolishing PondLow-grade Ore StockpileProposed Mine Rock Area (MRA)Proposed Tailings Management Facility (TMF)Proposed Landfill

    AA MNR Landfill

    NOTES:- Ontario base data extracted from Land Information Ontario (MNR)- TMF and subwatershed provided by Golder Associates.- Watercourse realignment and proposed lake area provided by Calder Engineering.- Surface infrastructure, open pit, landfill, MRA and transmission lines provided by IAMGOLD.

    MesomikendaLake

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES8

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES9

    SCOPEOFTHEPROJECTANDASSESSMENT

    PhysicalWorks

    PhysicalworksrelatedtotheProjectareproposedtoconsistof:

    Openpit:approximately210hectares (ha) inarea,withadepthofapproximately550m.Miningwilloccurata rateof approximately 60,000tpd of ore production over anapproximate15yearperiod.

    Mine Rock Area (MRA): approximately 20million tonnes(Mt)ofoverburdenand850Mtofminerock,notrequiredfor site constructionpurposes,willbe stored in a surfacestockpile.Alowgradeorestockpilewillalsobedeveloped.

    Ore processing plant: ore will be crushed, ground andprocessed on site to recover gold. The exact goldproduction ratewilldependonoregradeandgoldprices.Thedorgoldbarproductwillthenbesecurelytransportedoffsitebyroad.Typically,foraprojectofthissize,thefinalproductisshippedoffsitebytruckonceperweek.

    TailingsManagement Facility (TMF): a preferred area forTMFdevelopmenthasbeenselected.ThisTMFcoversanareaofapproximately840haandwillprovidecapacityforthestorageofapproximately261Mtof tailingsover theexpectedProject life.Themaximumprojecteddamheightsareexpectedtobeintherangeof40mto45mabovegrade.

    Watermanagement facilities: the principal flows at the Project site will bemanaged withdrainageworks,pipelinesandwatermanagementponds.Watercourse realignmentswillalsoberequiredaroundtheopenpitandTMF.

    Transmission line:powerduringtheoperationsphaseoftheProjectwillbesuppliedbyanew230kV transmission line connected to the existing Hydro One Network in Timmins at thePorcupinesubstation.

    Associated buildings, facilities and infrastructure: additional permanent onsite facilitiescurrentlyplanned,areexpected to include:amaintenancegarage,a fueland lube facility,awarehouse, an administration complex, a construction and operations accommodationscomplex, an explosivesmanufacturing and storage facility, an aggregate plant and pit, fuelstorage facilities,potableandprocesswater treatment facilitiesanddomesticand industrialsolidwastehandlingfacilities.Thesefacilitieswillbesupportedbyrelatedonsiteaccessroads,pipelinesandpowerinfrastructure.

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES10

    The proposed Project layout, showing themain Project components and associated facilities andinfrastructure,isshowninFigureES2andFigureES3.

    ProjectPhases

    Primaryconstructionphaseactivitieswillinclude:

    procurementofmaterialandequipment;

    movementofconstructionmaterialstoselectlaydownareasatandneartheProjectsite;

    constructionofadditionalsiteaccessroads;

    construction of dams and water realignment channels/ditches in preparation for thedevelopmentoftheopenpit,aswellastheconstructionoftheTMF;

    construction/placementofcompensatoryfishhabitatwithinchannelrealignmentsandworksauthorizedtooffsetthelossoflakehabitat;

    dewateringofCtLaketoallowfordevelopmentoftheopenpit;

    strippingofoverburdenandinitiationofopenpitminedevelopment;

    development of aggregate source(s) anticipated to be principally for concretemanufacture,foundationworkandTMFdamfilterzones;

    establishmentofsiteareadrainageworks,includingpipelinesfromfreshwater/recycledwatersources;

    developmentandinstallationofconstructionfacilities,includinglaydownareas,campfacilities,augmentationofelectricalsubstationcapacityandotherrelatedconstructioninfrastructure;

    constructionofassociatedbuildingsand facilities,suchasa fuelbay,sewagetreatmentplantandlandfill(ifdeveloped);

    preparationofonsitemineralwastehandlingfacilities,includingtheTMFdams;

    constructionandenergizingofa230kVfeedertransmissionline,includinganonsiteelectricalsubstation;and

    expansionofenvironmentalprotectionandmonitoringplan(s)forconstructionactivities;

  • CITY OF TIMMINS

    GOGAMA

    FLYING POST IR. 73

    MATACHEWAN IR. 72

    Mattagami IR. 71

    Hwy 101

    District of CochraneDistrict of Timiskaming

    Wapus Creek

    Schist Lake

    La Motte Lake

    BiscotasiLake

    GroundhogRiverWaterway

    MacmurchyTownshipEnd Moraine

    Grassy River-MonoLake Lowlands andFerris Lake Uplands

    Dana-JowseyLakes

    Akonesi Chain ofLakes Complex

    BromleyLake

    WhalsomLakeMesomikendaLakeRiceLake

    PebonishewiLakeRae LakeNevilleLake

    OpeepeeswayLakeBagsverdLakeClamLakeChesterLake MollieLake

    KetchiniLake

    MinisinakwaLake

    NightHawkLake

    KenogamissiLake

    PeterlongLakeKenogamingLakeHorwoodLake

    MattagamiLake

    SinclairLake

    NabakwasiLake

    RushLake

    GroundhogLake

    KapiskongLake

    TatachikapikaLake

    Hwy 560

    Hwy 101 W

    Hwy 101 W

    Hwy 144

    SubstationPorcupine(500 kV)

    SubstationTimmins(115 kV)

    CrossingStation

    ShiningTree DS(115 kV)

    400000 410000 420000 430000 440000 450000 460000 470000 480000 490000 500000 510000

    526000

    0527

    0000

    528000

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    CT GOLD PROJECT

    SCALE:PROJECT No: TC121522

    DATE: April 2014FIGURE: ES-3

    1:550,000

    NOTES:- All base data on this map was extacted from Land Information Ontario, MNDM, OBM Ontario Digital Geospatial Database and Ontario Road Network Database.Proposed Site Facilities Proposed Cross-Country 230 kV Transmission Line AlignmentProposed Shining Tree 230 kV Transmission Line AlignmentWaterbody / Large WatercourseWooded Area

    RailwayHighway/ExpresswayLocal RoadFirst Nation ReserveConservation Reserve (Regulated)Provincial Park

    Proposed Transmission Line Alignment Alternatives

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES12

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES13

    Activitiesthatwillbecarriedoutduringtheoperationsphaseareanticipatedtoinclude:

    oreandminerockextractionactivities;

    oreprocessing (gravityseparationandcyanidation,withacyanidedestructionprocess,usingrecycledwaterasmuchasfeasible);

    ongoingmanagementofchemicalsandwastes;

    watermanagement/treatment;

    environmentalmonitoringandreporting;

    followupenvironmentalstudies;and

    progressivesitereclamation,whereandtotheextentpractical.

    ThedecommissioningphaseactivitieswillconsistoftheclosureandreclamationofthevariousProjectcomponents, includingthe230kVtransmission line,shouldthetransfertoautilityprovenotfeasible.The objective of closure is to reclaim the Project site area to as near a naturalized and productiveconditionaspossibleuponcompletionofmining.

    Thepostclosurephasewillbecarriedoutintwodistinctstages.Followingtheremovalofinfrastructureandwaste,aswellas the revegetationofdisturbedareas, theopenpitwillcontinue to floodduringpostclosurestage I. It isanticipatedthatthisstagecould lastapproximately50to80years.Floodingwilloccur throughnaturalgroundwater infiltrationandprecipitation,aswellasbyactive fillingwithwater collected in someorallof theMRA seepage collectionponds. If thewaterquality isdeemedsuitablefordischargetotheenvironment,pumpingfromtheseepagecollectionpondsaroundtheMRAtothepitwouldcease.WatercourserealignmentsandassociateddamswillbeleftinplaceduringpostclosurestageI.

    PostclosurestageIIisthefinalstageofrehabilitationofthesiteandcommencesoncetheopenpitiscompletely flooded.Themainobjective is to reincorporate theopenpit lake into theexistingwatersystemsandtoreturnthesubwatershedstotheirpreminingconditions,asmuchaspracticable.

    Apreliminary schedule for thedevelopmentof theProjecthas the constructionphase commencingaftercompletionofthecoordinatedFederalandProvincialenvironmentalassessment(EA)processandthe feasibility studywhich is scheduled to be completed early 2016. The decision to proceedwithconstructionwilldependon theProjecteconomics,which isbasedon theprojectedgoldprice.Theoperations phase is expected to start approximately two years following the commencement ofconstructionandtocontinuefora15yearmine life,basedontheknownreserves.Theclosurephasewill requireapproximatelytwoyearsandthepostclosurephase isanticipatedtotakebetween50to80years.

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES14

    DESCRIPTIONOFTHEENVIRONMENTBaseline information for theProjectwas collected for eachdisciplineof thephysical,biological andhumanenvironments.Extensive studieswereconducted in2012and2013 inorder to informProjectdesigns,provide referencevalues for futuremonitoringactivitiesand toallow for theassessmentofpotentialProjecteffectsontheenvironment.

    Climate

    Theclimateat theProjectsite is typicalofnortheasternOntario,experiencingshort,warmsummersand long, coldwinters. Longterm climate statistics for the regional climate stationsmaintained byEnvironmentCanadaaremonitored inTimmins,ChapleauandSudbury,and indicatea totalannualprecipitationof800mm to900mm,with29% to37% fallingas snow in the region.Annualaveragetemperatures range from 17C to 19C,withminimumdaily temperaturesoccurring in JanuaryandmaximumdailytemperaturesoccurringinJuly.

    AirQuality,NoiseandVibration

    TheProjectsiteislocatedinaremoteareainaruralsetting.RegionalairqualitydatafromMinistryoftheEnvironment(MOE)stations, locatedatthenearesturbancentres(Sudbury,SaultSte.MarieandNorthBay),isconsideredtobeconservativewhenusedasexistingbaselinedatafortheregionalstudyarea.Regionalairqualityisconsideredtobegoodduetotheruralsetting,andisinfluencedbynaturalandmanmade emissions borne on southernwinds.Air quality data collected at the Project site isconsistentwith the regionalsettingwithnosignificantanthropogenicsourcesofairemissions in thevicinity.

    The noise survey data indicates that the environment in the regional and local study areas ischaracteristicofarural(Class3)area, inaccordancewithMOEguidelinepublicationNPC232averagenoiselevelsare34dBA(evening/night)and44dBA(daytime).

    GeochemistryandGeology

    TheProjectarea is located in theSwayzeGreenstone Belt, an extension of theAbitibiGreenstoneBeltlocatedwithintheSuperior province. The Swayze beltcontainsbothextrusiveandintrusiverockswithcompositionsrangingfromultramaficto felsic. It also contains chemical andclastic sedimentary rocks which mainlyoccur near the top of successions. TheCt Gold deposit is hosted within theChester Granitoid Complex, which

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES15

    comprisesthenorthernedgeoftheRamseyAlgomagranitoidcomplex.

    Selectedsamplesofoverburdenandrockavailablewereanalysedtoscreenforthepotentialofmetalleachingandacidrockdrainage.Testresults indicateavery lowpotentialformetal leachingandacidrockdrainage for tailingsandmine rockmaterials.Overburdenmaterials in thevicinityof the futureopenpitwerealsoassessedinasimilarmannerandlikewiseindicatelittlepotentialformetalleachingandacidrockdrainage.Geochemicalinvestigationsareongoingtofullycharacterizeminerock,tailingsandothermaterialstobeproducedorusedbytheProjecttoguidedesignandengineeringstudies.

    Results todate indicated that the likelihoodofnetacidconditionsoccurring in themine rockpiles isconsideredtobeverylow.Inclusionofthelimitedamountofpotentiallyacidgeneratingmaterialswiththe bulk of the mine rock is deemed to be an appropriate management method and as such,segregationofpotentiallyacidgeneratingmaterialsisnotnecessary.

    Hydrology&Hydrogeology

    TheProject site is locatedwithin theUpperMattagamiRiver Watershed, north of the intercontinentalwatershed divide between the James Bay and GreatLakesWatersheds,whichdrainsnorthward through theCity of Timmins and ultimately to James Bay. SurfacewaterflowsattheProjectsitearecontrolledbyanumberof lakes and creekswhich flow to theMollieRiver andMesomikenda Lake prior to discharging to theMinisinakwa Lake and ultimately theMattagami River.SurfacewaterflowpathsattheProjectsitearecurrentlymonitored by 14 hydrological stations distributedthroughout the Mesomikenda Lake and Mollie RiverSubwatersheds.Meanannual runoff for the region is inthe range of 300mm to 350mm, and groundwaterrecharge to streamflow is estimated at an annualaverage of 0% to 20%, indicating that surface flow isdominantintheregionalsystems.

    TheMattagamiRiverupstreamoftheCityofTimminsWaterFiltrationPlant(includingtheProjectsite)is within the Intake Protection Zone3 in the context of the Mattagami Conservation AuthorityProvincialDrinkingWaterSourceProtectionProgram.

    Groundwater is rechargedas infiltratingprecipitation is inferredona regional level to flow from thesouthsouthwest to the northnortheast. On a local level, groundwater flow is controlled by thetopography, flowing from highelevation recharge areas to discharge at lowlying areas and nearbysurfacewaterfeaturesandwetlands.

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES16

    Themovementofgroundwaterwithinoverburden throughout theProject site ishighlyvariableandtypicalofgranulartofinegranularmaterialssuchasgravelandsandmixtures.Granulartillmaterials,withequallyhighpermeabilityasoverburden,wereobservedatdepthinseverallocations,particularlyin the lowlying areas along the Mollie River and the Bagsverd Creek valleys. A wide range ofgroundwatermovement through thebedrockwasmeasured,as theupper10mconsistsof fracturedbedrock, while at greater depth there is unfractured bedrock. Groundwater movement generallydecreaseswithdepthwhichistypicalintheCanadianShield.

    SurfaceWater,SedimentandGroundwaterQuality

    Surfacewaterqualitysamplingwascompletedat22 locations,which includednumeroushydrologicalstationsneartheProjectsite,andresultswerereferentiallycomparedtowaterqualitystandardsandguidelines. The overallwater quality observed in the study area is considered typical of lakes andwatercoursespresentintheregionsoftheCanadianShield.Theresultsindicatethatatsomelocationstheconcentrationsof someparameterswereconsistentlyoroccasionallygreater than theProvincialWaterQualityObjectivesandCanadianEnvironmentalQualityGuidelinesfortheprotectionofaquaticlife. This is because flow is influenced by bedrock outcrops, and concentrations that exceedwaterquality criteria likely reflect the influenceofnaturalmineral ladenbedrockweatheringprocessesonsurface water quality. Water column profiling results indicate that most lakes in the study areaexperience a turnover during spring, and the profiles of dissolved oxygen, temperature, andconductivity(toalesserextent)indicatethatthewatercolumnisstratifiedfrommidtolatespringandthroughthesummermonths.

    Sediment analysis indicated good sediment quality,with themajority of parameter concentrationsbelowProvincialSedimentQualityGuidelinesandFederalCanadianEnvironmentalQualityGuidelines.Notedexceedances for totalorganiccarbonweredeemed typical innorthernOntario lakesdue toanaturally high organic content. Some metal parameters were detected at higher concentrations(copper, iron and magnesium) and are similarly attributable to the weathering of the underlyingmineralladenbedrock.

    Groundwater quality results indicate that field pH, aluminum, arsenic, cadmium, chromium, cobalt,copper, iron,molybdenum, silver, tungsten, uranium, vanadium, zinc, unionized ammonia and freecyanide were occasionally present in concentrations greater than water quality standards andguidelines (ProvincialWaterQualityObjectives and Canadian EnvironmentalQualityGuidelines). Inaddition, arsenic and uranium were occasionally greater than Ontario Drinking Water Standards,though this is not uncommon for regions in the Canadian Shield. All other parameters and/orconcentrationsanalysedwereconsistentlybelowwaterqualitycriteria.

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    Source:U.S.FishandWildlifeServicesNortheastRegion

    Vegetation

    The vegetationbaseline studies for the regionalandlocalstudyareasaroundtheProjectsitedemonstratethat the vegetation communities are typical of themixed boreal forest region of northernOntario.Thelocal study area and Project site are dominated byupland forested and nonforested communities,which comprise approximately 65% of the area.Upland communities and ecosites consisted ofdeciduous, mixed wood, coniferous and culturalhabitats. Wetland communities and ecositesconsistedofswamp,fenandmarshtypewetlands.

    ThemajorityoftherecordedplantspeciesarenativetoOntarioandnoprovinciallyorfederallylistedorrarespecieswereidentifiedthroughfieldstudies.FieldsurveysalsoindicatedthatnoRareVegetationCommunitiesarepresentwithinthelocalstudyarea.

    Wildlife

    Wildlifesurveysconductedbetween2012and2013identifiedspeciesofbirds,reptilesandamphibians,mammals and species at risk.The area exhibits arelatively high diversity of avian andmammalianspecies that reflect the diversity of availablehabitats (forests, wetlands, shrublands andclearings).Speciesobservedduring surveys in theregionalandlocalstudyareasareconsideredtobelargelyabundantandcommontoregion.

    Basedonareviewofecositespresent,fieldstudiesconfirmedthepresenceofSpecializedHabitatsforWildlife, namely Bald Eagle Nesting Habitat,RaptorNestingHabitat, andAmphibianBreedingHabitat(Wetlands).NosignificantHabitatforSpeciesofConservationConcernwasconfirmed.

    Speciesatriskdetectedthroughfieldsurveys inthe localandregionalstudyareasaroundtheProjectsitearelistedinTableES1.

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    TableES1:SpeciesatRiskDetectedwithintheLocalandRegionalStudyAreas

    SpeciesCommonName ESA SARA

    Birds

    BaldEagle SC NAR

    CanadaWarbler SC T

    CommonNighthawk SC T

    OlivesidedFlycatcher SC T

    RustyBlackbird SC

    Mammals

    LittleBrownMyotis(bat) E

    NorthernMyotis(bat) E

    Reptiles

    Nonedetected

    ESAEndangeredSpeciesAct,SARASpeciesatRiskAct.EEndangered,NARNotatRisk,SCSpecialConcern,TThreatened

    AquaticBiology

    As previously noted, the Project is located in theheadwaters of theMattagamiWatershed which ischaracterized by the presence of numerous lakesandrivers.Lakedepthsvaryfromapproximately3minCtLake,1.6m inUnnamedLake#1andup to5.8m in Little Clam Lake with the nearbyMesomikenda Lake being the only waterbody ofsignificantdepthatanaverageof32m.Most lakeshave a neutral to slightly acidic pH, with warmwaters,shallowSecchidepths(mostlyyellowbrowncolouredwaterwithmoderateclarity)anddissolvedoxygen levels typical for regional lake Thebanksofthesurveyed lakesweremostlyborderedbywetlandsand/or forested to theshoreline.BlackSpruceandCedarmainlyoverhungtheshorelineswithalders,shrubs,sedgesandgrassesintheunderstoryatthe lakesedges.Within the lakes,emergentmacrophyteswereobserved in theperiphery,providingspawninghabitatforYellowPerchandNorthernPikes.The lakessupported largebodiedfishspeciesprimarilyconsistingofNorthernPike,YellowPerchandWhiteSucker.SomeofthewaterbodiesalsosupportedLakeWhitefish andWalleye,which also represent important sport fish.Samplingsof thewaterbodiesdidnotprovideevidenceofanyaquaticSpeciesatRisk (suchasLakeSturgeon)underCOSEWIC.

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    The rivers, includingMollieRiver,BagsverdCreek andClamCreek,are characterizedby slow flows,exceptforshallowandrockyportionsandduetoextensivemacrophytecoverageobservedalongthebanks,thewatercoursesprovidesuitablespawninggroundsforNorthernPike.

    PondssurroundingtheProjectsitegenerallyhaveemergentmacrophytesandwooddebriswithAlders,sedges,shrubs,andgrassesdominatingthebanks.ExceptforthepresenceofWhiteSuckerinBagsverdPondandWestBeaverPond,nolargebodiedfishwerecapturedinsampledponds

    LandandResourceUse,TraditionalKnowledgeandLandUse

    The regional study area is primarily used for resource development (mineral exploration, forestry),cottaging and outdoor recreation, andwilderness pursuits such as canoeing, trapping, hunting andfishing.Miningandforestrelatedactivitiesarethepredominanttypesofindustrialorcommerciallandusesintheregionalstudyarea.Itappearsthatsomerecreationuses(suchasfishingandhunting)maynotbeaspopular in theareaas inadjacentareas;however, cottagingandcanoeingarevaluedandhistoricallanduses.

    TheMattagami First Nation and Flying Post First Nation were provided funding by IAMGOLD tocompleteatraditionalknowledgeandtraditionallandusestudy.Subsequently,someculturalresourcesthatmaybeaffectedbytheProjectwereidentified,includingawildlifepoint(baldeaglenest),portageroute,waterfowlhuntingrouteandawaterfowlhuntingpoint.Informationhasnotyetbeenprovidedbythecommunityonthecurrentuseofthesesitesorthevalueascribedbythecommunitytothem.Other resources thatmaybeusedby theMattagamiandFlyingPostFirstNation in theProjectareaincludepickerel,moose,ducks,partridge(grouse),andblueberries.

    SpecifictraditionallandusesandtraditionalknowledgerelatedtotheProjectareafromtheMtishasnotyetbeenreceived.AccordingtoreportspublishedbytheMtisNationofOntario,importantplantspecies in general for theMtis includemushrooms; specifically birch and chanterellemushrooms,ferns,andberries.Importantwildlifeincludesgrouse,deer,moose,ducksandgeese.FishspeciesintheareathatmaybeusedbytheMtisincludetrout,pike,walleye,andwhitefish.

    BuiltHeritageResources

    Nobuiltheritageresources,otherthanruinsfrompreviousminingactivities,havebeenidentifiedinthelocal studyarea.Twelve culturalheritage landscapesand 19builtheritage resourceswere identifiedwithintheregionalstudyarea.Theselandscapesare:fiveremnantsofCulturallyModifiedTrees(CMT)that served as Aboriginal and early EuroCanadian trailmarkers; and seven remains of early trailsystems,reflectedtodayinopencorridorsthroughwoodedareas.

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    Archaeology

    Archaeological assessmentsconducted for the Project followedapplicable regulations andguidelines as per the OntarioHeritage Act and the Ministry ofTourism,CultureandSport.Someofthe prime areas of potential weretested inthespringof2012.Stage1andStage2investigationsidentifiedatotalof37archaeologicalsitesand31 features, located and recordedwithin the Project property. Thisincludes 18 precontactarchaeological sites, 11 historicarchaeological sitesand8ancient trailsandportages. Ifany identified siteswere tobe impactedbyProjectactivities,thenStage3andStage4archaeologicalassessmentswouldbecarriedout.

    VisualAesthetics

    Theexisting landscapeat,andaroundtheProjectsite istypicalofnorthernOntario,characterizedbydensely populated coniferous and deciduous trees, rivers and lakes. Landscapes from the identifiedreceptor sitesduringwinterand summerpresentanatural settingwith viewsof lakesand/or rivers,treesandnaturalforestclearings.

    SocioEconomics

    The regional study area includes the areas ofGogama, Timmins, Sudbury, theUnorganizedNorthSudburySubdivision,UnorganizedTimiskamingWest,MattagamiFirstNation,FlyingPostFirstNation,Brunswick House First Nation and Matachewan First Nation. Timmins and Sudbury are urbancommunitieswhichhave increasinglybecomeservicehubsformining,educationandhealthservices.TheruralareasofGogamaandtheunorganizedsubdivisionshave,overthepastdecade,seennegativepopulationgrowthandanageingdemographic.TheFirstNation reserveshaveyoungerpopulationsandhaveseenpositivepopulationgrowth,althoughsome(MattagamiandMatachewan inparticular)seemtobeundergoingademographictransitiontoa largerworkingagepopulation.Themajorityoftheirmembersliveoffreserve.

    Theregionalstudyareaspopulationgrewby1.3%overtheperiodfrom2006to2011.Themajorityofregionalstudyarearesidents (97.3%) live inoneofthetwocities intheregionalstudyarea,TimminsandSudbury.BothCitieshavegrown inpopulation,while ruralpopulationsshrank.Highcommoditypriceshavestrengthenedtheregionalstudyareaseconomyoverthelastdecade,particularlyinurbanareas,whichhavealsobenefitedeconomicallyfromtheirroleasregionalservicehubs..

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    Thecultureoftheregionhasbeen influencedbytheAboriginalpeopleswhoreside(d) intheareaandthepatternofsettlementfromFrenchandEnglishCanada.GogamainparticularhasastrongFrancoOntarianinfluenceinitsculture.AccordingtoinformationfromStatisticsCanada,morethanhalfofitsresidents, 56.1%, consider French their mother tongue and 64.3% of residents are bilingual. AsubstantialandrisingshareoftheregionsresidentsidentifyasAboriginal,8.0%inTimminsand8.2%inSudbury.AmongthosewhoidentifyasAboriginaltherearemultipleidentities,withabouthalfofthepopulationidentifyingasMtisandhalfasFirstNation.

    Theregionaleconomyhasbeenstrengthenedbyasustainedincreaseincommodityprices,particularlyingold,whichhashelpedexpand themining industry.The regional studyareahasa longhistoryofminingand the industryhasplayeda role in forming its institutions,cultureand infrastructure.BothTimminsandSudburyhavehadorhaveminesinproductionwithintheircitylimits.Peopleworkinginminingmakeup14.5%oftheworkforceofTimminsand8.6%oftheworkforceofSudburycomparedto0.4%forOntarioasawhole.BothCitygovernmentsaresupportiveoftheminingindustry.Thestrongrelationship with natural resource based activities leaves it highly affected by globalmarkets andcommodityprices.

    The regional study area is accessible by road, rail and air services. The regional study areasinfrastructure and social services for Timmins and Sudbury provide adequate services for currentdemandsandneeds.Generally,waterandwastewatertreatmentisadequatethroughouttheregionalstudy area, including the First Nation communities, although Gogama's wastewater treatment iscurrentlynearcapacity.

    ALTERNATIVEMEANSOFCARRYINGOUTTHEPROJECTThe Ontario Environmental Assessment Act makes reference to both "alternatives to" a proposedundertaking,and"alternatemethods"ofcarryingoutaproposedundertaking.

    AspartofthedevelopmentoftheEAprocessandincompliancewithEnvironmentalImpactStatement(EIS)Guidelines,IAMGOLDcommittedtoassessalternativesto,andmeansofcarryingouttheProject.

    ProjectAlternatives

    AlternativesfortheProjecthavebeenconsideredwithrespecttothefollowingProjectcomponents:

    mining;

    minewatermanagement;

    minerockandoverburdenmanagement(minerockarea,MRA);

    oreprocessingplant;

    processeffluenttreatment;

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    tailingsmanagementfacility(TMF);

    watersupply;

    waterdischarge;

    watercourserealignments;

    siteinfrastructurepositioning;

    aggregatesupply;

    solidwastemanagementanddomesticsewagetreatment;

    powersupplyandrouting;and

    mineclosure.

    Asummaryof theproposedalternatives for theProjectarepresented inTableES2, followedby therationale for the selected alternatives. For some Project elements, technologies or processeswerereadilyselectedduetothetechnicalsuitabilityofthosesuitedtotheProjectsconditionsandthosethatcanbefinanciallysustainedbytheProject.Thepreferredalternatives,whichhavebeencarriedforwardinthepredictionofeffectsandimpactassessment,arehighlightedinTableES2.

    AlternativestotheProject

    ThreealternativestotheProjecthavebeenidentified,whichinclude:

    proceedwiththeProjectinthenearterm,asplannedbyIAMGOLD;

    delaytheProjectuntilcircumstancesaremorefavourable;and

    thedonothingalternative(developmentoftheProjectiscancelled).

    Fromanoverallperspective,thepreferredalternative istoproceedwiththeProject inthenearterm.Althoughthereisessentiallynodifferencesinenvironmentaleffectsassociatedwiththealternativeofproceedingwith theProjectasplanned versus timing commencementof theProjectwith improvedmarketconditions.

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    TableES2:SummaryofAlternativeMethodsfortheProject

    ProjectElement Alternative RationaleforSelection

    Mining

    OpenpitminingOrebodyisahightonnage,relativelylowgradedepositlocatednearthesurface,whichisbestsuitedtoopenpitmining.

    UndergroundminingOrebodynotsuitableforundergroundmining,duetothefactthatthegoldisfinelydisseminatedandclosetothesurface.

    Openpitandundergroundmining

    Itisnotanticipatedthatdevelopingasmalleropenpit,combinedwithanundergroundoperationisnotsuitableduetothefactthatthegoldisfinelydisseminatedintheorebody.

    MinewaterManagement

    Developaseparateminewatersystem

    AkeyobjectiveoftheProjectistorecycleasmuchoftheonsitewateraspracticable.Aseparateminewatertreatmentandmanagementsystemwouldgoagainstthisobjective.

    IntegrateminewaterwithTMFoperations

    ThisalternativeisbestsuitedtotheProjectsobjectiveofrecyclingonsitewater.

    MineRockandOverburdenManagement

    Placeandmanagetheminerockandtheoverburdeninstockpileadjacentorproximaltoopenpit

    Forlargeminingprojects,minimizingminerockmanagementcostisamajorcostdriver;therefore,itiscommontoplaceminerockandoverburdenasclosetothepitaspracticable.

    Establishatemporarystockpilelocation,withminerockandoverburdenretainedinthepitduringoperationsand/orreturnedtopitatclosure

    MovingthelargeamountsofoverburdenandminerockgeneratedduringtheconstructionandoperationsphasesagainuponclosurewouldincreasetheProjectfootprintandbeexcessivelycostly,whichmayrendertheProjectuneconomic.

    GoldRecovery

    NoncyaniderecoveryNoviableindustrialscaleapplicationalternativeavailable.

    CyaniderecoverymethodsThismethodisappliedwhenallgoldisextremelyfineandcannotberecoveredpartiallybyusinggravityseparation.

    Combinationofnoncyanideandcyaniderecoverymethods

    Inthisorebody,aportionofthegoldcanberecoveredusinggravityseparation,suchthatasmallerfractionwillrequirecyanideleaching,hencethecombinationofthesetwomethodsisthechosenalternative.

  • TableES2:SummaryofAlternativeMethodsfortheProject(contd)

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    ProjectElement Alternative RationaleforSelection

    ProcessEffluentTreatment

    InplantcyaniderecyclinganddestructionusingtheSO2/Airprocess

    Thisprocesspresentsthelowestrisktosurfacewaterqualityandpeopleinthecaseofanaccidentalreleaseoftailings.

    ProcessplanteffluentdischargetotheTMFwithnaturaldegradationforthedestructionofcyanide

    Theuseofnaturaldegradationpresentsagreateroverallenvironmentalrisk.

    ProcesseffluentdischargetotheTMFfornaturalcyanidedegradationandusesupplementalhydrogenperoxidedestructionofanyresidualcyanide

    HydrogenperoxidetreatmentwillhavealowercostthantheSO2/Air,butmaycarryenvironmentalrisks.

    TailingsManagement

    Tailingsslurry(~50%solidcontent)Thisisthemostcommonlyuseddepositionmethodincoolerclimatesandisthereforemostprovenmethodology.

    Thickenedtailings(~60%solidcontent) Thickeningoftailingsisverycostlyandisgenerallyonlycarriedoutinsettingswithverylimitedwateravailabilityandindryclimates.

    Pastethickenedtailings(~68%solidcontent)

    WaterSupply

    MesomikendaLake

    AllowsforareliablesourceofwaterfromthelargestbodyofwaterintheareaatarelativelyshortdistancefromtheProjectwithminimalpotentialforenvironmentaleffects.

    Otherareawatercourse(s),lake(s)andpond(s)

    Theonlyotherlocalsurfacewaterwithsufficientcapacity,andthatisreasonablyclose,isBagsverdLake.TakingwaterfromBagsverdLakeduringlowflowyearswouldaffectaquatichabitatandfishinthelakeanddownstream.

    Groundwaterwell(s)GroundwateryieldislimitedandinsufficienttomeetProjectneeds.

    WaterDischarge

    MesomikendaLake

    MesomikendaLakeiscapableofmeetingtheProjectswaterdischargeneeds.Howevercottagersanddownstreamusersmayperceivewaterdischargeasaninfringementorasadisturbance.

    BagsverdCreek

    WaterqualitymodellingpredictsthateffectsonBagsverdCreekwouldbeslightlylowerthanMesomikendaLake.TheresultingmixingzoneinNevilleLakeispredictedtobesmaller.

  • TableES2:SummaryofAlternativeMethodsfortheProject(contd)

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    ProjectElement Alternative RationaleforSelection

    WatercourseRealignments

    RealignmentofBagsverdCreekaroundtheTMFandrealignmentofportionsofThreeDuckLakes,ChesterLake,ClamLakeandtheMollieRiversystemaroundtheopenpitandMRA.

    Watercourserealignmentsweredesignedandoptimizedtominimizeimpactstoreceivingwatersandaquaticspecies.Inaddition,theyweredevelopedtominimizetransferbetweenwatershedsandalsoconsideredabilitytooffsetimpactstofishandfishhabitat

    OtherrealignmentsaroundProjectcomponents

    Additionaloptionswereconsideredtobelessfavourablewithregardstodesiredenvironmentaloutcomes.

    SiteInfrastructure

    Maintenancegarage,warehouseandadministrationcomplex

    AsfinalProjectdesignisconsideredtheoptimallocationsforthesecomponentsmaybefurtherrefinedandoptimizedtomeetProjectneedsandminimizeenvironmentaleffects.

    Accommodationcomplex

    Fuelandlubebay

    GenerallaydownareasandtemporarystoragefacilitiesExplosivesmanufacturingandstoragefacilities

    AggregateSupply

    Overburden/minerock

    Approximately40MtofminerockisexpectedtobeusedinvariousformsofProjectsiteconstruction.Qualityoverburdenandminerockarenotsufficienttomeetallconstructionneeds.

    DedicatedonsiteaggregatepitsResourcesavailablefromexistingonsitepitareapproximately0.5Mm3andareexpectedtohavelowpotentialforenvironmentaleffects.

    CommercialoffsiteaggregatepitsImpliesrelianceonexternalsuppliersandhighercostduetothetransportationofmaterialtotheProjectsite.

  • TableES2:SummaryofAlternativeMethodsfortheProject(contd)

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    ProjectElement Alternative RationaleforSelection

    NonHazardousSolidWaste

    Truckwasteoffsitetoanexistinglicensedlandfill

    Transportwouldincreasetrafficalonglocalroadsandreliesonprovisionofservicesbyothers.Transportingcouldbecontractedtoothersbutmaybetoocostly.

    DevelopanonsitelandfillThisalternativerequireslongtermmonitoringandpotentialclosureliabilities,makingitlessattractivefromacostperspective.

    Acquire/manageanoffsitelandfillproximaltotheProject

    CloseproximitytotheProjectsitewillreducecostofhaulingwastesandwouldeliminatetheneedfordevelopmentofaccessroads.Facilitylocationreducestheriskforpotentialeffectstogroundwaterduetolocaltopographyandgeology.

    IncinerationThisalternativeisnoteconomicallyviableandwillincreaseundesirableemissions.

    HazardousSolidWaste

    Shipmentoffsitetoanappropriatelicensedlandfill

    ShipmentofhazardoussolidwasteisgenerallythepreferredalternativetolimittheProjectfootprint.

    Developmentofanonsitehazardoussolidwastemanagementsystem(suchaslandfill)

    Thisalternativespotentialriskstotheenvironmentareunacceptableanditwasthereforenotconsideredfurther.

    DomesticSewage

    Septictank(s)andtilefield(s)

    Duetosoilconditionsatthesite,thistechnologywouldrequireimportofadditionalmaterial.Suitableonsitelocationswithoutaffectingwatercoursesarelimited.

    LagoonsSystemispoorlysuitedforcolderregionsduetothereductionofbiologicaloxidationprocesses.

    Packagesewagetreatmentplant

    Packagesewagetreatmentplantsareproventechnologyandcosteffective.RemainingsludgewillbetruckedoffsitetoalicensedlandfillordisposedofintheTMF.Posttreatmenteffluentcanbedirectlydischargedtotheenvironment.

    Truckingdomesticsewageoffsitetoalicensedtreatmentplant

    Alternativewouldminimizeonsiteenvironmentaleffects..Truckingwouldincreasetrafficalonglocalroadsandincreasethepotentialforaccidentsandspillsandisnoteconomical.

  • TableES2:SummaryofAlternativeMethodsfortheProject(contd)

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    ProjectElement Alternative RationaleforSelection

    PowerSupplyandRouting

    OnsitedieselgenerationThisalternativehashighenvironmentalimplicationsandisnoteconomicallyviablefortheProject.

    Tieintothe115kVlineneartheProjectThisalternativeisconsideredinsufficientbasedonthepowerrequirementsoftheProjectdesign.

    230kVShiningTreetransmissionlinealignment

    Thisalignmenthasgreatervegetationclearingrequirements.Thisalternativeismorecostlyduetoitsgreaterlength,whichalsocausesgreatertransmissionlosses.

    230kVCrossCountrytransmissionlinealignment

    Thisalignmenthasasmallerfootprint.Inaddition,transmissionlosseswillbereducedwhichreducesthedemandontheprovincial;electricalgrid.

    Alternativeenergysources(hydroelectric,solar,wind)

    RenewableenergycannotprovideconsistentuninterruptedpowerordonotmeetIAMGOLDstechnicalneeds.

    MineClosureOpenpitmine

    NaturalfloodingItwouldtakeapproximately100yearsormoreforthepittofloodnaturally,withoutadditionalinflows.

    Enhancedflooding

    Enhancedfloodingwillreducethetimeuntiltheopenpitisfullyflooded.RunoffandseepagecollectedfromtheMRAwillbeusedtoenhancefloodingoftheopenpit.

    BackfillwithmineralwasteThisalternativeisnoteconomicallyviablefortheProject.

    MineClosureWatermanagementsystem

    LeaveinplaceThisalternativewouldrequirelongtermmaintenanceandmonitoringofresidualsitedrainagefeatures.

    PartialremovalPartialremovalwouldhavebeenconsiderediffullremovalwasnottechnicallyfeasible.

    Fullremoval

    Minimizeslongtermmaintenanceandmonitoringrequirementswhilealsoreestablishing,asmuchaspossible,predisturbanceconditions.

  • TableES2:SummaryofAlternativeMethodsfortheProject(contd)

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    ProjectElement Alternative RationaleforSelection

    MineClosureStockpiles

    Reuse

    40Mtofminerockareexpectedtobeusedforsiteconstructionactivities.Useofminerockandoverburdenbeyondthisamountisnotrequired.ThereisnootherforeseenuseofminerockafterProjectclosure.

    Stabilizationandcovering/revegetation

    Thisalternativewillprovidetherequiredlongtermphysicalandchemicalstabilityoftheresidualstockpiles.Partialcoveringandrevegetationwillexpeditethegrowthofplantsandtrees.

    Useinbackfill

    Duetominesequencingoftheopenpit,backfillduringtheoperationsphaseisnotpracticable.Backfillingoftheopenpitpostclosureisuneconomical.

    Engineeredcover

    Engineercoversarerequiredtocontrolmetalsleachingoracidgeneration.TheminerockmanagementplansattheProjectaredesignedtopreventanyacidrockdrainagepotential.Thereforethismorecostlyalternativeisnotrequired.

    MineClosureTMF

    Permanentflooding

    ,Thetailingsareconsideredtohaveaverylowpotentialformetalsleachingandacidrockdrainage,thereforethisalternativeisnotrequired.

    Coveringandrevegetation

    Inthecaseofnonacidgeneratingtailings,suchasforthisProject,thetailingssurfacecanberevegetateddirectlywithouttheneedforalayeroftopsoil.

    MineClosureBuildings

    Disassemblyandremoval

    Thisisacommonpractice,andismorecostly,butdisassemblyandfullremovalofbuildingswillallowtheareatoreturntounobstructedterrestrialhabitat.

    ReuseofacceptablebuildingsAtthispoint,itisnotexpectedthattherewouldbeanyfollowupusesforanyoftheonsiteinfrastructure.

  • TableES2:SummaryofAlternativeMethodsfortheProject(contd)

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    ProjectElement Alternative RationaleforSelection

    MineClosureInfrastructure(accessroads,transmissionline)

    Decontaminationandremoval

    Thisisacommonpractice,ismorecostly,butdisassemblyandfullremovalofinfrastructurewillallowtheareatoreturntounobstructedterrestrialhabitat.

    Leaveinplaceforfutureuse

    Atthispoint,itisnotexpectedthattherewouldbeanyfollowupusesforanyoftheonsiteinfrastructureand/orthetransmissionline.

    ReclaiminplaceThisalternativeismorecostefficientbutlessenvironmentallyfriendlyandnotcompliantwithOntarioclosureregulations.

    MineClosureDrainage(watercourserealignments)

    Stabilizeandleaveinplace

    TheMollieRiversystemrealignmentsarenecessarytosupportthedevelopmentoftheopenpit,MRAandlowgradeorestockpiles.TheBagsverdCreekrealignmentisnecessarytosupportthedevelopmentoftheTMF.ThesefeatureswillneedtoremaininplaceduetotheexistenceoftheMRAandtheTMF.

    RemovalAcompleteremovalofrealignmentsisnotpossibleduetotheexistenceoftheMRAandtheTMF.

    Note:Shadingindicatespreferredalternatives.

    PUBLICANDABORIGINALENGAGEMENTAn important part of theProjectpermittingandplanningprocess is proactiveconsultation with potentiallyaffected and interestedstakeholders, Aboriginalcommunities and governmentagencies. For the Project,consultation has involvedinforming and engaging theserespective Parties about thedevelopment of the Project,responding to their interestsandconcerns,andcontinuingtobuild and maintain positiverelationships. This has been,

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    andiscurrentlybeingachieved,bycreatingavenuesfordialogueandinformationexchange(verbalandwritten), and by fostering an ongoing relationship between IAMGOLD and these stakeholder andAboriginalgroups.

    The goal of consultation for the Project is to provide stakeholders, Aboriginal communities andgovernmentagencieswithinformationandgathertheirfeedbackabout:

    theCompany;

    thestatusofexplorationandminingrelatedactivities;

    theEAprocessesandrelateddocumentsincludingtheProvincialToRandtheFederalPD;

    theenvironmentalbaselinestudiesandanyanticipatedenvironmentaleffectsandassociatedeffectsmanagementstrategies;and

    theclosureplanconcepts.

    Engagement of Aboriginal communities, local land users and community members, business andcommunityorganizationsandgovernmentagencieswasdonethroughaseriesofactivities, includingholding meetings, hosting open houses, conducting site visits and developing and issuing plainlanguagematerials (fact sheets, newsletters). IAMGOLD is committed to ongoing discussionswithAboriginal communities and other stakeholders about potential Project effects and appropriatemitigationstrategies.

    IAMGOLDhasidentifiedthefollowingstakeholdersthathave,orcouldhaveaninterestintheProject:

    BusinessandCommunityOrganizations:

    CambrianCollege;

    CollgeBoral;

    GogamaAreaCitizensCommittee;

    GogamaAreaChamberofCommerce;

    GogamaRecreationCommittee;

    GogamaSnowmobileClub;

    GreaterSudburyChamberofCommerce;

    GreaterSudburyDevelopmentCorporation;

    LaurentianUniversity;

    MattagamiRegionConservationAuthority;

    MesomikendaLakeCottagersAssociation;

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    NorthernCollege;

    SudburyAreaMiningSupplyandServiceAssociation;

    TimminsChamberofCommerce;

    TimminsEconomicDevelopmentCorporation;

    Locallandandresourceusers(e.g.traplinepermitholders);

    Adjacentorlocalminingrightsholders;

    Localsmallbusinessowners;and

    Localoutfitterandtourismoperators.

    EnvironmentalNonGovernmentOrganizations:

    MiningWatchCanada;

    Northwatch;and

    CanadianParksandWildernessSociety(WildlandsLeague).

    NonGovernmentOrganizations:

    NorthernandOutdoorTourismOntario;

    OntarioMiningAssociation;

    OntarioProspectorsAssociation;

    PorcupineProspectorsandDevelopersAssociation;and

    SudburyProspectorsandDevelopers.

    AnunderstandingoftheAboriginalcommunitiesthatcouldbeaffectedby,orhavean interest intheCtGoldProjectwasfirstestablishedthroughadvicefromtheMinistryofNorthernDevelopmentandMines (MNDM) toTrelawneyandalso throughadvice from theCanadianEnvironmentalAssessmentAgency (the Agency) based on information provided byAboriginalAffairs andNorthDevelopmentCanada (AANDC).Consideringadvice from regulators, theproposed footprintof the currentProjectdesignandthroughdiscussionwithlocalcommunities,IAMGOLDmadeapreliminarylistofpotentiallyaffectedAboriginalcommunitiesforearlyengagementactivities.

    OnMarch6,2013theAgencyinformedIAMGOLDthatthefollowingAboriginalcommunitiesshouldbeconsultedwithrespecttotheProject:

    AlgonquinAnishinabegNationTribalCouncil;

    BrunswickHouseFirstNation;

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    FlyingPostFirstNation;

    MattagamiFirstNation;and

    MtisFirstNationofOntarioRegion3.

    ItwasnotedthatastheFederalEAprogresses,theAgencywillnotify:

    BeaverhouseFirstNation;

    ChapleauOjibwayFirstNation;and

    MatachewanFirstNation.

    OnMay23,2013,IAMGOLDreceivedfurtherdirectionfromtheProvincialCrown,throughMNDM,thatthefollowingcommunitiesshouldbeconsultedwithrespecttotheProject:

    BrunswickHouseFirstNation;

    FlyingPostFirstNation;

    MatachewanFirstNation;

    MattagamiFirstNation;and

    MtisNationofOntario.

    During the Spring of 2013 IAMGOLD was also approached by Serpent River First Nation andMChigeengFirstNation, requestingthat IAMGOLDconsultwiththesecommunitiesonthepotentialimpactoftheProjectontheirharvestingrights.

    CommentsandquestionsreceivedfromstakeholdersabouttheProjectwereprimarilyregarding:

    effectsonwaterqualityanduse(suchaswaterintakeanddischarge,useofcyanide,etc.);

    effectsonlocalwatersystems;

    effectsonfishandwildlifehabitat;

    effectsonlandusessuchasfishing,canoerouteandforestry;

    locationandfunctionoftheMRAandtheTMF;

    acidrockgenerationstudyresultsandmanagement;

    effectsrelatedtonoiseandpotentialdecreasesinpropertyvalueforcottagers;

    currentandfutureaccessforlanduserstotheProjectarea;

    developmentofalargerskilledworkforceinmining;

    effectsrelatedtotheuseofcyanideandtailingdischargeonlanduseandfishpopulations;and

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES33

    lackofconsultationplanformanagingcottagerandcommunityrelations.

    CommentsandquestionsreceivedfromAboriginalgroupsabouttheProjectwereprimarilyregarding:

    waterqualityanddrainingofCtLake;

    effectsonwildlifehabitatandabundance;

    effectsonfishhabitatandabundance;

    effectsonlandusessuchasfishing,camping,trappingandhunting;

    developmentofanIBA;

    traditionalknowledgeandtraditionallandusestudies;

    closureplanningandfinancialassurance;

    business,trainingandemploymentopportunities;

    effectsonlocalwatersystems;and

    developmentofaMOU.

    Comments and questions received from government agencies about the Project were primarilyregarding:

    terminologyandtechnicalguidanceonthedraftToRandbaselinestudies;

    alternativeassessments;

    effectsassessments;

    waterqualityanduse;

    effectsonthelocalwatersystem;

    effectsonfishandwildlifehabitat;

    effectsonlandandresourceusers;

    effectsonsocioeconomicconditions;

    resultsofacidrockgenerationstudies;

    coordinationoftheProvincialandFederalEAprocesses;

    requirementoflandusepermits;

    transmissionlinealternatives;

    permittingalandfillonsiteforconstructionandoperationspurposes;

    noiseeffects;

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    archaeologicalandbuiltheritagestudies;

    terminologyandtechnicalguidanceontheToR;

    locationoflandfillandwastemanagementfacilities;

    indicatorsfortheassessmentofalternatives;

    abandonedandrehabilitatedminehazards;

    powerrequirementsandtheconstructionandoperationofthe230kVtransmissionline;and

    locationandfunctionoftheMRAandTMF.

    Furthertothetopicslistedabove,thefollowingisasummaryofsomeofthekeycommentsreceivedasofOctober15,2013abouttheProjectfromthegeneralpublic,Aboriginalcommunitiesandleadershiprepresentativesandgovernmentagencies,andhowIAMGOLDhasworkedtoaddressthem.

    AcidRockGeneration

    Stakeholders inquired about the results of any acid rock generation studies and how thiswould bemanaged.Geochemicaltestingofavailabletailingsmaterialsindicatesthatprincipally,thetailingsarenonpotentially acid generating. The investigations indicated that only 6% of nonore rock samplesindicatedapotentialforfutureacidgenerationandfurther,basedonrockhandlingproceduresandthegeologicstructureoftheorebody,itisnotanticipatedthattheMRAwillgenerateacidrockdrainage.

    AdjacentLandUsers

    Cottagers onMesomikenda Lake have expressed concern about an increased amount of noise onMesomikendaLake since the commencementofworkat theProjectsexploration site. IAMGOLD isaware that increased activity does generate noise whichmay disturb nearby cottagers. IAMGOLDassures that moving forward with the Project, measures will be taken to minimize the potentialdisruptioncausedbytheoperationsofanexplorationcamp.

    CottagersonMesomikendaLake have also expressed concerns about thepotential for futurenoiseeffects from the Project on cottagers, a devaluation of property value and a potential for reducedenjoymentofproperty.Potential futureeffectsoftheProjectonpropertyvalueandnoisehavebeenassessed in theEA. IAMGOLD iscommitted tocontinuingengagementwith theMesomikendaLakeCottagersAssociation, to ensure that appropriatemitigation strategies (e.g.,modification of trafficpatternsat site to reducenoise levels, timingofblasting in theopenpit to limitnoiseandvibrationimpactstocottagers,etc.)aredeveloped,asappropriate.

    Business,EmploymentandTrainingOpportunities

    Initialdiscussionsbetween IAMGOLDandstakeholdershighlighted thedesire to increase labourandtraining capacity in the region and theneed to integrate academia and the business community to

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES35

    attract people and investment into the regional Project area. In response to this, IAMGOLD hascompleted a labour effects assessment as part of the socioeconomic effects assessment for thisProject.

    IAMGOLD has been actively discussing education and training in addition to employment andprocurementopportunitieswithAboriginalgroupsaspartof theongoing ImpactBenefitAgreementnegotiations. IAMGOLD is also developing practices to facilitate the procurement of Aboriginalventuresand labour supply.Fundingand trainingprograms for localAboriginal communitieswillbeinitiatedasdevelopmentprospectsfortheProjectarefirmedup.

    MineClosure

    StakeholdergroupshaveinquiredaboutIAMGOLDsexperiencewithmineclosureandwhatassuranceswouldbe inplace for rehabilitationof themine site.Therewerealsoquestions related towhat theProject sitewould look likeafter closureandwhetherornotAboriginalgroups couldbe involved inreclamation planning. IAMGOLD has assured stakeholders that they have experience with closureplanninginCanadaaswellasotherpartsoftheworld.

    IAMGOLDmustfileClosurePlansandpostfinancialassurancewithProvincialauthoritiessothefundsareavailableforclosureandreclamation,ifrequired.CurrentclosureplansaretoreturntheProjectsitetoanaturalizedstateatclosure,howeverthroughouttheconsultationphasesoftheEA,IAMGOLD isinterestedinhearingfeedbackonthemanagementobjectivesoftheclosureplan.

    MineRockAreaandTailingsManagementFacility

    Stakeholdersidentifiedconcernsabouttheplanstostoreminerockandtailingsspecificallyrelatedtoacidrockgeneration,locationandsize.AspartofthealternativesassessmentrequiredfortheProject,IAMGOLD considered amultitude of locations for bothmine rock areas and tailingsmanagementfacilities. In accordance with approvedmethodologies, these sites were then narrowed down andpresented in the Project Description and draft Terms of Reference. Based on public commentsreceived, technical suitability, cost and environmental effects two mine rock areas close toMesomikendaLakehavenotbeenremovedfromtheproposedProject.

    PotentialEffectsonWaterResources,WaterQualityandWaterBodies

    StakeholdergroupshaveraisedconcernsaboutthenatureandextentofpotentialeffectsoftheProjectonwater.Specifically,questionsaroundthe impactonaquatichabitat,thedrainingofCtLakeandrealignmentswere raised. IAMGOLD iscommitted todesigningwatercourse realignments toconveyflows inanaturalmanner,andwherepossible, toenhance theecological functionof thewatershed.With respect to the draining of Ct Lake, IAMGOLDwill offset the loss of fish habitatwithin theadjacentlakesorstreams,tomaintaintheexistingfishcommunities.Inaddition,thehabitatpopulation

  • CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES36

    willbemonitoredthroughoutthe lifeoftheProjectandafterclosuretoensurethepopulationthrivesandfisharehealthy.

    Stakeholders also expressed concern about unintended tailings releases and potential watercontamination. IAMGOLD has assured stakeholders that the Companywill design andmanage theProjectusingprovenandeffectivesystemsforcontainmentandstoragetoavoidunintendedreleases.IAMGOLD is committed to recycling as much water as possible to reduce demands on adjacentwaterbodiesandlimitthereleaseofmineeffluent.

    TraditionalKnowledge,LandUseandProjectAgreements

    Aboriginalgroups raisedconcern that theTraditionalKnowledgeandTraditionalLandUse (TK/TLU)studieswouldbetoonarrowlyfocusedonpresentusesoftheProjectsitearea.Asthesestudieshelptodefine the potential impacts of the Project on local communities, IAMGOLD andMattagami FirstNationformedaworkinggrouptodiscussquestionsthatshouldbeaskedtocommunitymembers.Asaresult, theTK/TLU studieshavea regional focus,andalsoconsider thepastandpresentusesof theProjectsitewithinthelivingmemoryofcommunitymembers.Thestudiesalsomakenoteofhistoricalusesof the land thatmayhavebeenpreviouslydisplacedbyand/orhave thepotential tobe furtherimpactedby futureminingactivities. IAMGOLDwill relyon theTK/TLU studiesaspartof theEA toensureadequateAboriginalcommunityinputhasbeenreceivedaspartoftheprocess.

    WabunTribalCouncil,MattagamiFirstNationandFlyingPostFirstNation initiatednegotiationofanImpactBenefitAgreementwith IAMGOLD to address the potential impacts of the Project on theirTreatyrights.Additionally,IAMGOLDhasinitiatednegotiationswiththeMtisNationofOntarioonaMemorandum of Understanding. These negotiations are ongoing, and the agreement is beingdevelopedinparallelwiththeEAandpermittingprocess.

    TransmissionLineAlignments

    GiventhatIAMGOLDisproposingthepotentialdevelopmentofanewrouteforthepowertransmissionline,theMinistryofNaturalResources identifiedthat IAMGOLDwouldberequiredtoassessrelevantpublic value, consider alternative sources of power, outline the advantages and disadvantage ofdifferentroutesandidentifythevariouspotentialeffectsofthefeasibleoptions.

    Stakeholdershaveexpressedsomeconcernsabouttheconstructionofanew230kVtransmissionlinein theProjectarea.Consequently, IAMGOLD isaddressing theseconcerns in theEAbyoutlining thepotentialeffectsonwildlifeandpotential increase in traffic in thearea.Furthermore, IAMGOLDhastakentheseconcerns intoconsiderationbyproposingthatthetransmission linewouldberemovedatclosure to rehabilitate the site, unless otherwise negotiated with Aboriginal groups and/or localcommunities.

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    WasteManagement

    TheMinistry of Environment identified that placement of domesticwaste in local landfillsmust beplanned ahead of time to ensure that landfills have capacity. IAMGOLD has identified that theirdomesticwasteandrecycledmaterialiscurrentlytransportedtotheTimminsarealandfillandrecyclingfacility, but the Company is in the process ofworking in partnership with theMinistry of NaturalResourcestorehabilitatedandexpandanexistingnearbyfacility.

    HUMANHEALTHANDECOLOGICALRISKASSESSMENTUnacceptable health risks to human health receptors are not expected tooccurasaresultoftheProject. Themodellingstudypredictsapotentialforincreased exposure to impaired air quality. These periods are transient innatureanddependentonthefinalProjectboundaries.Asaresult,exposureisexpectedtobemuchlessthanthatpredictedbymodelling.

    Intermsofrisktoecologicalreceptors,nounacceptablerisksattributabletoProjectrelated emissions and discharges were identified for terrestrialreceptors.Foraquatic receptors,whilemodelling identifiedexceedancesofaquatic health benchmarks for certain substances and receivingenvironments, compared to riskbased toxicological reference values, nounacceptableriskwasidentified.

    ACCIDENTSANDMALFUNCTIONSPotential accidents and malfunctions that could affect the environment should they occur at theProject once in operation were identified to aid the preparation of emergency response andcontingency plans for the Project. Each credible potential accident andmalfunction identifiedwassubjectedtoariskassessmenttodetermineitslikelihoodofoccurrenceandmeasureofenvironmentalconsequence.Noaccidentsandmalfunctionswerefoundtobeofhighrisk.

    IAMGOLD is committed tooperate theProject, should itbeapproved, to thehighest standards foroperation,securityandhealthandsafety.

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    SUMMARYOFENVIRONMENTALEFFECTSASSESSMENT,MITIGATIONMEASURESANDPROPOSEDSIGNIFICANCEDETERMINATIONTheidentificationofpotentialeffectsisbasedonananalysisof the interactionsof the variousProject componentswiththe physical, biological and human environments. Effectsassessmentindicatorsareaspectsofthephysical,biologicaland human environment that are particularly notable orvaluedbecauseoftheirecological,scientific,resource,socioeconomic, cultural, health, aesthetic, or spiritualimportance, and which have a potential to be adverselyaffectedbyProjectdevelopment.

    The prediction of environmental effects consists of thefollowingsteps:

    Selectionofeffectsassessment indicators: Identificationofeffectsassessment indicators foreachdisciplinethatareused,whereappropriate,tocharacterizehowtheProjectcouldaffecttheenvironment.The indicatorsensure that the impactassessment ispractical, conciseandrelevant,andindicatorsarechosensuchthattheyrepresenttheeffectsontheenvironmentasawhole.

    Selection of study areas: Definition of study areas to describe the geographic extent ofpotentialenvironmentaleffects.

    Predictionofeffects:Basedon theProjectdesign, includingmitigation,effectsarepredictedthroughmodellingorqualitativeanalysis.Incarryingouttheenvironmentaleffectsanalysis,anumberofanalyticalmethodsandtoolshavebeenutilizedand include laboratorytests,massbalancecalculations,statisticalpackagesandvarioustypesofmodels. Itshouldbenotedthattheprocessofpredictingeffectsanddevelopingmitigationmeasuresisinherentlyiterative.

    Identificationofmitigationmeasures:EngineeringandProjectdesignmodificationsselectedtolimittheeffectoftheProjectontheenvironment.

    Determination of significance: Based on the results of the prediction of effects and theapplication of mitigation measures, the significance of the impact is assessed throughpredetermined assessment criteria (magnitude, geographic extent, duration, frequency,reversibilityandlikelihood)andadecisiontree.

    Ifan impact isdeterminedtobesignificant, itwouldnotbeacceptablefortheProject. Insuchcases,furthermitigation,monitoringandmanagementmeasureswouldbedevelopedand incorporated toreducethesignificancelevel.

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    The Project has been designed such that all impacts have been assessed to be not significant.KeyenvironmentaleffectspredictedfortheProjectaredescribedbelow.

    ThepredictionofairqualitydeterminedthatparticulatematterlevelsmayinfrequentlybehigherthanAmbientAirQuality Criteria in a small area proximate to themodelled Project site boundary. Theparticulatematter levels are predicted to be below theAmbientAirQualityCriteria at each of thesensitive receptors (cottages) located within the local study area. All other air quality assessmentindicatorsweredeterminedtobebelowtheAmbientAirQualityCriteriaatalltimes.

    Itisexpectedthatdaytimenoiselevelsatreceptorlocationswillbeat,orbelowbaselineambientnoiselevels.Nighttimenoise levelsmayexceedbaselineambientnoise levelsat some receptor locations.Withmitigationapplied,itispredictedthattheProjectwillmeetapplicablenoiseguidelinesatreceptorlocationsduringdaytimeandnighttime.

    ThewatermanagementsystemattheProjectsitewillbesetupsuchthatprocesswaterwillberecycledinordertominimizewater intakeandeffluentdischarges. Itshouldalsobenotedthatcyanide levelswillbereducedpriortodischargetotheTMFviaacyanidedestructionsystemandthatnowaterwillbedischargedfromtheTMFtotheenvironment.Althoughfinaleffluenttreatmentisnotexpectedtoberequired, IAMGOLDwill treat, as necessary, to ensure that any effluentmeets applicable receivingwatercriteriaandisprotectiveofaquaticspecies.

    Fish habitat will be affected by the construction of retention dams and watercourse realignmentsrequiredtoaccommodatetheremovalofCtLakeandthedevelopmentoftheopenpitandtheTMF.Thewatercourse realignment designwill offset the loss of fish habitatwithin the adjacent lakes orstreams,tomaintaintheexistingfishcommunitiesandfisheries.

    Terrestrial habitat will be affected as a result of Project site development and transmission lineconstruction.Habitatremovalwillaffectlocalwildlifespeciesbutthehabitatsthatwillberemovedarecommonplace in the regional environment. It is expected that therewill be nomeasurable residualeffecttopopulationabundanceanddistribution.

    With effects management strategies in place, it is expected that there may be effects to socioeconomicindicators,however,thesearepredictedtobewithinthenormalrangeofvariabilityandarenot substantive enough to require government or community investment. A number of positiveeconomiceffectsarepredicted in relation toemploymentandbusinessopportunities.TheProject isalsoexpectedtogeneratefederalandprovincialgovernmentrevenues.

    TheProjectmayaffectareasusedfortraditionalandnontraditionallandusessuchasfishing,huntingandcanoeingbut isnotexpectedto limittheabilitytocarryoutthosetraditionalandnontraditionalactivitiesinthearea.

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    Tables ES3 to ES6 present the effects,mitigation and significance determination for each effectsassessment indicator during the construction, operations, closure and postclosure phases,respectively.IndicatorsandeffectsthatareshadedindicatealinktoSection5ofCEAA2012.

    AnumberofpotentialeffectsthattheenvironmentcouldhaveontheProjecthavebeenidentifiedforassessment based on guidance provided from regulatory agencies and experiencewith othermineenvironmentalassessments:

    watersupplyavailability;

    naturalhazards;and

    climatechange.

    TheproposedProject isbeingplannedanddesigned,andwillbeconstructedandoperated,withdueconsiderationofthelocalenvironmentalconditionsinandaroundtheProjectsite.

    WithregardstoclimatechangeeffectsontheProject,theoveralleffectofclimatechangeacrossthecompleteensembleofclimatechangeprojectionsontheCtGoldProjectsitewillbeanetincreaseintheoverallwaterbalance.Thereisalsothepotentialforahigherdegreeofepisodicprecipitationeventsleading topulsesofhigher than usual runoff.However, thewaterbalance for theProjecthasbeenreviewedwithregardstoitsabilitytoaccommodatethesechangesandithasbeendeterminedthatthecurrentdesignandwaterbalancearesuitable.

    CUMULATIVEEFFECTSSeveralprojectsofvaryingscopeandscalerelatingtominingandexploration,forestryand,toalesserdegree,transportation,electricityandmunicipaldevelopment,areinthevicinityoftheProject.Therearenoknownproposedorplannedprojectsthatwouldbeexpectedtohaveacumulativeadverseeffecton effects assessment indicators defined for the Project. The cumulative effects which have beenidentifiedareanticipatedtobeeitherneutral(insignificant)orpositive.Thoughdifficulttoquantify,itisexpected that the combinedprojectswill lead topopulationgrowth in the local communities in thevicinityoftheProject,andisconsideredtobeapositiveanddesirableeffect.

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    TableES3: ImpactAssessmentMatrixfortheConstructionPhase

    Discipline Indicator EffectMitigation/EffectsManagement

    MeasuresMagnitude Extent Duration Frequency Reversibility

    ResidualImpact

    Significance

    LikelihoodoftheEffect

    AirQuality

    SuspendedParticulate

    Matter(Dust)asTotalParticulateMatter(PMtot.)

    Changesinairqualityduetoparticulateemissionsfromconstructionactivities.Theseactivitiesincludesitepreparationandconstruction,openpitoverburdenstrippingandstockpilingandonsiteroadtraffic.

    DustBestManagementPlan(DBMP) IAMGOLDiscommittingtomeetingFederaland/orProvincialcriteriaatthepropertyboundary

    LevelII LevelII LevelI LevelI LevelI

    Notsignificant

    Likely

    ConcentrationsarebelowFederal

    and/orProvincialcriteria

    (

  • TableES3:ImpactAssessmentMatrixfortheConstructionPhase(contd)

    CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES42

    Discipline Indicator EffectMitigation/EffectsManagement

    MeasuresMagnitude Extent Duration Frequency Reversibility

    ResidualImpact

    Significance

    LikelihoodoftheEffect

    AirQualityNitrogenDioxide(NO2);1Hour

    Average

    Changesinairqualityduetogaseousemissionsfromconstructionactivities,mainlyvehicleexhausts.

    EngineMaintenanceProgram EquipmentcompliantwithTransportCanadavehicleemissionsrequirements

    LevelII LevelII LevelI LevelI LevelI

    Notsignificant

    Likely

    ConcentrationsarebelowFederal

    and/orProvincialcriteria

    (

  • TableES3:ImpactAssessmentMatrixfortheConstructionPhase(contd)

    CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES43

    Discipline Indicator EffectMitigation/EffectsManagement

    MeasuresMagnitude Extent Duration Frequency Reversibility

    ResidualImpact

    Significance

    LikelihoodoftheEffect

    AirQualityHydrogen

    Cyanide(HCN);24HourAverage

    Nocyanideisusedduringtheconstructionphase.Therefore,thiseffectisnotassessedduringtheconstructionphase.

    Notapplicable

    Noise&Vibration

    DaytimeNoiseLevel

    Changesinnoiselevelsduetoconstructionactivities,includingequipmentmovement,haulageandstockpilingoperations.

    1kmsetbackdistancestobekeptattheProjectsitebetweentheconstructionlocationandthereceptors. ConstructionequipmentnottoexceednoiselevelsspecifiedinNPC115andNPC118.

    LevelII LevelII LevelI LevelIII LevelI

    Notsignificant

    Likely

    Noiselevelabovedaytimebaseline(44dBA)and

    beloworequalto45dBA.

    Effectextendsintothelocal

    studyarea.

    Thedurationoftheeffectislessthanorequalto2years.

    Effectoccursfrequentlyorcontinuously.

    Effectisfullyreversible.

    Noise&Vibration

    NighttimeNoiseLevel

    Changesinnoiselevelsduetoconstructionactivities,includingequipmentmovement,haulageandstockpilingoperations.

    1kmsetbackdistancestobekeptattheProjectsitebetweentheconstructionlocationandthereceptors. ConstructionequipmentnottoexceednoiselevelsspecifiedinNPC115andNPC118.

    LevelIII LevelII LevelI LevelIII LevelI

    Notsignificant

    LikelyNoiselevelabove40dBA.

    Effectextendsintothelocal

    studyarea.

    Thedurationoftheeffectislessthanorequalto2years.

    Effectoccursfrequentlyorcontinuously.

    Effectisfullyreversible.

    Noise&Vibration

    BlastingNoiseLevel

    ChangesinairvibrationlevelsduetoconstructionactivitiesattheProjectsiteandnearwatercourserealignments.Blastingisexpectedtooccurinfrequentlyduringtheconstructionphase.

    ChargesizeofconstructionblastingoutsideoftheopenpitboundarywillbesuchthattheobjectivesofNPC119willbeachieved. BlastingchargesizeintheopenpitisplannedtobeincompliancewithNPC119.

    LevelII LevelII LevelI LevelII LevelI

    Notsignificant

    Likely

    Blastingnoiselevelabovetheadjustedbaselinenoiselevel(39dBA)butbelowtheregulatorylimit

    of120dBL.

    Effectextendsintothelocal

    studyarea.

    Thedurationoftheeffectislessthanorequalto2years.

    Effectoccursintermittentlyorwithacertain

    degreeofregularity.

    Effectisfullyreversible.

    Noise&Vibration

    BlastingVibrationLevel

    Changesingroundvibrationlevelsduetoconstructionactivities.Blastingexpectedtooccurinfrequentlyduringtheconstructionphase.

    ChargesizeofconstructionblastingoutsideoftheopenpitboundarywillbesuchthattheobjectivesofNPC119willbeachieved. BlastingchargesizeintheopenpitisplannedtobeincompliancewithNPC119..

    LevelII LevelII LevelI LevelII LevelI

    Notsignificant

    Likely

    Blastingvibrationlevelatthe

    receptorisaboveperceptible

    vibrationlevel(0.14mm/s)and

    belowtheregulatorylimit

    (10mm/s).

    Effectextendsintothelocal

    studyarea.

    Thedurationoftheeffectislessthanorequalto2years.

    Effectoccursintermittentlyorwithacertain

    degreeofregularity.

    Effectisfullyreversible.

  • TableES3:ImpactAssessmentMatrixfortheConstructionPhase(contd)

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    Discipline Indicator EffectMitigation/EffectsManagement

    MeasuresMagnitude Extent Duration Frequency Reversibility

    ResidualImpact

    Significance

    LikelihoodoftheEffect

    Hydrology ChangeinFlow

    StreamflowchangesduetoconstructionofvariousProjectcomponents,suchaswatercourserealignments,TMFandMRA.

    Notapplicable LevelI LevelII LevelI LevelIII LevelII

    Notsignificant

    Likely

  • TableES3:ImpactAssessmentMatrixfortheConstructionPhase(contd)

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    Discipline Indicator EffectMitigation/EffectsManagement

    MeasuresMagnitude Extent Duration Frequency Reversibility

    ResidualImpact

    Significance

    LikelihoodoftheEffect

    AquaticBiology

    LossofAquaticHabitat

    LossofaquatichabitatduetoconstructionofProjectcomponents.LotichabitataffectedincludesMollieRiver,ClamCreekandBagsverdCreek.LentichabitataffectedincludesCtLake,BeaverPond,ClamLake,LittleClamLake,UnnamedPond#3andEastBeaverPond.

    SpawninghabitatwithinthewaterbodiesaffectedwillbeincludedintheFisheriesActAuthorizationforthesiteasalossofhabitatandwillbeaddressedthroughthecompensationplan(includingmodificationstoensureflow,fishpassageanduseofhabitats). Designoftherealignmentchannelswillincorporatethelifecyclerequirementsoftheresidentfishspeciesandpromote,wherepossible,anincreaseinhabitat.

    LevelI LevelII LevelI LevelIII LevelII

    Notsignificant

    Notlikely

    Lessthan10%oflotichabitat

    (streamlengthm)and/orlentic

    habitat(lakeaream2)withinthelocal

    studyarea.

    Effectextendsintothelocal

    studyarea.

    Thedurationoftheeffectislessthanorequalto2years.

    Effectoccursfrequentlyorcontinuously.

    Effectispartially

    reversible.

    TerrestrialBiology

    UplandPlantCommunity

    Types

    Vegetationlossduetositeclearing.TheProjectispredictedtoalterapproximately1,800haofthelandcover.

    LimittheareaofProjectfootprintanddisturbancefromemployeesandminingactivities. Constructthe230kVtransmissionlinetominimizepotentialforgrounddisturbanceandsoilerosion,anduseexistingroadsandrailsaspracticable. Rehabilitatehabitatforplantsaspracticable. Limit/preventthetransferofinvasiveplantspeciesfromequipmentandimportedsoil.

    LevelI LevelI LevelI LevelIII LevelII

    Notsignificant

    Notlikely

    Thereisnomeasurable

    residualeffecttotheabundanceand

    distributionofplantpopulationsandcommunities.

    EffectisrestrictedtotheProjectfootprint.

    Thedurationoftheeffectislessthanorequalto2years.

    Effectoccursfrequentlyorcontinuously.

    Effectispartially

    reversible.

    TerrestrialBiology

    Wetlands

    Lossofwetlandareasduetositeclearing.TheProjectispredictedtoalterapproximately185haofwetlands.

    Wherepractical,avoidplacementofstructuresinwaterbodiesalongthetransmissionlineROW,andtotheextentpracticable,inlowlyingareas.

    LevelI LevelI LevelI LevelIII LevelII

    Notsignificant

    Notlikely

    Thereisnomeasurable

    residualeffecttotheabundanceand

    distributionofplantpopulationsandcommunities.

    EffectisrestrictedtotheProjectfootprint.

    Thedurationoftheeffectislessthanorequalto2years.

    Effectoccursfrequentlyorcontinuously.

    Effectispartially

    reversible.

    TerrestrialBiology

    VegetationSpeciesatRisk,

    SpeciesofSpecialConcernandProvinciallyRareSpecies

    NopredictedeffectonSpeciesatRisk,SpeciesofSpecialConcernandProvinciallyRareSpeciesasnonewereidentifiedduringbaselinedatacollection.Therefore,thiseffectisnotassessed.

    Notapplicable

  • TableES3:ImpactAssessmentMatrixfortheConstructionPhase(contd)

    CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES46

    Discipline Indicator EffectMitigation/EffectsManagement

    MeasuresMagnitude Extent Duration Frequency Reversibility

    ResidualImpact

    Significance

    LikelihoodoftheEffect

    TerrestrialBiology

    Ungulates

    Potentialchangeinungulatespopulationabundanceanddistributionduetohabitatremovalduringtheconstructionphase.Siteconstructionwillremoveanestimated1,106haofsuitablemoosewinterhabitatand1,074haofsuitablemoosesummerhabitat.Additionaleffectsarepotentiallyassociatedwithgeneraldisturbanceandvehicularcollisions.

    ReduceriskofmortalitytowildlifeMinimizeconstructionofnewroads NohuntingbyProjectpersonnel EnforcespeedlimitsonProjectroads Awarenesstrainingsforemployees

    LevelI LevelIII LevelI LevelIII LevelII

    Notsignificant

    Notlikely

    Thereisnomeasurable

    residualeffecttopopulation

    abundanceanddistribution.

    Effectextendsintotheregionalstudyarea.

    Thedurationoftheeffectislessthanorequalto2years.

    Effectoccursfrequentlyorcontinuously.

    Effectispartially

    reversible.

    TerrestrialBiology

    Furbearers

    Potentialchangeinfurbearerspopulationabundanceanddistributionduetohabitatremovalduringtheconstructionphase.Siteconstructionwillremoveanestimated355haofsuitablebeaverhabitat.Between1,074and1,266haofsuitableblackbear,easternwolf,andAmericanmartenhabitatwillberemovedfromconstructionoftheProject.Additionaleffectsarepotentiallyassociatedwithgeneraldisturbanceandvehicularcollisions.

    Reduceriskofmortalitytowildlife Minimizeconstructionofnewroads NohuntingbyProjectpersonnel EnforcespeedlimitsonProjectroads Awarenesstrainingsforemployees

    LevelI LevelIII LevelI LevelIII LevelII

    Notsignificant

    Notlikely

    Thereisnomeasurable

    residualeffecttopopulation

    abundanceanddistribution.

    Effectextendsintotheregionalstudyarea.

    Thedurationoftheeffectislessthanorequalto2years.

    Effectoccursfrequentlyorcontinuously.

    Effectispartially

    reversible.

  • TableES3:ImpactAssessmentMatrixfortheConstructionPhase(contd)

    CtGoldProjectEIS/DraftEnvironmentalAssessmentReportMay2014Project#TC121522 PageES47

    Discipline Indicator EffectMitigation/EffectsManagement

    MeasuresMagnitude Extent Duration Frequency Reversibility

    ResidualImpact

    Significance

    LikelihoodoftheEffect

    TerrestrialBiology

    MigratoryBirds

    Potentialchangeinmigratorybirdspopulationabundanceanddistributionduetohabitatremovalduringtheconstructionphase.Siteconstructionwillremove99and216haofsuitablenightjar,olivesidedflycatcher,rustyblackbird,andwaterbirdhabitat.TheProjectispredictedtoremove1,203and1,233haofsuitableCanadawarblerandtreenestingraptorhabitat,respectively.TheProjectisnotanticipatedtoremoveanysuitableshortearedowlhabitat.Additionaleffectsarepotentiallyassociatedwithgeneraldisturbanceandvehicularcollisions.

    Limitriskofnestdestructionandmortalityofmigratorybirds ConstructthetransmissionlineROWoutsideofthemigratorybirdbreedingseason Installconductorwiresatasufficientdistancea


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