golder associates ltd. report

December 18, 2013

GolderAssociates

PRELIMINARY PORT METRO VANCOUVERPROJECT REVIEW APPLICATION - BURRARDIN LET PIPELINE REMOVAL

FORMER DISTRIBUTION TERMINAL2225 IOCO ROAD, PORT MOODY, BCSAP NO. 88006226

Submitted to:

Imperial Oil LimitedBurnaby, British Columbia

Authored by: Reviewed by:

Barbara Wernick, M.Sc., R.P.Bio.Associate/Senior EnvironmentalScientist

Golder Project No. 13-1520-0502-6075

Blair McDonald, MET, R.P.Bio.Associate/Senior Environmental Scientist

THIS REPORT CONTAINS PROWSIONS LIMITING LIABILITY,THE SCOPE OF THE REPORT AND THIRD PARTY RELIANCE

These documents and the information contained therein are confidential property of Imperial Oil Limited and anydisclosure of same is governed by the provisions of each of the applicable provincial and territorial freedom ofinformation legislation, the Privacy Act (Canada) 1980-81-83, c. 111, Sch ll”l “ and the Access to Information Act(Canada) 1980-81-82-83, c. 111, Sch.l”l ‘ as such legislation may be amended from time to time.

Barbara

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Distribution:

1 CopyI Copy

Imperial Oil LimitedGolder Associates Ltd.

Preliminary Port Metro Vancouver Project Review Application — Burrard Inlet Pipeline Removal2225 loco Road, Port Moody, BC December 2013

LIST OF ABBREVIATIONS

CD chart datumCEAA Canadian Environmental Assessment ActCEPA Canadian Environmental Protection ActCSA Canadian Standards AssociationCSR Contaminated Sites RegulationDaS disposal at seaDFO Fisheries and Oceans CanadaEAP Environmental Assessment ProcedureEMA Environmental Management ActHADD harmful alteration or disruption, or destructionlOL Imperial Oil LimitedNOl Notice of IntentNWPA Navigable Waters Protection ActOGC Oil and Gas CommissionPAH polycyclic aromatic hydrocarbonPCT Pacific Coast TerminalsPMV Port Metro VancouverROW right of waySARA Species at Risk ActSQCts Sediment Quality Criteria — typical sitesSRA Soil Relocation AgreementTSS total suspended solidsVFPA Vancouver Fraser Port Authority

LIST OF UNITS

m metrem2 square metremg/kg milligram per kilogrampsi pounds per square inch

Golder Project No. 13-1520-0502-6075 i

Preliminary Port Metro Vancouver Project Review Application — Burrard Inlet Pipeline Removal2225 loco Road, Port Moody, BC December2013

TABLE OF CONTENTS

LIST OF ABBREVIATIONS I

LIST OF UNITS I

r 1 0 INTRODUCTION 11.1 Background 11.2 Project Justification 11.3 Project Communications I1.4 Contact Information 2

2.0 REGULATORYSETTING 32.1 Federal 3

2.1.1 Fisheries Act 32.1.2 SpeciesatRiskAct 32.1.3 Navigable Waters Protection Act 42.1.4 Canadian Environmental Assessment Act 42.1.5 Canadian Environmental Protection Act 52.1.6 Canada Marine Act 6

U 2.2 Provincial 62.2.1 Environmental Management Act 62.2.2 Oil and Gas Activities Act 7

2.3 Municipal 72.3.1 Noise Bylaws 7

3.0 SITE AND PROJECT DESCRIPTION 83.1 Site History and Pipeline Information 83.2 Preliminary Project Description 8

3.2.1 Pipeline Sections 93.2.2 General Approach for Pipeline Removal 9

3.3 Equipment and Methods 103.4 Implementation Schedule 11

4.0 DESCRIPTION OF THE AQUATIC ENVIRONMENT 124.1 Type of Watercourse 124.2 Marine Habitat 124.3 Species at Risk 124.4 Sediment Quality in the Pipeline ROW 12

4.4.1 Classification of Sample Locations 124.4.2 Sediment Chemistry 134.4.3 Other Lines of Evidence 15

5.0 ASSESSMENT OF POTENTIAL EFFECTS AND MITIGATION MEASURES 165.1 Fish and Fish Habitat 16

5.1.1 Physical Habitat Disturbance 165.1.2 SpeciesatRisk 165.1.3 WaterQuality 165.1.4 Induced Turbidity 17

5.2 Exposure of Sediment Contamination at Depth 175.3 Terrestrial Vegetation and Wildlife 175.4 Navigation 175.5 AirQuality 175.6 Noise Assessment 175.7 Effects of the Environment on the Project 18

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CPreliminary Port Metro Vancouver Project Review Application — Burrard Inlet Pipeline Removal2225 loco Road, Port Moody, BC December 2013

5.8 Accidents, Malfunction, and Unplanned Events 18

r 5.9 Summary 18

L •••.• 6.0 REFERENCES 19

7.0 STATEMENT OF LIMITATIONS 20

FIGURES

Figure 1 Site LocationFigure 2 Sediment Sample Locations and Classificationsr Figure 3 Profile and Sediment Analytical Results — NPS6Figure 4 Profile and Sediment Analytical Results — NPS12Figure 5 Sediment Analytical Results — Sediment Managed or Potentially Managed by IOL

L APPENDICES

Appendix A Sediment Investigation

LI

E1

Golder Project No. 13-1520-0502-6075 (J4cr


to INTRODUCTION

ti BackgroundPacific Coast Terminals (PCT) is proposing to bring larger ships into its Port Moody, BCfacility in the Port Moody Arm of Burrard Inlet and the navigation channel in a section ofBurrard Inlet needs to be dredged to accommodate the larger draft of these vessels. PCThas made a separate application for project review by the Vancouver Fraser PortAuthority (VFPA; doing business as Port Metro Vancouver [PMV]) for their proposeddredging program.

The PCT project application requires that Imperial Oil (IOL) take action to remove

r segments of two pipelines buried in the seabed to avoid intersection with the proposed

[ navigation channel. Specifically, IOL has a six-inch and a twelve-inch pipeline formerlyused to convey product to and from the former IOCO Refinery. Segments of thesepipelines are located at a depth shallower than the final acceptable depth of -16 m belowchart datum (CD) (i.e., the proposed channel depth of -13.5 ± 0.5 m plus a 2 m safetymargin).

Golder Associates Ltd. (Golder) was retained by IOL to prepare this preliminary projectdescription for the proposed pipe removal project for PMV review. This preliminaryproject description is intended to be evaluated by PMV in conjunction with the PCTapplication IOL is working with PCT to synchronize the two projects and details with

respect to the final volume of sediment to be managed by IOL and specific technologiesfor pipeline removal will continue to be refined as PCT finalizes the timing and specifics oftheir project. This preliminary application provides a summary of the IOL-specificinformation related to pipeline removal. At present, it may be necessary to manage a

Li. relatively small volume of sediment that would not be already managed by PCT’sproposed works. This document describes the anticipated potential environmental effectsrelated to the IOL-specific works with proposed mitigative measures where applicable.

I 2 Project JustificationThe proposed project by IOL is being undertaken to facilitate the deepening of thenavigation channel proposed by PCT. IOL conducted a preliminary options analysis andconfirmed that the pipes could not be safely left in place, and that dropping the pipes to a

n deeper depth (i.e., deeper than -16 m CD) was not a preferred option. Removal of thepipes was selected as the preferred conceptual approach, and a subsequent options

Li analysis was conducted to determine that a submarine cut and lift strategy in conjunctionwith the PCT project was the preferred option for pipeline removal in terms of efficiencyand effectiveness

t3 Project CommunicationsIOL is in discussions with PCT to make the project as efficient and least disruptive aspossible. lOL has also had discussions with federal regulatory agencies (EnvironmentCanada for disposal at sea of dredged material; Fisheries and Oceans Canada for fishhabitat) regarding expectations for other relevant authorizations.

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Golder Project No. 13152o 5Q2 2

Preliminary Port Metro Vancouver Project Review Application — Burrard Inlet Pipeline Removal2225 Ioco Road, Port Moody, BC December2013

2M REGULATORY SETTINGThis section provides an overview of the expected regulatory considerations for thisproject.

21 Federal

2.tl Fisheries Act

Activities associated with the project (e.g., dredging of subtidal sediments) have thepotential to affect fish and fish habitat and, therefore, the proposed works are subject toreview by Fisheries and Oceans Canada (DFO) in accordance with the Fisheries Act.The Fisheries Act has recently been amended. One of the more significant amendmentsis that the previous Section 35 prohibition against the harmful alteration or disruption, orthe destruction (HADD) of habitat has now been combined with the Section 32 prohibitionagainst the killing of fish by means other than fishing to become a prohibition against theserious harm of fish that are part of a commercial, recreational or aboriginal fishery.Serious harm is defined as death of fish or any permanent alteration to, or destruction of,fish habitat. Where serious harm cannot be avoided or mitigated, an Authorizationpursuant to the amended Section 35(2) may be needed. DFO is in the process ofupdating their supporting policy and a new Fisheries Protection Policy came into force onNovember 25, 2013. The new Fisheries Protection Policy replaces the 1986 NationalPolicy for the Management of Fish Habitat. Golder understands that DFO has alreadybeen consulted with respect to the PCT application, and Golder has also initiatedpreliminary consultation directly with DFO with respect to the IOL application. Golderunderstands that DFO was waiting for the new Fisheries Protection Policy to come intoforce before they proceed with their review of the PCT application.

The Fisheries Act also contains a general prohibition against the deposit of deleterioussubstances to water frequented by fish (Section 36). Suspended sediment is considereda deleterious substance. This issue will be mitigated in the IOL project through the use ofan onsite environmental monitor and a detailed monitoring plan during constructionactivities. The Marine Mammal Regulation pursuant to the Fisheries Act also contains ageneral prohibition against disturbing marine mammals (Section 7) and requires a personwho kills or wounds a marine mammal to make a reasonable effort to retrieve the animal(Section 10). Aquatic mammals, potentially including species at risk (e.g., killer whales)may occur in the area of the project and the proposed works have the potential to affectthem (e.g., via underwater noise generated by construction activities). This issue will bemitigated in the lOL project through the use of an onsite environmental monitor and amonitoring plan during construction activities (e.g., a safety perimeter would be definedwithin which observations of marine mammals requires shutdown of constructionactivities until such time as the mammal leaves the safety perimeter).

2.1.2 Species at Risk Act

A general prohibition under the federal Species at Risk Act (SARA) is that ‘no personshall kill, harm, harass, capture or take an individual of a wildlife species that is listed asan extirpated species, an endangered species or a threatened species” (Section 32).SARA also prohibits the damage or destruction of the habitat (“residence”) used by listedspecies (Section 33) unless authorized or permitted (Section 73). As the project areasare owned by the federal Crown, Golder believes that SARA will likely apply (Section 58).The Species at Risk Registry will be reviewed for the project area to determine potentialfor presence of species at risk and appropriate mitigation measures that may need to beimplemented during the project. No additional species at risk other than those identified

Golder Project No. 13-1520-0502-6075 3 GóIder


by PCT would be expected and a similar mitigation as proposed by PCT would also like!yaddress risks associated with the IOL-specific construction activities.

2i3 Navigable Waters Protection ActThe Navigable Waters Protection Act (NWPA) is concerned in part with ensuring that aproject does not impede the safe navigation of vessels. The Act addresses any works”built or placed in, on, over, under, through or across navigable water in Canada (Part 1,Section 5). In Part 1, Section 3(b) of the NWPA regarding Works Subject to Approval, thedefinition of a “work” requiring authorization includes “any dumping of fill or excavation ofmaterials from the bed of a navigable water” and is, therefore, interpreted to includedredging operations of all kinds including for navigation. Although approvals under theNWPA no longer trigger an environmental assessment under the CanadianEnvironmental Assessment Act (see subsection 2.1 .4 of this report), the applicationprocess will likely still involve an assessment of its potential effect on navigation.

Transport Canada has recently developed new guidelines regarding minor works that areconsidered low risk, such as private docks and shoreline protection works. There arespecific standards and criteria under which Transport Canada considers projects to be“minor works” and does not require an application under the NWPA. Works that are not

r deemed to be minor works that are undertaken in a navigable waterway requireL Transport Canada’s approval prior to construction. The type of approval required and the

process to be followed varies depending on the type and complexity of the proposedwork. The Formal Approval process is followed when the work is considered to potentiallyhave a significant impact on navigation. Work Assessment letters can be issued in caseswhere the work is considered to not have a significant impact on navigation. TheNavigable Waters Protection Program also regulates the provision and maintenance oflights, markers, etc. required for safe navigation during construction.

Golder does not believe the project will result in substantial interference with navigationand the project would likely receive approval by the submission of a letter of application

LI through the Work Assessment Process.

21 .4 Canadian Environmental Assessment ActThe Canadian Environmental Assessment Act 1992 (CEAA) was recently replaced by anew CEAA (2012) with the passing of Bill C-38 by Parliament. Several important changesto the federal environmental assessment process were introduced with introduction ofCEAA 2012 and its associated regulations1on July 6, 2012.

The mere exercise of federal authority (i.e., issuing of a license, permit or authorization)is no longer a trigger for CEAA. Environmental assessments under CEAA 2012 are now

H triggered where a proposed project is a ‘designated project” prescribed by theRegulations Designating Physical Activities. Most projects are considered “designatedprojects” when a threshold production capacity is reached.

Two physical activities potentially applicable to the 10CC Pipeline Project are included inthe new Regulations Designating Physical Activities schedule of physical activities:

• Section 1(c) — The construction, operation, decommissioning and abandonment of anoil or gas facility or oil and gas pipeline, in a wildlife area or migratory bird sanctuary;and

Prescribed Information for the Description of a Designated Project Regulations; Cost Recovery Regulations andRegulations Designating Physical Activities.

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CSection 14(a) - The construction, operation, decommissioning and abandonment of

r an oil and gas pipeline more than 75 km in length on a new right of way (ROW).

L Golder understands that the project is not located in a wildlife area or migratory birdsanctuary and the pipeline ROW is less than 75 km in length; therefore, we anticipate

r that an environmental assessment under CEAA would not be required. This interpretation

U should be confirmed with the Canadian Environmental Assessment Agency.

2t5 Canadian Environmenta’ Protection Act

[ The Canadian Environmental Protection Act (CEPA) is the federal government’scomprehensive environmental protection statute enacted in 1988 and which incorporateda number of existing federal environmental protection statutes, including those governing

[ disposal at sea. Section 125 of CEPA states that no person or ship shall dispose of a- substance in waters over which Canada exercises jurisdiction, unless the substance is

“waste” and is done in accordance with a Canadian permit. Environment Canada mayissue a permit to allow ocean disposal of wastes under Section 127 of CEPA, subject to

L the limitations detailed in CEPA Schedules 5 and 6. Under CEPA, “waste” is defined inSchedule 5 to included “dredged material”, and “disposal is defined to include:

a) The disposal of a substance at sea from a ship, an aircraft, a platform or anotherstructure; or

b) The disposal of dredged material into the sea from any source not mentioned inparagraph (a).

The Disposal at Sea Regulations provide chemical concentration screening limits for thatmaterial and Environment Canada provides additional guidance regarding the minimumsampling requirements to support an application under the regulation.2

When disposal at sea is being contemplated, the sediment sampling program is typicallyprovided to Environment Canada for confirmation of the approach. Environment Canadamay also request that a member of the Disposal at Sea office attend the site to observethe sampling. The proponent screens the sediment chemistry results against the limitsoutlined in the Disposal at Sea Regulations (Section 4 Table Lower Level). If theconcentrations are lower than specified, Environment Canada may issue a permit for thedisposal of the material at a designated disposal site. If one or more limit is exceeded,Environment Canada may accept an evaluation of potential bioavailability of ther contaminant of concern, or may require toxicity testing (an assessment of biologicalresponse) as outlined in the Disposal at Sea Regulations to support the application.

Dialogue with Environment Canada has been initiated regarding obtaining applicable

[J permissions under the Disposal at Sea Regulations in the event that IOL wishes todispose of dredged material at sea. IOL intends to manage the incremental volume ofsediment directly related to the IOL-specific construction in conjunction with PCT. In theevent that a separate application becomes necessary, the incremental volume of

U sediment directly related to IOL-specific construction activities is expected to meet thenumerical screening limits.

Li9

2 http://www.ec.gc.ca/iem-das/default.asp?Iang=En&n=F25958B2-1.

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21.6 Canada Marine ActUnder the Canada Marine Act, PMV is responsible for the administration, managementand control of land and water within its jurisdiction. PMV requires that new developmentsmeet applicable standards and minimize environmental and community impacts. Newdevelopments are also expected to support PMV’s land use objectives as described inthe Port Metro Vancouver Land Use Plan.

PMV administers a Project Review Process that involves both a Planning Review and anEnvironmental Assessment Procedure (EAP). The Project Review Process applies toland use, construction, and demolition on land, water and air space administered byPMV, including all property leased or licensed to other parties. PMV’s proprietaryjurisdiction includes the water, seabed and over 460 ha of land in Burrard Inlet east of theFirst Narrows. There are limited numbers of exemptions from a formal Project Permit,and Golder understands that none of the exceptions apply to this specific project. Thisapplication document is intended to support the process of obtaining a PMV ProjectPermit for the IOL-specific construction activities that fall outside the footprint of the PCTapplication.

22 Provincial

221 Environmental Management ActThe Environmental Management Act (EMA) is the province’s principal pollution controlstatute. The EMA prohibits the introduction of waste to the environment unless theintroduction of that waste is conducted in accordance with a permit, approval, order orregulation. As federal legislation has no effluent permitting system, federal agencies(Environment Canada and DFO) often rely on the provincial permit process tocommunicate federal requirements to the proponent. Regulated activities or dischargeswhich are subject to a permit requirement or fall under a code of practice are listed inSchedule 1 or 2 of the Waste Disposal Regulation (pursuant to EMA). Dredging is not aprescribed activity and, accordingly, an effluent permit is not required for the dredgingactivity. However, EMA still has a general prohibition against causing pollution which isdefined in the EMA as ‘... the presence in the environment of substances or contaminantsthat substantially alter or impart the usefulness of that environment.” This issue will bemitigated in the IOL project through the use of an onsite environmental monitor and amonitoring plan during construction activities.

Provincial regulations with regards to contaminated soil and sediments under provincialjurisdiction are also outlined in the Contaminated Sites Regulation (CSR;Regulation 375/96 O.C. 1480/96) pursuant to the Environmental Management Act[SBC 2003]. PMV typically requires that proponents consider CSR requirements in theirmarine assessment program even though provincial regulations do not technically applyto areas under PMV authority.

For this particular project, provincial regulations would apply if any dredged material isdisposed upland. Depending on the specific disposal option, this could include a Notice ofIndependent Remediation in conjunction with: a) documentation for disposal in apermitted landfill; b) evaluation of potential near-shore sites for disposal via TechnicalGuidance 20; or c) a Soil Relocation Agreement. Upland disposal is not contemplated inthe current application and therefore no trigger under the CSR is anticipated.

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222 Oil and Gas Activities Act

The Oil and Gas Activities Act is administered by the British Columbia Oil and GasCommission. The submission of a Notice of Intent (NOl) is necessary for the reporting ofoperational changes and modifications or repairs to existing pipelines requiring no newacquisition of land, or additional surface tenures, and no modifications to the pipelinepermit. NOls are reviewed by the Commission’s Engineering division. For any NOlrequiring an engineering assessment, engineering assessments must be performed anddocumented to the standards outlined in the CSA Z662. They are considered engineeringdocuments and, as per Section 20(9) of the Engineers and Geoscientists Act, must besealed by a professional engineer licensed in the province of British Columbia. CL hasbeen consulting with the OGC and will provide the appropriate NOl.

23 Municipal

23i Noise Bylaws

City of Port Moody Bylaw BL1 399-C (Sound Level) prohibits “any noise or sound in or ona public or private place which disturbs or tends to disturb the quiet, peace, restenjoyment, comfort, or convenience of any person or persons in the neighbourhood orvicinity”. Notwithstanding this prohibition, the bylaw allows for construction activities to beconducted between 07:00 and 20:00 h, Monday through Saturday and between 09:00and 18:00 h on Sundays and statutory holidays. The IOL-specific construction activitiesare not expected to result in additional noise or community consultation issues that

U exceed the consultation activities and planning already conducted by PCT

El

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C: Preliminary Port Metro Vancouver Project Review Application — Burrard Inlet Pipeline Removal2225 loco Road, Port Moody, BC December 2013

3O SflE AND PROJECT DESCRIPI1ON

3i Site History and Pipeline Information

fl

ii

L

IOL has a leased ROW in Burrard Inlet between the 10CC Terminal (located at 2225 locoRoad, Port Moody) on the north side and adjacent to the Reed Point Marina (850 BarnetHighway, also in Port Moody) on the south side (Figure 1). This ROW extends from the10CC Boat Club (north side) to a point immediately east of Reed Point Marina (southside). A legal description of the ROW lease is described as metes and bounds on VFPALease Plan 2002-117. The ROW consists of two parallel parcels approximately 50 mapart that share a common terminus point on the north and south sides. Parcel A of theROW is 9,755 m2 and contains a 12-inch pipeline (NPS12) that carried crude oilnorthwards to the former 10CC Refinery. Parcel B of the ROW is 10,103 m2 and containsa 6-inch pipeline that carried refined products southwards from the former 10CCRefinery.

These pipelines were installed in 1955. Pipelines were installed by dredging a channelacross Burrard Inlet, dropping the pipes into place, and backfilling with dredged materialto achieve between 1 and 2 m of cover. Armouring (e.g., large rocks) and anchors (i.e.,concrete blocks attached to the pipes) were not used.

The pipelines were placed into maintenance status when refinery operations at the 10CCsite ceased in the late 1990s. The pipelines were drained, cleaned and filled with nitrogenat that time. Cathodic protection has been maintained as part of the maintenance status.The foreshore of the site is still an active distribution terminal that receives, stores anddistributes a number of petroleum products, including heavy fuel oil, asphalt andlubricating oils; however, the pipelines are not used as part of terminal operations.

The following tasks were conducted as part of the investigation for the pipeline removalproject:

I Sediment sampling for chemistry and toxicity was conducted in 2009 (see Figure 2).

t Pipelines were resurveyed in 2012 to confirm their exact location (in threedimensions), inspected for corrosion or defects, and recleaned. These three activitieswere conducted using appropriate in-pipe tools (pigs). These results confirmed: a)the vertical and horizontal locations of the pipes; b) that the pipes were in good repairand still suitable for use; and c) that there was no product or residues present ineither line.

Additional sediment core sampling for chemistry was conducted in 2013 (seeFigure 2).

32 Preliminary Project DescriptionThe project scope includes the cutting, removal and disposal of two sections of productpipelines that cross Burrard Inlet. This project is being conducted by lOL because thepipelines will interfere with the future depth of the navigational channel after thecompletion of the dredging project proposed by PCT (i.e., the IOL project would notproceed without the PCT project).

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3.2.1 Pipeline Sections

Figures 3 and 4 illustrate the sections to be removed relative to the navigational channel.The specific sections of pipelines to be removed include:

flThe length of pipe located in the footprint of the proposed PCT dredge channel.

The length of pipe located in the northern safety zone. This pipe is being removed atthe request of PMV as a safety precaution (i.e., to limit damage to vessels in theevent that a vessel strikes the side of the navigational channel). The width of thenorthern safety zone is 50 m as confirmed by PMV.

The length of pipe in the southern safety zone. The southern safety zone is relativelynarrow and is primarily intended to avoid the possibility of having the terminatedpipeline extend into the navigational channel in the event of long-term settling of thesouthern side of the navigational channel.

3.2.2 General Approach for Pipeline RemovalThe IOL project has been designed in conjunction with PCT’s planned dredging projectand a central element for the planning has been to minimize the volume of sediment thatmay require management by IOL. The strategy for minimizing the sediment volume is asfollows:

IOL will install submarine shoring boxes prior to the initiation of PCT’s dredgingprogram. These shoring boxes provide in situ access to the pipes (i.e., submarineand subsurface) Sediment within the shoring boxes will be temporarily stored on abarge or placed on the seabed while the divers cut the pipes into segments. Total

[ volume of sediment to be temporarily moved is approximately 200 m3 (i.e., 3 m ofL cover at slope of 2.5:1 x 6 shoring box locations). The cut segments will then be

capped and filled with nitrogen at 50 pounds per square inch (psi).

IOL has verified the location of the pipes in three dimensions so that the contractorselected by PCT can remove as much of the overburden over the pipes as possible(in the navigational channel). PCT will be responsible for the bulk removal of materialto a depth of -13.5 ± 0.5 m. IOL has confirmed with PCT that they intend to utilize adredge contractor who can selectively remove sediment to the desired depth ofchannel but leave a 0.5 m protective cover over the existing pipe lines. Risks in theevent that PCT’s contractor inadvertently snags the pipe are mitigated because the

L pipes will be cut and capped prior to dredging

• Once PCT has dredged the area, IOL will use a suction dredge or jet to exposerigging points on the pipe segment within the channel The pipe will then be lifted

j onto a barge and cut into segments for disposal

I The pipe segments in the safety zone will be mechanically extracted into thenavigational channel, lifted to the surface, and disposed. The intent of the mechanicalextraction is to pull the pipe without removal of additional overburden In the eventthat the pipe segment in the safety zone cannot be freed from the seabed, theoverburden in the safety zone will be removed in 1 m lifts until the pipe can be pulled

El free.

• The depth of the navigational channel will be confirmed once the pipes have beenremoved. If the depth at the location of the former pipes does not meet the targetdepth of -13 5 ± 0 5 m a cleanup pass will be conducted The timing of the works is

LI intended so that the cleanup pass can be integrated into the PCT dredging project.

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r Preliminary Port Metro Vancouver Project Review Application — Burrard Inlet Pipeline Removal2225 loco Road, Port Moody, BC December2013

Estimated volumes of sediment to be managed by IOL range from 0 to 3,800 m3depending on the specific outcome of the general approach described above. Specificvolumes of overburden were calculated as follows:

• Navigational Channel:

— NPS6 = 0.5 metre on each side of the pipe x 0.5 metre on top = 0.5 m2 x lineardistance of 46 m where PCT cannot dredge to the desired depth = 23 m3.

— NPS12 = 0.5 metre of each side of the pipe x 0.5 metre on top = 0.5 m2 x lineardistance of 22 m where PCT cannot dredge to the desired depth = 11 m3.

• Southern Safety Zone:

— NPS6 Removal of all overburden to the pipe assuming a 2.5:1 slope x lineardistance of 17 m = 400 m3.

— NPS12 = Removal of all overburden to the pipe assuming a 2.5:1 slope x lineardistance of 7 m = 160 m3.

• Northern Safety Zone:

rLi

L

nLi

— NPS6 = Removal of all overburden to the pipe assuming a 2.5:1 slope x lineardistance of 65 m = 1,400 m3.

— NPSI2 Removal of all overburden to the pipe assuming a 2.5:1 slope x lineardistance of 60 m = 1,800 m3.

Potential scenarios are as follows:

• The theoretical worst-case volume estimate of 3,800 m3 assumes that the entire0.5 m overburden in the navigational channel will need to be managed by IOLbecause it would exceed the target depth of -13.5 ± 0.5 m. This estimate alsoassumes that the entire overburden covering the pipes in the northern and southernsafety zone would need to be managed (i.e., mechanical extraction is not possiblewithout removal of all overburden).

• A reasonable worst-case volume estimate is 2,200 m3. This assumes the 0.5 moverburden in the channel plus the majority of the overburden (but not all) of thenorthern safety zones will need to be managed.

• The most optimistic scenario is 0 m3. This assumes that any overburden in thechannel would be insignificant in terms of influencing the final depth of the channeland that the depth meets the 13.5 ± 0.5 m criteria. The mechanical extraction issuccessful without the need to manage any overburden.

An illustration of the division of responsibility between PCT and IOL in terms of sedimentmanagement according to this scenario is provided in Figures 3 and 4.

33 Equipment and MethodsAdditional details regarding the specific equipment and methods for dredging andpipeline removal will be provided once the detailed engineering has been completed. Akey consideration for the design of the lOL project is that the goal is to utilize existingequipment and contractors for the PCT project. The PCT engineering plan is still indevelopment and lOL and PCT are maintaining open lines of communication to

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coordinate these two projects. The likely equipment and methods to be used toaccomplish the general approach described above is as follows:

Golder will mobilize to the site (with Fraser River Pile and Dredge Ltd., or anotherqualified subcontractor) via a barge transported by a tugboat. Equipment to bemobilized includes:

— 100 ton and 5 ton cranes;

—100 x 40 foot spud scow;

— 3 cubic yard clamshell bucket;

— 6 inch dredge pump;

— Materials scow;

— Dive service vessel with surface air supply and underwater burning gear; and

— Workboat

Divers will descend to marked locations (estimated maximum dive depth is 60 feet)and use a combination of jetting and low-turbidity suction dredging to expose thepipes. An aluminum shoring system constructed of 2 x 8 foot panels will beassembled on the deck of the scow and lowered into place to protect the excavation.This excavation will extend slightly (e.g., less than three feet) above the seabed.

The pipes will be flooded with freshwater to reduce seawater infiltration into the pipeand to equalize the pressure between the inside and outside of the pipe. Sandbagswill be used to secure the pipeline at the specific cut location.

Underwater burning gear will be used to remove a 1 m segment of pipe. The cutsegment will be hoisted to the surface for disposal. A mechanical plug with one-wayvalves will be installed in each end of the remaining pipe. The valves will initially beleft open. A foam pig will then be sent along the pipe using pressurized nitrogen toforce the freshwater from the pipe. Divers will then close the valves. The shoringboxes will be removed.

At the end of the PCT dredging operations, divers will expose rigging points along thesegment of pipe in the navigational channel and rig the pipe for extraction. The pipewill be lifted to the scow deck and cut into sections. Rigging will also be secured tosegments of pipe in the safety zone for extraction.

if segments of pipe in the safety zones do not release (i.e., the weight of theoverburden is holding them in place), a clamshell will be used to remove theoverburden in a succession of 1 m lifts. DL and PCT are in discussion aboutopportunities for collaboration and the preliminary project description currentlyassumes that any overburden generated during the lOL-specific project will bemanaged with PCT’s assistance. Ideally, works will be scheduled so that PCT’sselected dredge contractor would manage the overburden using the same approachas the overall navigational dredging program.

34 Imp’ementation SchedueThe project schedule is dependent on POT’s schedule to dredge the navigation channelwhich has not yet been finalized. DL and POT are maintaining open lines ofcommunication to coordinate these two projects.

Golder Project No. 13-1520-0502-6075 11 ‘Associates


Table A: Summary of Sediment Chemistry Guideline Exceedances

Observed ExceedanceParameter

CSR SQCts DaS Lower Level

Metals No exceedances observed. Cd in all surficial samples and inall but two samples from depth(sites south of the navigationchannel) (2 to 4 times the lowerlevel of 0.6 mg/kg)

Acenaphthylene 0.7 to 1.0 m interval at one site in the Not applicablenavigation channel to (IPS-SD13-07;2 times SQC of 0.15 mg/kg)

Anthracene Surface interval from one site south of the Not applicablenavigation channel (IPS-SD1D-09;1.3 times SQC of 0.29 mg/kg)

Chrysene Surface interval from one site south of the Not applicablenavigation channel (IPS-SD1 D-09;1.2 times SQC of 1.0 mg/kg)

Pyrene Surface interval from one site south of the Not applicablenavigation channel (IPS-SD1D-09; 3 timesSQC of 1.7 mg/kg) and one site in thenavigation channel (I PS-SD1 3-07;1.7 times SQC)

Total PAH No exceedances of the total PAH Surface interval at four sitessediment standard was observed. (three from south of the

navigation channel[IPS-SD13-09,10,11]; one from

I within the navigation channel[IPS-SD13-07]) (1 .2 to 4.4 timesthe lower level of 2.5 mg/kg)

Notes: na — not applicable; PAH — polycyclic aromatic hydrocarbon; SQCts — sediment quality criteria for typicalsites

Key findings from the available chemistry data:

s There were few exceedances of PAHs:

••

There were no exceedances of the DaS lower level for total PAHs and noexceedances of SEDQCts for individual PAHs in the core samples that representsediment to be managed by lOL. Concentrations of PAHs at the horizon closestto the pipelines were less than analytical detection limits.

— There were no exceedances of PAHs in surficial or core samples taken from thenorthern safety zone.

— There were four samples in the southern safety where total PAHs exceeded theDaS lower level (i.e., 6.0 to 16.0 mg/kg relative to a screening limit of 2.5 mg/kg).Three of those four samples had one or more individual PAHs that exceeded theSEDQCts. Vertical delineation for the PAH exceedances was achieved and thedata confirmed that exceedances were generally limited to the top 20 cm.

S Cadmium exceedances of the DaS lower level were common in surface and coresamples (down to the maximum achieved depth). Cadmium concentrations alsoexceeded the DaS lower level in reference area samples collected to the east of theROW (Golder 2010) and in samples collected in 1994 from the turn basin at the

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nearby Pacific Coast Terminals in Port Moody Arm as part of an application fordisposal of dredged sediments at sea (EVS 1994). This finding was not unexpectedas Burrard Inlet is known to be naturally enriched with cadmium. Cadmiumconcentrations did not exceed the SEDQCts.

443 Other Lines of EvidenceIn addition to the chemistry data summarized above and provided in Appendix A, severalother lines of evidence regarding sediment quality were collected by Golder (2010).Observations from Golder (2010) considered relevant to the question of management ofsediment as a result of this application include:

AVS-SEM data were collected for surficial samples. There was sufficient AVS to bindbioavailable cadmium in all but two samples collected from the entire ROW. Furtherinformation is available in subsection 2.5.2 of Golder (2010).

Toxicity testing on representative samples has generally shown minimal effect:

— Three toxicity tests (amphipod survival, sea urchin larval development, andMicrotoxTM) conducted in 1994 indicated that there was little or no toxicityassociated with sediment with elevated cadmium concentrations (EVS 1994).

Additional toxicity testing was conducted by Golder on 13 surficial samplescollected from the ROW (or from reference areas). Many of the samples had totalPAH concentrations that exceeded the DaS lower limit, as well as cadmiumconcentrations that exceeded the DaS lower limit. No adverse effects wereobserved in the MicrotoxTM or lO-amphipod survival tests in 12 of the samples.Seven of the twelve samples had more than a 25% reduction in sea urchinfertilization; however, there was no relationship observed between total PAHconcentration and percent fertilization. Rather, ammonia and suiphides wereidentified as contributing factors in all five samples with reduced sea urchinfertilization. Further information is available in Section 3.0 of Golder (2010).

PAH fingerprinting was conducted on selected samples by a specialty analyticallaboratory. The PAH fingerprinting showed that hydrocarbons in the samples werenot associated with pipeline operations (i.e., movement of crude oil and refinedproducts). Hydrocarbons were attributed to regional sources such as urban runoff orother localized point sources such as creosote, and appeared to be highlyweathered. Further information is available in Section 5.0 of Golder (2010).

15


Observed ExceedanceParameter

CSR SQCts DaS Lower Level

Metals No exceedances observed. Cd in all surficial samples and inall but two samples from depth(sites south of the navigationchannel) (2 to 4 times the lowerlevel of 0.6 mg/kg)

Acenaphthylene 0.7 to 1.0 m interval at one site in the Not applicablenavigation channel to (IPS-SD13-07;2 times SQC of 0.15 mg/kg)

Anthracene Surface interval from one site south of the Not applicablenavigation channel (I PS-SD 1 D-09;1.3 times SQC of 0.29 mg/kg)

Chrysene Surface interval from one site south of the Not applicablenavigation channel (IPS-SD1 D-09;1 .2 times SQC of 1.0 mg/kg)

Pyrene Surface interval from one site south of the Not applicablenavigation channel (IPS-SD1 D-09; 3 timesSQC of 1.7 mg/kg) and one site in thenavigation channel (I PS-SD1 3-07;1.7 times SQC)

Total PAH No exceedances of the total PAH Surface interval at four sitessediment standard was observed. (three from south of the

navigation channel[IPS-SD13-09,10,1 1]; one fromwithin the navigation channel[IPS-SD1 3-07]) (1.2 to 4.4 timesthe lower level of 2.5 mg/kg)

L

r

Key findings from the available chemistry data:

g There were few exceedances of PAHs:

There were no exceedances of the DaS lower level for total PAHs and noexceedances of SEDQCts for individual PAHs in the core samples that representsediment to be managed by lOL. Concentrations of PAHs at the horizon closestto the pipelines were less than analytical detection limits.

* There were no exceedances of PAHs in surficial or core samples taken from thenorthern safety zone.

— There were four samples in the southern safety where total PAHs exceeded theDaS lower level (i.e., 6.0 to 16.0 mg/kg relative to a screening limit of 2.5 mg/kg).Three of those four samples had one or more individual PAHs that exceeded theSEDQCts. Vertical delineation for the PAH exceedances was achieved and thedata confirmed that exceedances were generally limited to the top 20 cm.

Cadmium exceedances of the DaS lower level were common in surface and coresamples (down to the maximum achieved depth). Cadmium concentrations alsoexceeded the DaS lower level in reference area samples collected to the east of theROW (Golder 2010) and in samples collected in 1994 from the turn basin at the

(Go1derd’Associates

E

Table A: Summary of Sediment Chemistry Guideline Exceedances

nL

Notes: na — not applicable; PAH — polycyclic aromatic hydrocarbon; SQCts —sediment quality criteria for typicalsites



nearby Pacific Coast Terminals in Port Moody Arm as part of an application fordisposal of dredged sediments at sea (EVS 1994). This finding was not unexpectedas Burrard Inlet is known to be naturally enriched with cadmium. Cadmiumconcentrations did not exceed the SEDQCts.

443 Other Lines of EvidenceIn addition to the chemistry data summarized above and provided in Appendix A, severalother lines of evidence regarding sediment quality were collected by Golder (2010).Observations from Golder (2010) considered relevant to the question of management ofsediment as a result of this application include:

a AVS-SEM data were collected for surficial samples. There was sufficient AVS to bindbioavailable cadmium in all but two samples collected from the entire ROW. Furtherinformation is available in subsection 2.5.2 of Golder (2010).

aToxicity testing on representative samples has generally shown minimal effect:

— Three toxicity tests (amphipod survival, sea urchin larval development, andMicrotoxTM) conducted in 1994 indicated that there was little or no toxicityassociated with sediment with elevated cadmium concentrations (EVS 1994).

Additional toxicity testing was conducted by Golder on 13 surficial samplescollected from the ROW (or from reference areas). Many of the samples had totalPAH concentrations that exceeded the DaS lower limit, as well as cadmiumconcentrations that exceeded the DaS lower limit. No adverse effects wereobserved in the MicrotoxTM or lO-amphipod survival tests in 12 of the samples.Seven of the twelve samples had more than a 25% reduction in sea urchinfertilization; however, there was no relationship observed between total PAHconcentration and percent fertilization. Rather, ammonia and sulphides wereidentified as contributing factors in all five samples with reduced sea urchinfertilization. Further information is available in Section 3.0 of Golder (2010).

a PAH fingerprinting was conducted on selected samples by a specialty analyticallaboratory. The PAH fingerprinting showed that hydrocarbons in the samples werenot associated with pipeline operations (i.e., movement of crude oil and refinedproducts). Hydrocarbons were attributed to regional sources such as urban runoff orother localized point sources such as creosote, and appeared to be highlyweathered. Further information is available in Section 5.0 of Golder (2010).

Golder Project No. 13-1520-0502-6075 15 Associates


5.0 ASSESSMENT OF POTENTIAL EFFECTS AND MTlGAflONMEASURES

5.1 Fish and Fish Habitat

5.1.1 Physical Habitat DisturbanceThe majority of the footprint associated with the removal of lOL’s pipelines is expected tooccur primarily in the vicinity of the dredge cut depth after POT has dredged thenavigation channel, resulting in no additional disturbance to fish habitat. As acontingency, it may be necessary for lOL to temporarily remove some or all of theoverburden in the safety zone (primarily, the northern safety zone) in order to release thepipes. This would be a slot cut with a maximum surface area of 750 m2 (i.e., 2 lines x50 m x 7.5 m wide assuming a 2.5:1 slope) that may need to be disturbed. Thisdisturbance would be of a short duration and the dredged material would be replaced tograde, resulting in no permanent alteration or destruction of habitat.

The work will be undertaken during the Marine/Estuarine Timing Window of August 15 toFebruary 28 when practicable to minimize the potential for effects on sensitive fisheryresources that may utilize Burrard Inlet during that time.

5.1.2 Species at RiskA final evaluation of species at risk will be conducted, but no effects are anticipatedbeyond what would already result from the POT application. lOL and POT aremaintaining open lines of communication to coordinate these two projects.

5.1.3 Water QuaUtyThe pipes formerly carried hydrocarbon products. The lines were placed in maintenancestatus in the mid-1990s which included removal of products. The lines have not beenused since that time, and were recleaned in 2012 as part of the current investigation.Oleaning consisted between 7 and 9 different “pig” runs, which included:

An initial pig to remove any debris or liquid in the pipe. Approximately 3 gallons ofliquid were removed from NPS6, and approximately 1 cup of debris was removedfrom NPS12.

A slug of approximately 3 cubic metres of stove oil was pushed through NPS12. Thispipeline formerly carried crude product, and stove oil acts as solvent to furtherremove any residual product sorbed to the walls of the pipe. The entire volume ofstove oil was retrieved.

• A brush pig was sent through the pipes to scrape the sides of the pipe. No additionalsolids were recovered from either pipe.

• Multiple tool pigs were passed through the lines to make measurements. All tool pigswere “very clean” on retrieval.

• One or more foam pig were passed through the lines. Foam pigs have softer, lightcoloured sides for visual inspection of dirt, debris, and liquids. Foam pigs werepushed through the pipe until they came though dry and clean.

Based on this information, lOL has confirmed that the pipes are clean. The current planinvolves the flooding of the pipes with dechlorinated municipal tap water prior to cutting.This water would be slowly discharged from the one-way valves installed on the pipesinto the water column (albeit at the bottom of the shoring boxes at a depth of

Golder Project No. 13-1520-0502-6075 16 Aiciates


approximately 3 m below the sediment surface. No water quality effects are expected asa result of the IOL project.

5.t4 induced TurbdftyIt is possible that dredging can induce turbidity and/or total suspended sediment (TSS)concentrations in the water column. These effects may result in a disruption of feeding byvisual predators such as juvenile salmon (Berg 1982) or temporarily affectphotosynthesis. The engineering methods for the project have not yet been finalized;however, mitigation measures for induced turbidity are well known, and appropriatemethods will be applied to the project. IOL and POT are maintaining open lines ofcommunication to coordinate these two projects. Moreover, an environmentalmanagement plan will be developed for the project that includes dredge performanceobjectives. A qualified environmental monitor will be on site to verify that these objectivesare being met.

52 Exposure of Sediment Contamination at DepthThe chemistry of sediment samples obtained at the approximate dredge cut depthindicated that contamination by metals and PAHs does not exist (i.e., concentrations arebelow applicable sediment quality guidelines). A final program for confirmatory sampleswill be developed in consultation with PMV.

53 Terrestrial Vegetation and WildlifeThe project will not interact with shoreline or upland areas. No effects on terrestrialvegetation or wildlife are expected.

54 Navigation

Various types of vessels travel through and adjacent to the proposed project area andmay be impeded by dredging equipment during the project. To mitigate potential effectsto navigation, the contractor will follow harbour-control instructions issued by PMV; thework will be phased to minimize disruptions; and the conditions outlined in the NWPA forthe project, if one is issued, will be followed. IOL and POT are maintaining open lines ofcommunication to coordinate these two projects to minimize impacts on navigation.

55 Air QualityThe potential for impacts to air quality are related to exhaust from heavy machinery andservice vehicles and release of dust from dredged material during the construction phaseof the project. Vehicle emissions have the potential to contribute to elevated greenhousegases in the atmosphere. Both exhaust and dust have the potential to affect site workers.Residents are not likely to be impacted based on the distance between site activities andthe nearest residential property. The contractor will maintain equipment in good workingorder and will minimize engine idling. Dredged material is intended to be temporarilyplaced underwater, but if dredged material is stored on barges, it will be kept dampand/or covered.

56 Noise AssessmentThe primary noise sources of potential concern during the project will be combustionengines and the impact between metal parts on machinery. The contractor will maintainequipment in good working order and switch it off when not in use. Work will occur duringdaytime construction hours as indicated by the City of Port Moody’s Sound Level bylaw.Should work need to be conducted outside those hours, a variance will be applied for.

Golder Project No. 13-1520-0502-6075 17 Aces


Best practices such as installation of mufflers on machinery will be implemented andworkers will wear appropriate personal protective equipment. IOL and PCT aremaintaining open lines of communication to coordinate these two projects to minimizenoise impacts.

57 Effects of the Environment on the ProjectThe project will be undertaken on the marine waters of Burrard Inlet and interaction withenvironmental components such as tides, wind, waves and heavy rain are possible whichmay affect dredging and dewatering activities. These environmental factors may increaseinduced turbidity during dredging and heavy precipitation may overload containment andfiltering devices on the dredged material barge depending on how the material ishandled. The potential for negative effects of the environment on the project will bemitigated by the monitoring of appropriate tide and current tables and marine weatherforecasts and not undertaking the work during adverse environmental conditions.

52 Accidents, Maifunction, and Unp’anned EventsPotential accidents and/or malfunctions that may occur during construction activitiesinclude:

w Spills of fuel or other hazardous material; and

Generation of turbidity during in-water works.

The contractor will be required to have a spill contingency plan for addressing accidentalspills of fuel or other hazardous materials, and the environmental monitoring plan willinclude turbidity triggers to evaluate the effectiveness of the mitigation. Furtherdevelopment of the onsite monitoring and spill response plan will be completed once theengineering designs have been finalized.

59 SummarySignificant adverse effects from the proposed project are not expected once all mitigationmeasures have been applied. A detailed plan for implementation (including anenvironmental management plan) will be developed and this application will be updatedonce the engineering design of the PCT application has been finalized and opportunitiesto collaborate directly with PCT with the management of sediment related to the IOLproject have been explored.

U

Golder Project No. 13-1520-0502-6075 18 =As°oes


6O REFERENCESBerg, L. 1982. The effect of exposure to short-term pulses of suspended sediment on thebehavior ofjuvenile salmonids. In: Proceedings of the Carnation Creek workshop, a 10-year review. G. Hartman (ed.). Malaspina College, Nanaimo, B.C. p. 177-1 96.

DFO (Department of Fisheries and Oceans). 1992. Marine foreshore environmentalassessment procedures. Available at: http://www-heb.pac.dfompo.gc.ca/publications/pdf/shellfish_mfeap.pdf.

EVS (EVS Environment Consultants Ltd.). 1994. Bioaccumulation testing. Prepared forVancouver Port Corporation. Project No. 9/634 02.

Golder (Golder Associates Ltd.) 2010. Sediment assessment for IOCO Pipeline Right-ofWay, Burrard Inlet. Prepared for Imperial Oil Limited. Golder Project No. 08-1 436-0045-6075



7O STATEMENT OF LIMTATONSThis report has been prepared and the work referred to in this report has beenundertaken by Golder Associates Ltd. for Imperial Oil Limited. It is intended for the soleand exclusive use of Imperial Oil Limited, its affiliated companies and partners and theirrespective insurers, agents, employees and advisors (collectively, “Imperial Oil”). Anyuse, reliance on or decision made by any person other than Imperial Oil based on thisreport is the sole responsibility of such other person. Imperial Oil and Golder AssociatesLtd. make no representation or warranty to any other person with regard to this reportand the work referred to in this report, and they accept no duty of care to any otherperson or any liability or responsibility whatsoever for any losses, expenses, damages,fines, penalties or other harm that may be suffered or incurred by any other person as aresult of the use of, or reliance on, any decision made or any action taken based on thisreport or the work referred to in this report.

The investigation undertaken by Golder Associates Ltd. with respect to this report andany conclusions or recommendations made in this report reflect Golder Associates Ltd’sjudgement based on the site conditions observed at the time of the site inspection on thedate(s) set out in this report, and on information available at the time of preparation of thisreport. This report has been prepared for specific application to this site and it is based, inpart, upon visual observation of the site, subsurface investigation at discrete locationsand depths, and specific analysis of specific chemical parameters and materials during aspecific time interval, all as described in this report.

Unless otherwise stated, the findings cannot be extended to previous or future siteconditions, portions of the site which were unavailable for direct investigation, subsurfacelocations which were not investigated directly, or chemical parameters, materials oranalysis which were not addressed. Substances other than those addressed by theinvestigation described in this report may exist within the site, substances addressed bythe investigation may exist in areas of the site not investigated and concentrations ofsubstances addressed which are different than those reported may exist in areas otherthan the locations from which samples were taken.

If site conditions or applicable standards change or if any additional information becomesavailable at a future date, modifications to the findings, conclusions andrecommendations in this report may be necessary.

Other than by Imperial Oil, copying or distribution of this report, use of or reliance on theinformation contained herein, in whole or in part, is not permitted without the expresswritten permission of Golder Associates Ltd. Nothing in this report is intended toconstitute or provide a legal opinion.

Golder Project No. 13-1520-0502-6075 20 Aes

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LEGEND NOTESCANADIAN NYDROORAPHIC SERVICE EATHYMETRY (OBTAINED 1. VERTICAL REFERENCE: ALL ELEVATIONS SHOWN IN CHART DATUM-10FROM PACIFIC COASTTERMINALS, 1.0 m INTERVAL) 2. ALL DISTANCES AND ELEVATIONS SHOWN IN METRES (Os)

I 3. PIPELINE CHAINAGE SHOWN IS HORIZONTAL DISTANCE ONLY.I PIPELINE WTH CHAINAOE (m)DOES NOT CORRESPOND DIRECTLY WTN TOOL-RUN DISTANCES0+400

PROViDED IN PIPELINE TELEMETRY DATA.Q SEDIMENT GRAB SAMPLE LOCATiON (2000) 4. SAMPLE LOCATiONS HIGHLIGHTED RED AND GREEN INDICATES

• SEDIMENT CORING LOCATION (2013) EXCEEDANCE OR COMPLIANCE WTN DISPOSAL AT SEAREGULATIONS. (REFER TO POLYCYCLIC AROMATIC HYDROCARBON

LOCAT1ONIO SEDIMENT MANAGED BY IOL DETAILED ANALYTICAL RESULTS FIGURE.)

LOCATION ID SEDIMENT POTENTIALLY MANAGED BY IOLREFERENCESREFER TO PROFILE FIGURES FOR COMPLETE REFERENCE LIST.

0 20

TITLE-

SEDIMENT ANALYTICAL RESULTS -SEDIMENT MANAGED OR POTENTIALLY

MANAGED BY IOL

older CADO I 558 1201201129 FIGURE

Associates I I : I::::: I 5

PROJECT Nut 13-1520-0522.6075 FILE No. 101200505870206158

DESIGN EGM 120120Th25 SCALE SCALE

R

SEDIMENTINVESTIGATION

SUMMARY OF ENVIRONMENTAL INVESTIGATIONS RELATEDTO PIPELINE RIGHT-OFWAYGolder Associates Ltd. (Golder) was retained by Imperial Oil Limited (IOL) to characterize thesediment in the pipeline right-of-way (ROW) extending under Burrard Inlet between Burnaby andPort Moody, BC. The purpose of the investigation was to:

Support the removal of portions of pipes from the south portion of the ROW. The ROWcontains two subsurface pipelines (six and twelve inches in diameter) buried in parallel. Thetwelve-inch pipeline carried crude oil and the six-inch pipeline carried refined products. Thepipelines are in maintenance status and are not currently in use. Portions of the pipes need tobe removed to facilitate a dredging project being proposed by Pacific Coast Terminal.

Support lease renewal requirements from the Vancouver Fraser Port Authority.

The investigation has been ongoing since 2009. The level of sampling effort and generalobservations based on the data are as follows:

Surficial sediment chemistry data collected in 2009 indicated that concentrations of mostpotential contaminants of concern were lower than the SEDQCts numerical standards, withthe exception of polycyclic aromatic hydrocarbons (PAHs) in some of the 48 surficial samplescollected from the ROW. The areas with elevated PAHs were limited to the immediate vicinityof the Reed Point Marina (on the south side) and the IOCO Boat Club (on the north side).

Core sediment samples collected in 2013 confirmed that exceedances of SEDQCtsnumerical standards were limited in spatial extent. Samples collected at the current pipelineelevation found that concentrations of PAHs were less than analytical detection limits. A totalof 11 cores were advanced, each with up to 5 discrete samples collected.

• Sediment chemistry data (core and surficial) indicated that the concentrations of cadmiumexceeded Ocean Disposal screening limits in nearly all samples collected from the southportion of the ROW. Cadmium concentrations were similar to those measured in an adjacentproperty to the east, and an evaluation of AVS-SEM indicated that cadmium was unlikely tobe bioavailable.

Sediment chemistry data indicated that the concentrations of total PAHs exceeded OceanDisposal screening limits in 11 of the 14 samples collected from the south portion of the ROWin November 2009. Toxicity testing was conducted on these samples, and adverse effectswere limited to one sample for the Microtox test, and seven samples for the sea urchinfertilization test. There were no effects observed in the amphipod toxicity test.

• Further evaluation of the sea urchin fertilization toxicity data and other supporting dataindicated that the observed effects in the toxicity test were unlikely to be associated withhydrocarbons. Ammonia and sulphides were identified as likely confounding factors in allseven samples that failed to meet the interim pass/fail criterion for the sea urchin fertilizationtest.

• PAH fingerprinting was conducted on selected samples by a specialty analytical laboratory.The fingerprinting results indicate that hydrocarbons in the samples were not associated withpipeline operations (i.e., movement of crude oil and refined products). Hydrocarbons wereattributed to regional sources such as urban runoff or other localized point sources such ascreosote.

A detailed description of sampling methods, results and interpretation of the data collected in2009 have been provided under separate cover. Subsequent files in this appendix provide atabular summary of the 2013 core data as well as the individual certificates of analysis.Interpretation of the available data in the context of the IOL application to remove segments of thepipeline is provided in the body of this report.

Golder Project No. 13-1520-0502-6075 Acs

December 2013 13-1520-0502-6075

Table 1Summary of Sediment Analytical Results - Polycyclic Aromatic Hydrocarbons

Former loco Refinery2225 loco Road, Port Moody, BC

,

pSam te Sample Start End Maxxam .‘ . . .p Sample ID Collection Depth Depth Sample . ‘ . C 4 ,Location

Date (mbgs)(mbgs) ID .

4 . Li- 0.

c’1 x

Sediment Managed by IOLIPS-SD13-03-Ol 20-Apr-13 0.00 0.50 GF0881 <0050 <0.050 <0.050 <0.050 <0.050 0097 0.10 <0.050 <0.060 <0.050 014 <0.050 0.054 <0.090 0.11 0.11 0.23 0.60IPS-SD13-03-02 20-Apr-13 0.70 1.00 GF0883 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050

IPS-SD13-03 IPS-SD13-03-03 20-Apr-13 1.30 2.00 GF0884 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SDI3-03-04 20-Apr-13 2.00 3.00 GF0885 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0,050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0. <0.050 <0.050PS-SDI3-03-05 20-Apr-13 3.20 3.56 GF0886 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0. <0.050 <0.050

IPS-SD13-04-O1 20-Apr-13 0.00 0.50 GF0887 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0. <0.050 <0.050IPS-SDI3-04-02 20-Apr-13 0.70 1.00 GF0889 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0. 0 <0.050 <0.050

IPS-SD13-04 IPS-SD13-04-03 20-Apr-13 1.00 1.80 GF0890 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0. <0.050 <0.050IPS-SD13-04-04 20-Apr-13 2.00 3.00 GF0891 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0,050 <0.050 <0.050 <0.050 <0.050 <0,050 <0. <0.050 <0.050IPS-SD13-04-05 20-Apr-13 3.20 3.69 GF0892 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0. <0.050 <0.050IPS-SDI3-05-01 21-Apr-13 0.00 0.50 GF2339 <0.050 0.15 0.098 0.095 0.14 0.26 0.28 0.067 <0.12 <0.050 0.39 <0.050 0.14 0.054 0.38 0.28 0.62 2.2IPS-SD13-05-02 21-Apr-13 0.50 0.90 GF2341 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050

IPS-SD13-05 IPS-SD13-05-03 21-Apr-13 1.10 2.00 GF2342 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-05-04 21-Apr-13 2.30 3.00 GF2343 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-05-05 21-Apr-13 3.10 3.66 GF2344 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SDI3-08-01 22-Apr-13 0.00 0.50 GF2411 <0.050 <0.050 0.052 0.072 0.080 0.15 0.067 <0.050 0.14 <0.050 0.17 <0.050 <0.050 <0.050 0,063 0.11 0.34 1.0IPS-SD13-08-02 22-Apr-13 0.50 0.80 GF2412 <0.050 0.071 <0.050 0.056 0.089 0.15 0.15 <0.050 <0.080 <0.050 0.22 <0.050 0.079 <0.050 0.17 0.15 0.32 1.1

IPS-SD13-08 IPS-SD13-08-03 22-Apr-13 1.00 1.60 GF2413 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0,050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SDI3-08-04 22-Apr-13 2.00 3.00 GF2414 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0,050 <0.050 <0.050 <0.050 <0.050 <0,050IPS-SD13-08-05 22-Apr-13 3,00 3.35 GF2415 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050

Sediment Potentially Managed by IOLIPS-SDI3-02-0l 20-Apr-13 0.00 0.50 GF0873 <0.050 <0.050 <0.050 <0.050 <0.050 0.083 0.072 <0.050 <0.050 <0.050 0.15 <0.050 <0.050 <0.070 0.12 0.12 0.22 0.60IPS-SD13-02-02 20-Apr-13 0.70 1.00 GF0875 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050

IPS-SD13-02 IPS-SD13-02-03 20-Apr-13 1.20 2.00 GF0876 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SDI3-02-04 20-Apr-13 2.00 2.90 GF0879 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-02-05 20-Apr-13 3.00 3.39 GF0880 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SDI3-06-01 21-Apr-13 0.00 0.50 GF2345 <0.050 0.064 0.087 0.089 0.13 0.23 0.14 0.056 <0.14 <0.050 0.28 0.055 0.075 0.14 0.21 0.23 0.59 1.9IPS-SD13-06-02 21-Apr-13 0.50 0.95 GF2347 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050

IPS-SDI3-06 IPS-SD13-06-03 21-Apr-13 1,00 2.00 GF2348 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-06-04 21-Apr-13 2.00 2.50 GF2350 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-06-05 21-Apr-13 3.00 3.30 GF2351 <0.050 <0.050 <0.050 <0.050 <0,050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-07-01 21-Apr-13 0.00 0.50 GF2352 <0.050 0.052 0.25 0.47 0.57 1.1 0.28 0.32 0.78 0.073 0.64 0.11 0.22 0.094 0.11 0.44 j 6.5IPS-SDI3-07-02 21-Apr-13 0.70 1.00 GF2353 <0.050 0.093 0.092 0.14 0.24 0.26 0.057 <0.11 <0.050 0.41 <0.050 0.14 0.059 0.39 0.31 0.61 2.3

PS-SDI3-07 IPS-SD13-07-03 21-Apr-13 1.40 2.00 GF2354 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SDI3-07-04 21-Apr-13 2.00 3.00 GF2355 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-07-05 21-Apr-13 3.00 3.50 GF2356 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050

IPS-SDO9-15 IPS-SDO9-15 25-May-09 0.00 0.20 95799 0.04 0.09 0.20 0.41 0.43 NA NA NA 0.70 <0.06 0.58 0.10 NA 0.11 0.18 0.37 1.4 6.0IPS-SDO9-30 IPS-SD09-30 2-Dec-09 0.00 0.20 S01930 0.09 0.10 i Li NA NA NA 2.20 0.11 1.6 0.19 NA 0.14 0.17 0.75 4.5 16IPS-SDO9-19 IPS-SD09-19 30-Nov-09 0.00 0.20 R98109 0.05 0.10 0.29 0.85 0.60 NA NA NA 1.1 0.05 1.4 0.10 NA 0.11 0.14 0.49 2.3 9.5

IPS-SDO9-37B IPS-SDO9-37B 4-Dec-09 0.20 0.30 S07392 <0.01 0.01 0.07 0.09 0.07 NR NR NR 0.17 <0.02 0.12 0.02 NR 0.02 0.02 0.09 0.25 1.2Other Core Samples Outside Study Area

IPS-SD13-01-01 20-Apr-13 0.00 0.50 GF0867 <0.050 0.11 0.11 0.10 0.12 0.30 0.26 0.059 <0.15 <0.050 0.40 0.050 0.15 <0.16 0.29 0.30 0.62 2.1IPS-S013-01-02 20-Apr-13 0.70 1.00 GF0869 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050

IPS-SD13-01 IPS-SD13-01-03 20-Apr-13 1.20 2.00 GFOS7O <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SDI3-01-04 20-Apr-13 2.00 2.80 GF0871 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SDI3-01-05 20-Apr-13 3.00 3.63 GF0872 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-09-01 22-Apr-13 0.00 0.50 GF2416 0.099 0.066 0.81 0.91 1.7 0.37 0.53 1.2 0.11 1.0 0.17 0.31 0.18 0.19 0.60 5.3 II

IPS-SDI3-09 PS-SDI3-09-02 22-Apr-13 0.50 0.80 GF2417 <0.050 0.060 0.057 0.054 0.077 0.14 0.14 <0.050 <0.090 <0.050 0.22 <0.050 0.069 0.052 0.18 0.16 0.36 1.2IPS-SD13-09-03 22-Apr-13 1.55 2.00 GF2418 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-10-01 22-Apr-13 0.00 0.50 GF2419 <0.050 0.055 0.19 0.34 0.40 0.71 0.23 0.23 0.53 0.058 0.62 0.078 0.18 0.10 0.13 0.33 1.6 4.4

IPS-S013-10 IPS-SDI3-10-02 22-Apr-13 0.75 1,00 GF2420 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SDI3-10-03 22-Apr-13 1,00 1.40 GF2429 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-11-01 22-Apr-13 0.00 0.50 GF2430 <0.050 <0.050 0.14 0.30 0.28 0.51 0.14 0.16 0.42 <0.050 0.31 0.059 0.11 0.082 0.086 0.22 1.0 3.0

IPS-SD13-1l IPS-SD13-11-02 22-Apr-13 0.50 0.70 GF2431 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050IPS-SD13-11-03 22-Apr-13 1.00 1.89 GF2432 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050 <0.050

RDL 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050 0.050CSR SEDQC19 0.11 0.15 0.29 0.83 0.92 n/s nls n/s 1.0 0.16 1.8 0.17 n/s 0.24 0.47 0.65 1.7 20.0

Disposal at Sea Regulationt n/s n/s n/s n/s n/s n/s n/s n/s n/s n/s n/s n/s n/s n/s n/s n/s n/s 2.5

Notes:<Standards shown are from the BC Contaminated Sites Regulation (CSR) ScheduleS Generic Mel/ne Typical Sediment Criteria - enacted in 1997, and include updates to Janualy 2013.° Concentrations are the lower level l:mits fmm the Disposal at Sea Regulations (SOR1200I-27S) mirrent to November2, 2013 and last amended on September 9.2009.BoidlUndorlined - value eoceeds CSR SEDQCBoll/IRED - value eoceeds Disposal at Sea Regulation Lower Level concentrationmbgs - metres below ground surfacemg/kg - milligram per hilogram dry weightNA - not availablenf S - no standardRDL - reportable detection limit0-less thavAll values reported in mg/kg (milligrams per kilogram).

Page 1 of I Golder Associates

December 2013 13-1520-0502-6075

Table 2Summary of Sediment Analytical Results - Metals

Former loco Refinery2225 loco Road, Port Moody, BC

SampleSampieStartEndMaxxam ‘ . E . .

LocationSamplelD CollectionDepthDepthSamPle . 2 2 . . i

Sediment Managed by IOL

IPS-SD13-03 [ IPS-SDI3-03-O1 20-Apr-13 00 00 GF0881 99 2200 02 14M 61.1 0A7 09 1.47 7,200 43 IOA 72.6 33800 57 1500 359 0231 611 32 755 4,150 25 0A33 17500 7t8 217 Z02 888 61.6 126 75

[ IPS-SD13-03-03 20-Apr-13 1.30 2.00 GF0884 8.51 22200 0.33 10.3 58.5 0.55 0.16 1.45 9160 42.2 11.4 41.7 34500 9.62 11500 398 0.056 6.57 38.2 757 4,300 1.18 0.220 10900 71.4 0.193 0.47 1050 62.3 91.4 9.03

IPS-SD13-04IPS-SDI3-04-0l 20-Apr-13 0.00 0.50 GF0887 7.15 21,100 0.39 I 1 .3 55.4 51 0.17 1 .57 8,460 40.0 10 41 .0 33000 10.6 11,400 375 0.052 45 30 703 4040 1.21 0183 14.400 721 001 0.52 1010 58.8 87.1 8.11IPS-SDI3-04-03 20-Apr-13 1.00 1.80 GF0890 7.65 23,300 0.39 10.9 61.6 0.56 0.17 1.36 10,800 42.7 12.2 42.7 36,300 10.2 11,900 431 0.053 5.18 37.8 752 4620 1.22 0.230 9050 77.5 0.191 0.53 1,110 67.4 96.8 9.54

IPS-SD13-0IPS-SD13-05-01 21-Apr-13 L00 00 GF2339 T67 2700 08 12 59 <OAO 01 1.03 720 34.1 9M 841 3200 6t8 11,100 326 344 86 291 607 3M50 ZOl 0443 15A00 68.1 0183 20 832 55J 109 55

,-

IPS-SDI3-05-03 21-Apr-13 1.10 2.00 GF2342 8.12 22,400 0.33 9.50 55.2 <0.40 0.17 1.47 9,440 41.4 11.0 41.9 34,900 9.92 11800 401 <0.050 5.53 37.2 670 4,330 0.86 0.226 9,130 70.6 0.212 0.44 986 61.9 81.1 9.01

IPs SDI3 0IPS-SDI3-08-01 22-Apr-13 0.00 0.50 GF2411 7.71 19,500 0.36 9.97 48.5 <0.40 0.29 1.90 9,690 38.0 8.97 55.5 29,500 26.8 10400 326 0.198 6.15 30.7 653 3650 1.14 0.338 15,100 79.0 0.222 1.16 811 52.5 95.2 6.43IPS-SDI3-08-03 22-Apr-13 1.00 1.60 GF2413 8.12 20,800 0.35 8.93 53.8 <0.40 0.16 1.43 9,930 38.2 10.2 37.7 32300 8.94 10,600 365 <0.050 4.51 33.9 604 3,920 0.82 0.211 4,810 72.4 0.209 0.43 926 55.8 77.5 7.61

Sediment Pot ntlally Managed by IOL

IPS SD13-02IPS-SDI3-02-01 20-Apr-13 0.00 0.50 GF0873 7.56 21,700 0.56 14.4 58.6 0.46 0.46 1.53 6,810 40.2 10.4 71.2 33,400 40.2 11200 371 0.576 10.3 33.3 714 4,170 1.86 0.342 18,300 70.4 0.219 1.57 896 59.4 115 7.07IPS-SDI3-02-03 20-Apr-13 1.20 2.00 GF0876 7.59 22,700 0.38 12.3 60.7 0.58 0.17 1.76 8,020 43.5 11.5 43.5 36000 9.88 12,200 407 0.058 5.88 38.3 761 4510 1.35 0.221 14300 69.0 0.229 0.44 1,070 64.0 95.6 8.68

IPS-SD13 06IPS-SD13-06-01 21-Apr-13 00 00 GF2345 L87 2t300 81 127 68 <OAO 94 142 79O 5Z2 &97 867 3000 105 820 308 271 68 283 646 3M20 42 14M00 7t5 0242 20 882 56 181 67

-

IPS-SDI3-06-03 21-Apr-13 1.00 2.00 0F2348 8.07 20,500 0.30 8.80 54.7 <0.40 0.16 1.36 8,730 38.2 10.2 37.8 31,800 9.60 10900 358 <0.050 4.43 34.8 598 3690 0.70 0.199 8,540 67.5 0.181 0.43 938 56.1 75.4 7.58

IPS-SDI3-07IPS-SDI3-07-01 21-Apr-13 OMO 50 GF2352 717 2300 58 ill 53 <OAO 55 182 6A40 431 818 105 30j00 63J 110O 308 027 526 26 644 355O 129 676 16A00 657 301 251 822 526 155 6A0IPS-SDI3-07-03 21-Apr-13 1.40 2.00 GF2354 8.22 20400 0.33 9.05 53.3 <0.40 0.17 1.42 12,900 36.9 9.80 37.1 31,400 8.88 10100 354 <0.050 4.04 33.0 629 3,680 0.83 0.207 6050 110 0.205 0.49 949 55.3 73.8 7.63

IPS-SDO9-15 IPS-SDO9-15 25-May-09 0.00 0.20 95799 NA NA NA 11.7 NA NA NA 1.71 NA 42 NA 99.8 NA 49.8 NA NA 0.21 NA NA NA NA NA NA NA NA NA NA NA NA 165 NAIPS-SDO9-19 IPS-SDO9-19 30-Nov-0900 0.20 R98109NA NA NA 12.5 NA NA NA 1.8INA 43 NA 1O5NA 52.9 NA NA 0.21 NA NA NA NA NA NA NA NA NA NA NA NA 164 NAIPS-SDO9-30 IPS-SDO9-30 2-Dec-09 0.00 0.20 S01930 NA NA NA 10.8 NA NA NA 1.84 NA 39 NA 102 NA 45.7 NA NA 0.20 NA NA NA NA NA NA NA NA NA NA NA NA 159 NA

Other Core Samples Outside Study Area

IPS-SD13-O1IPS-SDI3-01-O1 20-Apr-13 0.00 0.50 GF0667 6.49 20400 0.59 15.5 57.4 0.41 0.83 1.56 6,400 451 9.23 96.9 31,000 78.3 10,100 321 0.376 7.75 3(13 698 3,900 2.07 0.516 1800 6T2 (1234 2.79 851 57.3 156 6.83IPS-SD13-01-03 20-Apr-13 1.20 2.00 0F0870 8.14 21,400 0.36 11.0 57.6 0.43 0.16 2.05 9,320 41.1 10.5 40.4 32,800 8.96 11,500 377 0.050 5.52 35.3 753 4,100 1.27 0.202 15,300 73.8 0.233 0.47 1,000 59.1 89.5 7.87

IPS-SD13-09IPS-SDI3-09-01 22-Apr-13 (100 (150 GF2416 92 21,900 010 13.4 5&9 OAO 0.64 2.25 1000 52 (155 120 3900 762 1000 334 0242 6(2 31.1 749 3,810 1.42 0109 15,700 81.2 (1378 Z98 876 5(18 193 615IPS-SDI3-09-03 22-Apr-13 1.55 2.00 GF2418 8.20 7,790 0.19 5.20 18.3 <0.40 <0.10 0.543 8,450 12.4 4.38 11.6 13,000 3.42 3,810 153 <0.050 2.58 11.3 325 961 <0.50 0.076 520 49.5 0.351 0.16 442 24.5 27.2 2.34

IPS-SD13-10IPS-SD13-10-01 22-Apr-13 0.00 0.50 GF2419 7.64 21,200 (167 12.8 57.7 <0.40 0.66 2.27 8,310 48.6 9.00 91.7 31,500 73.6 9,930 323 0223 6.41 29.1 694 3,730 1.47 0.571 13,900 76.9 0.298 2.57 875 59.2 156 7.04IPS-SDI3-10-03 22-Apr-13 1.00 1.40 GF2429 9.10 5,800 0.15 3.68 13.6 <0.40 <0.10 0.383 6,560 8.60 3.34 7.41 9.520 2.39 2,940 115 <0.050 1.5 7.37 226 758 <0.50 0.051 555 39.5 0.326 0.13 336 19.2 20.0 1.49

IPS SDI3 11IPS-SD13-11-01 22-Apr-13 0.00 0.50 GF2430 7.83 15,100 0.44 9.45 39.8 <0.40 0.33 1.20 12300 30.8 7.16 57.8 23,800 36.9 7,470 257 0.121 3.9 20.8 518 2,450 0.78 0.349 8,780 86.6 0.237 1.41 665 43.2 95.9 4.47

- IPS-SD13-11-03 22-Apr-13 1.00 1.89 GF2432 7.81 21,400 0.34 9.95 54.3 <0.40 0.17 1.38 11,300 39.0 10.5 38.4 33,800 9.29 10,200 374 <0.050 4.58 34.6 601 3,290 0.71 0.219 2,580 85.7 0.230 0.43 966 58.6 77.1 7.73RDL 0.010 100 0.10 0.50 0.10 0.40 0.10 0.050 100 1.0 0.30 0.50 100 0.10 100 0.20 0.050 0.10 0.80 10 100 0.50 0.050 100 0.10 0.050 0.10 1.0 2.0 1.0 0.50

CSR SEDQC1t n/s n/s n/s 50.0 n/s fl/S fl/S 5.0 fl/S 190.0 n/s 130.0 n/s 130.0 n/s n/S 0.84 n/s fl/S n/s n/s n/s fl/S fl/S n/s n/s fl/S fl/S n/s 330.0 n/SDisposal at Sea Regulation n/s n/s n/s n/s fl/S n/s n/s 0.6 n/s n/s n/s n/s n/s n/s n/s n/s 0.75 nfs n/s n/s n/s n/s fl/S n/s n/s n/s n/s n/s n/s n/s n/s

Notes:<Standards shown are from the BC Contaminated Sites Regulation (CSR) Schedule 9 Generic Marine Typical Sediment Cnitena - enacted in 1997, and include updates to January 2013.° Concentrations are the lower level limts from the Disposal at Sea Regalationa (50R/2001-275) canent to Novemher 2, 2013 and last amended on September 9, 2009.BotdlUnderllned. valae exceeds CSR SEDQCBold/RED. value exceeds Disposal at Sea Regalation Lower Level concentrationmbgs- metres below ground surfacemg/kg - milligram per kilogram dry weightiv’s. no standardRDL- reportable detectiun limit<.lece thanAll values reported in mg/kg (milligrams per kilogram>

Page 1 of 1 Golder Associates

rvl 2121 m SL,cce Throuçj Sere

Attention: Dan ParksGOLDER ASSOCIATES500-4260 STILL CREEK DRIVEBURNABY, BCCANADA V5C6C6

Task Order#: 4410104800Line Item: 10Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)Your C.O.C. #: 36248601, 36248620, 36248619

Report Date: 2013/05/22This report supersedes all previous reports with the same Maxxam job number

MAXXAM JOB #: B331 191Received: 2013104120, 16:30

Sample Matrix: Sediment# Samples Received: 24

CERTIFICATE OF ANALYSIS

AnalysesElements by ICPMS (total)MoisturePAH in Soil by GO/MS (SIM)Total LMW. HMW, Total PAH CalcpH (2:1 Dl Water Extract)

Remarks:

Quantity Laboratory Method11 BBY7SOP-0000424 BBY8SOP-0001724 BBY8SOP-0002224 BBY Wl-0003311 BBY6SOP-00028

Primary referenceBCMOE.SALMOnt MOE -E 3139EPA 8270DBC MOE Lab MethodCarter, SSMA 16.2

All Blank values are reported. Associated data are not blank corrected.Solids results are based on dry weight except Biota Analyses & Special Waste Oil & Grease.

r Organic Analyses are not corrected for extraction recovery or method blanks. Certain methods (e.g. CARB 429, quinoline,

L all PCDD/F and DBD/DBF) quantitate by the method of isotope dilution

Maxxam Analytics has performed all analytical testing herein in accordance with ISO 17025.

All CCME results met required criteria unless otherwise stated in the report. The CWS PHC methods employed byMaxxam conform to all prescribed elements of the reference method and performance based elements have been

fl validated. All modifications have been validated and proven equivalent following the ‘Alberta Environment Draft Addenda to

U the CWS-PHC, Appendix 6, Validation of Alternate Methods’. Documentation is available upon request. Deviations fromReference Method for the Canada-wide Standard for Petroleum Hydrocarbons in Soil-Tier 1 Method:F2/F3/F4 data reported using validated cold solvent extraction instead of Soxhlet extraction.

Reporting results to two significant figures at the RDL is to permit statistical evaluation and is not intended to be anindication of analytical precision.

All analysis data reported was generated when the analytical methods were in statistical control and criteria for spikerecoveries, reference material recoveries, method blanks data and duplicate precision were met unless otherwise stated.

r All samples were analysed within hold time unless otherwise flagged. All soil samples for BTEX analysis were methanolextracted within 24 hours unless otherwise flagged.

Page 1 of 34

F%./I 21 21 rri

Task Order#: 4410104800Line Item: 10Site#: TP.00131Site Location: 2225 10CC ROAD,PORT MOODY BCProject#: 13-1520-0502-6075 (1327)Your C.O.C. #: 36248601, 36248620, 36248619

500-4260 STILL CREEK DRIVEBURNABY, BCCANADA V5C 6C6

Report Date: 2013105122This report supersedes all previous reports with the same Maxxam job number

CERTIFICATE OF ANALYSIS-2-

MAXXAMJOB#: B331191Received: 2013104120, 16:30This report shall not be reproduced except in full, without the written approval of the laboratory.

Methods used by Maxxam are based upon those found in ‘Standard Methods for the Examination of Water and [Wastewater’, 22nd Edition, published by the American Public Health Association, or on US EPA, protocols found in the’Test Methods for Evaluating Solid Waste’, Physical/Chemical Methods, SW846, 3rd Edition. Other procedures are based

on the methodologies accepted by the appropriate regulatory agency. Methodology briefs are available by written request. rAll work recorded herein has been done in accordance with normal professional standards using accepted testingmethodologies, quality assurance and quality control procedures except where otherwise agreed to by the client and

testing company in writing. Maxxam Analytics is limited in liability to the actual cost of analysis unless otherwise agreed in

writing. There is no other warranty expressed or implied. Your samples will be retained at Maxxam for a period of 45 daysfrom receipt of data or as per contract.

* RPDs calculated using raw data. The rounding of final results may result in the apparent difference.

Encryption KeyVJOco

22 May 2013 17:34:-C7:30‘

Please direct all question regarding this Certificate of Analysis to your Project Manager.

VJ Oco. Burnaby Project ManagerEmail: [email protected]# (604) 639-8422

Maxxam has procedures in place to guard against improper use of the electronic signature and have the required “signatories”, as per section5.10.2 of ISO/IEC 17025:2005(E), signing the reports. For Service Group specific validation please refer to the Validation Signature Page.

LM*am ArIytic* I*temat,*nal Corporation oI M*xx*r* Anaa** *n*by 4606 C*nada Way V5G 160 Telephora(604) 734-7276 Fex(604) 731-0386

Page 2of34

t,i m

Maxxam Job #: B331191Report Date: 2013/05/22

Scc Thrcuo Serce

GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

RESULTS OF CHEMICAL ANALYSES OF SEDIMENT

Maxxam ID GF0867 GF0867 GF0868 GF0870 GF0873Sampling Date 2013/04/20 2013/04/20 2013/04/20 2013/04/20 2013/04/20. 09:20 09:20 09:20 09:40 10:10DCC Number 36248601 36248601 36248601 36248601 36248601

UNITS IPS-SD1301-O1 IPS-SDI3-O1-01 DUP-A IPS-SDI3-01-03 IPS-SDI3-02-01 RDL C BatchLab-Dup

Soluble (2:1) pH pH Units 649 6.50 7.53 8.14 7.56 Io.oio 16763383

RDL = Reportable Detection Limit

h’— ‘ I I GF0874 I GFOS7S I GFOP.81 I GF0882 I GF0884 I=‘‘=““-, I I -- - -- - - --- - - I

Sampling Date 201 3/04/20 201 3/04/20 201 3/04/20 201 3/04/20 201 3/04/2010:10 10:30 11:00 11:00 11:20

I I I I ICCC Number I 36248601 36248601 36248620 36248620 36248620

I IUNITS DUP-B I IPS-SDI 3-02-03 I IPS-SDI3-03-01 DUP-C IPS-SDI3-03-03 I RDL bC Batch

Soluble (2:l)pH IPH Units I 6.89 6.99 J 7.65 I 8.51 0.010 6763383


Maxxam ID GF0887 GF0890Sampling Date 201 3/04/20 201 3/04/20

12:00 13:10DCC Number 36248620 36248619

UNITS IPS-SDI 3-04-01 IPS-SDI 3-04-03 RDL C Batch

Soluble (2:1) pH pH Units 7.15 7.65 10.010 6763383


IPage 3 of 34

I\I1 E2i m


PHYSICAL TESTING (SEDIMENT)

&uc Through Scence

GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10Site#: TROO131Site Location: 2225 IOCO ROAD,PORT MOODY BC

Project #: 13-1520-0502-6075 (1327) rLLiLi

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Li-

Maxxam ID GF0867 GF0868 GF0869 GF0870Sampling Date 2013/04/20 2013/04/20 2013/04/20 2013/04/20

09:20 09:20 09:30 09:40OC Number 36248601 I 36248601 36248601 36248601

UNITS IPS-SDI3-O1-O1 bC Batch DUP-A IPS-SDI3-O1-02 bC Batch IPS-SDI3-01-03 RDL C Batch


Moisture j % 69 I6761640 j 69 68 16761651 64 10.30 16761640

DOC Number

Sampling Date 2013/04/20 2013/04/2009:50 10:00

I UNITS36248601

I GF0871 I GF0872 I I CF0873 I I GP0874 I I=‘.--- I - -- I - — - -- - I I - I

I IPS-SDI3-0i-0436248601

I IPS-SDI3-01-05

I I I I

2013/04/2010:10


I I I I I36248601

C Batch I IPS-SDI3-02-O1

2013/04/2010:10

Moisture I I 61 I I6761640 64 6761651 I 65 Io.3o 6761640

VC Batch36248601

DUP-B

Sampling Date

OC Number

IROL C Batch

2013/04/2010:20

I UNITS36248601

‘1axxam ID I GF0875 I GF0876 I GF0879 I GF0880 I GF0881 I I2013/04/20

10:30

I IPS-SDI3-02-0236248601

2013/04/2010:40

I IPS-SDI3-02-03

———— ————— —— — I I I36248620

—— -—

- I — - I —I I


I IPS-SDI3-02-04

2013/04/20 2013/04/2010:50 11:00

36248620I IPS-SDI3-02-05

Moisture I I I 62 I 61 I 56 I 65 Io30 16761640

36248620I IPS-SDI3-03-O1

Sampling Date

IROL

OC Number

bC Batch

2013/04/2011:00

I UNITS36248620

Maxxam ID I GF0882 GF0883 I GF0884 I GF0885 I GF0886 I I2013/04/20

11:10

ntJp-c36248620

2013/04/2011:20

I ips-sni -flfl236248620

2013/04/2011:30

I IPS-Sr)i.03-O336248620

2013/04/2011:40

I IPS-SD13-fl-0436248620

Moisture I I 63 I 62 61 I I I0.30 16761640

RDL = Reportable Detection Limit -

IRDL bC Batch

Li

LiLiL

LiLi

Page 4of34

P%.’I 21 21 rri mroup

COLDER ASSOCIATESMaxxam Job #:B331191 TaskOrder#:4410104800,Lineltem:10Report Date: 2013/05/22 Site#: TP.00131

Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)



12:00 12:00 13:00 13:10QC Number 36248620 36248620 36248619 36248619

UNITS IPS-SDI 3-04-01 bC Batch DUP-D IPS-SDI 3-04-02 IPS-SDI 3-04-03 RDL C Batch

Moisture % 62 6761651 58 60 60 J030 J6761640

RDL Reportable Detection Limit

Maxxam ID GF0891 GF0892 GF0892Sampling Date 2013/04/20 2013/04/20 2013/04/20

13:20 13:30 13:30COO Number 36248619 36248619 36248619

UNITS IPS-SDI3-04-04 IPS-SDI3-04-05 IPS-SDI3-04-05 RDL C BatchLab-Dup

Moisture I I I 1030 6761640


Page 5 ot34

I\,1 m

Maxxam Job #:B331191Report Date: 2013/05/22

GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10

Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BC

Project #: 13-1520-0502-6075 (1327)

LLH

ELEMENTS BY ATOMIC SPECTROSCOPY(SEDIMENT)

Maxxam ID GF0867 GF0867 GF0868 GF0870

Sampling Date 2013/04/20 2013/04/20 2013/04/20 2013/04/2009:20 09:20 09:20 09:40 —

DOC Number 36248601 36248601 36248601 36248601 —

UNITS IPS-SDI3-O1-O1 IPS-SDI3-O1-O1 DUP-A PS-SD13-O1-O3 RDL C BatchLab-Dup —

rotal Aluminum (Al) mg/kg 20400 20900 22200 21400 100 6763375

rotal Antimony (Sb) mg/kg 0.59 0.60 0.69 0.36 0.10 6763375

fotal Arsenic (As) mg/kg 15.5 15.8 17.0 11.0 0.50 6763375

Total Barium (Ba) mg/kg 57.4 57.8 63.5 57.6 0.10 6763375

Total Beryllium (Be) mg/kg 0.41 0.42 0.43 0.43 0.40 6763375

Total Bismuth (Bi) mg/kg 0.83 0.83 0.89 0.16 0.10 6763375

Total Cadmium (Cd) mg/kg 1.56 1.55 1.67 2.05 0.050 6763375

Total Calcium (Ca) mg/kg 6400 6550 6860 9320 100 6763375

rotal Chromium (Cr) mg/kg 45.7 47.5 48.9 41.1 1.0 6763375

Total Cobalt(Co) mg/kg 9.23 9.43 10.1 10.5 0.30 6763375

fotal Copper (Cu) mg/kg 96.9 98.5 107 40.4 0.50 6763375

Total Iron (Fe) mg/kg 31000 32200 33900 32800 100 6763375

Total Lead (Pb) mg/kg 78.3 79.1 88.0 8.96 0.10 6763375

Total Magnesium (Mg) mg/kg 10100 10300 11100 11500 100 6763375

Total Manganese (Mn) mg/kg 321 324 356 377 0.20 6763375

Total Mercury (Hg) mg/kg 0.376 0.364 0.371 0.050 0.050 6763375

Total Molybdenum (Mo) mg/kg 7,75 7.66 8.47 5.52 0.10 6763375

Total Nickel (Ni) mg/kg 30.3 30.6 32.5 35.3 0.80 6763375

Total Phosphorus (P) mg/kg 698 717 770 753 10 6763375

Total Potassium (K) mg/kg 3900 3970 4230 4100 100 6763375

Total Selenium (Se) mg/kg 2.07 2.31 2.39 1.27 0.50 6763375

Total Silver (Ag) mg/kg 0.516 0.598 0.623 0.202 0.050 6763375

Total Sodium (Na) mg/kg 18000 18100 18400 15300 100 6763375

Total Strontium (Sr) mg/kg 67.2 69.5 73.4 73.8 0.10 6763375

Total Thallium (TI) mg/kg 0.234 0.248 0.259 0.233 0.050 6763375

Total Tin (Sn) mg/kg 2.79 2.80 3.19 0.47 0.10 6763375

Total Titanium (Ti) mg/kg 851 849 884 1000 1.0 6763375

Total Vanadium (V) mg/kg 57.3 58.6 61.0 59.1 2.0 6763375

Total Zinc (Zn) mg/kg 156 160 167 89.5 1.0 6763375

Total Zirconium (Zr) mg/kg 6.83 6.79 7.05 7.87 0.50 6763375


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Page 6 of 34

E IT1 SucceTrcuç

GOLDER ASSOCIATES

Maxxam Job #: B331191 Task Order#: 4410104800, Line Item: 10

Report Date: 2013/05/22 Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

ELEMENTS BY ATOMIC SPECTROSCOPY (SEDIMENT)

Maxxam ID GF0873 GF0874 GF0876 GF0881Sampling Date 2013/04/20 2013/04/20 201 3/04/20 201 3/04/20

10:10 10:10 10:30 11:00QC Number 36248601 36248601 36248601 36248620

UNITS IPS-SDI3-02-01 DUP-B IPS-SDI3-02-03 IPS-S013-03.O1 RDL C Batch

Total Aluminum (Al) mg/kg 21700 20100 22700 22000 100 6763375

otal Antimony (Sb) mg/kg 0.56 0.55 0.38 0.62 0.10 6763375

Total Arsenic (As) mg/kg 14.4 14.1 12.3 14.0 0.50 6783375


Total Beryllium (Be) mg/kg 0.46 0.44 0.58 0.47 0.40 6763375




Total Chromium (Cr) mg/kg 40.2 38.8 43.5 43.3 1.0 6763375

Total Cobalt(Co) mg/kg 10.4 9.59 11.5 10.4 0.30 6763375

otal Copper (Cu) mg/kg 71.2 69.0 43.5 72.6 0.50 6763375


Total Lead (Pb) mg/kg 40.2 43.1 9.88 57.6 0.10 6763375

otal Magnesium (Mg) mg/kg 11200 10900 12200 11500 100 6763375

otal Manganese (Mn) mg/kg 371 336 407 359 0.20 6763375

Total Mercury (Hg) mg/kg 0.576 0.206 0.058 0.231 0.050 6763375

Total Molybdenum (Mo) mg/kg 10.3 9.16 5.88 6.71 0.10 6763375




Total Selenium (Se) mg/kg 1.86 1.72 1.35 2.15 0.50 6763375





Total Tin (Sn) mg/kg 1.57 1.64 0.44 2.02 0.10 6763375



Total Zinc (Zn) mg/kg 115 116 95.6 126 1.0 6763375



Page 7of34


Succ. Thrcuçjh Senc1



Project #: 13-1520-0502-6075 (1327)


Li

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Maxxam ID GF0882 GF0882 GF0884 GF0887

Sampling Date 2013/04/20 2013/04/20 2013/04/20 2013/04/2011:00 11:00 11:20 12:00 —

CCC Number 36248620 36248620 36248620 36248620UNITS DUP-C DUP-C Lab-Dup C Batch IPS-SDI3-03-03 IPS-SDI3-04-01 RDL C Batch

Total Aluminum (Al> mg/kg 20800 6763375 22200 21100 100 6763375

Total Antimony (Sb) mg/kg 0.72 6763375 0.33 0.39 0.10 - 6763375

Total Arsenic (As) mg/kg 15.0 6763375 10.3 11.3 0.50 6763375

Fotal Barium (Ba) mg/kg 62.4 6763375 58.5 55.4 0.10 6763375

Total Beryllium (Be) mg/kg 0.44 6763375 0.55 0.51 0.40 6763375

Total Bismuth (Bi) mg/kg 0.96 6763375 0.16 0.17 0.10 6763375

Total Cadmium (Cd) mg/kg 1.38 6763375 1.45 1.57 0.050 6763375


Total Chromium (Cr) mg/kg 42.6 6763375 42.2 40.0 1.0 6763375

Total Cobalt (00) mg/kg 9.97 6763375 11.4 10.6 0.30 6763375

Total Copper (Cu) mg/kg 85.3 6763375 41.7 41.0 0.50 6763375


Total Lead (Pb) mg/kg 82.0 6763375 9.62 10.6 0.10 6763375



Total Mercury (Hg) mg/kg 0.290 0.307 6830378 0.056 0.052 0.050 6763375

Total Molybdenum (Mo) mg/kg 5.57 6763375 6.57 4.95 0.10 6763375

Total Nickel (Ni) mg/kg 29.9 6763375 38.2 35.0 0.80 6763375



Total Selenium (Se) mg/kg 2.27 6763375 1.18 1.21 0.50 6763375

Total Silver (Ag) mg/kg 0.574 6763375 0.220 0.183 0.050 6763375


Total Strontium (Sr) mg/kg 70.5 6763375 71.4 72.7 0.10 6763375

Total Thallium (TI) mg/kg 0.215 6763375 0.193 0.201 0.050 6763375

Total Tin (Sn) mg/kg 2.61 6763375 0.47 0.52 0.10 6763375

otal Titanium (Ti) mg/kg 886 6763375 1050 1010 1.0 6763375

Total Vanadium (V) mg/kg 59.3 6763375 62.3 58.8 2.0 6763375

Total Zinc (Zn) mg/kg 140 6763375 91.4 87.1 1.0 6763375

otal Zirconium (Zr) mg/kg 6.99 6763375 9.03 8.11 0.50 6763375

RDL Reportable Detection LimitLab-Dup = Laboratory Initiated Duplicate

Page 8of34

I’sA m

Maxxam Job #: 8331191Report Date: 2013/05/22

Succ Thruçjh 5cerr*



Maxxam ID GF0890Sampling Date 2013/04/20

13:10OC Number 36248619 —

UNITS IPS-SDI 3-04-03 RDL C Batch

Total Aluminum (Al) mg/kg 23300 100 6763375

Total Antimony (Sb) mg/kg 0.39 0.10 6763375

Total Arsenic (As) mg/kg 10.9 0.50 6763375

Total Barium (Ba) mg/kg 61.6 0.10 6763375

Total Beryllium (Be) mg/kg 0.56 0.40 6763375

Total Bismuth (Bi) mg/kg 0.17 0.10 6763375

Total Cadmium (Cd) mg/kg 1.36 0.050 6763375

Total Calcium (Ca) mg/kg 10800 100 6763375

Total Chromium (Cr) mg/kg 42.7 1.0 6763375

Total Cobalt(Co) mg/kg 12.2 0.30. 6763375

Total Copper (Cu) mg/kg 42.7 0.50 6763375

Total Iron (Fe) mg/kg 36300 100 6763375

Total Lead (Pb) mg/kg 10.2 0.10 6763375

Total Magnesium (Mg) mg/kg 11900 100 6763375

otal Manganese (Mn) mg/kg 431 0.20 6763375

Total Mercury (Hg) mg/kg 0.053 0.050 6763375

Total Molybdenum (Mo) mg/kg 5.18 0.10 6763375

Total Nickel (Ni) mg/kg 37.8 0.80 6763375

Total Phosphorus (P) mg/kg 752 10 6763375

Total Potassium (K) mg/kg 4620 100 6763375

Total Selenium (Se) mg/kg 1.22 0.50 6763375

Total Silver (Ag) mg/kg 0.230 0.050 6763375

Total Sodium (Na) mg/kg 9050 100 6763375

Total Strontium (Sr) mg/kg 77.5 0.10 6763375

Total Thallium (TI) mg/kg 0.191 0.050 6763375

Total Tin (Sn) mg/kg 0.53 0.10 6763375

Total Titanium (Ti) mg/kg 1110 1.0 6763375

Total Vanadium (V) mg/kg 67.4 2.0 6763375

Total Zinc (Zn) mg/kg 96.8 1.0 6763375

Total Zirconium (Zr) mg/kg 9.54 0.50 6763375


Page 9of34

I\/1 m


Page 10of34

SucGe ThroUgh Scênc

GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BC

uL0UL

Project #: 13-1520-0502-6075 (1327>

CSR PAH IN SOIL BY GC-MS (SEDIMENT)

Maxxam ID GF0867 GF0868 GF08683ampling Date 2013/04/20 201 3/04/20 201 3/04/20

09:20 — 09:20 09:20)QC Number 36248601 — 36248601 — 36248601 —

UNITS IPS-SDI3-O1-O1 RDL DUP-A RDL DUP-A Lab-Dup RDL C Batch

Naphthalene mg/kg 0.29 0.050 0.26 0.050 0.22 0.050 6767379

2-Methylnaphthalene mg/kg <0.16 (1) 0.16 <0.13 (1) 0.13 <0.15 (1) 0.15 6767379

cenaphthyIene mg/kg 0.11 0.050 0.091 0.050 0.083 0.050 6767379

Acenaphthene mg/kg <0.050 0.050 <0.050 0.050 <0.050 0.050 6767379

Fluorene mg/kg 0.050 0.050 <0.050 0.050 <0.050 0.050 6767379

Phenanthrene mg/kg 0.30 0.050 0.24 0.050 0.23 0.050 6767379

Anthracene mg/kg 0.11 0.050 0.084 0.050 0.076 0.050 6767379

Fluoranthene mg/kg 0.40 0.050 0.32 0.050 0.28 0.050 6767379

Pyrene mg/kg 0.62 0.050 0.50 0.050 0.46 0.050 6767379

Benzo(a)anthracene mg/kg 0.10 0.050 0.071 0.050 0.076 0.050 6767379

Chrysene mg/kg <0.15 (1) 0.15 <0.12 (1) 0.12 <0.12 (1) 0.12 6767379

Benzo(b&j)fluoranthene mg/kg 0.30 0.050 0.20 0.050 0.19 0.050 6767379

Benzo(k)fluoranthene mg/kg 0.059 0.050 0.071 0.050 0.071 0.050 6767379

Benzo(a)pyrene mg/kg 0.12 0.050 0.084 0.050 0.085 0.050 6767379

Indeno(1,2,3-cd)pyrene mg/kg 0.15 f050 0.095 0.050 0.098 050 6767379

Dibenz(a,h)anthracene mg/kg <0.050 0.050 <0.050 0.050 <0.050 050 6767379

Benzo(g,h,i)perylene mg/kg 0.26 0.050 0.18 0.050 0.18 0.050 6767379

Low Molecular Weight PAH’s mg/kg 0.86 0.16 0.68 0.13 — 6758782

High MolecularWeightPAH’s mg/kg 1.2 0.15 0.97 0.12 — 6758782

Total PAH mg/kg 2.1 0.16 1.6 0.13 — 6758782

ExtractionSurrogate Recovery (%)

D10-ANTHRACENE (sur.) % 102 — 77 71 — 6767379

D8-ACENAPHTHYLENE (sur.) % 96 — 79 — 79 — 6767379

D8-NAPHTHALENE (sur.) % 99 — 83 — 83 — 6767379

TERPHENYL-D14 (sur.) % 106 — 77 — 76 — 6767379

RDL = Reportable Detection LimitLab-Dup = Laboratory Initiated Duplicate

( 1 ) RDL raised due to sample matrix interference.

C

I\/I 21 21 rn Thugji

GOLDER ASSOCIATESMaxxam Job #: B331191 Task Order#: 4410104800, Line Item: 10

Report Date: 2013/05/22 Site#: TROO131Site Location: 2225 10CC ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)


Maxxam ID GF0869 GF0870 GF0871 GF0872Sahipling Date 201 3/04/20 201 3/04/20 201 3/04/20 201 3/04/20

. 09:30 09:40 09:50 10:00 —

)OC Number 36248601 36248601 36248601 36248601•. UNITS IPS-SDI3-01-02 IPS-S013-O1-03 IPS-SDI3-O1-04 IPS-SDI3-O1-05 RDL C Batch

Naphtflalene mg/kg <0050 <0.050 <0.050 <0.050 0.050 6767379

2-MethIhaphthaIene mg/kg <0.050 <0.050 <0.050 <0050 0.050 6767379

cenaphthyIene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Acenphthene mg/kg <0.050 <0.050 <0050 <0.050 0.050 6767379

Iuoei; mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Phenäñthierie mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

nthãde mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

FIuàiañthene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Pyrehe’’ mg/kg <0.050 <0.050 <0.050 <0050 0.050 6767379

Benzó(a)anthracene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Chrysehe mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Beri±o(b&j)fluoranthene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Benzo(k)fluoranthene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Benzo(a)pyrene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

lndeno(1,2.3-cd)pyrene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Dibenz(a,h)anthracene mg/kg <0.050 <0.050 <0.050 <0050 0.050 6767379

Benzo(g,h,i)perylene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Low Molecular Weight PAHs mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6758782

High Molecular Weight PAH’s mg/kg <0.050 <0050 <0.050 <0.050 0.050 6758782

Total PAH mg/kg <0.050 <0050 <0.050 <0.050 0050 6758782

ExtractionSurrogate Recovery (%) —

D10-ANTHRACENE (sur.) % 97 91 87 87 — 6767379

08-ACENAPHTHYLENE (sur.) % 84 80 80 67 6767379

D8-NAPHTHALENE (sur.) % 89 85 93 85 6767379

TERPHENYL-D14 (sur.) % 95 90 92 84 6767379


Page 11 of 34

m Sjces Thrjh .Scerc

GOLDER ASSOCIATES


Report Date: 2013/05/22 Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BC

Project #: 13-1520-0502-6075 (1327)


Maxxam ID GF0873 GF0874 GF0874Sampling Date 2013/04/20 2013/04/20 2013/04/20

10:10 — 10:10 j 10:10 —

OC Number 36248601 — 36248601 36248601 —

UNITS IPS-SDI3-02-O1 RDL C Batch DUP-B IDUP-B Lab-Dup RDL C Batch

Naphthalene mg/kg 0.12 0.050 6767379 0.050 0.075 0.050 6767389

2-Methylnaphthalene mg/kg <0.070 (1) 0.070 6767379 <0.050 <0.050 050 6767389

tcenaphthylene mg/kg <0.050 0.050 6767379 <0.050 <0.050 0.050 6767389

tcenaphthene mg/kg <0.050 0.050 6767379 <0.050 <0.050 0.050 6767389

Fluorene mg/kg <0.050 0.050 6767379 <0.050 <0.050 0.050 6767389

Phenanthrene mg/kg 0.12 0.050 6767379 0.067 0.074 0.050 6767389

Anthracene mg/kg <0.050 0.050 6767379 <0.050 <0.050 0.050 6767389

Fluoranthene mg/kg 0.15 0.050 6767379 0.11 0.12 0.050 6767389

Pyrerie mg/kg 0.22 0.050 6767379 0.16 0.19 0.050 6767389

Benzo(a)anthracene mg/kg <0.050 0.050 6767379 <0.050 <0.050 0.050 6767389

Chrysene mg/kg <0.050 0.050 6767379 <0.050 <0.050 0.050 6767389

Benzo(b&j)fluoranthene mg/kg 0.083 0.050 6767379 0.087 0.088 0.050 6767389

Benzo(k)fluoranthene mg/kg <0.050 0.050 6767379 <0.050 <0.050 0.050 6767389

Benzo(a)pyrene mg/kg <0.050 0.050 6767379 <0.050 <0.050 0.050 6767389

Indeno(1 ,2,3-cd)pyrene mg/kg <0.050 0.050 6767379 <0.050 <0.050 0.050 6767389

Dibenz(a.h)anthracene mg/kg <0.050 0.050 6767379 <0.050 <0.050 0.050 6767389

Benzo(g,h,i)perylene mg/kg 0.072 0.050 6767379 0.072 0.081 0.050 6767389

Low Molecular Weight PAH’s mg/kg 0.23 0.070 6758782 0.12 0.050 6758782

High Molecular Weight PAH’s mg/kg 0.37 0.050 6758782 0.27 0.050 6758782

Total PAH mg/kg 0.60 0.070 6758782 0.38 0.050 6758782


D10-ANTHRACENE (sur.) % 83 — 6767379 82 83 — 6767389

D8-ACENAPHTHYLENE (sur.) % 77 — 6767379 82 86 — 6767389

D8-NAPHTHALENE (sur.) % 83 — 6767379 80 81 — 6767389

TERPHENYL-D14 (sur.) % 78 — 6767379 93 95 — 6767389

RDL = Reportable Detection LimitLab-Dup = Laboratory Initiated Duplicate


Page 12 of 34

rd1 2521 m


Sxe1ujh Scece’

GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10Site#: TP.00131Site Location: 2225 10CC ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

CC


CCCCC


10:20 10:30 10:40 10:50 —

OC Number 36248601 36248601 36248620 36248620 —

: ‘- UNITS IPS-SDI3-02-02 IPS-SDI3-02-03 IPS-SDI3-02-04 IPS-S013-02-05 RDL C Batch

Naphthalene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

2-Methylnaphthalene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Acenaphthylene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

ene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

rene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

ne mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

ene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

mg/kg <0.050

Benzo(b&j)fluoranthene

o(8)anthracene mg/kg <0.050 <0.050 <0 050

<0.050 <0.050

mg/kg <0.050 <0.050 <0.050

<0.050 0.050 6767379

mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

<0.050 0.050 6767379

<0.050 0.050 6767379Chiyene

Benzo(k)fluoranthene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379


lndeno(1 ,2,3-cd)pyrene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Dibenz(a,h)anthracene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Benzo(g,h,i)perylene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Low Molecular Weight PAHs mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6758782

High Molecular Weight PAHs mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6758782

Total PAH mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6758782


D10-ANTHRACENE (sur.) % 86 98 90 98 — 6767379

D8-ACENAPHTHYLENE (sur.) % 74 79 76 79 6767379

D8-NAPHTHALENE (sur.) % 81 90 87 93 6767379

TERPHENYL-D14 (sur.) % 80 92 86 93 6767379


Page 13of34

ri m


SucC Through Sc

GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10Site#: TP.00131Site Location: 2225 10CC ROAD PORT MOODY BC

Project #: 13-1520-0502-6075 (1327>

Maxxam ID GF0881 GF0882 GF08833ampIing Date 2013/04/20 201 3/04/20 2013/04/20

11:00 11:00 11:10)OC Number 36248620 — 36248620 — 36248620 —

UNITS IPS-SDI3-O3-01 RDL DUP-C RDL IPS-SDI3-03-02 RDL C Batch

Naphthalene mg/kg 0.11 0.050 0.17 0.050 <0.050 0.050 6767379

2-Methylnaphthalene mg/kg <0.090 (1) 0.090 <0.12 (1) 0.12 <0.050 0.050 6767379

.cenaphthylene mg/kg <0.050 0.050 0.060 0.050 <0.050 0.050 6767379

cenaphthene mg/kg <0.050 0.050 <0.050 0.050 <0.050 0.050 6767379

Fluorene mg/kg <0.050 0.050 <0.050 0.050 <0.050 0.050 6767379

Phenanthrene mg/kg 0.11 0.050 0.16 0.050 <0.050 0.050 6767379

Anthracene mg/kg <0.050 0.050 0.070 0.050 <0.050 0.050 6767379

Fluoranthene mg/kg 0.14 0.050 0.22 0.050 <0.050 0.050 6767379

Pyrene mg/kg 0.23 0.050 0.37 0.050 <0.050 0.050 6767379

Benzo(a)anthracene mg/kg <0.050 0.050 0.059 0.050 <0.050 0.050 6767379

Chrysene mg/kg <0.060 (1) 0.060 <0.10 (1) 0.10 <0.050 0.050 6767379

Benzo(b&j)fluoranthene mg/kg 0.097 050 0.16 0.050 <0.050 0.050 6767379

Benzo(k)fluoranthene mg/kg <0.050 0.050 0.054 0.050 <0.050 0.050 6767379

Benzo(a)pyrene mg/kg <0.050 0.050 0.067 0.050 <0.050 t050 6767379

ncleno(1,2,3-cd)pyrene mg/kg 0.054 0.050 0.082 0.050 <0.050 0.050 6767379

Dibenz(a,h)anthracene mg/kg <0.050 0.050 <0.050 0.050 <0.050 0.050 6767379

Benzo(g,h.i)perylene mg/kg 0.10 0.050 0.16 0.050 <0.050 0.050 6767379

Low Molecular Weight PAHs mg/kg 0.23 0.090 0.46 0.12 <0.050 0.050 6758782

High Molecular Weight PAHs mg/kg 0.37 0.060 0.72 0.10 <0.050 0.050 6758782

Total PAH mg/kg 0.60 0.090 1.2 0.12 <0.050 0.050 6758782


D10-ANTHRACENE (sur.) % 85 — 90 — 87 — 6767379



TERPHENYL-D14 (sur.) % 80 — 86 — 85 — 6767379



UED


Li

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U

Page 14 of 34

IMaxxam Job #: B331191Report Date: 2013/05/22


Succs-Thrug Scerc

GOLDER ASSOCIATESTask Orcier#: 4410104800, Line Item: 10Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)


U

Maxxam IDSampling Date

GF08842013/04/20

11:20

GF08852013/04/20

11:30

GF08862013/04/20

11:402013/04/20

12:00[.

OC Number 36248620 36248620 36248620 36248620UNITS IPS-SDI3-03-03 IPS-SDI3-03-04 IPS-S013-03-05 IPS-S013-04-01 RDL C Batch

4aphthalene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

-MethyInaphthalene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

cena$hthylene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

ceriaphthene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Iuôre,e. mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

éne mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

e mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

he mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Benzo(a)anthracene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Ceri& mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Benzo(b&j)fluoranthene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Benzq(k)fluoranthene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379


Indeno(1 2,3-cd)pyrene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Dibenz(a,h)anthracene mg/kg <0.050 <0.050 <0.050 <0.050 X050 6767379

Benzo(gh,i)perylene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6767379

Low Molecular Weight PAHs mg/kg <0.050 <0.050 <0.050 <0.050 0050 6758782

High Molecular Weight PAH’s mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6758782

otal PAH mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6758782


D10-ANTHRACENE (sur.) % 88 85 96 75 — 6767379

D8-ACENAPHTHYLENE (sur.) % 66 73 79 73 6767379

D8-NAPHTHALENE (sur.) % 82 83 94 84 — 6767379

ERPI-IENYL-D14 (sur.) % 83 80 93 76 6767379

czPage 15of34

I’sl El rTl



Success Thruu0hSceflcee



Project #: 13-1520-0502-6075 (1327)

Maxxam ID GF0888 GF0889 I GF0890 GF0891

Sampling Date 2013/04/20 2013/04/20 2013/04/20 2013/04/2012:00 13:00 1 13:10 13:20

COC Number 36248620 36248619 I 36248619 36248619 —

UNITS DUP-D IPS-S013-04-02 pc Batch IPS-SDI3-04-03 IPS-SDI3-04-04 C Batch

Naphthalene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

2-Methylnaphthalene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

cenaphthylene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Acenaphthene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Fluorene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Phenanthrene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Anthracene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Fluoranthene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Pyrene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Benzo(a)anthracene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Chrysene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Benzo(t&j)fluoranthene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Benzo(k)fluoranthene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Benzo(a)pyrene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Indeno(1,2,3-cd)pyrene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Dibenz(a,h)anthracene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Benzo(g,h,i)perylene mg/kg <0.050 <0.050 6767379 <0.050 <0.050 0.050 6767389

Low Molecular Weight PAH’s mg/kg <0.050 <0.050 6758782 <0.050 <0.050 0.050 6758782

High Molecular Weight PAHs mg/kg <0.050 <0.050 6758782 <0.050 <0.050 0.050 6758782

lotal PAH mg/kg <0.050 <0.050 6758782 <0.050 <0.050 0.050 6758782


D10-ANTHRACENE (sur.) % 90 89 6767379 88 86 — 6767389

D8-ACENAPHTHYLENE (sur.) % 68 65 6767379 79 76 — 6767389

D8-NAPHTHALENE (sur.) % 84 84 6767379 82 81 — 6767389

TERPHENYL-D14 (sur.) % 84 85 6767379 100 97 — 6767389


[LL

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11

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Page 16 of 34 L

lvi m


Succe Thruh Scen,%

GOLDER ASSOCIATESTask Orcler#: 4410104800, Line Item: 10Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

Maxxam ID GF0892Sampling Date 2013/04/20

13:30)OC Number 36248619

UNITS IPS-SDI3-04-05 RDL C Batch

Naphthalene mg/kg <0.050 0.050 6767389

2-Methylnaphthalene mg/kg <0.050 0.050 6767389

Acenaphthyleno mg/kg <0.050 0.050 6767389

cenaphthene mg/kg <0.050 0.050 6767389

Fluorene mg/kg <0.050 0.050 6767389

Phenanthrene mg/kg <0.050 0.050 6767389

tnthracene mg/kg <0.050 0.050 6767389

Fluoranthene mg/kg <0.050 0.050 6767389

Pyrene mg/kg <0.050 0.050 6767389

Benzo(a)anthracene mg/kg <0.050 0.050 6767389

Chrysene mg/kg <0.050 0.050 6767389

Benzo(b&j)fluoranthene mg/kg <0.050 0.050 6767389

Benzo(k)fluoranthene mg/kg - <0.050 0.050 6767389

Benzo(a)pyrene mg/kg <0.050 0.050 6767389

lndeno(1,23-cd)pyrene mg/kg <0.050 0.050 6767389

Dibenz(a,h)anthracene mg/kg <0.050 0.050 6767389

Benzo(g,h,i)perylene mg/kg <0.050 0.050 6767389

Low Molecular Weight PAH’s mg/kg <0.050 0.050 6758782

High Molecular Weight PAH’s mg/kg <0.050 0.050 6758782

Total PAH mg/kg <0.050 0.050 6758782


D10-ANTHRACENE (sur.) % 79 — 6767389

D8-ACENAPHTHYLENE (sur.) % 62 — 6767389

D8-NAPHTHALENE (sur.) % 77 — 6767389

TERPHENYL-D14 (sur.) % 91 — 6767389



Page 17of34

r%/i


Succ Through Sr%ce


Test Summary

Maxxam ID GF0867Sample ID IPS-SD13-01-01

Matrix Sediment

Collected 2013/04/20Relinquished 201 3/04/20

Received 2013/04/20

Test Description Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6763375 201 3/04/24 201 3/04/24 David JungMoisture BAL/BAL 6761640 N/A 2013/04/24 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/25 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6758782 N/A 2013/04/26 Automated StatchkoH (2:1 DI Water Extract) PH/PH 6763383 201 3/04/24 2013/04/24 Nadzida Stanic

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Maxxam ID GF0867 Dup Collected 201 3/04/20Sample ID IPS-SD13-01-01 Relinquished 2013/04/20 V

Matrix Sediment Received 2013/04/20

Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPMIMS 6763375 201 3/04/24 2013/04/24 David JungpH (2:1 Dl Water Extract) PH/PH 6763383 201 3/04/24 201 3/04/24 Nadzida Stanic

Maxxam ID GF0868 Collected 2013/04/20Sample ID DUP-A Relinquished 2013/04/20


Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6763375 201 3/04/24 201 3/04/24 David JungMoisture BAL/BAL 6761651 N/A 201 3/04/24 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/25 Vidya BorshettarTotal LMW, HMW, Total PAH Caic GC/MSD 6758782 N/A 201 3/04/26 Automated Statchk V

pH (2:1 Dl Water Extract) PH/PH 6763383 201 3/04/24 2013/04/24 Nadzida Stanic

Maxxam ID GF0868 Dup Collected 2013/04/20Sample ID DUP-A Relinquished 2013/04/20

Matrix Sediment Received 201 3/04/20

Test Description Instrumentation Batch Extracted Analyzed AnalystIPAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/25 Vidya Borshettar

Maxxam ID GF0869 Collected 2013/04/20Sample ID IPS-SD13-01-02 Relinquished 2013/04/20


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6761651 N/A 2013/04/24 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/25 Vidya BorshettarTotal LMW, HMW, Total PAH Caic GC/MSD 6758782 N/A 2013/04/26 Automated Statchk

[7p1L

LPU

Page 18of34

rvl m


Succs Tmc’ugh Scnc

GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10Site#: TP00131Site Location: 2225 1000 ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

Test Summary

Page 19 of 34

Maxxam ID GF0870Sample ID PS-SD13-01-03

Matrix Sediment

Test Description

1 Elements by ICPMS (total)

r MoisturePAH in Soil by GC/MS (SIM)Total LMW, HMW, Total PAH CaicH (2:1 Dl Water Extract)

JZ

ICPM/MSBAL/BALGC/MSDGC/MSDPH/PH

Batch67633756761640676737967587826763383

Extracted2013/04/24N/A2013/04/23N/A2013/04/24

Collected 2013/04/20Relinquished 2013/04/20

Received 2013/04/20

AnalystDavid JungLolita ObusanVidya BorshettarAutomated StatchkNadzida Stanic

Analyzed2013/04/242013/04/242013/04/252013/04/262013/04/24

Maxxam ID GF0871 Collected 2013/04/20Sample ID IPS-SD1 3-01-04 Relinquished 2013/04/20


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6761640 N/A 201 3/04/24 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/25 Vidya BorshettarTotal LMW, HMW, Total PAH Cab GC/MSD 6758782 N/A 201 3/04/26 Automated Statchk

Maxxam ID GF0872 Collected 201 3/04/20Sample ID IPS-SD13-01-05 Relinquished 2013/04/20


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6761640 N/A 201 3/04/24 Lolita ObusanPAH in Soil by GCfMS (SIM) GC/MSD 6767379 2013/04/23 201 3/04/25 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6758782 N/A 201 3/04/26 Automated Statchk

Maxxam ID GF0873 Collected 2013/04/20Sample ID IPS-SD13-02-O1 Relinquished 2013/04/20


Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6763375 201 3/04/24 201 3/04/24 David JungMoisture BALJBAL 6761651 N/A 201 3/04/24 Lolita ObusanPAH in Soil by GO/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/25 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6758782 N/A 201 3/04/26 Automated StatchkpH (2:1 DI Water Extract) PH/PH 6763383 201 3/04/24 201 3/04/24 Nadzida Stanic

Maxxam ID GF0874 Collected 2013/04/20Sample ID DUP-B Relinquished 2013/04/20


Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6763375 201 3/04/24 201 3/04/24 David JungMoisture BAL/BAL 6761640 N/A 201 3/04/24 Lolita ObusanPAH in Soil by GO/MS (SIM) GC/MSD 6767389 201 3/04/23 201 3/04/26 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GO/MSD 6758782 N/A 201 3/04/26 Automated StatchkpH (2:1 Dl Water Extract) PH/PH 6763383 201 3/04/24 201 3/04/24 Nadzida Stanic

lvi m


SuccesThroujh Sence4


Site#: TP.00131Site Location: 222510CC ROAD,PORT MOODY BC

Project #: 13-1520-0502-6075 (1327)

Maxxam ID GF0874 DupSample ID DUP-B

Matrix Sediment

Extracted2013/04/23


Received 2013/04/20

Maxxam ID GF0875Sample ID IPS-SDI3-02-02

Matrix Sediment


Received 2013/04/20

{Jri

Test Summary

I

Test Description Instrumentation Batch Analyzed Analyst

PAH in Soil by GC/MS (SIM) GC/MSD 6767389 201 3/04/26 Vidya Borshettar

Test Description Instrumentation Batch Extracted Analyzed Analyst

Moisture BAL/BAL 6761640 N/A 201 3/04/24 Lolita Obusan

PAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/25 Vidya Borshettar

Total LMW, HMW, Total PAH Caic GC/MSD 6758782 N/A 201 3/04/26 Automated Statchk

Maxxam ID GF0876 Collected 2013/04/20

Sample ID IPS-SD13-02-03 Relinquished 2013/04/20


Test Descriptionjents by ICPMS (total)MoisturePAH in Soil by GC/MS (SIM)Total LMW, HMW, Total PAH CaIcpH (21 Dl Water Extract)

InstrumentationICPM/MSBAL/BALGC/MSDGC/MSDPH/PH

Batch6763375676164067673796758782ETh333

Extracted2013/04/24N/A2013/04/23N/A201 3/04/24

LI

LiAnalyzed2013/04/242013/04/242013/04/252013/04/262013/04/24

AnalystDavid JungLolita ObusanVidya BorshettarAutomated Statnhk

Q+-,.,;


Sample ID IPS-SD13-02-04 Relinquished 2013/04/20Matrix Sediment Received 201 3/04/20


Moisture BAL/BAL 6761640 N/A 2013/04/24 Lolita Obusan

PAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04/23r: 201’3/04/25 Vidya Borshettar

Total LMW. HMW, Total PAH CaIc GC/MSD 6758782 N/A 201:3/04/26 Automated Statchk


Sample ID IPS-SD13-02-05 Relinquished 2013/04/20Matrix Sediment Received 2013/04/20

Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6761640 N/A 2013/04/24 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04/23 2013/04/25 Vidya BorshettarTotal LMW, HMW, Total PAH Caic GC/MSD 6758782 N/A 2013/04/26 Automated Statchk Li

LiLiLi

Page200f34

m


Succ Thruch Sienc


$


Matrix Sediment

Test Summary


Received 2013/04/20

Maxxam ID GF0882 DupSample ID DUP-C

Matrix Sediment

ic

Collected 2013/04/20Relinquished 201 3/04/20

Received 2013/04/20

IC

0

C

Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6763375 201 3/04/24 201 3/04/24 David JungMn,fr BAL/BAL 6761640 N/A 2013/04/24 rilit (Thiisn

PAH’in Soil by GO/MS (SIM) GC/MSD 6767379 2013/04)23 2013/04/25 Vidya BorshettarTotal LMW, HMW. Total PAH CaIc GC/MSD 6758782 N/A 201 3/04/26 Automated StatchkpH (2:1 Dl Water Extract) PH/PH 6763383 201 3/04/24 201 3/04/24 Nadzida Stanic

Maxxam ID GF0882 Collected 201 3/04/20Sample ID DUP-C Relinquished 2013/04/20


Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6763375 201 3/04/24 201 3/04/24 David JungMoisture BAL/BAL 6761640 N/A 201 3/04/24 Lolita ObusanPAHin Soil by GO/MS (SIM) GC/MSD 6767379 2013/04/23 2013/04/25 Vidya BorshettarTotal LMW, HMW. Total PAH Calc GC/MSD 6758782 N/A 201 3/04/26 Automated StatchkpH (2:1 DI Water Extract) PH/PH 6763383 201 3/04/24 201 3/04/24 Nadzida Stanic

Test Description Instrumentation Batch Extracted Analyzed AnalystlElements by ICPMS (total> ICPM/MS 6830378 2013/05/22 2013/05/22 John Choo



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6761640 N/A 2013/04/24 Lolita Obusan V

V

V

PAH in Soil by GO/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/25 Vidya Borshettar :Total LMW, HMW, Total PAH OaIc GO/MSD 6758782 N/A 2013/04/26 Automated Statchk VVV V

VV

Maxxam ID GF0884 Collected 2013/04/20Sample ID IPS-SD13-03-03 V V ReIinquished 2013/04/20


Test Description Instrumentation Batch Extracted V Analyzed AnalystElements by ICPMS (total) ICPM/MS 6763375 ‘2013/04/24 V

V

‘2013/04/24 David JungMoisture BAL/BAL 6761640 N/A V 2013/04/24 Lolita ObusanPAH in Soil by GO/MS (SIM) GC/MSD 6767379 2013/04/23 V

2013/04/25 Vidya BorshettarTotal LMW, HMW, Total PAH Caic GC/MSD 6758782 N/A V 2013/04/26 Automated StatctikpH (2:1 DI Water Extract) PH/PH 6763383 201 3/04/24 201 3/04/24 Nadzida Stanic

Page 21 of34

m



Matrix Sediment

Page 22 of 34

Succe Th c qt



Project #: 13-1520-0502-6075 (1327)


Received 2013/04/20 r[rrDLiU[3Li

U

0

Test Summary

[3.

Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BALJBAL 6761640 N/A 2013/04/24 Lolita Obusan

PAH in Soil by GO/MS (SIM) GCIMSD 6767379 2013/04/23 201 3/04/25 Vidya Borshettar

Total LMW. HMW. Total PAl-I Calc GC/MSD 6758782 N/A 201 3/04/26 Automated Statchk




Moisture BAL/BAL 6761640 N/A 201 3/04/24 Lolita Obusan

PAH in Soil by GO/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/26 Vidya BorshettarTotal LMW. HMW, Total PAH CaIc GC/MSD 6758782 N/A 2013/04/26 Automated Statchk




Elements by ICPMS (total) ICPMIMS 6763375 201 3/04/24 201 3/04/24 David JungMoisture BAL/BAL 6761651 N/A 2013/04/24 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/26 Vidys Borshettar

Total LMW, HMW, Total PAH CaIc GC/MSD 6758782 N/A 201 3/04/26 Automated Statchk

pH (2:1 Dl Water Extract) PH/PH 6763383 201 3/04/24 201 3/04/24 Nadzida Stanic

Maxxam ID GF0888 Collected 2013/04/20Sample ID DUP-D Relinquished 2013/04/20


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6761640 N/A 201 3/04/24 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04123 201 3/04/26 Vidya BorshettarTotal LMW. HMW, Total PAH CaIc GC/MSD 6758782 N/A 201 3/04/26 Automated Statchk


Matrix Sediment Received 201 3104/20


Moisture BAL/BAL 6761640 N/A 2013/04/24 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6767379 201 3/04/23 201 3/04/26 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6758782 N/A 201 3/04/26 Automated Statchk


Succe Thrih Sconc


Test Summary


Matrix Sediment


Received 2013/04/20

Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6761640 N/A 2013/04/24 Lolita ObusanPAH in Soil by GO/MS (SIM) GC/MSD 6767389 201 3/04/23 2013/04/26 Vidya BorshettarTotal LMW. HMW, Total PAH Caic GC/MSD 6758782 N/A 2013/04/26 Automated Statchk

Maxxam ID GF0892 Collected 2013/04/20Sample ID IPS-SD1 3-04-05 Relinquished 201 3/04/20


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6761640 N/A 201 3/04/24 Lolita ObusanPAH in Soil by GO/MS (SIM) GO/MSD 6767389 201 3/04/23 201 3/04/26 Vidya BorshettarTotal LMW, HMW, Total PAH OaIc GC/MSD 6758782 N/A 201 3/04/26 Automated Statchk

Maxxam ID GF0892 Dup Collected 2013/04/20Sample ID IPS-SD1 3-04-05 Relinquished 2013/04/20


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6761640 N/A 201 3/04/24 Lolita Obusan

Test Description Instrumentation Batch Extracted Analyzed AnalystElements by IOPMS (total) ICPM/MS 6763375 201 3/04/24 201 3/04/24 David JungMoisture BAL/BAL 6761640 N/A 2013/04/24 Lolita Obusan

• PAH in Soil by GO/MS (SIM) GC/MSD 6767389 201 3/04/23 2013/04/26 Vidya Borshettartotél LMW, HMW, Total PAH Cab GC/MSD 6758782 N/A 2013/04/26 Automated StatchkoH (2:1 Dl Water Extract) PH/PH 6763383 201 3/04/24 201 3/04/24 Nadzida Stanic



Page 23 of 34

m LGOLDER ASSOCIATES


Report Date: 2013/05/22 Site#: TP.00131Site Location: 2225 0CC ROAD,PORT MOODY BCProject #. 13-1520-0502-6075 (1327)

Epackage 1 12.7°C [Each temperature is the average of up to three cooler temperatures taken at receipt

General Comments

Report re-issued. Hg re-analyzed for samples GF0881 and GF0882 as per dient request. May 22, 2013 USample GF0882, Elements by ICPMS (total): Test repeated.

Results relate only to the items tested.

[1IRL

Page 24 of 34

r%/1 21 21 rri Throuçjh

GOLDER ASSOCIATESTask Order#: 4410104800Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

Quality Assurance Report JMaxxam Job Number: B331191

QNQC DateBatch AnalyzedNum nit QC Type Parameter yyyy/mm/dd Value Recovery UNITS QC Limits

6761640 LOl Method Blank Moisture 2013/04/24 <0.30 %6761651 LOl Method Blank Moisture 2013/04/24 <0.30 %6763375 DJ Method Blank Total Aluminum (Al) 2013/04/24 <100 mg/kg

Total Antimony (Sb) 2013/04/24 <0.10 mg/kgTotal Arsenic (As) 201 3/04/24 <0.50 mg/kgTotal Barium (Ba) 201 3/04/24 <0.10 mg/kgTotal Beryllium (Be) 201 3/04/24 <0.40 mg/kgTotal Bismuth (Bi) .201 3/04/24 <0.10 mg/kgTotal Cadmium (Cd) 201 3/04/24 <0 050 mg/kgTotal Calcium (Ca) 201 3/04/24 <100 mg/kgTotal Chromium (Cr) 2013/04/24 <1 0 mg/kgTotal Cobalt (Co) 2013/04/24 <0 30 mg/kgTotal Copper (Cu) 201 3/04/24 <0 50 mg/kgTotal Iron (Fe) 2013/04/24 <100 mg/kgTotal Lead (Pb) 201 3/04/24 <0.10 mg/kgTotal Magnesium (Mg) 201 3/04/24 <100 mg/kgTotal Manganese (Mn) 201 3/04/24 <0.20 mg/kgTotal Mercury (Hg) 2013/04/24 <0.050 mg/kgTotal Molybdenum (Mo) 201 3/04/24 <0.10 mg/kgTotal Nickel (Ni) 2013/04/24 <0.80 mg/kgTotal Phosphorus (P) 201 3/04/24 <10 mglkgTotal Potassium (K) 201 3/04/24 <100 mg/kgTotal Selenium (Se) 2013/04/24 <0.50 mg/kgTotal Silver (Ag) 2013/04/24 <0.050 mg/kgTotal Sodium (Na) 201 3/04/24 <100 mg/kgTotal Strontium (Sr) 201 3/04/24 <0.10 mg/kgTotal Thallium (TI) 201 3/04/24 <0.050 mg/kgTotal Tin (Sn) 201 3/04/24 <0.10 mg/kgTotal Titanium (Ti) 201 3/04/24 <1.0 mg/kgTotal Vanadium (V) 201 3/04/24 <2.0 mg/kg

c... . Total Zinc (Zn) 2013/04/24 <1.0 mg/kgTotal Zirconium (Zr) 2013/04/24 <0.50 mg/kg

6767379 VB1 Method Blank D10-ANTHRACENE (sur.) 201 3/04/25 100 % 60- 130

D8-ACENAPHTHYLENE

(sur.) 2013/04/25 90 % 50- 130D8-NAPHTHALENE (sur.) 2013/04/25 94 % 50- 130

U TERPHENYL-D14 (sur.) 2013/04/25 99 % 60- 130Naphthalene 2013/04/25 <0.050 mg/kg2-Methylnaphthalene 201 3/04/25 <0.050 mg/kgAcenaphthylene 201 3/04/25 <0.050 mg/kgAcenaphthene 201 3/04/25 <0.050 mg/kgFluorene 201 3/04/25 <0 050 mg/kgPhenanthrene 201 3/04/25 <0 050 mg/kgAnthracene 201 3/04/25 <0 050 mg/kgFluoranthene 201 3/04/25 <0 050 mg/kgPyrene 2013/04/25 <0 050 mg/kgBenzo(a)anthracene 2013/04/25 <0 050 mg/kgChrysene 201 3/04/25 <0.050 mg/kgBenzo(b&j)fluoranthene 2013/04/25 <0.050 mg/kgBenzo(k)fluoranthene 201 3/04/25 <0.050 mg/kgBenzo(a)pyrene 201 3/04/25 <0.050 mg/kglndeno(1.2,3-cd)pyrene 2013/04/25 <0.050 mg/kgDibenz(a,h)anthracene 201 3/04/25 <0.050 mg/kgBenzo(gh.i)perylene 2013/04/25 <0.050 mg/kg

6767389 VB1 Method Blank D10-ANTHRACENE (sur.) 201 3/04/25 90 % 60 130D8-ACENAPHTHYLENE (sur.) 201 3/04/25 90 % 50- 130

[ Ma,varn Analytics International Corporation o/a Maxxarn Analytics Burriaby. 4606 Canada Way V5G 1K5 TeIephone604) 734-7276 Fax(604) 731-2346

Page 25 of 34

m Sccs ThrDugh Scenc

GOLDER ASSOCIATESTask Order#: 4410104800Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)E

Quality Assurance Report (Continued)Maxxam Job Number: B331191

QNQC DateBatch AnalyzedNum mit QC Type Parameter yyyy/mm/dd Value Recovery UNITS QC Limits

6767389 VB1 Method Blank D8-NAPHTHALENE (sur.) 201 3/04/25 86 % 50- 130TERPHENYL-D14(sur.) 2013/04/25 101 % 60-130

Naphthalene 2013/04/25 <0.050 mg/kg2-Methylnaphthalene 201 3/04/25 <0.050 mg/kgAcenaphthylene 201 3/04/25 <0.050 mg/kgAcenaphthene 201 3/04/25 <0.050 mg/kgFluorene 201 3/04/25 <0.050 mg/kgPhenanthrene 201 3/04/25 <0.050 mg/kgAnthracene 201 3/04/25 <0.050 mg/kgFluoranthene 201 3/04/25 <0.050 mg/kgPyrene 2013/04/25 <0.050 mg/kgBenzo(a)anthracene 201 3/04/25 <0.050 mg/kgChrysene 201 3/04/25 <0.050 mg/kgBenzo(b&j)fluoranthene 2013/04/25 <0.050 mg/kgBenzo(k)fluoranthene 201 3/04/25 <0.050 mg/kgBenzo(a)pyrene 201 3/04/25 <0.050 mg/kgndeno( 1 ,2.3-cd)pyrene 2013/04/25 <0.050 mg/kgDibenz(ah)anthracene 2013/04/25 <0.050 mg/kgBenzo(gh.i)perylene 201 3/04/25 <0.050 mg/kg

6830378 JC8 Method Blank Total Mercury (Hg) 201 3/05/22 <0.050 mg/kg

6763375 DJ RPD [GF0867-021 Total Aluminum (Al) 2013/04/24 2.6 % 35Total Antimony (Sb) 201 3/04/24 1.9 % 30Total Arsenic (As) 2013/04/24 1.9 % 30Total Barium (Ba) 201 3/04/24 0.7 % 35Total Beryllium (Be) 201 3/04/24 NC % 30Total Bismuth (Bi) 201 3/04/24 0.06 % 30Total Cadmium (Cd) 2013/04/24 1 % 30Total Calcium (Ca) 201 3/04/24 2.3 % 30Total Chromium (Cr) 2013/04/24 3.8 % 30

Total Cobalt(Co) 2013/04/24 2.0 % 30Total Copper (Cu) 2013/04/24 1.7 % 30Total Iron (Fe) 201 3/04/24 3.8 % 30Total Lead (Pb) 201 3/04/24 1.0 % 35Total Magnesium (Mg) 201 3/04/24 2.1 % 30Total Manganese (Mn) 2013/04/24 1.1 % 30Total Mercury (Hg) 201 3/04/24 3.2 % 35Total Molybdenum (Mo) 2013/04/24 1.2 % 35Total Nickel (Ni) 201 3/04/24 1 % 30Total Phosphorus (P) 201 3/04/24 2.7 % 30Total Potassium (K) 2013/04/24 1.7 % 35Total Selenium (Se) 201 3/04/24 NC % 30

Total Silver (Ag) 2013/04/24 14.7 % 35Total Sodium (Na) 201 3/04/24 0.5 % 35Total Strontium (Sr) 2013/04/24 3.4 % 35Total Thallium (TI) 201 3/04/24 NC % 30Total Tin (Sn) 201 3/04/24 0.2 % 35Total Titanium (Ti) 2013/04/24 0.2 % 35Total Vanadium (V) 201 3/04/24 2.3 % 30

-

Total Zinc (Zn) 2013/04/24 2.6 % 30Total Zirconium (Zr) 201 3/04/24 0.6 % 30

6763383 NS6 RPD [GF0867-02J Soluble (2:1) pH 201 3/04/24 0.2 % 20

6767379 VB1 RPD [GF0868-01} Naphthalene 201 3/04/25 NC % 502-Methylnaphthalene 201 3/04/25 NC (1) % 50Acenaphthylene 201 3/04/25 NC % 50 -

Acenaphthene 201 3/04/25 NC % 50

Maxxam AnaIytcs ntematonai Corporation 0/a Maxxam Malytics Burnaby 4606 Canada Way V5G 1K5 Teldphone(604) 734-7276 Fax(604) 731-2386

Page 26 of 34

Quality Assurance Report (Continued)Maxxam Job Number: 8331191

Suoc lbcuuah Sctercs


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Maxxam Analytics International Corporation 0/a Maxxam Analytics Bumaby: 4606 Canada Way V5G I K5 Telephone(604) 734-7276 Fax(604) 731 -2386

Page 27 of 34

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5050505050505050505050505050505050505050505050505050505050503520

QA/QC DateBatch AnalyzedNum mit QC Type Parameter yyyy/mm/dd Value Recovery UNITS QC Limits

6767379 VB1 RPD [GF0868-01] Fluorene 201 3/04/25Phenanthrene 2013/04/25Anthracerie 2013/04/25Fluoranthene 2013/04/25Pyrene 2013/04/25Benzo(a)anthracene 2013/04/25Chrysene 2013/04/25Benzo(b&j)fluoranthene 2013/04/25Benzo(k)fluoranthene 2013/04/25Benzo(a)pyrene 2013/04/25lndeno(1 2,3-cd)pyrene 2013/04/25Dibenz(a,h)anthracene 2013/04/25Benzo(g,h,i)perylene 2013/04/25

6767389 VB1 RPD [GF0874-01J Naphthalene 2013/04/262-Methylnaphthalene 2013/04/26Acenaphthylene 2013/04/26Acenaphthene 2013/04/26Fluorene 2013/04/26Phenanthrene 2013/04/26Anthracene 2013/04/26Fluoranthene 2013/04/26Pyrene 2013/04/26Benzo(a)anthracene 2013/04/26Chrysene 2013/04/26Benzo(b&j)fluoranthene 2013/04/26Benzo(k)fluoranthene 201 3/04/26Benzo(a)pyrene 2013/04/26Indeno(1 ,23-cd)pyrene 2013/04/26Dibenz(a,h)anthracene 2013/04/26Benzo(g.h,i)perylene 2013/04/26

6830378 JC8 RPD [GF0882-02] Total Mercury (Hg) 201 3/05/226761640 LOl RPD [GF0892-011 Moisture 2013/04/246763375 DJ Matrix Spike

[GF0867-02] Total Antimony (Sb) 201 3/04/24 102 % 75- 125Total Arsenic (As) 2013/04/24 110 % 75- 125Total Barium (Ba) 201 3/04/24 NC % 75- 125Total Beryllium (Be) 2013/04/24 114 % 75- 125Total Cadmium (Cd) 201 3/04/24 110 % 75- 125Total Chromium (Cr) 2013/04/24 NC % 75 - 125Total Cobalt (Co) 201 3/04/24 -. 105 % 75- 125Total Copper (Cu) 2013/04/24 NC % 75- 125Total Lead (Pb) 2013/04/24 u: NC % 75- 125Total Manganese (Mn) 2013/04/24 NC % 75- 125Total Mercury (Hg) 201 3/04/24 108 % 75- 125Total Molybdenum (Mo) 2013/04/24 .. NC % 75- 125Total Nickel (Ni) 2013/04/24 NC % 75- 125Total Selenium (Se) 2013/04/24 114 % 75- 125Total Silver (Ag) 2013/04/24 100 % 75- 125Total Strontium (Sr) 2013/04/24 NC % 75 - 125Total Thallium (TI) 2013/04/24 104 % 75- 125Total Tin (Sn) 2013/04/24 109 % 75- 125Total Titanium (Ti) 2013/04/24 NC % 75- 125Total Vanadium (V) 2013/04/24 NC % 75 - 125Total Zinc (Zn) 2013/04/24 NC % 75- 125

6767379 VB1 Matrix Spike1GF0868-011 D10-ANTHRACENE (sur.) 2013/04/25 81 % 60- 130


5Uccasn Thrcsh Scmncsn&


D8-ACENAPHTHYLENE (sur.)D8-NAPHTHALENE (sur.)TERPHENYL-D14 (sur.)Naphthalene2-MethylnaphthaleneAcenaphthyleneAcenaphtheneFluorenePhenanthreneAnthraceneFluoranthenePyreneBenzo(a)anthraceneChryseneBenzo(b&j)fluorantheneBenzo(k)fluorantheneBenzo(a)pyrenetndeno(1 ,2,3-cd)pyreneDibenz(a.h)anthraceneBenzo(g.h,i)perylene

D10-ANTHRACENE (sur.)D8-ACENAPHTHYLENE (sur.)D8-NAPHTHALENE (sur.)TERPHENYL-D14 (sur.)Naphthalene2-MethylnaphthaleneAcenaphthyleneAcenaphtheneFluorenePhenanthreneAnthraceneFluoranthenePyreneBenzo(a)anthraceneChryseneBenzo(b&j)fluorantheneBenzo(k)fiuorantheneBenzo(a)pyrenelndeno(1 ,2,3-cd)pyreneDibenz(a.h)anthraceneBenzo(g.h,i)perylene

2013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/262013/04/26

79 % 60-13082 % 50-13080 % 50-13087 % 60-13082 % 50-13087 % 50-13086 % 50-13088 % 50-13089 % 50-13083 % 60-13087 % 60-13093 % 60-13095 % 60-13085 % 60-13080 % 60-130

108 % 60-13090 % 60-13087 % 60-130

105 % 60-130106 % 60-130

95 % 60-130

Maxxam Analytics International Corporation ola Macsam Analytics Burnabyr 4606 Canada Way V5G 1K5 Telephone(604) 734-7276 Fax(604) 731-2386

ri m

QA/QC DateBatch AnalyzedNum nit QC Type Parameter yyyy/mm/dd Value Recovery UNITS QC Limits

2013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/252013/04/25

86 %89 %86 %90 %96 %92 %94 %92 %87 %95 %91 %90 %78 %80 %66 %

103 %81 %82 %80 %80 %

6767379 VB1 Matrix Spike[GF0868-01]

6767389 VB1 Matrix Spike1GF0874-011

6830378 JC8 Matrix Spike[GF0882-02]

6763375 DJ LOS

50- 13050- 13060- 13050-13050- 13050 - 13050 - 13050- 13060- 13060 - 13060 - 13060- 13060 - 13060- 13060 - 13060- 13060- 13060- 13060- 13060 - 130

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Total Mercury (Hg) 201 3/05/22 92 % 75- 125Total Antimony (Sb) 201 3/04/24 107 % 75- 125Total Arsenic (As) 2013/04/24 103 % 75- 125Total Barium (Ba) 2013/04/24 100 % 75- 125Total Beryllium (Be) 2013/04/24 107 % 75- 125Total Cadmium (Cd) 201 3/04/24 105 % 75- 125Total Chromium (Cr) 2013/04/24 101 % 75- 125Total Cobalt (Co) 2013/04/24 102 % 75- 125Total Copper (Cu) 201 3/04/24 105 % 75- 125Total Lead (Pb) 2013/04/24 101 % 75- 125Total Manganese (Mn) 2013/04/24 102 % 75- 125

Page 28 of 34

m ScSs Through Scence

GOLDER ASSOCIATESTask Order#: 4410104800

Site#: TP.00131Site Location: 2225 10CC ROAD,PORT MOODY BC

1 Project #: 13-1520-0502-6075 (1327)


QA/QO DateBatch AnalyzedNum lnit CC Type Parameter yyyy/mm/dd Value Recovery UNITS CO Limits

6763375 DJ LOS Total Mercury (Hg) 2013/04/24 109 % 75 - 125Total Molybdenum (Mo) 2013/04/24 110 % 75-125Total Nickel (Ni) 201 3/04/24 100 % 75 - 125Total Selenium (Se) 2013/04/24 111 % 75- 125Total Silver (Ag) 201 3/04/24 95 % 75- 125Total Strontium (Sr) 201 3/04/24 100 % 75- 125Total Thallium (TI) 201 3/04/24 101 % 75- 125Total Tin (Sn) 2013/04/24 104 % 75- 125Total Titanium (Ti) 201 3/04/24 106 % 75-125Total Vanadium (V) 2013/04/24 102 % 75- 125Total Zinc (Zn) 2013/04/24 114 % 75- 125

6763383 NS6 LOS Soluble (2:1) pH 2013/04/24 102 % 96- 1046767379 VB1 LOS D10-ANTHRACENE (sur.) 201 3/04/26 98 % 60- 130

D8-ACENAPHTHYLENE (sur.) 2013/04/26 97 % 50- 130D8-NAPHTHALENE (sur.) 201 3/04/26 101 % 50- 130TERPHENYL-D14 (sur.) 2013/04/26 96 % 60- 130Naphthalene 201 3/04/26 86 % 50- 1302-Methylnaphthalene 2013/04/26 88 % 50- 130Acenaphthylene 201 3/04/26 85 % 50- 130Acenaphthene 201 3/04/26 88 % 50- 130Fluorene 201 3/04/26 83 % 50- 130Phenanthrene 201 3/04/26 82 % 60- 130Anthracene 201 3/04/26 95 % 60- 130Fluoranthene 201 3/04/26 84 % 60- 130Pyrene 2013/04/26 83 % 60-130Benzo(a)anthracene 201 3/04/26 82 % 60- 130Chrysene 201 3/04/26 85 % 60- 130Benzo(b&j)fluoranthene 2013/04/26 70 % 60- 130Benzo(k)fluoranthene 2013/04/26 103 % 60- 130Benzo(a)pyrene 2013/04/26 86 % 60- 130lndeno(1,2,3-cd)pyrene 2013/04/26 77 % 60- 130Dibenz(a,h)anthracene 201 3/04/26 74 % 60- 130Benzo(g,h.i)perylene 2013/04/26 76 % 60- 130

6767389 VBI LOS D10-ANTHRAOENE (sur.) 2013/04/25 100 % 60- 130D8-AOENAPHTHYLENE (sur.) 2013/04/25 98 % 50- 130D8-NAPHTHALENE (sur.) 2013/04/25 94 % 50- 130TERPHENYL-D14(sur.) 2013/04/25 113 % 60-130Naphthalene 2013/04/25 79 % 50- 1302-Methylnaphthalene 2013/04/25 85 % 50- 130Acenaphthylene 2013/04/25 83 % 50- 130Acenaphthene 2013/04/25 86 % 50- 130Fluorene 2013/04/25 87 % 50-130Phenanthrene 2013/04/25 83 % 60- 130Anthracene 2013/04/25 89 % 60- 130Fluoranthene 2013/04/25 98 % 60- 130Pyrene 2013/04/25 94 % 60-130Benzo(a)anthracene 2013/04/25 86 % 60- 130Ohrysene 2013/04/25 84 % 60- 130Benzo(b&j)fluoranthene 2013/04/25 105 % 60- 130Benzo(k)fluoranthene 2013/04/25 88 % 60- 130Benzo(a)pyrene 2013/04/25 91 % 60- 130lndeno(1,23-cd)pyrene 2013/04/25 96 % 60- 130Dibenz(a.h)anthracene 2013/04/25 97 % 60- 130Benzo(g,h.i)perylene 2013/04/25 88 % 60- 130

6830378 JO8 LOS Total Mercury (Hg) 201 3/05/22 96 % 75 125

Mao<arn Analytics International corporation n/a Maorarn Analytics Bumaby: 4606 Canada Way V5G 1K5 Teiephone(604) 734-7276 Fax(604) 73-2386

Page 29 of 34

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2 ?‘421 rn Suxe Through Scrce

GOLDER ASSOCIATESTask Order#: 4410104800Site#: TP.00131Site Location: 2225 10CC ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)



6763375 DJ SRM Total Aluminum (Al) 2013/04/24 99 % 70- 130Total Antimony (Sb) 2013/04/24 88 % 70- 130Total Arsenic (As) 2013/04/24 92 % 70- 130 -

Total Barium (Ba) 201 3/04/24 109 % 70- 130Total Cadmium (Cd) 201 3/04/24 104 % 70- 130 -—

Total Calcium (Ca) 201 3/04/24 97 % 70- 130Total Chromium (Cr) 2013/04/24 100 % 70 - 130Total Cobalt (Co) 2013/04/24 92 % 70- 130Total Copper (Cu) 2013/04/24 88 % 70-130Total Iron (Fe) 2013/04/24 96 % 70- 130Total Lead (Pb) 2013/04/24 96 % 70-130Total Magnesium (Mg) 2013/04/24 84 % 70-130Total Manganese (Mn) 2013/04/24 101 % 70-130Total Mercury (Hg) 2013/04/24 88 % 70-130Total Molybdenum (Mo) 201 3/04/24 106 % 70- 130Total Nickel (Ni) 2013/04/24 90 % 70- 130 —j

Total Phosphorus (P) 201 3/04/24 88 % 70- 130Total Strontium (Sr) 2013/04/24 105 % 70- 130Total Thallium (TI) 201 3/04/24 88 % 70- 130Total Titanium (Ti) 201 3/04/24 105 % 70- 130Total Vanadium (V) 2013/04/24 104 % 70-130Total Zinc (Zn) 2013/04/24 91 % 70- 130

6830378 JC8 SRM Total Mercury (Hg) 201 3/05/22 82 % 70- 130

Duplicate: Paired analysis of a separate portion of the same sample. Used to evaluate the variance in the measurement.Matrix Spike: A sample to which a known amount of the analyte of interest has been added. Used to evaluate sample matrix interference.

SRM: A sample of known concentration prepared by an external agency under stringent conditions. Used as an independent check of method accuracy.

LCS: A blank matrix sample to which a known amount of the analyte, usually from a second source, has been added. Used to evaluate method accuracy.

Method Blank: A blank matrix containing all reagents used in the analytical procedure. Used to identify laboratory contamination.Surrogate: A pure or isotopically labeled compound whose behavior mirrors the analytes of interest. Used to evaluate extraction efficiency.NC (Matrix Spike): The recovery in the matrix spike was not calculated. The relative difference between the concentration in the parent sample and thespiked amount was not sufficiently significant to permit a reliable recovery calculation.NC (RPD): The RPD was not calculated. The level of analyte detected in the parent sample and its duplicate was not sufficiently significant to permit a

reliable calculation.(1 ) RDL raised due to sample matrix interference.

Mao<am Ana’ytics Intematona Corporaon 0/a Maxxam Maytcs Burnaby 4606 Canada Way V5G 1K5 Telephone(604) 734-7276 Fax(604) 731-2386

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Validation Signature Page

Maxxam Job #: B331191

The analytical data and all QC contained in this report were reviewed and validated by the following individual(s).

Andy Lu, ta Validation Coordinator

Maxxain has procedures in place to guard against improper use of the electronic signature and have the required “signatories, as per section 5.10.2 ofISO/IEC 17025:2005(E), signing the reports. For Service Group specific validation please refer to the Validation Signature Page.

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DATA OUALITY REVIEW CHECKLIST - IMPERIAL OIL PROJECTS

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Was a Data Quality Waiver (DQW) issued (Yes/No)?:

Date Issued: ala

No

Date of Response: ala

Data Quality Review Checklist (Rev 13)

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Consultant Golder Associates Sampling Date April 20, 2013

Location: 2225 loco Road, Port Moody, BC Laboratory: Maxxam Analytics Burnaby

Consultant Project Number: 13-1520-0502-6075 Sample Submission Number: B33 1191

Are All Laboratory QC Within Acceptance Criteria (Yes, No, Not Applicable)?

Yes No NA CommentsInstrument Surrogate Recovery X All laboratory QC results are withinExtraction Surrogate Recovery X acceptance criteria.

Method Blank Concentration XMatrix Duplicate RPD X

Matrix Spike Recovery XLab Control Sample Recovery X

Are All Field QC Samples Within Alert Limits (Yes, No, Not Applicable)?

Yes No NA CommentsField Blank Concentration X All field QC samples are withinTrip Blank Concentration X alert limits.

Field Duplicate RPD X

Has CoA been signed off (Yes/No)?:Has lab warranted all tests were in statistical control in CoA (Yes/No)?:Has lab warranted all tests were analyzed following SOP’s in CoA (Yes/No)?:Were all samples analyzed within hold times (Yes/No)?:All volatiles samples methanol extracted (if required) within 48 hours (Yes/No)?:Is Chain of Custody completed and signed (Yes/No)?:Were sample temperatures acceptable when they reached lab (Yes/No)?:

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YesYesYesn/aYesYes

Is data considered to be reliable (Yes/No)?: YesIf answer is “No”, describe and provide rationale:

Data Reviewed by (Print): Amanda Newberry Data Reviewed by (Signature):

___________________

Date: May7,2013

For Use on Imperial Oil Projects Only

Attention: Dan ParksGOLDER ASSOCIATES500-4260 STILL CREEK DRIVEBURNABY, BCCANADA V5C6C6

Task Order#: 4410104800Line Item: 10Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)Your C.O.C. #: 36248602, 36248604

Report Date: 2013104129r


Received: 2013/04122, 14:50 pSample Matrix: Sediment# Samples Received: 17

Analyses Quantity Laboratory Method Primary reference

Remarks:

All Blank values are reported. Associated data are not blank corrected.Solids results are based on dry weight except Biota Analyses & Special Waste Oil & Grease.Organic Analyses are not corrected for extraction recovery or method blanks. Certain methods (e.g. CARB 429, quinoline,all PCDD/F and DBD/DBF) quantitate by the method of isotope dilution LMaxxam Analytics has performed all analytical testing herein in accordance with ISO 17025.

All CCME results met required criteria unless otherwise stated in the report. The CWS PHC methods employed byMaxxam conform to all prescribed elements of the reference method and performance based elements have beenvalidated. All modifications have been validated and proven equivalent following the ‘Alberta Environment Draft Addenda tothe CWS-PHC, Appendix 6, Validation of Alternate Methods’. Documentation is available upon request. Deviations fromReference Method for the Canada-wide Standard for Petroleum Hydrocarbons in Soil-Tier 1 Method:F21F31F4 data reported using validated cold solvent extraction instead of Soxhiet extraction.


All analysis data reported was generated when the analytical methods were in statistical control and criteria for spikerecoveries, reference material recoveries, method blanks data and duplicate precision were met unless otherwise stated.All samples were analysed within hold time unless otherwise flagged. All soil samples for BTEX analysis were methanolextracted within 24 hours unless otherwise flagged.This report shall not be reproduced except in full, without the written approval of the laboratory.

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MAXXAM JOB #: B331479

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Elements by ICPMS (total)MoisturePAH in Soil by GC/MS (SIM)Total LMW, HMW, Total PAH CaIcpH (2:1 Dl Water Extract)

6 BBY7SOP-0000417 BBY8SOP-0001717 BBY8SOP-0002217 BBY Wl-000336 BBY6SOP-00028

BCMOE-SALMOnt MOE -E 3139EPA 8270DBC MOE Lab MethodCarter, SSMA 16.2

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Task Order#: 4410104800Line Item: 10Site#:TP.00131Site Location: 2225 1Q00 RQAD.PORT MOODY BCProject#: 13-1520-0502-6075 (1327)YourC.O.C. I/: 36248602, 36248604

500-4260 STILL CREEK DRIVEBURNABY, BCCANADA V5C6C6

Report Date: 2013/04129


MAXXAM JOB #: B331479Received: 2013/04122, 14:50

Methods used by Maxxam are based upon those found in ‘Standard Methods for the Examination of Water and

‘—

Wastewater’, 22nd Edition, published by the American Public Health Association, or on US EPA, protocols found in the’Test Methods for Evaluating Solid Waste’, Physical/Chemical Methods, SW846, 3rd Edition. Other procedures are basedon the methodologies accepted by the appropriate regulatory agency. Methodology briefs are available by written request.

All work recorded herein has been done in accordance with normal professional standards using accepted testingmethodologies, quality assurance and quality control procedures except where otherwise agreed to by the client andtesting company in writing. Maxxam Analytics is limited in liability to the actual cost of analysis unless otherwise agreed inwriting. There is no other warranty expressed or implied. Your samples will be retained at Maxxam for a period of 45 daysfrom receipt of data or as per contract.


Encryption Key

[ ! 29Apr2013 13:55: -07:00

Please direct all questio4 regarding this Certificate of Analysis to your Project Manager.

VJ Oco, Bumaby Project ManagerEmail: [email protected]# (604) 639-8422

Maxxam has procedures in place to guard against improper use of the electronic signature and have the required “signatories”, as per section5.10.2 of ISO/IEC 17025:2005(E), signing the reports. For Service Group specific validation please refer to the Validation Signature Page.

Maaxan A*aIyt** *ter*ationeI Coparati*o ala Ma,oaa AaaIytics Bar*aby. 4606 Canada Way V5G I K5 TeIephone(604) 734-7278 Fax(604) 731-2388

Page 2 of22

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Report Date: 2013/04/29 Site#: TP.00131Site Location: 2225 10CC ROADPORT MOODY BC

Project #: 13-1520-0502-6075 (1327)


Maxxam ID GF2339 GF2342 GF2345 GF2348 GF2352Sampling Date 2013/04/21 201 3/04/21 201 3/04/21 2013/04/21 2013/04121

09:00 09:20 10:00 10:20 13:00

OC Number 36248602 36248602 36248602 36248602 36248604UNITS IPS-SDI3-05-01 IPS-SDI3-05-03 IPS-SDI3-06-01 IPS-SDI3-06.03 IPS-SD13-07-01 RDL C Batch

Soluble (2:1)pH IPH Units 7.67 8.12 7.87 8.07 7.77 0.010 6766558


Maxxam ID GF2354Sampling Date 201 3/04/21

13:20OC Number 36248604

UNITS IPS-SDI 3-07-03 RDL C Batch

Soluble (2:1) pH IPH Units 8.22 10.010 16766558


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Page 3 of 22

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GOLDER ASSOCIATES

Li Maxxam Job #: B331479 Task Order#: 4410104800, Line Item: 10Report Date: 2013/04/29 Site#: TP.00131

Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)


Aaxxam ID GF2339 GF2340 GF2341 GF2342 GF2343Sampling Date 201 3/04/21 2013/04/21 2013/04/21 201 3/04/21 201 3/04/21

09:00 09:00 09:10 09:20 09:30COC Number 36248602 36248602 36248602 36248602 36248602

UNITS IPS-SDI3-05-O1 DUP-E IPS-SDI3-05-02 IPS-SDI3-05-03 IPS-SDI3-05-04 RDL C Batch

Moisture % 65 63 62 59 10.30 16763014



09:40 10:00 10:00 10:10COC Number 36248602 36248602 36248602 36248602

UNITS IPS-SDI3-05-05 IPS-SDI3-06-01 DUP-F IPS-SDI3-06-02 RDL C Batch

Moisture 56 58 60 55 030 6763014


Maxxam ID GF2348 GF2350 GF2351 I GF2352Sampling Date 201 3/04/21 201 3/04/21 201 3/04/21 j 201 3/04/21

10:20 10:30 10:40 13:00COC Number 36248602 36248604 36248604 36248604

UNITS IPS-SDI3-06-03 IPS-SDI3-06-04 IPS-SDI3-06-05 bC Batch IPS-SDI3-07-01 RDL C Batch

Moisture I I 56 53 6763037 69 j0.30 16763014



13:10 13:20 13:30 13:40COC Number 36248604 36248604 36248604 36248604

UNITS IPS-S013-07-02 IPS-SDI3-07-03 IPS-SDI3-07-04 IPS-SDI3-07-05 RDL C Batch

Moisture I I I 58 I 10.30 6763014


Page 4 of22

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Maxxam Job #: B331 479Report Date: 2013/04129

Sucr, Tnrauqh Scieacew


ELEMENTS BY ATOMIC SPECTROSCOP’((SEDIMENT)

.laxxam ID GF2339 GF2342 GF2345 GF2348

Sampling Date 2013/04/21 2013/04/21 2013/04/21 2013/04/2109:00 09:20 10:00 10:20 —

CCC Number 36248602 36248602 36248602 36248602 —

UNITS IPS-SDI3-05-O1 IPSSD13-05-O3 IPS-SDI3-06-O1 IPS-SDI3-06-03 RDL C Batch


rotal Antimony (Sb) mg/kg 0.58 0.33 0.81 0.30 0.10 6766555


rotal Barium (Ba) mg/kg 56.9 55.2 60.8 54.7 0.10 6766555

Total Beryllium (Be) mg/kg <0.40 <0.40 <0.40 <0.40 0.40 6766555





Fotal Cobalt(Co) mg/kg 9.64 11.0 8.97 10.2 0.30 6766555

rotal Copper (Cu) mg/kg 84.7 41.9 86.7 37.8 0.50 6766555


Total Lead (Pb) mg/kg 61.6 9.92 105 9.60 0.10 6766555



rotal Mercury (Hg) mg/kg 0.344 <0.050 0.271 <0.050 0.050 6766555

Fotal Molybdenum (Mo) mg/kg 7.86 5.53 6.18 4.43 0.10 6766555




Total Selenium (Se) mg/kg 2.01 0.86 142 0.70 0.50 6766555




Fotal Thallium (TI) mg/kg 0.183 0.212 0.242 0.181 0.050 6766555

Total Tin (Sn) mg/kg 2.60 0.44 3.20 0.43 0.10 6766555



Total Zinc (Zn) mg/kg 109 81.1 181 75.4 1.0 6766555



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Project #: 13-1520-0502-6075 (1327)


MaxxamlD GF2352 GF2354Sampling Date 2013/04/21 2013/04/21

13:00 13:20OC Number 36248604 36248604

UNITS IPS-SDI3-07-O1 IPS-S013-07-03 RDL C Batch

Total Aluminum (Al) mg/kg 20300 20400 100 6766555

Total Antimony (Sb) mg/kg 058 0.33 0.10 6766555

Total Arsenic (As) mg/kg 11.7 9.05 0.50 6766555

Total Barium (Ba) mg/kg 53.8 53.3 0.10 6766555

Total Beryllium (Be) mg/kg <0.40 <0.40 0.40 6766555

Total Bismuth (Bi) mg/kg 0.55 0.17 0.10 6766555

Total Cadmium (Cd) mg/kg 1.82 1.42 0.050 6766555

Total Calcium (Ca) mg/kg 6440 12900 100 6766555

Total Chromium (Cr) mg/kg 43.1 36.9 1.0 6766555

Total Cobalt (Co) mg/kg 8.78 9.80 0.30 6766555

Total Copper (Cu) mg/kg 105 37.1 0.50 6766555

rotal Iron (Fe) mg/kg 30700 31400 100 6766555

Total Lead (Pb) mg/kg 63.7 8.88 0.10 6766555

rotal Magnesium (Mg) mg/kg 10100 10100 100 6766555

Fotal Manganese (Mn) mg/kg 308 354 0.20 6766555

Total Mercury (Hg) mg/kg 0.227 <0.050 0.050 6766555

Fotal Molybdenum (Mo) mg/kg 5.26 4.04 0.10 6766555

Fotal Nickel (Ni) mg/kg 28.6 33.0 0.80 6766555

Total Phosphorus (P) mg/kg 644 629 10 6766555

Total Potassium (K) mg/kg 3550 3680 100 6766555

Total Selenium (Se) mg/kg 1.29 0.83 0.50 6766555

Total Silver (Ag) mg/kg 0.676 0.207 0.050 6766555

Total Sodium (Na) mg/kg 16400 6050 100 6766555

Total Strontium (Sr) mg/kg 65.7 110 0.10 6766555

Total Thallium (TI) mg/kg 0.301 0.205 0.050 6766555

Total Tin (Sn) mg/kg 2.51 0.49 0.10 6766555

Total Titanium (Ti) mg/kg 822 949 1.0 6766555

Total Vanadium (V) mg/kg 52.6 55.3 2.0 6766555

Total Zinc (Zn) mg/kg 155 73.8 1.0 6766555

Total Zirconium (Zr) mg/kg 6.40 7.63 0.50 6766555


Page 6 of22

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Success Through Scencer


Site#: TP.00131Site Location: 2225 10CC ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)


Maxxam ID GF2339 GF2340 GF2341Sampling Date 201 3/04/21 201 3/04/21 201 3/04/21

09:00 09:00 09:10)QC Number 36248602 — 36248602 36248602 —

UNITS IPS-SDI3-05-O1 RDL DUP-E RDLJ IPS-SDI3-05-02 RDL C Batch


2-Methylnaphthalene mg/kg 0.054 0.050 <0.050 0.050 <0.050 0.050 6770714

cenaphthyIene mg/kg 0.15 0.050 0.12 0.050 <0.050 0.050 6770714

ceriaphthene mg/kg <0.050 0.050 <0.050 0.050 <0.050 0.050 6770714

Fluorene mg/kg <0.050 0.050 <0.050 0.050 <0.050 0.050 6770714


Anthracene mg/kg 0.096 0.050 0.076 0.050 <0.050 0.050 6770714


Pyrene mg/kg 0.62 0.050 0.46 0.050 <0.050 0.050 6770714

Benzo(a)anthracene mg/kg 0.095 0.050 0.080 0.050 <0.050 0.050 6770714

Chrysene mg/kg <0.12 (1) 0.12 <0.10 (1) 0.10 <0.050 0.050 6770714

Benzo(b&j)fluoranthene mg/kg 0.26 0.050 0.20 0.050 <0.050 0.050 6770714

Benzo(k)fluoranthene mg/kg 0.067 0.050 <0.050 0.050 <0.050 0.050 6770714

Benzo(a)pyrene mg/kg 0.14 0.050 0.11 0.050 <0.050 0.050 6770714

lndeno(1,2,3-cd)pyrene mg/kg 0.14 0.050 0.11 0.050 <0.050 0.050 6770714


Benzo(g,h,i)perylene mg/kg 0.28 0.050 0.21 0.050 <0.050 0.050 6770714

Low Molecular Weight PAH’s mg/kg 0.96 0.050 0.70 0.050 <0.050 0.050 6760702

High Molecular Weight PAH’s mg/kg 1.2 0.12 0.96 0.10 <0.050 0.050 6760702

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Total PAH mg/kg 2.2 0.12 1.7 0.10 <0.050 0.050 6760702


D10-ANTHRACENE (sur.) % 95 — 79 — 91 — 6770714



ERPHENYL-D14 (stir.) % 104 — 87 — 100 — 6770714

DL Reportable Detection Limit

: 1 ) RDL raised due to sample matrix interference. [t

Page 7 of22

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Aaxxam ID GF2342 GF2343 GF2344 GF2345Sampling Date 2013/04/21 2013/04/21 2013/04/21 2013/04/21

09:20 09:30 09:40 — 10:00OC Number 36248602 36248602 36248602 36248602

UNITS IPS-SDI3-05-03 IPS-SDI3-05-04 IPS-SD13-05-05 RDL IPS-SDI 3-06-01 RDL C Batch

Page 8of22


Naphthalene ] mg/kg <0.050 <0.050 <0.050 1050 0.21 0.050 6770714

2-MèttLylnaphthalene mg/kg <0.050 <0.050 <0.050 0.050 0.14 0.050 6770714

ceäahthyIene mg/kg <0.050 <0.050 <0.050 0.050 0.064 0.050 6770714

Acenaphthene mg/kg <0 050 <0 050 <0 050 0050 <0 050 0050 6770714

Fluorene mg/kg <0 050 <0 050 <0 050 0050 0 055 0050 6770714

Phenanthrene mg/kg <0 050 <0 050 <0 050 0050 023 0050 6770714

nthracene mg/kg <0 050 <0 050 <0 050 0050 0 087 0050 6770714

Fluoranthene mg/kg <0 050 <0 050 <0 050 0050 0 28 0050 6770714

Pyrene mg/kg <0 050 <0 050 <0 050 0050 0 59 0050 6770714

Benzo(a)anthracene mg/kg <0 050 <0 050 <0 050 0050 0 089 0050 6770714

Chrysine mg/kg <0 050 <0 050 <0 050 0050 <0 14 (1) 014 6770714

Benzo(b&j)fluoranthene mg/kg <0.050 <0.050 <0.050 0.050 0.23 0.050 6770714

Benzo(k)fluoranthene mg/kg <0.050 <0.050 <0.050 0.050 0.056 1.050 6770714

Benzo(a)pyrene mg/kg <0.050 <0.050 <0.050 1.050 0.13 0.050 6770714

Indeno(1,2,3-cd)pyrene mg/kg <0.050 <0.050 <0.050 0.050 0.075 1.050 6770714

Dibenz(a,h)anthracene mg/kg <0.050 <0.050 <0.050 1.050 <0.050 1.050 6770714

Benzo(g,h,i)perylene mg/kg <0.050 <0.050 <0.050 1.050 0.14 1.050 6770714

Low Molecular Weight PAH’s mg/kg <0.050 <0.050 <0.050 0.050 0.79 1.050 6760702

High Molecular Weight PAH’s mg/kg <0.050 <0.050 <0.050 0.050 1.1 0.14 6760702

Total PAH mg/kg <0.050 <0.050 <0.050 0.050 1.9 0.14 6760702


D10-ANTHRACENE (sur.) % 90 87 91 — 98 — 6770714

D8-ACENAPHTHYLENE (sur.) % 80 78 80 — 99 — 6770714

D8-NAPHTHALENE (sur.) % 87 86 92 — 100 — 6770714

TERPHENYL-D14 (sur.) % 99 95 102 — 107 — 6770714



of 22

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Maxxam Job #: B331 479Report Date: 2013/04/29



Maxxam ID GF2346 GF2347 GF2347 GF2348Sampling Date 201 3/04/21 2013/04/21 201 3/04/21 201 3/04/21

10:00 10:10 10:10 10:20OC Number 36248602 36248602 36248602 36248602

UNITS DUP-F IPS-SDI 3-06-02 IPS-SDI3-06-02 IPS-SDI 3-06-03 RDL C BatchLab-DuD

Naphthalene mg/kg 0.23 <0.050 <0.050 <0.050 0.050 6770714

2-Methylnaphthalene mg/kg 0.20 <0.050 <0.050 <0.050 0.050 6770714

Acenaphthylene mg/kg 0.065 <0.050 <0.050 <0.050 0.050 6770714

Acenaphthene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6770714

Fluorene mg/kg 0.099 <0.050 <0.050 <0.050 0.050 6770714

Phenanthrene mg/kg 0.36 <0.050 <0.050 <0.050 0.050 6770714

Anthracene mg/kg 0.16 <0.050 <0.050 <0.050 0.050 6770714

Fluoranthene mg/kg 0.38 <0.050 <0.050 <0.050 0.050 6770714

Pyrene mg/kg 0.99 <0.050 <0.050 <0.050 0.050 6770714

Benzo(a)anthracene mg/kg 0.18 <0.050 <0.050 <0.050 0.050 6770714

Chrysene mg/kg 0.33 <0.050 <0.050 <0.050 .050 6770714

Benzo(b&j)fluoranthene mg/kg 0.41 <0.050 <0.050 <0.050 L050 6770714

Benzo(k)fluoranthene mg/kg 0.12 <0.050 <0.050 <0.050 0.050 6770714

Benzo(a)pyrene mg/kg 0.21 <0.050 <0.050 <0.050 0.050 6770714

ndeno(1,2,3-cd)pyrene mg/kg 0.11 <0.050 <0.050 <0.050 0.050 6770714

Dibenz(a.h)anthracene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6770714

Benzo(g,h,i)perylene mg/kg 0.17 <0.050 <0.050 <0.050 0.050 6770714

Low Molecular Weight PAH’s mg/kg 1.1 <0.050 <0.050 L050 6760702

High Molecular Weight PAH’s mg/kg 2.1 <0.050 <0.050 0.050 6760702

Total PAH mg/kg 3.2 <0.050 <0.050 0.050 6760702


D10-ANTHRACENE (sur.) % 85 92 89 91 — 6770714

D8-ACENAPHTHYLENE (sur.) % 86 87 81 80 — 6770714


TERPHENYL-D14 (sur.) % 92 101 99 101 — 6770714


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Report Date: 2013/04/29 Site#: TP.00131Site Location: 2225 lOCO ROADPORT MOODY BCProject #: 13-1520-0502-6075 (1327)


lAaxxarn ID GF2350 GF2351 1 GF2352 GF2353Sampling Date 2013/04/21 2013/04/21 201 3/04/21 2013/04/21

10:30 10:40 13:00 — 13:10 —

DOC Number 36248604 36248604 36248604 — 36248604 —

UNITS IPS-SDI3-06-04 IPS-SDI3-06-05 IPS-SDi3-07-01 RDL IPS-SDI3-07-02 RDL C Batch

Naphthalene mg/kg <0.050 <0.050 0.11 ).050 0.39 0.050 6770714

2-Methylnaphthalene mg/kg <0.050 <0.050 0.094 0.050 0.059 0.050 6770714

cenaphthyIene mg/kg <0.050 <0.050 0.052 0.050 0.17 0.050 6770714

Acenaphthene mg/kg <0.050 <0.050 <0.050 0.050 <0.050 0.050 6770714

Fluorene mg/kg <0.050 <0.050 0.11 0.050 <0.050 0.050 6770714

Phenanthrene mg/kg <0.050 <0.050 0.44 0.050 0.31 0.050 6770714

nthracene mg/kg <0.050 <0.050 0.25 0.050 0.093 0.050 6770714

Fluoranthene mg/kg <0.050 <0.050 0.64 0.050 0.41 0.050 6770714

Pyrene mg/kg <0.050 <0.050 2.9 0.050 0.61 0.050 6770714

Benzo(a)anthracene mg/kg <0.050 <0.050 0.47 0.050 0.092 0.050 6770714

Chrysene mg/kg <0.050 <0.050 0.78 0.050 <0.11 (1) 0.11 6770714

3enzo(b&j)fluoranthene mg/kg <0.050 <0.050 1.1 1.050 0.24 0.050 6770714

Benzo(k)fluoranthene mg/kg <0.050 <0.050 0.32 0.050 0.057 0.050 6770714

Benzo(a)pyrene mg/kg <0.050 <0.050 0.57 1.050 0.14 0.050 6770714

lrideno(1,2,3-cd)pyrene mg/kg <0.050 <0.050 0.22 0.050 0.14 1.050 6770714

Dibenz(a,h)anthracene mg/kg <0.050 <0.050 0.073 1.050 <0.050 0.050 6770714

Benzo(ghi)perylene mg/kg <0.050 <0.050 0.28 1.050 0.26 1.050 6770714

Low Molecular Weight PAH’s mg/kg <0.050 <0.050 1.1 1.050 1.0 1.050 6760702

High Molecular Weight PAH’s mg/kg <0.050 <0.050 5.4 0.050 1.3 0.11 6760702

Total PAH mg/kg <0.050 <0.050 6.5 0.050 2.3 0.11 6760702


D10-ANTHRACENE (sur.) % 88 96 97 — 80 — 6770714

D8-ACENAPHTHYLENE (sur.) % 78 83 96 — 83 6770714

08-NAPHTHALENE (sur.) % 86 93 97 — 86 6770714

TERPHENYL-D14 (sur.) % 98 104 103 — 89 6770714

RDL Reportable Detection Limit( 1 ) RDL raised due to sample matrix interference.

Page 10 of22

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Page 11 of22

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CSR PAH IN SOIL BY GC-MS (SEDIMENT>

UMaxxam ID GF2354 GF2355 GF2356Sampling Date 2013/04/21 2013/04/21 2013/04/21

13:20 13:30 13:40DCC Number 36248604 36248604 36248604

UNITS IPS-SDI3-07-03 IPS-S013-07-04 IPS-SDI3-07-05 RDL 2C Batch

Naphthalene mg/kg <0.050 <0.050 <0.050 0.050 6770714

2-Methylnaphthalene mg/kg <0.050 <0.050 <0.050 0.050 6770714

cenaphthylene mg/kg <0.050 <0.050 <0.050 0.050 6770714

\cenaphthene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Fluorene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Phenanthrene mg/kg <0.050 <0.050 <0.050 0.050 6770714

\nthracene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Fluoranthene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Pyrene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Benzo(a)anthracene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Chrysene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Benzo(b&j)fluoranthene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Benzo(k)fluoranthene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Benzo(a)pyrene mg/kg <0.050 <0.050 <0.050 0.050 6770714

lndeno(1,2,3-cd)pyrene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Dibenz(a,h)anthracene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Benzo(g,hi)perylene mg/kg <0.050 <0.050 <0.050 0.050 6770714

Low Molecular Weight PAH’s mg/kg <0.050 <0.050 <0.050 0.050 6760702

High Molecular Weight PAHs mg/kg <0.050 <0.050 <0.050 0.050 6760702

Total PAH mg/kg <0.050 <0.050 <0.050 0.050 6760702


D10-ANTHRACENE (sur.) 99 88 87 — 6770714

D8-ACENAPHTHYLENE (sur.) % 86 73 72 — 6770714

D8-NAPHTHALENE (sur.) % 95 87 86 — 6770714

FERPHENYL-D14 (sur.) % 112 99 98 — 6770714


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GOLDER ASSOCIATESMaxxam Job #: B331 479 Task Order#: 4410104800, Line Item: 10Report Date: 2013/04/29 Site#: TP.00131

Site Location: 2225 000 ROADPORT MOODY BCProject #: 13-15200502-6075 (1327)

Test Summary

Maxxam ID GF2339 Collected 2013/04/21Sample ID lPSSD1 3O5-01 Relinquished 2013/04/22


Test Description Instrumentation Batch Extracteth Analyzed Analyst[rnents by ICPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David Jung

BAL/BAL 6763014 N/A 2013/04/25 Lolita ObusanPAR in Soil by GC/MS (SIM) GC/MSD 6770714 201 3/04/24 201 3/04/26 Vidya BorshettarTotal LMW, HMW, Total PAR Calc GC/MSD 6760702 N/A 2013/04/29 Automated Statchkol-1 (2:1 Dl Water Extract) PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic

Maxxam ID GF2340 Collected 2013/04/21Sample ID DUP-E Relinquished 2013/04/22


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763014 N/A 2013/04/25 Lolita ObusanPAR in Soil by GC/MS(SIM) GC/MSD 6770714 201 3/04/24 201 3/04/26 Vidya BorshettarTotal LMW. RMW, Total PAR Calc GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763014 N/A 2013/04/25 Lolita ObusanPAH in Soil by GO/MS (SIM) GC/MSD 6770714 201 3/04/24 201 3/04/26 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk



Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungMoisture BAL/BAL 6763014 N/A 201 3/04/25 Lolita ObusanPAR in Soil by GO/MS (SIM) GC/MSD 6770714 201 3/04/24 2013/04/27 Vidya BorshettarTotal LMW, HMW, Total PAR Calc GC/MSD 6760702 N/A 2013/04/29 Automated StatchkpH (2:1 Dl Water Extract) PH/PH 6766558 201 3/04/25 2013/04/25 Nadzida Stanic



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763014 N/A 201 3/04/25 Lolita ObusanPAR in Soil by GO/MS (SIM) GO/MSD 6770714 201 3/04/24 2013/04/27 Vidya BorshettarTotal LMW, HMW, Total PAR Oalc GO/MSD 6760702 N/A 201 3/04/29 Automated Statchk

Page 12 of 22

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Test Summary


Matrix Sediment


Received 2013/04/22

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Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763014 N/A 2013/04/25 Louts ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770714 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6760702 N/A 2013/04/29 Automated Statchk

Maxxam ID GF2345 Collected 2013/04/21Sample ID IPS-SDI3-06-01 Relinquished 2013/04/22


Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungMoisture BAL/BAL 6763014 N/A 2013/04/25 Louts ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770714 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW. HMW, Total PAH Caic GC/MSD 6760702 N/A 201 3/04/29 Automated StatchkpH (2:1 Dl Water Extract) PH/PH 6766658 201 3/04/25 201 3/04/25 Nadzids Stanic

Maxxam ID GF2346 Collected 2013/04/21Sample ID DUP-F Relinquished 2013/04/22


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763014 N/A 2013/04/25 Lolita ObusanPAH in Soil by GO/MS (SIM) GCIMSD 6770714 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW. HMW, Total PAH Caic GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture . BAL/BAL 6763014 N/A 201 3/04/25 Louts ObusanPAH in Soil by GO/MS (SIM) GC/MSD 6770714 ‘2013/04/24 ‘2013/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH Caic GC/MSD 6760702’ N/A ‘20i3/04/29 Automated Statchk

Maxxam ID GF2347 Dup . Collected 2013/04/21Sample ID IPS-SD13-06-02 . Relinquished 2013/04/22

Matrix Sediment . Received 2013/04/22

Test Description Instrumentation Batch Extracted. Analyzed AnalystPAH in Soil by GO/MS (SIM) GC/MSD 6770714 2013/04/24 2013/04/27 Vidya Borshettar

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TILV Test Descriptfr.ngments by ICPMS (total)Moisture

I I PAH in Soil by GO/MS (SIM)NLI Total LMW, HMW. Total PAR Cale

ñH (2:1 Dl Water Extracfi

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GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-15200502-6075 (1327)

Collected 201 3/04/2 1Relinquished 2013/04/22

Received 2013/04/22


Matrix Sediment

Test Summary

.. Instrumentation Batch Extracted Analyzed AnalystICPM/MS 6766555 201 3/04/25 2013/04/25 David JungBAL/BAL 6763037 N/A 201 3/04/25 Lolita ObusanGC/MSD 6770714 2013/04/24 2013/04/27 Vidya Borshettar

- GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk• PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic

Maxxam ID GF2350 Collected 2013/04/21Sample ID IPSSD1306-04 Relinquished 2013/04/22


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763037 N/A 201 3/04/25 Lolita ObusanPAR in Soil by GO/MS (SIM) GO/MSD 6770714 201 3/04/24 201 3/04/27 Vidya Borshettar V

Total LMW, HMW, Total PAR CaIc GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763037 N/A 201 3/04/25 Lolita ObusanPAH in Soil by GO/MS (SIM) GO/MSD 6770714 201 3/04/24 201 3/04/27 Vidys BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk

Maxxam ID GF2352 Collected 2013/04/21V Sample ID IPS-SD13-07-01 Relinquished 2013/04/22


Test Description Instrumentation Batch Extracted Analyzed AnalystElements by IOPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungMoisture BAL/BAL 6763014 N/A 2013/04/25 Lolita ObusanPAH in Soil by GO/MS (SIM) GC/MSD 6770714 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GO/MSD 6760702 N/A 201 3/04/29 Automated StatchkpH (2:1 Dl Water Extract) PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic

Maxxam ID GF2353 Collected 2013/04/21Sample ID lPS-SD1307-02 Relinquished 2013/04/22


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763014 N/A 2013/04/25 Lotita ObusanPAR in Soil by GO/MS (SIM) GC/MSD 6770714 2013/04/24 2013/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH OaIc GO/MSD 6760702 N/A 2013/04/29 Automated Statchk

Page 14 of 22

Success TnrQugh Scerice

GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10Site#: TP00131Site Location: 2225 10CC ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)I

Test Summary



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Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungMoisture BAL/BAL 6763014 N/A 2013/04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770714 201 3/04/24 2013/04/27 Vidya BorshettarTotal LMW, HMW. Total PAH Cab GC/MSD 6760702 N/A 2013/04/29 Automated StatchkpH (2:1 DI Water Extract) PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic

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Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763014 N/A 201 3/04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770714 2013/04/24 201 3/04/27 Vidya BorshettarTotal LMW. HMW, Total PAH Caic GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763014 N/A 201 3/04/25 Lolita ObusanPAH in Soil by GO/MS (SIM) GC/MSD 6770714 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH Caic GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk

C m Sue rough

GOLDER ASSOCIATESMaxxam Job #: B331479 Task Order#: 4410104800, Line Item: 10Report Date: 2013/04/29 Site#: TP.00131

Site Location: 2225 CCC ROAD,PORT MOODY BCProject # 13-1520-0502-6075 (1327)

Package 1 I 1.7°C IEach temperature is the average of up to three cooler temperatures taken at receipt

General Comments

Results relate only to the items tested.

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Page 16 of 22

I\/I i 21 Scces* Through

GOLDER ASSOCIATESTask Order#: 4410104800Site#: TP.00131Site Location: 2225 10CC ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

Quality Assurance ReportMaxxam Job Number: B331 479


6763014 LOl Method Blank Moisture 2013/04/25 <0.30 %6763037 LOl Method Blank Moisture 2013/04/25 <0.30 %6766555 DJ Method Blank Total Aluminum (Al) 2013/04/25 <100 mg/kg

Total Antimony (Sb) 2013/04/25 <0.10 mg/kgTotal Arsenic (As) 201 3/04/25 <0.50 mg/kgTotal Barium (Ba) 201 3/04/25 <0.10 mg/kgTotal Beryllium (Be) 201 3/04/25 <0.40 mg/kgTotal Bismuth (Bi) 201 3/04/25 <0.10 mg/kgTotal Cadmium (Cd) 201 3/04/25 <0.050 mg/kgTotal Calcium (Ca) 201 3/04/25 <100 mg/kgTotal Chromium (Cr) 2013/04/25 <1.0 mg/kgTotal Cobalt (Co) 201 3/04/25 <0.30 mg/kgTotal Copper (Cu) 2013/04/25 <0.50 mg/kgTotal Iron (Fe) 2013/04/25 <100 mg/kgTotal Lead (Pb) 2013/04/25 <0.10 mg/kgTotal Magnesium (Mg) 201 3/04/25 <100 mg/kgTotal Manganese (Mn) 2013/04/25 <0.20 mg/kgTotal Mercury (Hg) 201 3/04/25 <0.050 mg/kgTotal Molybdenum (Mo) 201 3104/25 <0.10 mg/kgTotal Nickel (Ni) 2013/04/25 <0.80 mg/kgTotal Phosphorus (P) 201 3/04/25 <10 mg/kgTotal Potassium (K) 201 3/04/25 <100 mg/kgTotal Selenium (Se) 2013/04/25 <0.50 mg/kgTotal Silver (Ag) 201 3/04/25 <0.050 mg/kgTotal Sodium (Na) 201 3/04/25 <100 mg/kgTotal Strontium (Sr) 201 3/04/25 <0.10 mg/kgTotal Thallium (TI) 201 3/04/25 <0.050 mg/kgTotal Tin (Sn) 201 3/04/25 <0.10 mg/kgTotal Titanium (Ti) 2013/04/25 1.4, RDL=1.0 mg/kgTotal Vanadium (V) 201 3/04/25 <2.0 mg/kgTotal Zinc (Zn) 201 3/04/25 <1.0 mg/kgTotal Zirconium (Zr) 2013/04/25 <0.50 mg/kg

6770714 VB1 Method Blank D10-ANTHRACENE (sur.) 2013/04/26 99 % 60- 130D8-ACENAPHTHYLENE (sur.) 2013/04/26 100 % 50- 130D8-NAPHTHALENE (sur.) 2013/04/26 101 % 50- 130TERPHENYL-D14 (sur.) 2013/04/26 108 % 60- 130Naphthalene 201 3/04/26 <0.050 mg/kg2-Methylnaphthalene 201 3/04/26 <0.050 mg/kgAcenaphthylene 2013/04/26 <0.050 mg/kgAcenaphthene 201 3/04/26 <0.050 mg/kgFluorene 201 3/04/26 <0.050 mg/kg LPhenanthrene 201 3/04/26 <0.050 mg/kgAnthracene 201 3/04/26 <0.050 mg/kgFluoranthene 201 3/04/26 <0.050 mg/kgPyrene 201 3/04/26 <0.050 mg/kgBenzo(a)anthracene 2013/04/26 <0.050 mg/kgChrysene 2013/04/26 <0.050 mg/kgBenzo(b&j)fluoranthene 201 3/04/26 <0.050 mg/kgBenzo(k)fluoranthene 201 3/04/26 <0.050 mg/kgBenzo(a)pyrene 201 3/04/26 <0.050 mg/kglndeno(1 ,2,3-cd)pyrene 2013/04/26 <0.050 mg/kgDibenz(a,h)anthracene 2013/04/26 <0.050 mg/kgBenzo(g,h,i)perylene 2013/04/26 <0.050 mg/kg

RPD (GF2347-01] Naphthalene 201 3/04/27 NC % 502-Methylnaphthalene 201 3/04/27 NC % 50

Mav<an Aralytics Internatio1a Corporation o/a Maxxam Aralytics Bumaby 4606 Canada Way VSG 1 (c Teiephone(604) 734 7276 Fax(o04) 731 236o

Pagel7of22

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Quality Assurance Report (Continued)Maxxam Job Number: B331 479

NCNCNCNCNCNCNCNCNCNCNCNCNCNCNC

%%%%%%%%%%%%%%%

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6770714 VB1 RPD [GF2347-01J Acenaphthylene 2013/04/27Acenaphthene 2013104/27Fluorene 2013/04/27Phenanthrene 2013/04/27Anthracene 2013/04/27Fluoranthene 201 3/04/27Pyrene 201 3/04/27Benzo(a)anthracene 2013/04/27Chrysene 201 3/04/2 7Benzo(b&j)fluoranthene 2013/04/27Benzo(k)fluoranthene 2013/04/27Benzo(a)pyrene 2013/04/27Indeno(1 ,2,3-cd)pyrene 2013/04/27Dibenz(a,h)anthracene 2013/04/27Benzo(g,h,i)perylene 2013/04/27

Matrix Spike[GF2347-01] D10-ANTHRACENE (sur.) 201 3/04/27 96 % 60- 130

D8-ACENAPHTHYLENE (sur.) 201 3/04/27 90 % 50- 130D8-NAPHTHALENE (sur.) 201 3/04/27 95 % 50- 130TERPHENYL-D14 (sur.) 201 3/04/27 104 % 60- 130Naphthalene 201 3/04/27 92 % 50- 1302-Methylnaphthalene 2013/04/27 96 % 50- 130Acenaphthylene 2013/04/27 96 % 50 - 130Acenaphthene 2013/04/27 97 % 50-130Fluorene 2013/04/27 99 % 50- 130Phenanthrene 2013/04/27 95 % 60- 130

‘ Anthracene 2013/04/27 99 % 60- 130Fluoranthene 201 3/04/27 109 % 60- 130Pyrene 201 3/04/27 104 % 60- 130Benzo(a)anthracene 201 3/04/27 97 % 60- 130Chrysene 201 3/04/27 95 % 60- 130Benzo(b&j)fluoranthene 2013/04/27 111 % 60- 130Benzo(k)fluoranthene 201 3/04/27 95 % 60- 130Benzo(a)pyrene 2013/04/27 102 % 60-130lndeno(1,2,3-cd)pyrene 2013/04/27 104 % 60- 130Dibenz(a,h)anthracene 2013/04/27 102 % 60- 130Benzo(g,h,i)perylene 201 3/04/27 97 % 60- 130

6766555 DJ LCS Total Antimony (Sb) 201 3/04/25 97 % 75- 125Total Arsenic (As) 2013/04/25 91 % 75- 125Total Barium (Ba> 2013/04/25 98 % 75- 125Total Beryllium (Be> 2013/04/25 90 % 75- 125Total Cadmium (Cd> 2013/04/25 94 % 75- 125Total Chromium (Cr) 2013/04/25 98 % 75- 125Total Cobalt (Ce) 2013/04/25 101 % 75- 125Total Copper (Cu) 2013/04/25 101 % 75- 125Total Lead (Pb) 201 3/04/25 101 % 75- 125Total Manganese (Mn) 2013/04/25 102 % 75- 125Total Mercury (Hg) 201 3/04/25 99 % 75- 125Total Molybdenum (Mo) 201 3/04/25 107 % 75- 125Total Nickel (Ni) 201 3/04/25 96 % 75- 125Total Selenium (Se) 201 3/04/25 88 % 75- 125Total Silver (Ag) 2013/04/25 98 % 75- 125Total Strontium (Sr> 201 3/04/25 103 % 75- 125Total Thallium (TI) 2013/04/25 101 % 75- 125Total Tin (Sn) 2013/04/25 103 % 75- 125U,

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Maoam Analytics International Corporailon 0/a Maxxam Analytics Burnaby: 4606 Canada Way V5G 1 K5 Telephone(604) 734-7276 Fax(604) 731-2386

Page 18 of 22

I’/I 21 2I rTi Succ.a hruçh



QA/QC DateBatch AnalyzedNum Init QC Type Parameter yyyy/mm/dd Value Recovery UNITS QC Limits

6766556 DJ LCS Total Titanium (Ti) 201 3104/25 106 % 75-125Total Vanadium (V) 201 3/04/25 95 % 75- 125Total Zinc (Zn) 201 3/04/25 92 % 75- 125

6766558 NS6 LCS Soluble (2:1) pH 201 3/04/25 102 % 96- 1046770714 VB1 LCS D10-ANTHRACENE (sur.) 201 3/04/27 97 % 60- 130

D8-ACENAPHTHYLENE (sur.) 2013/04/27 92 % 50- 130D8-NAPHTHALENE (sur.) 2013/04/27 92 % 50- 130TERPHENYL-D14 (sur.) 2013/04/27 103 % 60- 130Naphthalene 2013/04/27 87 % 50- 130 •.

2-Methylnaphthalene 2013/04/27 91 % 50 - 130Acenaphthylene 2013/04/27 89 % 50-130Acenaphthene 2013/04/27 92 % 50- 130Fluorene 2013/04/27 91 % 50- 130Phenanthrene 2013/04/27 92 % 60- 130Anthracene 201 3/04/27 97 % 60- 130Fluoranthene 201 3/04/27 104 % 60- 130Pyrene 2013/04/27 101 % 60-130Benzo(a)anthracene 201 3/04/27 89 % 60- 130Chrysene 201 3/04/27 90 % 60- 130Benzo(b&j)fluoranthene 201 3/04/27 93 % 60- 130Benzo(k)fluoranthene 2013/04/27 94 % 60- 130Benzo(a)pyrene 201 3/04/27 96 % 60- 130lnderro(1,2,3-cd)pyrene 2013/04/27 98 % 60- 130Dibenz(a,h)anthracene 201 3/04/27 95 % 60- 130Benzo(g,h,i)perylene 201 3/04/27 91 % 60- 130

6766555 DJ SRM Total Aluminum (Al) 2013/04/25 113 % 70-130Total Antimony (Sb) 201 3/04/25 104 % 70- 130Total Arsenic (As) 201 3/04/25 96 % 70- 130Total Barium (Ba) 2013/04/25 114 % 70- 130Total Cadmium (Cd) 201 3/04/25 105 % 70- 130Total Calcium (Ca) 2013/04/25 105 % 70- 130Total Chromium (Cr) 2013/04/25 106 % 70- 130Total Cobalt(Co) 2013/04/25 100 % 70-130 \..-‘

Total Copper (Cu) 2013/04/25 97 % 70- 130Total Iron (Fe) 2013/04/25 105 % 70- 130Total Lead (Pb) 2013/04/25 108 % 70- 130Total Magnesium (Mg) 201 3/04/25 .. 98 % 70- 130 LTotal Manganese (Mn) 201 3/04/25 109 % 70- 130Total Mercury (Hg) 2013/04/25 89 % 70 130Total Molybdenum (Mo) 201 3/04/25 110 % 70 130Total Nickel (Nt) 201 3/04/25 99 % 70 130Total Phosphorus (F) 201 3/04/25 86 % 70- 130Total Strontium (Sr) 2013/04/25 116 % 70 - 130Total Thallium (TI) 201 3/04/25 97 % 70- 130Total Titanium (Ti) 2013/04/25 . 112 % 70 - 130Total Vanadium (V) 2013/04/25 105 % 70- 130Total Zinc (Zn) 2013/04/25 88 % 70- 130

Duplicate: Paired analysis of a separate portion of the same sample. Used to evaluate the variance in the measurement.Matrix Spike: A sample to which a known amount of the analyte of interest has been added. Used to evaluate sample matrix interference.SRM: A sample of known concentration prepared by an external agency under stringent conditions. Used as an independent check of method accuracy.LCS: A blank matrix sample to which a known amount of the analyte, usually from a second source, has been added. Used to evaluate method accuracy.Method Blank: A blank matrix containing all reagents used in the analytical procedure. Used to identify laboratory contamination.Surrogate: A pure or isotopically labeled compound whose behavior mirrors the analytes of interest. Used to evaluate extraction efficiency.NC (RPD): The RPD was not calculated. The level of analyte detected in the parent sample and its duplicate was not sufficiently significant to permit areliable calculation.

Maxxam Analytics international Corporation 0/a Maxxam Analytics Burnaby: 4606 Canada Way V5G 1K5 Telephone(604) 734-7276 Fax(604) 7312386

Page 19of22

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Maxxam Job #: B331 479

The analytical data and all QC contained in this report were reviewed and validated by the following individual(s).

Andy Lu, ta Validation Coordinator

Maxxam has procedures in place to nuard against improper use of the electronic signature and have the required “signatories”, as per section 5.10.2 ofISO/IEC 17025:2005(E), signing the reports. For Service Group specific validation please refer to the Validation Signature Page.

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Consultant: Golder Associates Sampling Date: April 21, 2013

Location: 2225 loco Road, Port Moody, BC Laboratory: Maxxam Analytics Burnaby



Yes No NA CommentsInstrument Surrogate Recovery X All laboratory QC results are within

Extraction Surrogate Recovery X acceptance criteria.Method Blank Concentration X

Matrix Duplicate RPD XMatrix Spike Recovery X

Lab Control Sample Recovery X


Yes No NA CommentsField Blank Concentration________ X All field QC samples are within

Trip Blank Concentration________ X alert limits.Field Duplicate RPD X

Has CoA been signed off (Yes/No)?: Yes

Has lab warranted all tests were in statistical control in CoA (Yes/No)?: YesHas lab warranted all tests were analyzed following SOP’s in CoA (Yes/No)?: YesWere all samples analyzed within hold times (Yes/No)?: YesAll volatiles samples methanol extracted (if required) within 48 hours (Yes/No)?: n/aIs Chain of Custody completed and signed (Yes/No)?: YesWere sample temperatures acceptable when they reached lab (Yes/No)?: Yes

Was a Data Quality Waiver (DQW) issued (Yes/No)?: No

Date Issued: n/a Date of Response: n’a

Is data considered to be reliable (Yes/No)?: YesIf answer is “No”, describe and provide rationale:

Data Reviewed by (Print): Amanda Newberry Data Reviewed by (Signature):

Date: May 7, 2013

Data Quality Review Checklist (Rev 13) For Use on Imperial Oil Projects Only

I\A m 5uccss Thruçh Sc,enc

Attention: Dan ParksGOLDER ASSOCIATES500-4260 STILL CREEK DRIVEBURNABY, BCCANADA V5C 6C6

Task Order#: 4410104800Line Item: 10Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)Your C.O.C. #: 36248605, 36248607

Report Date: 2013/04/29

MAXXAM JOB #: B331494Received: 2013104122, 14:50

Sample Matrix: Sediment# Samples Received: 14


AnalysesElements by ICPMS (total)MoisturePAH in Soil by GO/MS (SIM)Total LMW, HMW, Total PAH CaicpH (2:1 Dl Water Extract)

Remarks:

Quantity Laboratory Method8 BBY7SOP-0000414 BBY8SOP-0001 714 BBY8SOP-0002214 BBY Wl-000338 BBY6SOP-00028

Primary referenceBCMOE-SALMOnt MOE -E 3139EPA 8270DBC MOE Lab MethodCarter, SSMA 16.2

All Blank values are reported. Associated data are not blank corrected.‘-- Solids results are based on dry weight except Biota Analyses & Special Waste Oil & Grease.

Organic Analyses are not corrected for extraction recovery or method blanks. Certain methods (e.g. CARB 429, quinoline,all PCDD/F and DBD/DBF) quantitate by the method of isotope dilution

Maxxam Analytics has performed all analytical testing herein in accordance with ISO 17025.

All CCME results met required criteria unless otherwise stated in the report. The CWS PHC methods employed byMaxxam conform to all prescribed elements of the reference method and performance based elements have beenvalidated. All modifications have been validated and proven equivalent following the ‘Alberta Environment Draft Addenda to

fl the CWS-PHC, Appendix 6, Validation of Alternate Methods’. Documentation is available upon request. Deviations fromL Reference Method for the Canada-wide Standard for Petroleum Hydrocarbons in Soil-Tier 1 Method:

F2/F3/F4 data reported using validated cold solvent extraction instead of Soxhlet extraction.


All analysis data reported was generated when the analytical methods were in statistical control and criteria for spikerecoveries, reference material recoveries, method blanks data and duplicate precision were met unless otherwise stated.All samples were analysed within hold time unless otherwise flagged. All soil samples for BTEX analysis were methanolextracted within 24 hours unless otherwise flagged.This report shall not be reproduced except in full, without the written approval of the laboratory.

Page 1 of24

21 21 rn

TaskOrder#: 4410104800Line Item: 10Site#:TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)YourC.O.C. #: 36248605, 36248607

(500-4260 STILL CREEK DRIVE \1BURNABY,BCCANADA V5C 6C6



MAXXAM JOB #: B331494Received: 2013/04122, 14:50

Methods used by Maxxam are based upon those found in ‘Standard Methods for the Examination of Water andWastewater’, 22nd Edition, published by the American Public Health Association, or on US EPA, protocols found in the’

Test Methods for Evaluating Solid Waste’, Physical/Chemical Methods, SW846, 3rd Edition. Other procedures are based

on the methodologies accepted by the appropriate regulatory agency. Methodology briefs are available by written request.

All work recorded herein has been done in accordance with normal professional standards using accepted testingmethodologies, quality assurance and quality control procedures except where otherwise agreed to by the client and ‘iZ!testing company in writing. Maxxam Analytics is limited in liability to the actual cost of analysis unless otherwise agreed in

writing. There is no other warranty expressed or implied. Your samples will be retained at Maxxam for a period of 45 daysfrom receipt of data or as per contract.


Encryption Key

29r2013 135425 0700

Please direct all question regarding this Certificate of Analysis to your Project Manager.

VJ Oco, Burnaby Project ManagerEmail: [email protected]# (604) 639-8422

Maxxam has procedures in place to guard against improper use of the electronic signature and have the required *signatories. as per section5.10.2 of ISOIIEC 17025:2005(E), signing the reports. For Service Group specific validation please refer to the Validation Signature Page.

Maxxa*, Ana1y8os nterna8o*al corp*ratio* oia Maxxar* An*]lic* Bar,aby: 4606 Canada Way V5G 160 Telnphone(604) 734-7276 Fax(604) 731-2386

Page 2 of 24

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JF Maocam Job #


ir

Sampling Date


LV

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GF2411 GF2413 GF2416 GF2418 GF24192013/04/22 201.3/04/22 2013/04/22 2013/04/22 2013/04/22

09:20 09:40 10:10 10:30 10:40DOC Number I I 36248605 I 36248605 I 36248605 I 36248605 I 36248605 I I

I UNITS I IPS-SDI3-08-O1 IPS-SDI3-08-03 IPS-SDI3-09-O1 I IPS-SDI3-09-03 IPS-SDI3-1O-01 I RDL k2C Batch

Soluble (2:1) p1-I IPH Units 7.71 8.12 7.92 8.20 7.64 10.010 16766558


Maxxam ID GF2429 GF2429 GF2430 GF2432Sampling Date 201 3/04/22 201 3/04/22 201 3/04/22 201 3/04/22

11:00 11:00 11:10 11:30DCC Number 36248607 36248607 36248607 36248607

UNITS IP$-SDI3-10-03 IPS-SDI3-10-03 IPS-SDI3-11-O1 IPS-SDI3-11-03 RDL C BatchLab-Dup

Soluble (2:1) pH pH Units I 9.10 I 9.10 7.83 I 7.81 0.010 6766558


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Page 3 of 24

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Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

0n


AaxxamID I I GF2411 I GF2412 I GF2413 I GF2414 I GF2415 I I3ampling Date 2013/04/22 2013/04/22 2013104/22 2013/04/22 2013/04/22

09:20 09:30 09:40 09:50 10:00OC Number 36248605 36248605 36248605 36248605 36248605

UNITS IPS-SDI3-08-O1 IPS-SDI3-08-02 IPS-SDI3-08-03 IPS-SDI3-08-04 IPS-SDI3-08-05 RDL C Batch

DL Reportable Detection Limit

Aoisture j 65 63 59 59 56 0.30 16763037Li

OC Number 36248605

‘“-‘ ID I I GF2416 I GF2417 I GF2418 I GF2418 GF2419 I II I I I I I

Sampling Date 2013/04/22 2013/04/22 2013/04/22 2013/04/22 2013/04/2210:10 10:20 10:30 10:30 10:40

136248605I I

36248605. I

36248605

Moisture I I 66 52 23 24 64 10.30 j6763014


UNITS IPS-SDI3-09-01 IPS-SDI3-09-02 IPS-SDI3-09-03 IPS-SDI3-09-03 IPS-SDI3-1O-O1 RDL 2C BatchLab-Dup I

36248605


10:50 11:00 11:00 11:10OC Number 36248605 36248607 36248607 36248607

UNITS IPS-SDI3-1O-02 IPS-SDI3-1O-03 IPS-SDI3-10-03 C Batch IPS-SDI3-11-O1 RDL C BatchLab-Dup

Moisture I 20 20 I 19 16763037 I 55 j0.30 I6763014


Maxxam ID GF2431•

GF2432Sampling Date 2013/04/22 2013/04/22

11:20 j 11:30OC Number 36248607 36248607

UNITS IPS-SDI3-11-02 kC Batch IPS-SDI3-11-03 RDL C Batch

Moisture 26 6763014 I 030 6763037


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Page 4of24

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Site#: TP.00131Site Location: 2225 10CC ROAD,PORT MOODY BC

Project #: 13-1520-0502-6075 (1327)


MaxxamlD GF2411 GF2413 GF2416 GF2418ampIing Date 2013/04/22 2013/04/22 2013/04/22 2013/04/22

09:20 09:40 10:10 10:30 —

CCC Number 36248605 36248605 36248605 36248605UNITS IPS-SDI3-08-O1 IPS-SDI3-08-03 IPS-SDI3-09-01 IPS-SD13-09-03 RDL C Batch


Total Antimony (Sb) mg/kg 0.36 0.35 0.70 0.19 0.10 6766555



Total Beryllium (Be) mg/kg <0.40 <0.40 0.40 <0.40 0.40 6766555





Total Cobalt (Co) mg/kg 8.97 10.2 9.55 4.38 0.30 6766555

Total Copper (Cu) mg/kg 55.5 37.7 120 11.6 0.50 6766555


Total Lead (Pb) mg/kg 26.8 8.94 76.2 3,42 0.10 6766555



Total Mercury (Hg) mg/kg 0.198 <0.050 0.242 <0.050 0.050 6766555





Total Selenium (Se) mg/kg 1.14 0.82 1.42 <0.50 0.50 6766555





Total Tin (Sn) mg/kg 1.16 0.43 2.98 0.16 0.10 6766555



Total Zinc (Zn) mg/kg 95.2 77.5 193 27.2 1.0 6766555



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Project #: 13-1520-0502-6075 (1327)

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MaxxamlD GF2419 GF2429 GF2429 GF2430Sampling Date 2013/04/22 2013/04/22 2013/04/22 2013/04/22

10:40 11:00 11:00 11:10 —

OC Number 36248605 36248607 36248607 36248607UNITS IPS-SDI3-1O-O1 IPS-SDI3-1O-03 IPS-SDI3-10-03 IPS-SDI3-11-O1 RDL tC Batch

Lab-Dup —

Fotal Aluminum (Al) mg/kg 21200 5800 5640 15100 100 6766555

Total Antimony (Sb) mg/kg 0.67 0.15 0.15 0.44 0.10 6766555



Total Beryllium (Be) mg/kg <0.40 <0.40 <0.40 <0.40 0.40 6766555

Total Bismuth (Bi) mg/kg 0.66 <0.10 <0.10 0.33 0.10 6766555




Total Cobalt (Co) mg/kg 9.00 3.34 3.27 7.16 0.30 6766555

Total Copper (Cu) mg/kg 91.7 7.41 6.89 57.8 0.50 6766555


Fotal Lead (Pb) mg/kg 73.6 2.39 2.25 36.9 0.10 6766555

Fotal Magnesium (Mg) mg/kg 9930 2940 2940 7470 100 6766555

TotalManganese(Mn) mg/kg 323 115 117 257 0.20 6766555

Total Mercury (Hg) mg/kg 0.223 <0.050 <0.050 0.121 0.050 6766555





Total Selenium (Se) mg/kg 1.47 <0.50 <0.50 0.78 0.50 6766555

Total Silver (Ag) mg/kg 0.571 0.051 <0.050 0.349 0.050 6766555



rotal Thallium (TI) mg/kg 0.298 0.326 0.326 0.237 0.050 6766555

Total Tin (Sn) mg/kg 2.57 0.13 0.12 1.41 0.10 6766555



Total Zinc (Zn) mg/kg 156 20.0 19.9 95.9 1.0 6766555



Page 6 of 24

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ELEMENTS BY ATOMIC SPECTROSCOP’ (SEDIMENT)

H

Maxxam ID GF2432Sampling Date 201 3/04/22

11:30DOC Number 36248607 —

UNITS IPS-SDI3-11-03 RDL C Batch

Total Aluminum (Al) mg/kg 21400 100 6766555

Total Antimony (Sb) mg/kg 0.34 0.10 6766555

Total Arsenic (As) mg/kg 9.95 0.50 6766555

Total Barium (Ba) mg/kg 54.3 0.10 6766555

Total Beryllium (Be) mg/kg <0.40 0.40 6766555

Total Bismuth (Bi) mg/kg 0.17 0.10 6766555

Total Cadmium (Cd) mg/kg 1.38 0.050 6766555

Total Calcium (Ca) mg/kg 11300 100 6766555

Total Chromium (Cr) mg/kg 39.0 1.0 6766555

Total Cobalt(Co) mg/kg 10.5 0.30 6766555

Total Copper (Cu) mg/kg 38.4 0.50 6766555

Total Iron (Fe) mg/kg 33800 100 6766555

Total Lead (Pb) mg/kg 9.29 0.10 6766555

Total Magnesium (Mg) mg/kg 10200 100 6766555

Total Manganese (Mn) mg/kg 374 0.20 6766555

Total Mercury (Hg) mg/kg <0.050 0.050 6766555

Total Molybdenum (Mo) mg/kg 4.58 0.10 6766555

Total Nickel (Ni) mg/kg 34.6 0.80 6766555

Total Phosphorus (P) mg/kg 601 10 6766555

Total Potassium (K) mg/kg 3290 100 6766555

Total Selenium (Se) mg/kg 0.71 0.50 6766555

Total Silver (Ag) mg/kg 0.219 0.050 6766555

Total Sodium (Na) mg/kg 2580 100 6766555

Total Strontium (Sr) mg/kg 85.7 0.10 6766555

Total Thallium (TI) mg/kg 0.230 0.050 6766555

Total Tin (Sn) mg/kg 0.43 0.10 6766555

Total Titanium (Ti) mg/kg 966 1.0 6766555

Total Vanadium (V) mg/kg 58.6 2.0 6766555

Total Zinc (Zn) mg/kg 771 10 6766555

Total Zirconium (Zr) mg/kg 7.73 0.50 6766555


Page 7 of24

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Aaxxam ID GF2411 GF2412 GF2413Sampling Date 2013/04/22 2013/04/22 2013/04/22

09:20 09:30 09:40OC Number 36248605 — 36248605 - — 36248605 —

UNITS IPS-SDI3-08-01 RDL IPS-SDI3-O8-02 RDL IPS-SDI3-08-03 RDL C Batch


2-Methylnaphthalene mg/kg <0.050 0.050 <0.050 0.050 <0.050 0.050 6770714

.cenaphthylene mg/kg <0.050 0.050 0.071 0.050 <0.050 0.050 6770714

cenaphthene mg/kg <0.050 0.050 <0.050 0.050 <0.050 0.050 6770714

Fluorene mg/kg <0.050 0.050 <0.050 0.050 <0.050 0.050 6770714


Anthracene mg/kg 0.052 0.050 <0.050 0.050 <0.050 0.050 6770714


Pyrene mg/kg 0.34 0.050 0.32 0.050 <0.050 0.050 6770714

Benzo(a)anthracene mg/kg 0.072 0.050 0.056 0.050 <0.050 0.050 6770714

Chrysene mg/kg 0.14 0.050 <0.080 (1) 080 <0.050 0.050 6770714

Benzo(b&j)fluoranthene mg/kg 0.15 0.050 0.15 0.050 <0.050 0.050 6770714

Benzo(k)fluoranthene mg/kg <0.050 0.050 <0.050 0.050 <0.050 0.050 6770714

Benzo(a)pyrene mg/kg 0.080 0.050 0.089 0.050 <0.050 050 6770714

ndeno(1,2,3-cd)pyrene mg/kg <0.050 0.050 0.079 0.050 <0.050 cLO5O 6770714


Benzo(g,h,i)perylene mg/kg 0.067 0.050 0.15 0.050 <0.050 0.050 6770714

Low Molecular Weight PAH’s mg/kg 0.23 0.050 0.39 0.050 <0.050 0.050 6760702

High Molecular Weight PAH’s mg/kg 0.80 0.050 0.69 0.080 <0.050 0.050 6760702

Total PAH mg/kg 1.0 0050 1.1 0.080 <0.050 0.050 6760702


D10-ANTHRACENE (sur.) % 87 — 82 — 101 — 6770714



TERPHENYL-D14 (sur.) % 96 — 90 — 111 — 6770714



PageS of 24

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Maxxam Job #: B331494- Report Date: 2013/04/29

Succ ThrouCh 5cc



Project #: 13-15200502-6075 (1327)



09:50 10:00 10:00 10:10DCC Number 36248605 36248605 36248605 36248605 —

UNITS IPS$D13O804 IPSSD13-O8-O5 IPS-SDI3-08-05 IPS-SD13-O901 ROL C BatchLab-Dup —

Naphthalene mg/kg <0.050 <0.050 <0.050 0.19 0.050 6770725

Methylnaphthalene mg/kg <0 050 <0 050 <0 050 0 18 0050 6770725

Acenaphthylene mg/kg <0.050 <0.050 <0.050 0.066 0.050 6770725

cerphthene mg/kg <0.050 <0.050 <0.050 0.099 0.050 6770725

uorene mg/kg <0 050 <0 050 <0 050 0 17 0050 6770725

enanthrene mg/kg <0 050 <0 050 <0 050 0 60 0050 6770725

A thracene mg/kg <0 050 <0 050 <0 050 0 39 0050 6770725

tioranthene mg/kg <0 050 <0 050 <0 050 1 0 0050 6770725

rene mg/kg <0 050 <0 050 <0 050 5 3 0050 6770725

Benzo(a)anthracene mg/kg <0 050 <0 050 <0 050 0 81 0050 6770725

Chrysei’ië mg/kg <0 050 <0 050 <0 050 1 2 0050 6770725

Beh(b&j)fluoranthene mg/kg <0.050 <0.050 <0.050 1.7 0.050 6770725

Benzo(k)fluoranthene mg/kg <0.050 <0.050 <0.050 0.53 0.050 6770725

-, Benzo(a)pyrene mg/kg <0.050 <0.050 <0.050 0.91 0.050 6770725

Indeno(1,2,3-cd)pyrene mg/kg <0.050 <0.050 <0.050 0.31 0.050 6770725

Dibenz(a,h)anthracene mg/kg <0.050 <0.050 <0.050 0.11 0.050 6770725

Benzo(g,h,i)perylene mg/kg <0.050 <0.050 <0.050 0.37 0.050 6770725

Low Molecular Weight PAH’s mg/kg <0.050 <0.050 1.7 0.050 6760702

High Molecular Weight PAHs mg/kg <0.050 <0.050 9.3 0.050 6760702

Total PAH mg/kg <0.050 <0.050 11 0.050 6760702


D10-ANTHRACENE (sur.) % 83 90 96 92 6770725

D8-ACENAPHTHYLENE (six.) % 74 83 86 91 — 6770725


TERPHENYL-D14 (stir.) % 91 98 105 99 6770725


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IPage 9 of 24

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Project #: 13-1520-0502-6075 (1327) r

axxam ID GF2417 GF2418 GF2419 GF2420Sampling Date 2013/04/22 2013/04/22 2013/04/22 2013/04/22

10:20 10:30 10:40 10:50)OC Number 36248605 — 36248605 36248605 36248605 —

UNITS IPS-SDI3-09-02 RDL IPS-SDI3-09-03 IPS-SDI3-1O-O1 IPS-S013-1O-02 RDL C Batch

Naphthalene mg/kg 0.18 0.050 <0.050 0.13 <0.050 .050 6770725

2-Methylnaphthalene mg/kg 0.052 0.050 <0.050 0.10 <0.050 0.050 6770725

cenaphthylene mg/kg 0.060 0.050 <0.050 0.055 <0.050 0.050 6770725

Acenaphthene mg/kg <0.050 0.050 <0.050 <0.050 <0,050 0.050 6770725

Fluorene mg/kg <0.050 0.050 <0.050 0.078 <0.050 0.050 6770725

Phenanthrene mg/kg 0.16 0.050 <0.050 0.33 <0.050 0.050 6770725

Anthracene mg/kg 0.057 0.050 <0.050 0.19 <0.050 0.050 6770725

Fluoranthene mg/kg 0.22 0.050 <0.050 0.62 <0.050 0.050 6770725

Pyrene mg/kg 0.36 0.050 <0.050 1.6 <0.050 0.050 6770725

Benzo(a)anthracene mg/kg 0.054 0.050 <0.050 0.34 <0.050 0.050 6770725

Chrysene mg/kg <0.090 (1) 0.090 <0.050 0.53 <0.050 0.050 6770725

Benzo(b&j)fluoranthene mg/kg 0.14 0.050 <0.050 0.71 <0.050 ).050 6770725

Benzo(k)fluoranthene mg/kg <0.050 0.050 <0.050 0.23 <0.050 ).050 6770725

Benzo(a)pyrene mg/kg 0.077 0.050 <0.050 0.40 <0.050 0.050 6.70725

Indeno(1,2,3-cd)pyrene mg/kg 0.069 0.050 <0.050 0.18 <0.050 0.050 6770725

Dibenz(a,h)anthracene mg/kg <0.050 .050 <0.050 0.058 <0.050 ).050 6770725

Benzo(g,h,i)perylene mg/kg 0.14 0.050 <0.050 0.23 <0.050 ).050 6770725

Low Molecular Weight PAH’s mg/kg 0.50 0.050 <0.050 0.88 <0.050 0.050 6760702

High Molecular Weight PAH’s mg/kg 0.71 0.090 <0.050 3.5 <0.050 0.050 676b702

Total PAH mg/kg 1.2 0.090 <0.050 4.4 <0.050 0.050 6760702


D10-ANTHRACENE (sur.) % 80 — 96 93 106 — 677d725

D8ACENAPHTHYLENE (sur.) % 85 — 92 91 96 — 6770725

D8-NAPHTHALENE (sur.) % 85 — 92 91 93 — 6770725

TERPHENYL-D14 (sur.) % 87 — 106 101 113 — 6770725



Page 10 of 24

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Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

CSR PAK IN SOIL BY GC-MS (SEDIMENT)

hit //

Iaxxam ID GF2429 GF2430 GF2431 GF2432Sampling Date 2013/04/22 2013/04122 2013/04/22 2013/04/22

11:00 11:10 11:20 11:30 —

DOC Number 36248607 36248607 36248607 36248607UNITS IPS-SDI3-1O-03 IPS-SDI3-11-O1 IPS-SDI3-11-02 IPS-SDI3-11-03 RDL C Batch

Naphthalene mg/kg <0 050 0 086 <0 050 <0 050 0050 6770725

2 Methylnaphthalene mg/kg <0 050 0 082 <0 050 <0 050 0.050 6770725

Acenáphthylene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6770725

Acenaphthene mg/kg <0 050 <0 050 <0 050 <0 050 0050 6770725

Fluorene mg/kg <0.050 0.059 <0.050 <0.050 0.050 6770725

Phenanthrene mg/kg <0.050 0.22 <0.050 <0.050 0.050 6770725

Anthracene mg/kg <0 050 0 14 <0 050 <0 050 0050 6770725

Fluoranthene mg/kg <0 050 0 31 <0 050 <0 050 0050 6770725

Pyrehe mg/kg <0.050 1.0 <0.050 <0.050 0.050 6770725

B&no(a)anthracene mg/kg <0 050 0 30 <0 050 <0 050 0050 6770725

Chrysene mg/kg <0.050 0.42 <0.050 <0.050 0.050 6770725

C:

U”

Benzo(b&j)fluoranthene mg/kg <0.050 0.51 <0.050 <0.050 1.050 6770725

Benzo(k)fluoranthene mg/kg <0.050 0.16 <0.050 <0.050 0.050 6770725

Benzo(a)pyrene mg/kg <0.050 0.28 <0.050 <0.050 1.050 6770725

ndeno(1 2,3-cd)pyrene mg/kg <0.050 0.11 <0.050 <0.050 0.050 6770725

Dibenz(a,h)anthracene mg/kg <0.050 <0.050 <0.050 <0.050 0.050 6770725

Benzo(g,h,i)perylene mg/kg <0.050 0.14 <0.050 <0.050 0.050 6770725

Low Molecular Weight PAH’s mg/kg <0.050 0.59 <0.050 <0.050 0.050 6760702

High Molecular Weight PAH’s mg/kg <0.050 2.4 <0.050 <0.050 0.050 6760702

Total PAH mg/kg <0.050 3.0 <0.050 <0.050 0.050 6760702


D10-ANTHRACENE (sur.) % 103 95 94 88 — 6770725

D8-ACENAPHTHYLENE (sur.) % 93 92 89 75 — 6770725


TERPHENYL-D14 (sur.) % 110 103 103 94 — 6770725


Page 11 of 24

Tbrough Scenco’

GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)a

Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungMoisture BALJBAL 6763037 N/A 201 /04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770714 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6760702 N/A 201 3/04/29 Automated StatchkpH (2:1 Dl Water Extract) PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763037 N/A 201 3/04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770714 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW. HMW, Total PAH CaIc GC/MSD 6760702 N/A 2013/04/29 Automated Statchk



Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungMoisture BAL/BAL 6763037 N/A 201 3/04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770714 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH Caic GC/MSD 6760702 N/A 2013/04/29 Automated StatchkpH (2:1 Dl Water Extract) PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763037 N/A 2013/04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770725 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW. HMW, Total PAH Calc GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763037 N/A 201 3/04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770725 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk

Page 12 of 24

r,i m



Matrix Sediment

Test Summary

Collected 2013/04/22Relinquished 2013104/22

Received 2013/04/22

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Maxxam ID GF2415 DupSample ID lPSSD13-08-O5

Matrix Sediment

SLcc*s Thrnuh Scrc



Received 2013/04/22

Test Summary

Extracted2013/04/24

Test Description Instrumentation Batch Analyzed AnalystPAH in Soil by GO/MS (SIM) GC/MSD 6770725 2013/04/27 Vidya Borshettar



Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungMoisture BAL/BAL 6763014 N/A 201 3/04/25 Lolita ObusanPAH in Soil by GO/MS (SIM) GC/MSD 6770725 201 3/04/24 2013/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH Caic GC/MSD 6760702 N/A 2013/04/29 Automated StatchkpH (2:1 Dl Water Extract) PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763014 N/A 201 3/04/25 Lolita ObusanPAH in Soil by GO/MS (SIM) GC/MSD 6770725 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH Caic GC/MSD 6760702 N/A 201 3/04/29 Automated Statchk


IMatrix Sediment

4 Test Description:IElements by ICPMS (total)


Received 2013/04/22

Moisture

PAH

ir Soil by GO/MS (SIM)Total LMW, HMW, Total PAH CabpH (2:1 Dl Water Extract)

Instrumentation Batch Extracted Analyzed AnalystICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungBALIBAL 6763014 N/A 2013/04/25 Lolita ObusanGC/MSD 6770725 2013/04/24 2013/04/27 Vidya BorshettarGC/MSD 6760702 N/A 201 3/04/29 Automated StatchkPH/PH 6766558 201 3/04/25 2013/04/25 Nadzida Stanic

Maxxam ID GF2418 Dup Collected 2013/04/22Sample ID IPS-SD13-09-03 Relinquished 2013/04/22


Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763014 N/A 2013/04/25 Lolita Obusan

Page 13 of 24

I’vl m


Succ Through Sciencer


Site#: TP00131Site Location: 2225 0CC ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

Test Summary


Matrix Sediment


Received 2013/04/22

U

Test Description instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 2013/04/25 David JungMoisture BAL/BAL 6763014 N/A 2013/04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770725 201 3/04/24 201 3/04/27 Vidya Borshettar

Total LMW, HMW, Total PAH CaIc GC/MSD 6760702 N/A 2013/04/29 Automated StatchkpH (2:1 Dl Water Extract) PH/Pt-I 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic



Test Description Instrumentation Batch Extracted Analyzed AnalystMoisture BAL/BAL 6763037 N/A 201 3/04/25 Lolita ObusanPAt-i in Soil by GC/MS (SIM) GC/MSD 6770725 201 3/04/24 201 3/04/27 Vidya Borshettar

Total LMW. HMW, Total PAH Caic GC/MSD 6760702 N/A 2013/04/29 Automated Statchk

Maxxam ID GF2429 Collected 2013/04/22Sample ID IPS-SD1 3-1 0-03 Relinquished 201 3/04/22


Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 2013/04/25 David JungMoisture BAL/BAL 6763037 N/A 2013/04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770725 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6760702 N/A 201 3/04/29 Automated StatchkpH (2:1 Dl Water Extract) PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic

Maxxam ID GF2429 Dup Collected 2013/04/22Sample ID IPS-SD13-10-03 Relinquished 2013/04/22


Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungMoisture BAL/BAL 6763037 N/A 2013/04/25 Lolita ObusanpH (2:1 Dl Water Extract) PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic



Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungMoisture BAL/BAL 6763014 N/A 2013/04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770725 201 3/04/24 201 3/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH CaIc GC/MSD 6760702 N/A 201 3/04/29 Automated StatchkpH (2 1 Dl Water Extract) PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic

13

Jz

Page 14 of 24

m


iJ\Test Description

( [AH in SoH by GC/MS (SIM)1 ITàtal LMW, HMW. Total PAl-I Caic

5ucce Thr,uh Scic’

GOLDER ASSOCIATESTask Order#: 4410104800, Line Item: 10Site#: TP.00131Site Location: 2225 IOCO ROAD.PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

(4


Matrix Sediment

Test Summary


Received 2013/04/22

Instrumentation Batch Extracted Analyzed AnalystBAL/BAL 6763014 N/A 201 3/04/25 Lolita ObusanGC/MSD 6770725 201 3/04/24 201 3/04/27 Vidya BorshettarGC/MSD 6760702 N/A 201 3/04/29 Automated Statchk



Test Description Instrumentation Batch Extracted Analyzed AnalystElements by ICPMS (total) ICPM/MS 6766555 201 3/04/25 201 3/04/25 David JungMoisture BAL/BAL 6763037 N/A 2013/04/25 Lolita ObusanPAH in Soil by GC/MS (SIM) GC/MSD 6770725 201 3/04/24 2013/04/27 Vidya BorshettarTotal LMW, HMW, Total PAH Caic GC/MSD 6760702 N/A 2013/04/29 Automated StatchkpH (2:1 Dl Water Extract) PH/PH 6766558 201 3/04/25 201 3/04/25 Nadzida Stanic

HiL

Page 15of24

r%/I 21 21 I—Ti e’ rh’,ug sct


Report Date: 2013/04/29 Site#: TP.00131Site Location: 2225 000 ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

11

Package I 5.7CCEach temperature s the average of up to three cooler temperatures taken at receipt

General Comments

UResults relate only to the items tested.

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GOLDER ASSOCIATESTask Order#: 4410104800Site#: TP.00131Site Location: 2225 10CC ROAD PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

Maoam Analytics International Corporation 0/a Maxxam Analytics Burnaby: 4606 Canada Way V5G 1 K5 Telephone(604) 734-7276 Fax(604) 731-2386

Quality Assurance Report -

Maxxam Job Number: B331494

QAIQC DateBatch AnalyzedNum nit QC Type Parameter yyyy/mm/dd Value Recovery UNITS QC Limits

6763014 LOl Method Blank Moisture 2013/04/25 <0.30 %6763037 LOl Method Blank Moisture 201 3/04/25 <0.30 %6766555 DJ Method Blank Total Aluminum (Al) 201 3/04/25 <100 mg/kg

Total Antimony (Sb) 201 3/04/25 <0.10 mg/kgTotal Arsenic (As) 201 3/04/25 <0.50 mg/kgTotal Barium (Ba) 201 3/04/25 <0.10 mg/kgTotal Beryllium (Be) 201 3/04/25 <0.40 mg/kgTotal Bismuth (Bi) 201 3/04/25 <0.10 mg/kgTotal Cadmium (Cd) 201 3/04/25 <0.050 mg/kgTotal Calcium (Ca) 201 3/04/25 <100 mg/kgTotal Chromium (Cr) 2013/04/25 <1.0 mg/kgTotal Cobalt (Co) 201 3/04/25 <0.30 mg/kgTotal Copper (Cu) 2013/04/25 <0.50 mg/kgTotal Iron (Fe) 201 3/04/25 <100 mg/kgTotal Lead (Pb) 201 3/04/25 <0.10 mg/kgTotal Magnesium (Mg) 2013/04/25 <100 mg/kgTotal Manganese (Mn) 201 3/04/25 <0.20 mg/kg

Total Mercury (Hg) 201 3/04/25 <0.050 mg/kg

Total

Molybdenum (Mo) 201 3/04/25 <0.10 mg/kgTotal Nickel (Ni) 201 3/04/25 <080 mg/kg

. ...:.* :. Total Phosphorus (P) 201 3/04/25 <10 mg/kgTotal Potassium (K) 201 3/04/25 <100 mg/kgTotal Selenium (Se) 201 3/04/25 <0.50 mg/kgTotal Silver (Ag) 201 3/04/25 <0.050 mg/kgTotal Sodium (Na) 201 3/04/25 <100 mg/kgTotal Strontium (Sr) 2013/04/25 <0.10 mg/kgTotal Thallium (TI) 201 3/04/25 <0.050 mg/kgTotal Tin (Sn) 2013/04/25 <0.10 mg/kgTotal Titanium (Ti) 2013/04/25 1.4, RDL=1 .0 mg/kgTotal Vanadium (V) 201 3/04/25 <2.0 mg/kgTotal Zinc (Zn) 2013/04/25 <1.0 mg/kgTotal Zirconium (Zr) 2013/04/25 <0.50 mg/kg

6770714 VB1 Method Blank D10-ANTHRACENE (sur.) 201 3/04/26 99 % 60- 130D8-ACENAPHTHYLENE (sur.) 201 3/04/26 100 % 50- 130D8-NAPHTHALENE (sur.) 201 3/04/26 101 % 50- 130TERPHENYL-D14 (sur.) 2013/04/26 108 % 60- 130Naphthalene 2013/04/26 <0.050 mg/kg2-Methylnaphthalene 201 3/04/26 <0.050 mg/kgAcenaphthylene 201 3/04/26 <0.050 mg/kgAcenaphthene 201 3/04/26 <0.050 mg/kgFluorene 201 3/04/26 <0.050 mg/kgPhenanthrene 201 3/04/26 <0.050 mg/kgAnthracene 201 3/04/26 <0.050 mg/kgFluoranthene 2013/04/26 <0.050 mg/kgPyrene 201 3/04/26 <0.050 mg/kgBenzo(a)anthracene 201 3/04/26 <0.050 mg/kgChrysene 201 3/04/26 <0.050 mg/kgBenzo(b&j)fluoranthene 201 3/04/26 <0.050 mg/kgBenzo(k)fluoranthene 201 3/04/26 <0.050 mg/kgBenzo(a)pyrene 201 3/04/26 <0,050 mg/kglndeno(1 ,2,3-cd)pyrene 2013/04/26 <0.050 mg/kgDibenz(a,h)anthracene 2013/04/26 <0.050 mg/kgBenzo(g,h,i)perylene 2013/04/26 <0.050 mg/kg

6770725 VB1 Method Blank D10-ANTHRACENE (sur.) 201 3/04/27 98 % 60- 130D8-ACENAPHTHYLENE (sur.) 2013/04/27 98 % 50- 130

Page 17of24

I\JI 21 21 Il9 Through cehce

GOLDER ASSOCIATESTask Order#: 4410104800Site#: TP.00131Site Location: 2225 IOCO ROADPORT MOODY BCProject #: 13-1520-0502-6075 (1327)

Quality Assurance Report (Confinued)Maxxam Job Number: B331494

QNQC DateBatch AnalyzedNum nit QC Type Parameter yyyy/mmfdd Value Recovery UNITS QC Limits

6770725 VB1 Method Blank D8-NAPHTHALENE (sur.) 2013/04/27 98 % 50- 130 fTERPHENYL-D14 (sur.) 201 3/04/27 107 % 60- 130Naphthalene 201 3/04/27 <0.050 mg/kg2-Methylnaphthalene 201 3/04/27 . <0.050 mg/kgAcenaphthylene 201 3/04/27 <0.050 mg/kgAcenaphthene 201 3/04/27 <0.050 mg/kgFluorene 2013/04/27 <0.050 mg/kgPhenanthrene 2013/04/27 <0.050 mg/kgAnthracene 201 3/04/27 <0050 mg/kgFluoranthene 2013/04/27 <0.050 mg/kgPyrene 2013/04/27 <0.050 mg/kgBenzo(a)anthracene 2013/04/27 <0.050 mg/kgChrysene 201 3/04/27 <0.050 mg/kgBenzo(b&j)fluoranthene 2013/04/27 <0.050 mg/kgBenzo(k)fluoranthene 2013/04/27 <0.050 mg/kgBenzo(a)pyrene 2013/04/27 <0.050 mg/kglndeno(1 2,3-cd)pyrene 2013/04/27 <0.050 mg/kgDibenz(a,h)anthracene 2013/04/27 <0.050 mg/kgBenzo(g,h.i)perylene 201 3/04/27 <0.050 mg/kg

RPD [GF2415-01J Naphthalene 201 3/04/27 NC % 50 t-

2-Methylnaphthalene 201 3/04/27 NC % 50Acenaphthylene 201 3/04/27 NC % 50Acenaphthene 2013/04/27 NC % 50Fluorene 201 3/04/27 NC % 50Phenanthrene 2013/04/27 NC % 50Anthracene 2013/04/27 NC 50Fluoranthene 201 3/04/27 NC % 50Pyrene 201 3/04/27 NC % 50Benzo(a)anthracene 201 3/04/27 NC % 50Chrysene 201 3/04/27 NC % 50Benzo(b&j)fluoranthene 201 3/04/27 NC % 50Benzo(k)fluoranthene 201 3/04/27 NC % 50Benzo(a)pyrene 201 3/04/27 NC % 50lndeno(1 ,2,3-cd)pyrene 2013/04/27 NC % 50Dibenz(a,h)anthracene 2013/04/27 NC % 50Benzo(g,h,i)perylene 2013/04/27 NC % 50

6763014 LOl RPD [GF2418-01] Moisture 201 3/04/25 0.4 % 206763037 LOl RPD [GF2429-01] Moisture 2013/04/25 5.8 % 206766555 DJ RPD [GF2429-02] Total Aluminum (Al> 201 3/04/25 2.8 % 35

Total Antimony (Sb) 201 3/04/25 NC % 30 iiTotal Arsenic (As) 2013/04/25 5.1 % 30Total Barium (Ba) 201 3/04/25 5.5 35Total Beryllium (Be) 201 3/04/25 NC % 30Total Bismuth (Bi) 201 3/04/25 NC % 30Total Cadmium (Cd) 201 3/04/25 8.3 % 30Total Calcium (Ca) 2013/04/25 11.6 % 30Total Chromium (Cr) 2013/04/25 5.2 % 30Total Cobalt(Co) 201 3/04/25 2.1 30Total Copper (Cu) 201 3/04/25 7.4 % 30Total Iron (Fe) 2013/04/25 1,8 % 30Total Lead (Pb) 2013/04/25 6.0 % 35Total Magnesium (Mg) 201 3/04/25 0.2 % 30Total Manganese (Mn) 2013/04/25 1.9 % 30Total Mercury (Hg) 201 3/04/25 NC % 35Total Molybdenum (Mo) 2013/04/25 2.2 % 35

Maxxam Ana’ytics Intemationa Corporation 0/a Maxxarn MaIytcs Burnaby: 4606 Canada Way V50 1K5 Telephorre(604) 734-7276 Fax(604) 731-2386

Page 18 of 24

6766558 NS6 RPD [GF2429-02]6766555 DJ Matrix Spike

[GF2429-02J

Dl 0-ANTHRACENE (sur.)D8-ACENAPHTHYLENE (sur.)D8-NAPHTHALENE (sur.)TERPHENYL-D14 (sur.)Naphthalene2-MethylnaphthaleneAcenaphthyleneAcenaphtheneFluorenePhenanthreneAnthra caneFluoranthenePyreneBenzo(a)anthraceneChryseneBenzo(b&j)fluorantheneBenzo(k)fiuorantheneBenzo(a )pyrene

2013/04/272013/04/272013/04/272013/04/272013/04/272013/04/272013/04/272013/04/272013/04/27201 3/04/27201 3/04/272013/04/27201 3/04/27201 3/04/27201 3/04/27201 3/04/272013/04/27201 3/04/27

81 % 60-13071 % 50-13082 % 50-13090 % 60-13083 % 50-13085 % 50-13084 % 50-13086 % 50-13087 % 50-13084 % 60-13088 % 60-13095 % 60-13093 % 60-13085 % 60-13083 % 60-13094 % 60-13087 % 60-13089 % 60-130

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GOLDER ASSOCIATESTask Order#: 4410104800Site#: TP.00131Site Location: 222510CC ROAD.PORT MOODY BCProject #: 13-1520-0502-6075 (1327)

CC Type

Quality Assurance Report (Continued)Maxxam Job Number: 8331494

DJ RPD [GF2429-02]

DateAnalyzed

Parameter yyyy/mm/dd Value Recovery UNITS QC LimitsTotal Nickel (Ni) 201 3/04/25 0.3 % 30Total Phosphorus (P) 201 3/04/25 4.2 % 30Total Potassium (K) 2013/04)25 1.5 % 35Total Selenium (Se) 201 3/04)25 NC % 30Total Silver (Ag) 2013/04/25 NC % 35Total Sodium (Na) 2013/04/25 4.3 % 35Total Strontium (Sr) 2013/04/25 8.4 % 35Total Thallium (TI) 201 3/04/25 0.01 % 30Total Tin (Sn) 201 3/04/25 NC % 35Total Titanium (Ti) 201 3/04/25 3.9 % 35Total Vanadium (V) 201 3/04/25 2.8 % 30Total Zinc (Zn) 2013/04/25 0.3 % 30Total Zirconium (Zr) 201 3/04/25 NC % 30Soluble (2:1) pH 2013/04/25 0 % 20

Total Antimony (Sb) 201 3/04/25 105 % 75- 125Total Arsenic (As) 2013/04/25 96 % 75- 125Total Barium (Ba) 201 3/04/25 98 % 75- 125Total Beryllium (Be) 201 3/04/25 95 % 75- 125Total Cadmium (Cd) 201 3/04/25 100 % 75- 125Total Chromium (Cr) 2013/04/25 100 % 75- 125Total Cobalt (00) 2013/04/25 103 % 75- 125Total Copper (Cu) 2013/04/25 101 % 75- 125Total Lead (Pb) 2013/04/25 111 % 75-125Total Manganese (Mn) 2013/04/25 NC % 75- 125Total Mercury (Hg) 201 3/04/25 106 % 75- 125Total Molybdenum (Mo) 2013/04/25 111 % 75- 125Total Nickel (Ni) 2013/04/25 101 % 75- 125Total Selenium (Se) 2013/04/25 93 % 75- 125Total Silver (Ag) 2013/04/25 96 % 75- 125Total Strontium (Sr) 2013/04/25 NC % 75- 125Total Thallium (TI) 2013/04/25 103 % 75- 125Total Tin (Sn) 2013/04/25 107 % 75- 125Total Titanium (Ti) 201 3/04/25 NC % 75- 125Total Vanadium (V) 201 3)04/25 97 % 75- 125Total Zinc (Zn) 201 3)04/25 102 % 75- 125

6770725 VB1 Matrix Spike[GF241 5-Oh

Maxxam Analytics International Corporation 0/a Maxxam Analytics Surnaby: 4606 Canada Way V5G 1K5 Telephonel6o4) 734-7276 Fax(604) 731-2386

Page 19 of24

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GOLDER ASSOCIATESTask Order#: 4410104800Site#: TP.00131Site Location: 2225 IOCO ROAD,PORT MOODY BCProject #: 13-1520-0502-6075 (1327)$

QuaHty Assurance Report (Continued)Maxxam Job Number: B331 494

QNQC DateBatch AnalyzedNum nit QC Type Parameter yyyylmmidd Value Recovery UNITS QC Limits

6770725 VBI Matrix Spike ill[GF2415-01] lndeno(1.23-cd)pyrene 2013)04/27 93 % 60-130

Dibenz(a.h)anthracene 2013)04/27 91 % 60- 130Benzo(g,h,i)perylene 2013/04/27 86 % 60- 130

6766555 DJ LCS Total Antimony (Sb) 201 3/04/25 97 % 75- 125Total Arsenic (As) 2013/04/25 91 % 75- 125Total Barium (Ba) 201 3/04/25 98 % 75-125Total Beryllium (Be) 201 3/04/25 90 % 75- 125Total Cadmium (Cd) 201 3/04/25 94 % 75- 125Total Chromium (Cr) 2013/04/25 98 % 75- 125Total Cobalt (Co) 201 3/04)25 101 % 75- 125Total Copper (Cu) 201 3/04/25 101 % 75- 125Total Lead (Pb) 2013/04/25 101 % 75-125Total Manganese (Mn) 201 3/04/25 102 % 75- 125Total Mercury (Hg) 2013)04/25 99 % 75-125Total Molybdenum (Mo) 201 3/04/25 107 % 75- 125Total Nickel (Ni) 201 3/04/25 96 % 75- 125Total Selenium (Se) 2013/04/25 88 % 75- 125Total Silver (Ag) 2013/04/25 98 % 75- 125Total Strontium (Sr) 2013/04/25 103 % 75- 125Total Thallium (TI) 2013/04/25 101 % 75- 125Total Tin (Sn) 2013/04/25 103 % 75- 125Total Titanium (Ti) 2013/04/25 106 % 75- 125Total Vanadium (V) 2013/04/25 95 % 75- 125Total Zinc (Zn) 2013/04/25 92 % 75- 125

6766558 NS6 LCS Soluble (2:1) pH 201 3/04/25 102 % 96- 1046770714 VB1 LCS D10-ANTHRACENE (sur.) 201 3/04/27 97 % 60- 130

D8-ACENAPHTHYLENE (sur.) 2013/04/27 92 % 50- 130D8-NAPHTHALENE (sur.) 2013/04/27 92 % 50- 130TERPHENYL-D14 (sur.) 2013/04/27 103 % 60- 130Naphthalene 2013/04/27 87 % 50- 130 !

2-Methylnaphthalene 2013/04/27 91 % 50- 130Acenaphthylene 2013/04/27 89 % 50- 130Acenaphthene 2013/04/27 92 % 50-130Fluorene 2013/04/27 91 % 50-130Phenanthrene 2013/04/27 92 % 60- 130Anthracene 2013/04/27 97 % 60- 130Fluoranthene 2013/04/27 104 % 60- 130Pyrene 2013/04/27 101 % 60-130 ,_-.

Benzo(a)anthracene 2013/04/27 89 % 60- 130 /Chrysene 201 3/04/27 90 % 60- 130Benzo(b&j)fluoranthene 201 3/04/27 93 % 60- 130Benzo(k)fluoranthene 201 3/04/27 94 % 60- 130Benzo(a)pyrene 201 3/04/27 96 % 60- 130lndeno(1,2,3-cd)pyrene 2013/04/27 98 % 60-130Dibenz(ah)anthracene 2013/04/27 95 % 60- 130Benzo(g,h.i)perylene 2013/04/27 91 % 60- 130

6770725 VB1 LCS D10-ANTHRACENE (sur.) 201 3/04/27 96 % 60- 130D8-ACENAPHTHYLENE (sur.) 201 3/04/27 92 % 50- 130D8-NAPHTHALENE (sur.) 201 3/04/27 92 % 50- 130TERPHENYL-D14 (sur.) 201 3/04/27 105 % 60- 130Naphthalene 201 3/04/27 87 % 50- 1302-Methylnaphthalene 201 3/04)27 91 % 50- 130Acenaphthylene 2013/04/27 89 % 50- 130Acenaphthene 2013/04/27 93 % 50-130

Maoarn Ana’ytics nternalional Corporation oia Maxxam Maiytics Burnaby: 4606 Canaua Way V5G 1K5 Telephone(604) 734-7276 Fax(604) 731-2386

Page 200124

m

Quality Assurance Report (Continued)

Sxeo 7hrouh SCerce


Maxxam Job Number: B331 494

Maxxam Anaytios lnternabona Corporaon 0/a Maxxarn Analytics Burnaby: 4606 Canada Way V5G 1 K5 Teiephone(604) 734-7276 Fax(604) 731 -2386

Page 21 of 24


6770725 VB1 LCS Fluorene 201 3/04/27 92 % 50- 130Phenanthrene 2013/04/27 92 % 60-130Anthracene 2013/04/27 96 % 60- 130Fluoranthene 201 3/04/27 105 % 60-130Pyrene 201 3/04/27 102 % 60- 130Benzo(a)anthracene 2013/04/27 90 % 60- 130Chrysene 201 3/04/27 90 % 60- 130Benzo(b&j)fluoranthene 201 3/04/27 97 % 60- 130Benzo(k)fluoranthene 201 3/04/27 97 % 60- 130Benzo(a)pyrene 2013/04/27 98 % 60- 130lndeno(1,2,3-cd)pyrene 2013/04/27 96 % 60- 130Dibenz(a.h)anthracene 2013/04/27 94 % 60- 130Benzo(gh,i)perylene 2013/04/27 90 % 60- 130

6766555 DJ SRM Total Aluminum (Al) 2013/04/25 113 % 70- 130Total Antimony (Sb) 2013/04/25 104 % 70- 130Total Arsenic (As) 2013/04/25 96 % 70 - 130Total Barium (Ba) 2013/04/25 114 % 70- 130Total Cadmium (Cd) 201 3/04/25 105 % 70- 130Total Calcium (Ca) 201 3/04/25 105 % 70- 130Total Chromium (Cr) 201 3/04/25 106 % 70- 130Total Cobalt (Co) 2013/04/25 100 % 70- 130Total Copper (Cu) 2013/04/25 97 % 70- 130Total Iron (Fe) 2013/04/25 105 % 70- 130Total Lead (Pb) 201 3/04/25 108 % 70- 130Total Magnesium (Mg) 201 3/04/25 98 % 70- 130Total Manganese (Mn) 201 3/04/25 109 % 70- 130Total Mercury (Hg) 201 3/04/25 89 % 70- 130Total Molybdenum (Mo) 201 3/04/25 110 % 70- 130Total Nickel (Ni) 2013/04/25 99 % 70-130Total Phosphorus (P) 201 3/04/25 86 % 70 - 130Total Strontium (Sr) 2013/04/25 116 % 70- 130Total Thallium (TI) 2013/04/25 97 % 70- 130Total Titanium (Ti) 2013/04/25 112 % 70-130Total Vanadium (V) 201 3/04/25 105 % 70- 130Total Zinc (Zn) 201 3/04/25 88 % 70- 130

Duplicate: Paired analysis of a separate portion of the same sample. Used to evaluate the variance in the measurement.Matrix Spike: A sample to which a known amount of the analyte of interest has been added. Used to evaluate sample matrix interference.SRM: A sample of known concentration prepared by an external agency under stringent conditions. Used as an independent check of method accuracy.LCS: A blank matrix sample to which a known amount of the analyte, usually from a second source, has been added. Used to evaluate method accuracy.Method Blank: A blank matrix containing all reagents used in the analytical procedure. Used to identify laboratory contamination.Surrogate: A pure or isotopically labeled compound whose behavior mirrors the analytes of interest. Used to evaluate extraction efficiency.NC (Matrix Spike): The recovery in the matrix spike was not calculated. The relative difference between the concentration in the parent sample and thespiked amount was not sufficiently significant to permit a reliable recovery calculation.NC (RPD): The RPD was not calculated. The level of analyte detected in the parent sample and its duplicate was not sufficiently significant to permit areliable calculation.

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Maxxam Job #: B331494

CThe analytical data and all QC contained in this report were reviewed and validated by the following individual(s).

Andy Lu. ifa Validation Coordinator

C

__ __ __

UMaxxam has procedures in place to guard against improper use of the electronic signature and have the required signatories, as per section 5.10.2 of

ISOIEC 17025:2005(E), signing the reports. For Service Group specific validation please refer to the Validation Signature Page.

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Page 22 of24

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Consultant: Golder Associates Sampling Date: April 22, 2013

Location: 2225 loco Road, Port Moody, BC Laboratory: Maxxam Analytics Bumaby



Yes No NA CommentsInstrument Surrogate Recovery X All laboratory QC results are withinExtraction Surrogate Recovery X acceptance criteria.

Method Blank Concentration XMatrix Duplicate RPD X

Matrix Spike Recovery XLab Control Sample Recovery X


Yes No NA CommentsField Blank Concentration X INo field QC samples were collected.Trip Blank Concentration X

Field Duplicate RPD X

Has CoA been signed off (Yes/No)?: YesHas lab warranted all tests were in statistical control in CoA (Yes/No)?: YesHas lab warranted all tests were analyzed following SOP’s in CoA (Yes/No)?: YesWere all samples analyzed within hold times (Yes/No)?: YesAll volatiles samples methanol extracted (if required) within 48 hours (Yes/No)?: n/aIs Chain of Custody completed and signed (Yes/No)?: YesWere sample temperatures acceptable when they reached lab (Yes/No)?: Yes

Was a Data Quality Waiver (DQW) issued (Yes/No)?: No

Date Issued: n/a Date of Response: n/a

Is data considered to be reliable (Yes/No)?: YesIf answer is “No’, describe and provide rationale:

(}rrrnci.Data Reviewed by (Print): Amanda Newberry Data Reviewed by (Signature): ci

Date: May 7, 2013

Data Quality Review Checklist (Rev 13) For Use on Imperial Oil Projects Only

-

golder associates ltd. report

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