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REPORT Quality Assurance and Quality Control Plan · REPORT Quality Assurance and Quality Control Plan Tuktoyaktuk Exploration Logistics Base Camp Submitted to: Imperial Oil Environmental

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REPORT

Quality Assurance and Quality Control Plan Tuktoyaktuk Exploration Logistics Base Camp

Submitted to:

Imperial Oil Environmental & Property Solutions 505 Quarry Park Blvd S.E. Calgary, Alberta T2C 5N1

Submitted by:

Golder Associates Ltd. 16820 107 Avenue, Edmonton, Alberta, T5P 4C3, Canada

+1 780 483 3499

18105460

June 21, 2019

THIS REPORT CONTAINS PROVISIONS 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 any disclosure of same is

governed by the provisions of each of the applicable provincial and territorial freedom of information legislation, the Privacy Act (Canada)

1980-81-83, c.111, Sch II"1", and the Access to Information Act (Canada) 1980-81-82-83, c.111, Sch.I"1", as such legislation may be

amended from time to time.

June 21, 2019 18105460

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Distribution List

1 Electronic copy: Imperial Oil Ltd.

1 Electronic copy: Golder Associates Ltd.

1 Electronic copy: Environment and Natural Resources, Government of the Northwest Territories

1 Electronic copy: Inuvialuit Water Board

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Table of Contents

1.0 INTRODUCTION ............................................................................................................................................. 4

2.0 SURVEILLANCE NETWORK PROGRAM QUALITY ASSURANCE/ QUALITY CONTROL ....................... 4

2.1 Water Sampling Equipment ................................................................................................................. 4

2.2 Sampling Methods ............................................................................................................................... 5

2.2.1 Field Analysis Samples ................................................................................................................... 5

2.2.2 Laboratory Analysis Samples ......................................................................................................... 5

2.2.3 Field Data Recording ...................................................................................................................... 7

2.2.4 Field Sample Collection .................................................................................................................. 7

2.2.5 QA / QC Sample Collection ............................................................................................................ 9

2.2.6 Sample Handling ........................................................................................................................... 10

2.3 Sample Shipping and Tracking .......................................................................................................... 10

2.3.1 Packaging ..................................................................................................................................... 10

2.3.2 Chain of Custody Forms ............................................................................................................... 10

2.3.3 Tracking ........................................................................................................................................ 10

2.3.4 Hold Times .................................................................................................................................... 10

2.4 Laboratory Analysis ............................................................................................................................ 11

2.4.1 Laboratory Accreditation ............................................................................................................... 11

2.4.2 Laboratory Analysis Methods, Hold Times and Targeted Report Detection Limits ...................... 11

2.5 Notifications and Reporting ................................................................................................................ 12

3.0 REMEDIATION SAMPLING PROGRAM QUALITY ASSURANCE/ QUALITY CONTROL ........................ 13

3.1 Soil Sampling Equipment ................................................................................................................... 13

3.2 Sampling Methods ............................................................................................................................. 14

3.2.1 Field Observations ........................................................................................................................ 14

3.2.2 Field Samples Analysis ................................................................................................................. 14

3.2.3 Laboratory Analysis Samples ....................................................................................................... 14

3.2.4 Field Data Recording .................................................................................................................... 15

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3.2.5 Field Sample Collection ................................................................................................................ 15

3.2.6 QA / QC Sample Collection .......................................................................................................... 16

3.2.7 Sample Handling ........................................................................................................................... 16

3.2.8 Sample Hold Times ....................................................................................................................... 17

3.3 Laboratory Analysis ............................................................................................................................ 17

3.3.1 Laboratory Accreditation ............................................................................................................... 17

3.3.2 Laboratory Analysis Methods, Hold Times and Targeted Report Detection Limits ...................... 17

3.4 Notifications and Reporting ................................................................................................................ 22

4.0 ANALYTICAL REQUIREMENTS AND QA/QC ............................................................................................ 22

TABLES WITHIN TEXT

Table A: List of Sampling Equipment ................................................................................................................... 4

Table B: Surveillance Network Program Sample Bottles Summary ................................................................. 5

Table C: Surveillance Network Program Sample Bottle Summary ................................................................... 6

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1.0 INTRODUCTION Golder Associates Ltd. (Golder) was contracted by Imperial Oil Environmental & Property Solutions (Imperial) to develop a Quality Assurance and Quality Control (QA/QC) Plan for the former Tuktoyaktuk Exploration Logistics Base Camp (Tuk Base or the Site) Remedial Excavation program. The plan consolidates all the QA/QC methods for work being completed at Tuk Base for monitoring events as required by the Inuvialuit Water Board Water Licence N5L8-1841 and for remedial activities on site as detailed in the Remediation Action Plan (Advisian 2019).

Quality assurance/quality control procedures and requirements are an important aspect of any field or laboratory testing program. The objective of the QA/QC program is to standardize methods so that field sampling, data entry, data analysis, and report preparation produce technically sound and scientifically defensible results. This QA/QC plan specifies sampling and analysis requirements for surveillance network program (SNP) as well as for remedial activities proposed on site. This plan forms a part of the overall QA/QC plan for the project.

2.0 SURVEILLANCE NETWORK PROGRAM QUALITY ASSURANCE/ QUALITY CONTROL

2.1 Water Sampling Equipment A list of sampling equipment is included in Table A.

Table A: List of Sampling Equipment

Equipment

pH probe and calibration solutions Field notebook

Turbidity meter and calibration vials Sharpie markers

Camera Pens/Pencils

GPS Nitrile gloves

Sample bottles (laboratory supplied) Project documentation (Work Plans, safety plans, etc.)

Sample preservatives (laboratory supplied) Maps

Deionized water (laboratory supplied) SNP Plan document

Ice packs Chain of custody forms

Bottle labels (laboratory supplied) Field data sheets

Total Residual Chlorine Test Kit GeoPump, tubing and filters (for filtering CaCO3 samples)

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2.2 Sampling Methods Golder has developed technical procedures for groundwater and surface water sampling which are consistent with the methods prescribed in the current edition of Standard Methods for the Examination of Water and Wastewater (APHA 2017).

2.2.1 Field Analysis Samples Field analyses will be conducted for pH, turbidity, and total residual chlorine as described in Table B.

Table B: Surveillance Network Program Sample Bottles Summary

Analyte Test Method Notes

pH Handheld pH probe

Field pH for 1841-1 samples must be collected because laboratory hold time for pH is 15 minutes, which is not possible to meet

Turbidity

Field test kit

Turbidity is not required in the Water Licence; however, it will be collected to establish a correlation between turbidity and TSS for 1841-1 to 1841-6 samples. This will allow for real-time TSS monitoring at the Site.

TRC Field test kit Field TRC for 1841-1 samples must be measured because laboratory hold time for TRC is 15 minutes, which is not possible to meet

Notes: TRC = total residual chlorine; TSS = total suspended solids.

Although Total Suspended Solids (TSS) cannot be directly measured in the field, data will be collected to determine the correlation between turbidity and TSS. Establishing this correlation will allow field crews to calculate TSS immediately in the field based on field turbidity measurements, rather than waiting for laboratory results.

2.2.2 Laboratory Analysis Samples Sample bottles and preservatives for all analyses to be conducted at the laboratory will be provided by Taiga Environmental Laboratory (TEL) in Yellowknife, Northwest Territories and Bureau Veritas Canada Inc. (BVC), in Edmonton, Alberta, and are summarized in Table C.

Some samples require addition of a laboratory provided preservative.

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Table C: Surveillance Network Program Sample Bottle Summary

SNP Number Analysis Bottle Preservative Laboratory Notes

1841-1 TSS, pH, Total Phosphorus, Ammonia

750 mL HDPE bottle

None TEL No preservative required

1841-1 Oil and grease 1 x 1 L amber glass bottle

Hydrochloric acid

TEL Preservative to be added

1841-1 Biological Oxygen Demand

300 mL HDPE None TEL No preservative required

1841-1 Fecal Coliforms 500 mL sterile bottle

Sodium thiosulphate (pre-charged)

TEL Preservative pre-charged; do not add preservative

1841-1 Total Phenols 1 x 125mL HDPE bottle

Sulfuric Acid BVC Preservative pre-charged; do not add preservative

1841-1 Mercury 1 x 100 mL clear glass bottle

Hydrochloric acid

BVC Preservative pre-charged; do not add preservative

1841-1 Total Chromium, Total Iron, Total Zinc, Total Copper, Total Nickel, Total Cadmium

1 x 125mL HDPE bottle

Nitric Acid BVC Preservative pre-charged; do not add preservatives

1841-1, 1841-2, 1841-3, 1841-4

Total lead 1 x 125 mL HDPE bottle

Nitric acid (pre-charged)

BVC Preservative pre-charged; do not add preservative

1841-2, 1841-3, 1841-4, 1841-5, 1841-6

TSS 1 x 250 mL HDPE bottle

None BVC No preservative required

1841-2, 1841-3, 1841-4

Total petroleum hydrocarbons

2 x 100 mL amber bottle

Sodium bisulphate

BVC Preservative pre-charged; do not add preservative

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SNP Number Analysis Bottle Preservative Laboratory Notes

1841-1, 1841-2, 1841-3, 1841-4

Benzene, toluene, ethylbenzene, xylene

3 x 44 mL vials Sodium hydrogen sulphate

BVC Preservative pre-charged; do not add preservative

1841-2, 1841-3, 1841-4

Hardness 1 x 125mL HDPE bottle

Nitric Acid BVC Requires field filtration and preservation nitric acid

Note: TRC = total residual chlorine; TSS = total suspended solids; TPH = Total petroleum hydrocarbons, comprises BTEX (benzene, toluene,

ethylbenzene, and xylene) and F1 sampled from 40 mL glass vials, and F2, F3 and F4 hydrocarbon fractions sampled from 100 mL amber

glass vials.

2.2.3 Field Data Recording Field data will be recorded on the Field Data Sheet. All sections of the Field Data Sheet must be filled out, and sections that are not applicable must have a ‘strike-through’. Field data sheets must be reviewed by office or QA/QC staff and stored electronically in addition to the original hard copy.

2.2.4 Field Sample Collection Surface water sampling will be conducted at the SNP stations as indicated in the water licence. A new field data sheet will be used for each sample collected, and all sections of the form completed.

The following field tests will be conducted, as applicable:

1) Field pH: tested using a hand-held pH meter, calibrated daily;

2) Turbidity: field test kit, calibrated daily;

3) Total Residual Chlorine: Digital Colorimeter, calibrated daily; and

4) Partway through the day, a calibration check (“bump test”) will be conducted to detect calibration drifts throughout the day.

Following data recording on the field data sheet, a water sample will be collected using the following procedure:

1) Confirm station location;

5) Confirm bottle label contains all relevant information: sample control number, date, time, sampling personnel, analysis to be performed and project name;

6) Using new nitrile gloves, remove sample bottles from plastic bags;

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7) For surface samples insert new 1 L or 500 mL routine sample bottle into sampling device (dipper), collect sample water by extending sampling device into water at sample location (rinse and repeat three times), and then decant sample water into target bottles;

8) For treatment cell samples fill new 1 L or 500 mL routine sample bottle (rinse and repeat three times), and then decant sample water into target bottles;

9) Follow laboratory handling instructions regarding preservation of samples;

10) Replace sample bottle cap;

11) Place sample bottle into a cooler with ice packs;

12) Following each sample collection, discard the routine sample bottle used for collecting sample water; and

13) Enter sample details into the chain of custody (COC) form.

Specific sampling requirements for each SNP station are shown in Table D.

Table D: Specific Sampling Method Requirements for SNP Stations

Station Specific Method Requirements

1841-1 (Discharge from former sewage lagoon)

Collect sample using remote sampling device (dipper device). Measure turbidity, pH and TRC.

1841-2 (Discharge from soil treatment cell)

Collect sample from treatment cell valve. Measure turbidity.

1841-3 (Discharge from excavation area)

Collect sample from treatment cell valve. Measure turbidity.

1841-4 (Discharge from material processing area)

Collect sample from treatment cell valve. Measure turbidity.

1841-5 (Discharge to receiving water body at a distance of 50 m from the dock to be removed)

Use caution to avoid mobilizing sediment into sample location water. Stand downstream of the sample location. Sample the downstream location prior to the upstream location via remote sampling device (dipper device). Measure turbidity and pH.

1841-6 (Discharge to receiving waterbody at a distance of 50 m from the dock to be repaired)

Use caution to avoid mobilizing sediment into sample location water. Stand downstream of the sample location. Sample the downstream location prior to the upstream location via remote sampling device (dipper device). Measure turbidity and pH.

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2.2.5 QA / QC Sample Collection The following quality control samples will be collected:

1) Duplicate Water Samples:

a) Prepare and label two bottle sets with the location sample control number and appropriate duplicate sample control number;

b) Use stabilized water in sampling device to alternate filling sample bottles in the ‘sample’ and ‘duplicate’ bottle sets. Preserve samples if required; and

c) Store and transport the sample sets together under the same conditions.

d) Submission of blind field duplicate QC samples will be at a minimum rate of 10 percent of total samples.

2) Field Blank Water Samples:

e) Prepare and label two bottle sets with the location sample control number and appropriate blank sample control number;

f) For the location sample, collect sample water using the appropriate/specified method from the desired source, fill one set of sample bottles and preserve if required;

g) For the field blank sample, fill one set of required sample bottles directly at the sampling location using laboratory-supplied de-ionized water and preserve if required; and

h) Store and transport the blank samples together with the corresponding sample location under the same conditions.

3) Trip Blank Samples:

i) Check that the laboratory-prepared blank is sealed and full; keep the bottles sealed throughout the field program;

j) Transport the blank samples into the field with the other sample bottles;

k) Label the blank bottles with the appropriate sample control number; and

l) Store and transport the blank samples together with the corresponding sample location under the same conditions.

m) Trip and field blanks will be submitted for analysis, as necessary, to evaluate the potential for cross-contamination during the sampling and transportation of the samples

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2.2.6 Sample Handling All samples will be handled using nitrile gloves and packed into coolers containing ice packs immediately following sample collection. If shipping is occurring the same day, coolers can be prepared for shipping as described in Section 2.3. If shipping is occurring at a later date, store samples in a designated (non-food) fridge until just prior to shipping. If there is no non-food fridge available ice packs will be maintained and replaced as required in sample coolers until samples are shipped.

2.3 Sample Shipping and Tracking 2.3.1 Packaging Samples must be packed into coolers with ice packs to maintain samples as close to 4 degrees Celsius as possible, and packaging material (e.g. bubble wrap) to prevent breakage or leakage. All samples are to be packed upright and each sample stored in a separate sealed plastic bag in the event of leakage of ice in the coolers. Seal coolers closed using packing tape or straps, and securely affix a shipping label on the cooler top indicating the sender, receiver, and number of coolers. Also indicated on the shipping label which cooler contains the COC form (see section 2.3.2).

2.3.2 Chain of Custody Forms The COC form is a critical piece of documentation used to record the sample handling from the source water to the laboratory. Chain of custody documentation will be prepared legibly and accurately including any notes with respect to holding samples for future analysis signed by sampling personnel and shipped with the samples to the receiving laboratory. A current COC form will be provided by TEL and BVC laboratories.

Samples will be driven from Tuk Base to Inuvik Airport. The samples will be shipped to TEL and BVC laboratories via air. The samples will be picked up by Golder staff in Yellowknife (TEL laboratory) and Edmonton (BVL laboratory). A separate COC shall be attached to the cooler to describe the hand-off of the coolers from the field Site, project aircraft transport and ultimately to the analytical laboratories. A custody seal will be applied to the cooler by the shipping personnel on-Site. The custody seal will remain in place on the cooler until pickup by Golder staff at the airport warehouse in Yellowknife/Edmonton. A new custody seal will be applied to the cooler after Golder staff confirm that samples have not been damaged during shipment, and that a sufficient amount of ice is present in the cooler.

2.3.3 Tracking Sample tracking methods will be established as soon as the samples leave the Site. Samples will be handed from the Golder site supervisor to subcontractor for ground transport between Tuktoyaktak and Inuvik followed by air transportation via Canadian North. Golder employees in Yellowknife/Edmonton will pick up the coolers once they arrive and deliver them to the laboratory. Sample shipping will be monitored by Golder personnel in Yellowknife/Edmonton.

2.3.4 Hold Times The laboratory recommends that a set amount of time between sample collection and sample extraction at the laboratory, referred to as the ‘hold time’, is not exceeded or uncertainty in analytical results may be present. It is anticipated that hold times will be met, notwithstanding flight delays or other unavoidable circumstancesA summary of analyses, hold times and comments is shown in Table E.

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Table E: Water Sample Analysis Hold Times

Analysis Hold Time Notes

TSS 7 days Sampled in field and submitted to lab for analysis

BOD 48 hours Sampled in field and submitted to lab for analysis

Fecal Coliforms 24 hours Sampled in field and submitted to lab for analysis

Oil and Grease, Total Phosphorus, Ammonia

28 days Sampled in field and submitted to lab for analysis

TRC 15 minutes Analyzed in field

pH 15 minutes Analyzed in field; sample collected and submitted to lab for quality control comparison to field pH

Mercury 28 days Sampled in field and submitted to lab for analysis

Total metals 180 days Sampled in field and submitted to lab for analysis

BTEX and TPH 14 days Sampled in field and submitted to lab for analysis

Turbidity n/a Analyzed in field; correlation between TSS and turbidity used to calculate TSS

Total Phenols 28 days Sampled in field and submitted to lab for analysis

Hardness as CaCO3 28 days Sampled in field and submitted to lab for analysis TSS = total suspended solids; TRC = total residual chlorine; TPH = Total petroleum hydrocarbons comprising BTEX (benzene, toluene, ethylbenzene, and xylene) and F1, F2, F3 and F4 hydrocarbon fractions; n/a = not applicable.

2.4 Laboratory Analysis 2.4.1 Laboratory Accreditation Laboratory Accreditation from TEL and BVC are shown in Appendix A.

2.4.2 Laboratory Analysis Methods, Hold Times and Targeted Report Detection Limits A summary of the laboratory analysis methods and targeted report detection limits for analyses required in the SNP are included as Table F. These detection limits are listed as ‘targets’ because sample characteristics can affect detection limits used by the laboratory.

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Table F: Water Sample Analysis Reportable Detection Limits

Analysis Field / Laboratory Analysis Targeted Report Detection Limit

TSS Laboratory 1.0 mg/L

BOD Laboratory 2.0 mg/L

Fecal Coliforms Laboratory 1.0 MPN/100mL

Oil and Grease Laboratory 2.0 mg/L

TRC Field 0.01 mg/L

pH Field / Laboratory 0.1 units / 0.10 units

Mercury Laboratory 0.002 ug/L

Benzene Laboratory 0.0004 ug/L

Toluene Laboratory 0.0004 ug/L

Ethylbenzene Laboratory 0.0004 ug/L

Xylene Laboratory 0.0004 ug/L

TPH Laboratory 2.0 ug/L

Turbidity Field 0.1 NTU

Total Phenols Laboratory 0.0015 mg/L

Hardness as CaCO3 Laboratory 0.50 mg/L

Note: TSS = total suspended solids; TPH = Total petroleum hydrocarbons comprising BTEX (benzene, toluene, ethylbenzene, and xylene)

and F1, F2, F3 and F4 hydrocarbon fractions; TRC = total residual chlorine; BOD = biological oxygen demand.

2.5 Notifications and Reporting All SNP data will be reported in the Water Licence Annual Report, due to the IWB on March 31 on the year following a sampling year. Ongoing notification requirements are shown in Table G.

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Table G: Surveillance Network Program Notification Requirements

Notification Trigger

SNP Station Locations – Signage Posting 7 days prior to beginning remedial activities

Initiating decant from former sewage lagoon 5 days prior to discharge

SNP Station Water Quality Exceedances Immediately

3.0 REMEDIATION SAMPLING PROGRAM QUALITY ASSURANCE/ QUALITY CONTROL

The remediation sampling program for the project includes soil sampling of the surfaces of remedial excavations, sampling of soil stockpiles and sampling of surface soils as outlined in the Remediation Action Plan (Advisian 2019), and the Project Description.

3.1 Soil Sampling Equipment A list of soil sampling equipment is included in Table H.

Table H: List of Soil Sampling Equipment

Equipment

Camera Field notebook

GPS Sharpie markers

Sample jars (laboratory supplied) Pens/Pencils

Methabol vials (laboratory supplied) Nitrile gloves

Terra Core (laboratory supplied) Project documentation (Work Plans, safety plans, etc.)

Deionized water (laboratory supplied) and Liquinox Maps

Ice packs Field data sheets

Labels (laboratory supplied) Chain of custody forms

Organic vapour monitor (OVM) MiniRae 3000

Shovel/Sampling Tool (metal) Resealable plastic bags

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3.2 Sampling Methods Golder has developed technical procedures for soil sampling which are consistent with the industry standard protocol described in the United States Environment Protection Agency (US EPA), the American Society for Testing and Materials (ASTM) and other regulatory jurisdictions in Canada.

3.2.1 Field Observations Field physical observations will be completed by Golder field technician. Visual observations of soil condition will be recorded on the field data sheet following the Golder IOL Division Soil Classification System.

3.2.2 Field Samples Analysis Field screenings of soil vapour concentration will be completed at all sampling locations. Soil samples will be placed in a resealable plastic bag and organic vapour concentration will be measured using an OVM. An OVM will be calibrated at least daily. The peak headspace vapour concentration results will be recorded on the field data sheet.

3.2.3 Laboratory Analysis Samples Sample bottles and preservatives for all analyses to be conducted at the laboratory will be provided by Bureau Veritas Canada Inc. (BVC) and are summarized in Table I.

Table I: Soil Sampling Bottle Summary

Analysis Bottle Preservative Laboratory Notes

Petroleum Hydrocarbons (PHCs)

2 x 40 mL glass vials 1 x 125 mL glass jar

Methanol BVC Preservative pre-charged; do not add preservative

Petroleum Hydrocarbons and Volatile Organic Compounds (VOCs)

4 x 40 mL glass vials 1 x 125 mL glass jar

Methanol BVC Preservative pre-charged; do not add preservative

Polycyclic Aromatic Hydrocarbons (PAHs)

2 x 125 mL glass jar

None BVC No preservative required

Polyclhlorinated biphenyl (PCBs)

2 x 125 mL glass jar

None BVC No preservative required

Metals/Arsenic 1 x Resealable Plastic Bag

None BVC No preservative required

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Analysis Bottle Preservative Laboratory Notes

Barite 1 x Resealable Plastic Bag

None BVC No preservative required

Landfill Acceptance Criteria

1 x 250 mL glass jar

None BVC No preservative required

3.2.4 Field Data Recording Field data will be recorded on the Field Data Sheet. All sections of the Field Data Sheet must be filled out, and sections that are not applicable must have a ‘strike-through’. Field data sheets must be reviewed by office or QA/QC staff and stored electronically at the end of each day in addition to the original hard copy.

3.2.5 Field Sample Collection The Excavation Sampling Plan (Golder 2019) details confirmatory and background soil samples to be taken as per sampling grid density described in the Abandoned Military Site Remediation Protocol (INAC 2009). Soil samples will be collected as grab samples and will be sealed in laboratory supplied resealable plastic bag, 125 millilitre (mL) glass jars with Teflon-lined lids for analysis of metals and inorganics, respectively; Terracore sampling devices and 40 mL glass vials pre-charged with methanol for analysis of volatiles. The soil samples will be collected using industry standard protocols including decontamination of the sampling shovel with liquinox and water then rinsing with water before each use. Soil samples will be collected by hand using single-use disposable nitrile gloves and placed into new/clean glass sample jars provided by the laboratory. The sampling jars will be clearly labelled and submitted to the laboratory with a completed COC form. With the exception for Terra-Core sample with methanol preservative, there will be sufficient soil within the sample for the analyses and to eliminate headspace, as some parameters require more sample material than others. If soil samples are stored prior to being submitted to the laboratory, they will be stored upright in sealed plastic bags within ice-packed coolers or non-food fridges and submitted to the lab within the appropriate holding time.

Each sampling container will be labelled with the following information:

Sample name;

Sample depth;

Date;

Project number; and

Sampler’s name

The naming convention of samples is designed to follow the identified area of potential environmental concerns (APEC): two capital letters followed by area name. Soil samples will be named accordingly:

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Universal Transverse Mercator (UTM) coordinates will be taken for every sample using handheld Global Positioning System (GPS) units. Coordinates will be tied into previous locations using Real-Time Kinematic Global Positioning System (RTK-GPS) surveying. Coordinates will also be provided from a known geo-referenced stake (i.e., with a tape measure) at each excavation area in the event the GPS unit is not available.

3.2.6 QA / QC Sample Collection The following quality control samples will be collected:

Duplicate Soil Samples:

a. Prepare and label two jar/vial sets with the location sample control number and appropriate duplicate sample control number;

b. Grab discrete sample from the source, homogenized the grab sample, then collect sample for submission via terracore and filling sample jars in the ‘sample’ and ‘duplicate’ sampling sets; and

c. Store and transport the sample sets together under the same conditions.

d. Submission of blind field duplicate QC samples will be at a minimum rate of 10 percent of total samples.

3.2.7 Sample Handling All samples will be handled using nitrile gloves and packed into coolers containing ice packs immediately following sample collection. If shipping is occurring the same day, coolers can be prepared for shipping as described in Section 2.3. If shipping is occurring at a later date, samples will be stored in a designated (non-food) fridge until just prior to shipping. If there is no non-food fridge available ice packs will be maintained and replaced as required in sample coolers until samples are shipped.

‘EX’ stands for excavation will be consistent for every soil sample.

EX A – SW01-01

Each APEC is assigned with letter as per RAP (A – Z).

Numbers will be unique for each sample per remediation area and will begin at 01 for every remediation area.

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3.2.8 Sample Hold Times The laboratory recommends that a set amount of time between sample collection and sample extraction at the laboratory, referred to as the ‘hold time’, is not exceeded or uncertainty in analytical results may be present. It is anticipated that hold times will be met, notwithstanding flight delays or other unavoidable circumstances.

A summary of analyses, hold times and comments is shown in Table J.

Table J: Soil Sample Analysis Hold Times

Analysis Hold Time Notes

PHCs 14 days Sampled in field and submitted to lab for analysis

VOCs 14 days Sampled in field and submitted to lab for analysis

PAHs 14 days Sampled in field and submitted to lab for analysis

Metals 180 days Sampled in field and submitted to lab for analysis

Mercury 28 days Sampled in field and submitted to lab for analysis

Arsenic 180 days Sampled in field and submitted to lab for analysis

Barite 180 days Sampled in field and submitted to lab for analysis

Landfill Acceptance 7 days Sampled in field and submitted to lab for analysis

3.3 Laboratory Analysis 3.3.1 Laboratory Accreditation Laboratory Accreditation from BVC are shown in Appendix A.

3.3.2 Laboratory Analysis Methods, Hold Times and Targeted Report Detection Limits

A summary of the laboratory analysis methods and targeted report detection limits for analyses required in the SNP are included as Table K. These detection limits are listed as ‘targets’ because sample characteristics can affect detection limits used by the laboratory.

Table K: Soil Sample Analysis Reportable Detection Limits

Analysis Field / Laboratory Analysis Targeted Report Detection Limit

Unit

Benzene Laboratory 0.005 mg/kg

Ethylbenzene Laboratory 0.01 mg/kg

F1 (C6-C10) Laboratory 10 mg/kg

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Analysis Field / Laboratory Analysis Targeted Report Detection Limit

Unit

LH (C5-C10) Laboratory 10 mg/kg

m & p-Xylene Laboratory 0.04 mg/kg

o-Xylene Laboratory 0.02 mg/kg

Toluene Laboratory 0.05 mg/kg

1,1,1,2-tetrachloroethane Laboratory 0.05 mg/kg

1,1,1-trichloroethane Laboratory 0.02 mg/kg

1,1,2,2-tetrachloroethane Laboratory 0.05 mg/kg

1,1,2-trichloroethane Laboratory 0.02 mg/kg

1,1-dichloroethane Laboratory 0.02 mg/kg

1,1-dichloroethene Laboratory 0.02 mg/kg

1,2,3-trichlorobenzene Laboratory 0.04 mg/kg

1,2,4-trichlorobenzene Laboratory 0.04 mg/kg

1,2,4-trimethylbenzene Laboratory 0.5 mg/kg

1,2-dibromoethane Laboratory 0.002 mg/kg

1,2-dichlorobenzene Laboratory 0.02 mg/kg

1,2-dichloroethane Laboratory 0.002 mg/kg

1,2-dichloropropane Laboratory 0.02 mg/kg

1,3,5-trichlorobenzene Laboratory 0.04 mg/kg

1,3,5-trimethylbenzene Laboratory 0.5 mg/kg

1,3-dichlorobenzene Laboratory 0.02 mg/kg

1,4-dichlorobenzene Laboratory 0.02 mg/kg

Bromodichloromethane Laboratory 0.03 mg/kg

Bromoform Laboratory 0.05 mg/kg

Bromomethane Laboratory 0.02 mg/kg

Carbon tetrachloride Laboratory 0.0005 mg/kg

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Analysis Field / Laboratory Analysis Targeted Report Detection Limit

Unit

Chlorobenzene Laboratory 0.001 mg/kg

Chlorodibromomethane Laboratory 0.02 mg/kg

Chloroethane Laboratory 0.02 mg/kg

Chloroform Laboratory 0.01 mg/kg

Chloromethane Laboratory 0.03 mg/kg

cis-1,2-dichloroethene Laboratory 0.02 mg/kg

cis-1,3-dichloropropene Laboratory 0.02 mg/kg

Dichloromethane Laboratory 0.03 mg/kg

Methyl methacrylate Laboratory 0.04 mg/kg

Methyl-tert-butylether (MTBE)

Laboratory 0.03

mg/kg

Styrene Laboratory 0.02 mg/kg

Tetrachloroethene Laboratory 0.01 mg/kg

trans-1,2-dichloroethene Laboratory 0.02 mg/kg

trans-1,3-dichloropropene

Laboratory 0.02

mg/kg

Trichloroethene Laboratory 0.01 mg/kg

Trichlorofluoromethane Laboratory 0.02 mg/kg

Vinyl chloride Laboratory 0.0003 mg/kg

1-Methylnaphthalene Laboratory 0.005 mg/kg

2-Methylnaphthalene Laboratory 0.005 mg/kg

Acenaphthene Laboratory 0.005 mg/kg

Acenaphthylene Laboratory 0.005 mg/kg

Acridine Laboratory 0.01 mg/kg

Anthracene Laboratory 0.004 mg/kg

Benzo(a)anthracene Laboratory 0.005 mg/kg

June 21, 2019 18105460

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Analysis Field / Laboratory Analysis Targeted Report Detection Limit

Unit

Benzo(a)pyrene Laboratory 0.005 mg/kg

Benzo(b&j)fluoranthene Laboratory 0.005 mg/kg

Benzo(c)phenanthrene Laboratory 0.005 mg/kg

Benzo(g,h,i)perylene Laboratory 0.005 mg/kg

Benzo(k)fluoranthene Laboratory 0.005 mg/kg

Benzo[e]pyrene Laboratory 0.005 mg/kg

Chrysene Laboratory 0.005 mg/kg

Dibenz(a,h)anthracene Laboratory 0.005 mg/kg

Fluoranthene Laboratory 0.005 mg/kg

Fluorene Laboratory 0.005 mg/kg

Indeno(1,2,3-cd)pyrene Laboratory 0.005 mg/kg

Naphthalene Laboratory 0.005 mg/kg

Perylene Laboratory 0.005 mg/kg

Phenanthrene Laboratory 0.005 mg/kg

Pyrene Laboratory 0.005 mg/kg

Quinoline Laboratory 0.01 mg/kg

Aroclor 1016 Laboratory 0.01 mg/kg

Aroclor 1221 Laboratory 0.01 mg/kg

Aroclor 1232 Laboratory 0.01 mg/kg

Aroclor 1242 Laboratory 0.01 mg/kg

Aroclor 1248 Laboratory 0.01 mg/kg

Aroclor 1254 Laboratory 0.01 mg/kg

Aroclor 1260 Laboratory 0.01 mg/kg

Aroclor 1262 Laboratory 0.01 mg/kg

Aroclor 1268 Laboratory 0.01 mg/kg

June 21, 2019 18105460

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Analysis Field / Laboratory Analysis Targeted Report Detection Limit

Unit

Aluminum (Al) Laboratory 100 mg/kg

Antimony (Sb) Laboratory 0.5 mg/kg

Arsenic (As) Laboratory 1 mg/kg

Barium (Ba) Laboratory 1 mg/kg

Beryllium (Be) Laboratory 0.4 mg/kg

Boron (B) Laboratory 0.8 mg/kg

Cadmium (Cd) Laboratory 0.05 mg/kg

Chromium (Cr) Laboratory 1 mg/kg

Cobalt (Co) Laboratory 0.5 mg/kg

Copper (Cu) Laboratory 1 mg/kg

Iron (Fe) Laboratory 100 mg/kg

Lead (Pb) Laboratory 0.5 mg/kg

Magnesium (Mg) Laboratory 50 mg/kg

Manganese (Mn) Laboratory 1 mg/kg

Mercury (Hg) Laboratory 0.05 mg/kg

Molybdenum (Mo) Laboratory 0.4 mg/kg

Nickel (Ni) Laboratory 1 mg/kg

Selenium (Se) Laboratory 0.5 mg/kg

Silver (Ag) Laboratory 0.2 mg/kg

Thallium (Tl) Laboratory 0.1 mg/kg

Tin (Sn) Laboratory 1 mg/kg

Uranium (U) Laboratory 0.2 mg/kg

Vanadium (V) Laboratory 1 mg/kg

Zinc (Zn) Laboratory 10 mg/kg

June 21, 2019 18105460

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3.4 Notifications and Reporting Soil data will be included in the remedial excavation report after all field activities are completed.

4.0 ANALYTICAL REQUIREMENTS AND QA/QC In conjunction with the field investigations, a QA/QC program will be implemented to ensure the integrity of the analytical testing results, as follows:

1) Chain of Custody (COC) documentation will be prepared legibly and accurately. Samples will be shipped to TEL or BVS Laboratories. Soil and water samples will be analyzed, based on the historically identified contaminant of concerns identified in the Remedial Action Plan (Advisian 2019) for each excavation, and the SNP Plan, respectively.

2) Confirm that all parameters requested in quote and on COC form were collected and analyzed;

3) The laboratory QA/QC program will include adherence to laboratory sampling and analysis protocols (e.g., temperature, hold times, sample containers, preservatives, detection limits and approved methodology) and the analysis of laboratory method blanks, laboratory control sample (blank spike), laboratory sample duplicates, surrogate recovery and matrix spikes;

4) Once laboratory analytical results are received, a review of field and laboratory quality will be completed. This includes the review of laboratory QC performance to confirm results are within acceptance criteria, as well as evaluation of field duplicate and blank results to confirm they are within alert limits. Exceedances of the QC acceptance or alert criteria will be investigated with the laboratory and, if warranted, a corrective action report will be requested from the laboratory;

a. Ten percent of all samples will be collected in duplicate (i.e., one duplicate sample for every ten samples) during the excavation and SNP program. Two sample sets with the location sample control number and appropriate duplicate sample control number will be prepared and filled from sample material.

b. The laboratory will conduct internal duplicate analysis on samples to assess whether the accuracy and repeatability of the analysis program was within acceptable ranges. The relative percent difference (RPD) between the samples’ results will be used to assess the sample variability. The RPD is a measure of the variability between two outcomes from the same procedure or process and is calculated by the following formula:

RPD% =|S − D|

12 (S + D)

× 100

Where: RPD = relative percent difference

S = sample value

D = blind field duplicate or replicate value.

c. Analytical error increases near the Reportable Detection Limit (RDL), the RPD will only be calculated where the concentrations of both the original and blind field duplicate samples were greater than five times the RDL. The calculated RPDs will then be compared to parameter specific alert limits.

June 21, 2019 18105460

23

d. Exceedances of the QC acceptance or alert criteria will be investigated with the laboratory and, if warranted, a corrective action report will be requested from the laboratory. RPD values greater than the project objectives suggest variability has been introduced through sample collection, sampling handling, or sample analysis.

e. Check for parameters detected in blank samples above five times the detection limit.

June 21, 2019 18105460

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APPENDIX A

This certificate is the property of the Standards Council of Canada (SCC) and must be returned on request; reproduction is prohibited except on written approval of SCC. Ce certificat est la propriété du Conseil canadien des normes (CCN) et doit lui être remis sur demande; toute reproduction est interdite sans l’autorisation écrite du CCN.

Bureau Veritas Canada (2019) Inc.

Petroleum Technology Center

6744 - 50 Street NW, Edmonton, AB, T6B 3M9 and Edmonton Environmental,

9331 48 Street NW, Edmonton, AB, T6B 2R4, Canada having been assessed by the Standards Council of Canada (SCC) and found to conform with the requirements of ISO/IEC 17025:2017 and the conditions for accreditation established by SCC is hereby recognized as an

ayant fait l’objet d’une évaluation du Conseil canadien des normes (CCN), et ayant été trouvé conforme aux exigences énoncées dans ISO/IEC 17025:2017 et aux conditions d’accréditation établies par le CCN, est de ce fait reconnu comme étant un

ACCREDITED TESTING LABORATORY LABORATOIRE D’ESSAIS ACCRÉDITÉ

for the specific tests or types of tests listed in the scope of accreditation approved by SCC and found on the SCC website at www.scc.ca.

pour les essais ou types d’essais énumérés dans la portée d’accréditation approuvée par le CCN et figurant dans le site Web du CCN au www.ccn.ca.

Accredited laboratory number: / Numéro de laboratoire accrédité : 160

SCC file number: / Dossier du CCN no : 15229

Initial accreditation date: / Date de la première accréditation : 1995-03-06

………………………………………………………………………

Vice-President – Accreditation Services / Vice-président – Services d’accréditation Issued on: / Délivré le : 2019-06-07

The validity of this certificate, including the date of last re-accreditation and its expiry can be confirmed by the accompanying Scope of Accreditation document in the Directory of Accredited Laboratories on the SCC website at www.scc.ca.

This laboratory is accredited in accordance with the recognized International Standard ISO/IEC 17025:2017. The accreditation demonstrates technical competence for a defined scope and the operation of a laboratory quality management system (refer to joint ISO-ILAC-IAF communiqué dated April 2017).

Pour vérifier la validité du présent certificat, y compris la date de la dernière réaccréditation et la date d’expiration du certificat, consulter la portée d’accréditation qui se trouve dans le répertoire des laboratoires accrédités dans le site Web du CCN au www.ccn.ca.

Ce laboratoire est accrédité conformément à la Norme internationale reconnue ISO/IEC 17025:2017. Cette accréditation démontre la compétence technique d’un organisme pour une portée définie et l’exploitation d’un système de management de la qualité de laboratoire (cf. communiqué conjoint ISO-ILAC-IAF date de avril 2017).

SCOPE OF ACCREDITATION

Bureau Veritas Canada (2019) Inc., formerly known as Maxxam Analytics

Petroleum Technology Center

6744 - 50 Street NW

Edmonton, AB

T6B 3M9

Accredited Laboratory No. 160

(Conforms with requirements of ISO/IEC 17025:2017)

CONTACT: Maria de Chavez, Lalaine Mabanta

TEL: +1 780 378 8508 +1 780 577 7151

FAX: +1 780 378 8699

EMAIL: [email protected]

URL: http://www.bvlabs.com

CLIENTS SERVED: All interested parties

FIELDS OF

TESTING:

Biological, Chemical/Physical

PROGRAM

SPECIALTY AREA:

Environmental

INITIAL

ACCREDITATION

DATE:

1995-03-06

SCOPE ISSUED ON: 2019-06-03

ACCREDITATION

VALID TO:

2023-03-06

Note: Environmental testings except for Adsorbable Organic Halides, Total Sulfide by Titration,

and Air matrices are performed at:

Bureau Veritas

Edmonton Environmental

9331 48 Street NW

Edmonton, AB

T6B 2R4

ENVIRONMENTAL AND OCCUPATIONAL HEALTH AND SAFETY

Environmental

Air

PTC SOP - 00128 VOCs by Thermal Desorption Diffusive Tube [EPA 325B]

1, 3-Butadiene

Benzene

Ethylbenzene

m,p-Xylenes

o-Xylene

Toluene

PTC SOP - 00148 Monitoring NO2 in the Atmosphere by using All-Season Passive

Samplers [SM4500-NO2-B/AWMA 91st PAPER 98-TP44.03]

Nitrite

PTC SOP - 00149 Monitoring SO2 in the Atmosphere by using All-Season Passive

Samplers [H. Tang, B. Brassard, R. Brassard and E. Peake, "A

New Passive Sampling System for Monitoring SO2 in the

Atmosphere" Proceedings, Clean Air '96: Second North American

Conference and Exhibition, Nov. 19-22, 1996 Orlando USA]

Sulfite

PTC SOP - 00150 Monitoring H2S in the Atmosphere by using All-Season Passive

Samplers

[Hongmao Tang "A New All-Season Passive Sampling System for

Monitoring H2S in Air" The Scientific World, (2002)2, 155-168]

Hydrogen Sulfide

PTC SOP - 00156 Volatile Organic Compounds on Passive Samplers using GC/MS

[Modified from BP 36-126-NIOSH Method 1500, Issue 2 (Aug.

15,1994) and Aromatic-NIOSH Method 1501, Issue 2 (Aug 15,

1994)]

1,1,1-Trichloroethane

1,1,2-Trichloroethane

1,2,4-Trimethylbenzene

1,2-Dichlorobenzene

1,3,5-Trimethylbenzene

1,4-Dichlorobenzene

2-Hexanone

2-methyl-4-Pentanone (MIBK)

3-Ethyltoluene

Benzene

Chlorobenzene

Chloroform

Decane

d-Limonene

Dodecane

Ethylbenzene

Heptane

Isopropylbenzene

Methylcyclohexane

Naphthalene

Nonane

Octane

Styrene

Tetrachloroethylene

Toluene

Trichloroethylene

Undecane

Xylene, Total

PTC SOP - 00157 Monitoring NH3 in the Atm by using the Ogawa Passive Samplers

[ASTM D6919]

Ammonia

PTC SOP - 00197 Monitoring Ozone in the Atmosphere by using Maxxam All-

Season Passive Samplers [H. Tang and T. Lau "A New All-Season

Passive Sampling System for Monitoring Ozone in Air",

Environmental Monitoring and Assessment, 65 (1-2) 129-137,

2000.]

Ozone

Air Filter

PTC SOP - 00151 Mass Determination of Particulate Matter (PM 2.5 and 10)

Gravimetric [Modified from US EPA, Quality Assurance

Guidance Document, 2.12: Monitoring PM2.5 in Ambient Air

Using Designated Reference or Class I Equivalent Method, Nov.

1998.]

PM10

PM2.5

PTC SOP - 00180 Dustfall, Total and Fixed, Gravimetric [Modified from AMD,

Appendix 4-6]

Dustfall, Fixed

Dustfall, Total

Soil/Solid

AB SOP-00002 Moisture Content in Soil [modified from CCME Petroleum

Hydrocarbons In Soil - Tier 1 Method, Gravimetric]

% Moisture

AB SOP-00003 Analysis of PAH in Water, Soil, Oil and Leachates by GC/MS

[Modified from EPA 8270, GC/MS]

Also includes Water (Organic)

1-Methylnaphthalene

2-Methylnaphthalene

Acenaphthene

Acenaphthylene

Acridine

Anthracene

Benzo (a) anthracene

Benzo (a) pyrene

Benzo (b, j) fluoranthene

Benzo (g,h,i) perylene

Benzo (k) fluoranthene

Benzo(c)phenanthrene

Benzo(e)pyrene

Chrysene

Dibenzo (a,e) pyrene

Dibenzo (a,h) anthracene

Dibenzo(a,h)pyrene

Dibenzo(a,i)pyrene

Dibenzo(a,l)pyrene

Fluoranthene

Fluorene

Indeno (1,2,3 - cd) pyrene

Naphthalene

Perylene

Phenanthrene

Pyrene

Quinoline

AB SOP-00004 Determination of Electrical Conductivity by Manual Meter

[Modified From SM 2510 B, Conductivity Meter (Manual)] . Also

includes Water - Inorganic

Conductivity (25°C)

AB SOP-00005 Alkalinity Conductivity Fluoride and pH by PC-Titrate

[Modified From SM 2320 B, Titrimetric/PC Titrate, Modified

from SM 4500-F C, Ion Selective Electrode/PC Titrate, Modified

From SM 2510 B, Conductivity Meter/PC Titrate and Modified

From SM 4500-H+ B, pH Meter/PC Titrate] Also includes Water-

Inorganic

Alkalinity

Conductivity (25ºC)

Fluoride

pH

AB SOP-00006 pH by Manual Meter

[Modified From SM 4500-H+ B, pH Meter] Also includes Water -

Inorganic

pH

AB SOP-00007 Ammonia-Nitrogen by Konelab - phenate colorimetric method

[Modified From SM 4500-NH3 A,G] Also includes Water -

Inorganic

Ammonia

AB SOP-00008 TKN by Konelab

[Modified From EPA 351.1 Colorimetric] Also includes Water -

Inorganic

Dissolved Kjeldahl Nitrogen

Total Kjeldahl Nitrogen

AB SOP-00012 Total Organic Carbon and Organic Matter in Soil [Modified From

Methods Manual For Forest and Plant Analyses, Pages 27-30,

Reflux - Titrimetric]

Organic Matter

Total Organic Carbon

AB SOP-00019 Calcium Carbonate Equivalence by pH [Modified From SSMA

20.2, pH Meter]

Calcium Carbonate Equivalence (CCE)

AB SOP-00020 Chloride by Konelab - Automated Ferric Thiocyanate Method

[Modified From SM 4500-Cl E, Colorimetric] Also includes

Water - Inorganic

Chloride

AB SOP-00022 Particle Size Distribution by Sieve Analysis [Modified from

ASTM D6913, Gravimetric]

% grain size > 75 um

% grain size < 75 um

Particle Size by sieve (Dry)

Particle size by sieve (Special)

AB SOP-00023 Nitrite and Nitrate by Ion Chromatography [Modified from SM

4110B, Ion Chromatography]

Also includes Water - Inorganic

Nitrate

Nitrite

AB SOP-00025 Ortho-phosphate (Dissolved) by Konelab - Ascorbic Acid

Reduction Method [Modified from SM 4500-P A, F Colorimetric]

Also includes Water - Inorganic

Ortho-phosphate

AB SOP-00026 Chloride, Sulphate and Bromide by Ion Chromatography

[Modified from SM 4110B, Ion Chromatography] Also includes

Water- Inorganic

Bromide

Chloride

Sulfate

AB SOP-00030 PSA by Hydrometer - Texture (Sand, Silt, Clay and Gravel)

Analysis [Modified from SSMA 55.3, Hydrometer]

% clay

% gravel

% sand

% silt

AB SOP-00033 Preparation of Saturation and Water-Soil Ratio Samples [Modified

from SSMA Method 15.2, Gravimetric]

% Saturation

AB SOP-00039 Extraction and Analysis of BTEX/F1 by HS/GC/MS/FID Water,

Soil and Oil [BTEX: Modified from EPA 8260 and EPA 5021,

GC/MS – Headspace and F1: Modified from CCME Petroleum

Hydrocarbons In Soil - Tier 1 Method, GC/FID - Headspace]

[Also includes Water - Organic, BTEX: Modified from EPA 8260

and EPA 5021, GC/MS - Headspace and F1: Modified from

CCME Petroleum Hydrocarbons - Tier 1 Method and EPA 5021,

GC/FID - Headspace. [Also includes Leachates - EPA SW-846

1311 and In-House Modified Method, GC/MS - Headspace]

1,2,4-Trimethyl Benzene

Benzene

Ethylbenzene

F1: C6-C10

Hexane

m/p-xylene

Methyl tert-butyl ether (MTBE)

o-xylene

Styrene

Toluene

AB SOP-00040 Analysis of Extractable Hydrocarbons in Water and Soils by

GCFID [Modified from CCME Petroleum Hydrocarbons In Soil -

Tier 1 Method, GC/FID, Gravimetric [Also includes Water –

Organic, Modified from CCME Petroleum Hydrocarbons In Soil -

Tier 1 Method, GC/FID, and Modified from Static Sheen Test

(EPA Method 1617), Visual

F2: C10-C16

F3: C16-C34

F4: C34-C50

F4: Gravimetric

Sheen

Total Extractable Hydrocarbons (TEH) (C11-C30)

AB SOP-00042 Metals on Liquids and Solids by ICPOES

[Modified from EPA SW-846 6010, ICP/OES]

Also includes Water - Inorganic

Aluminum

Barium

Boron

Calcium

Chromium

Iron

Lithium

Magnesium

Manganese

Phosphorus

Potassium

Silicon

Sodium

Strontium

Sulfur

AB SOP-00043 Metals Analysis on Soils and Waters Using ICPMS

[Modified from EPA SW-846 6020, ICP/MS] Also includes

Water - Inorganic and Paint. Also includes Leachates - EPA SW-

846 1311 and In-House Modified Method.

Aluminum

Antimony

Arsenic

Barium

Beryllium

Boron

Cadmium

Chromium

Cobalt

Copper

Iron

Lead

Magnesium

Manganese

Mercury

Molybdenum

Nickel

Selenium

Silver

Thallium

Tin

Titanium

Uranium

Vanadium

Zinc

Zirconium

AB SOP-00049 Particle Size Distribution by Hydrometer [Modified from ASTM

D7928, Hydrometer]

Particle Size Distribution

AB SOP-00050 Dry Bulk Density and Wet Bulk Density [Modified from MSSMA

Section 2.21, Gravimetric]

Dry Bulk Density

AB SOP-00056 Preparation and Analysis VOC/F1 Water and Soil by

HS/GC/MS/FID [Modified from EPA SW-846 8260 and EPA

SW-846 5021, GC/MS - Headspace] Also includes Water -

Organic

1,1,1,2-Tetrachloroethane

1,1,1-Trichloroethane

1,1,2,2-Tetrachloroethane

1,1,2-Trichloroethane

1,1-Dichloroethane

1,1-dichloroethylene

1,2,3-Trichlorobenzene

1,2,4-Trichlorobenzene

1,2,4-Trimethylbenzene

1,2-dichlorobenzene

1,2-dichloroethane

1,2-Dichloropropane

1,3,5 Trichlorobenzene

1,3,5-Trimethylbenzene

1,3-Dichlorobenzene

1,4-dichlorobenzene

Benzene

Bromodichloromethane

Bromoform

Bromomethane

Carbon Tetrachloride

Chlorobenzene

Chlorodibromomethane

Chloroethane

Chloroform

Chloromethane

cis-1,2-Dichloroethylene

cis-1,3-Dichloropropene

Dichloromethane

Ethylbenzene

Ethylene Dibromide

m/p-xylene

Methyl methacrylate

Methyl t-butyl ether

o-xylene

Styrene

Tetrachloroethylene

Toluene

trans-1,2-Dichloroethylene

trans-1,3-Dichloropropene

Trichloroethylene

Trichlorofluoromethane

Vinyl Chloride

AB SOP-00062 Flashpoint by Small Scale Closed Cup Tester (Setaflash)

[Modified from ASTM D3828 Method A, Seta Flash Closed Cup]

Also includes Water – Inorganic

Flashpoint Temperature

AB SOP-00063 Hexavalent Chromium by Konelab [Modified from SM 3500-Cr

B, Colorimetric] Also includes Water - Inorganic

Hexavalent Chromium

AB SOP-00082 Nitrite and Nitrate by Technicon

[Modified from Atlas Chemical Industries Industrial Method No.

857-871, Colorimetric] Also includes Waters - Inorganic

Nitrate

Nitrite

EENVSOP-00061 Phenols Technicon

[Modified from Methods Manual for Chemical Analysis of Water

and Wastes, Updated, Alberta Enviro. Centre, Phenolics, Method

Code 154 EPA 9066, SSMA 40, Colorimetric]

Also includes Waters - Inorganic

Phenols

EENVSOP-00062 The Determination of Cyanide by Technicon [Modified from SM

4500-CN, Colorimetric] Also includes Water - Inorganic

Cyanide (SAD)

Cyanide (WAD)

Total Cyanide

Water soluble Cyanide

EENVSOP-00069 Elemental Sulfur [Modified from Canadian Journal Of Soil

Science, 65, Pp 811-813, Colorimetric]

Elemental Sulphur

Soil/Solid Industrial Waste

AB SOP-00045 Specific Gravity [Modified from SM 2701 F, Petroleum and

Natural Gas Industries- Field Testing of Drilling Fluids, Specific

Gravity] Also includes Water - Inorganic Specific Gravity

AB SOP-00047 Free Liquid (Paint Filter Test) [Modified from EPA 9095,

Volumetric]

Free Liquid in Waste Samples

Water (Inorganic)

AB SOP-00011 Silica (Reactive) by Konelab - Molybdate/ANSA Reduction

Method [Modified From EPA 370.1, Colorimetric]

Reactive Silica

AB SOP-00016 Chemical Oxygen Demand (Total and Dissolved) [Modified From

SM 5220 D, Colorimetric]

COD

AB SOP-00017 Biochemical Oxygen Demand [Modified From SM 5210 B, D.O.

Meter]

BOD (5 day)

CBOD (5 day)

AB SOP-00018 Sulfate by Konelab - Automated Turbidimetry Method [Modified

From SM 4500-SO4 E, Turbidimetric]

Sulfate

AB SOP-00024 Total Phosphorus by Konelab - Ascorbic Acid Reduction Method

[Modified from EPA 365.1 and SM 4500-P A, B, F, Colorimetric]

Total Phosphorus

AB SOP-00032 The Determination of Residual Chlorine in Waters [Modified from

SM 4500-Cl G, Colorimetric]

Free Chlorine

Total Chlorine

AB SOP-00041 Ferrous and Ferric Iron in Water-Colorimetric Determination

[Modified from SM 3500-Fe A, B, Colorimetric]

Ferrous Iron

AB SOP-00058 Dissolved Oxygen- Modified Winkler Method [Modified from SM

4500-O C, Titrimetric]

Dissolved Oxygen

AB SOP-00061 Total Suspended Solids, Total Fixed Solids, and Total Volatile

Solids [Modified from SM 2540 C, D, E, Gravimetric]

Fixed Solids

Total Suspended Solids

Volatile Suspended Solids

AB SOP-00065 Total Dissolved Solids (TDS) [Modified from SM 2540 C, D, E,

Gravimetric]

Total Dissolved Solids

AB SOP-00080 Low Level Sulfide [Modified from SM 4500-S2 D, Colorimetric]

Sulfide

EENVSOP-00031 Mercury in Water Samples by Cold Vapour Atomic Absorption

Spectrometry [Modified from EPA 245.7, Cold Vapour AA]

Mercury

EENVSOP-00060 Organic Carbon Technicon [Modified from Methods Manual For

Chemical Analysis Of Water and Wastes, Updated, Alberta

Enviro. Centre, Method Code 119, Colorimetric]

Organic Carbon

EENVSOP-00065 True Colour [Modified from SM 2120 C, Colorimetric]

True Colour

EENVSOP-00066 Turbidity - Nephelometric Method [Modified from SM 2130 B,

Nephelometric]

Turbidity

EENVSOP-00093 Oil and Grease Water Analysis by Gravimetric Hexane Extraction

Method [Modified from SM 5520 B, Gravimetric]

Total Oil and Grease

Total Petroleum Hydrocarbons (TPH)

EENVSOP-00146 Manganese Divalent Species in Water and Wastewaters [Modified

from Hach Method 8149, Colorimetric]

Divalent Manganese

EENVSOP-00159 pH Analysis in Bioassay Lab

[Modified From SM 4500-H+ B, pH Meter]

pH

PTC SOP -00173 Sulphide - Total, Titration Method [SM 4500-S2 F]

Water (Microbiology)

EENVSOP-00157 Fecal Coliforms by Membrane Filtration [Modified from SM

9222, D, Membrane Filtration]

Fecal (Thermotolerant) Coliforms

EENVSOP-00162 Total Coliforms and Escherichia Coli (E. Coli) by DST [Modified

from SM 9223 A, B, Most Probable Number (Colilert)]

Escherichia coli (E. coli)

Total Coliforms

EENVSOP-00163 Heterotrophic Plate Count [Modified from SM 9215 A, B, Pour

Plate]

Heterotrophic Plate Count (HPC)

EENVSOP-00188 Determination of Iron Related and Sulfate Reducing Bacteria

Using BART

[Modified from Dbi Env Tech Verification Of The IRB-Bart

Tester For The Detection and Eval. Of Iron Bacteria In Water, Dbi

Bio Activity Reaction Test Bart User Manual, and from Dbi

Enviro Tech Verification Of The Srb-Bart Tester For The

Detection and Verification Of Sulfate Reducing Bacteria In Water,

Dbi Bio Activity Reaction Test Bart User Manual, BART]

Iron Related Bacteria (IRB)

Sulfate Reducing Bacteria (SRB)

Water (Organic)

(Adsorbable Organic Halides - Water [028])

PTC SOP - 00056 Adsorbable Organic Halides [AE128.1 March 1992/ ASTM

D4744]

Colormetric Titration

Water (Toxicology)

AB SOP-00083 15 min. Microtox BioAssay using Vibrio fischeri [EPS 1/RM/24,

Bioluminescence]

Microtox IC50 (15 min)

EENVSOP-00154 48-Hr Acute Static Bioassay using Daphnia magna [EPS 1/Rm/11

and EPS 1/RM/14, Acute Lethality (Survival)]

Daphnia LC50 (48 h)

Daphnia Single Concentration (48h)

EENVSOP-00155 Ceriodaphnia dubia Reproduction Inhibition and 7-Day Survival

Chronic [EPS 1/RM/21, Survival and Reproduction Inhibition]

Ceriodaphnia dubia (7d)

EENVSOP-00156 Fathead Minnow Larval Growth and Survival 7 Day Chronic Test

[EPS 1/RM/22, Survival and Growth Inhibition]

Fathead Minnow (7d)

EENVSOP-00160 96-Hour Acute Static Bioassay using Rainbow Trout [EPS 1/RM/9

and EPS 1/RM/13, Acute Lethality (Survival)]

Trout LC50 (96 h)

Trout Single Concentration (96h)

NON METALLIC MINERALS AND PRODUCTS

Petroleum Refinery Products: (Including asphalt materials; petrochemicals; fuels and

lubricants)

Fuels and Lubricants

PTC SOP-00010 Determination of Water in Lubricating Oil by the Visual Crackle

Test

[Fitch, J. C., The Lubrication Field Test and Inspection Guide,

Noria Publishing, Booklet, 2000]

PTC SOP-00011 Additives, Wear Metals and Contaminants in Lubricating Oils by

ICPOES

[ASTM D5185]

PTC SOP-00012 Kinematic Viscosity of Lubricating Oils

[ASTM D7279]

PTC SOP-00013 Oxidation, Nitration, Sulphation and Soot of Engine oils by FTIR

[ASTM D7418]

PTC SOP-00014 Determination of Fuel Dilution for In-Service Engine Oils by GC

[ASTM D7593]

PTC SOP-00015 Determination of Glycol Contamination for In-Service Engine Oils

by GC

[ASTM D7922]

PTC SOP-00016 Acid Number of Lubricating Oils by Potentiometric Titration

[ASTM D664]

PTC SOP-00017 Base Number of Lubricating Oils by Potentiometric Titration

[D4739]

PTC SOP-00018 Water Content in Lubricating Oils by Coulometric KF Titration

[ASTM D6304]

PTC SOP-00020 ISO Particle Count of Lubricating Oils Using an Optical Particle

Counter

[ISO 11500:2008]

PTC SOP-00027 Soot Percentage of Diesel Engine Oil by Wilks Soot Meter

PTC SOP-00028 PQ Index of Lubricating Oil

PTC SOP-00029 Analysis of Hydrocarbon Condensates by Heated Flash

[GPA 2177, 2186, 2103, 2261]

PTC SOP-00030 Analysis of C4 Components in Condensate

[GPA 2177]

PTC SOP-00031 Calibration and Analysis of Trace Sulfur Compounds in Petroleum

Products

[ASTM D-5504 Modified]

PTC SOP-00033 Calibration and Analysis of Trace Sulfur Compounds in Petroleum

Products

[ASTM D5623]

PTC SOP-00035 Analysis of Elemental and Polysulphide Sulphur

["Quantitative Determination of Elemental Sulphur in

Hydrocarbons, Soils, and Other Materials", Journal of

Chromatographic Science, Vol. 27, May 1989 by P.D. Clarke &

K.L. Lesage]

PTC SOP-00036 Hydrocarbon C30 Analysis by Gas Chromatography

[ASTM D2887/CAN/CGSB 3.0, No.14.3]

PTC SOP-00037 Density of Light Hydrocarbons (condensate) by Digital

Densitometer

[ASTM D4052/ ASTM D5002]

PTC SOP-00038 Trace Methanol by Gas Chromatography

[UOP 569 (modified)]

PTC SOP-00039 Boiling Range Distribution by ASTM D7900

PTC SOP-00040 Hydrogen Sulphide Determination by Tutweiler

[Adapted from UOP 9-59 and C-1 of the GPA Plant Operations

Test Manual]

PTC SOP-00041 H2S Content in Hydrogen Gas or Air by Stain Detection Tubes

[GPA 2377]

PTC SOP-00044 Analysis of LPG/NGL to C15+ (Extended)

[GPA 2186]

PTC SOP-00045 Ponau Analysis

[CAN/CGSB 3.0 No. 14.3]

PTC SOP-00048 Hydrocarbon C100 Analysis by Gas Chromatography

[ASTM D6352]

PTC SOP-00049 Component Analysis of Glycols, Amines, and Sulfinols by GC

[UOP 523 modified]

PTC SOP-00050 Total Organic Halogens and Organic Chlorides

[modified ASTM D4929]

PTC SOP-00051 Boiling Range Distribution of Petroleum Fractions by Gas

Chromatography

[ASTM D2887]

PTC SOP-00052 High Pressure Density

[ASTM D4052/5002]

PTC SOP-00054 Extractable Organic Halogens

[U.S EPA 9023]

PTC SOP-00055 Boiling Range Distribution by ASTM D6352

PTC SOP-00057 Total Base Number of Lubricating Oils by Potentiometric Titration

[ASTM D2896]

PTC SOP-00058 Molecular Weight by Freezing Point Depression

[Cryette Instrument Manual]

PTC SOP-00062 Analysis of Hydrocarbon Gas

[GPA 2286]

PTC SOP-00067 Measurement of Viscosity by Cannon - Fenske Opaque

Viscometer

[ASTM D445;D446]

PTC SOP-00068 Pour Point Analysis of Petroleum Products

[ASTM D97; D5853]

PTC SOP-00071 Distillation of Petroleum Products at Atmospheric Pressure

[ASTM D86]

PTC SOP-00072 Reid Vapour Pressure of Petroleum Products

[ASTM D323A]

PTC SOP-00082 Flash-Point by Pensky-Martens Closed Cup Tester

[ASTM D93]

PTC SOP-00083 Detection of Copper Corrosion from Petroleum Products by the

Copper Strip

[ASTM D130]

PTC SOP-00084 Water and Sediment in Crude by the Centrifuge Method

(Laboratory Procedure)

[ASTM D4007; ASTM D1796; ASTM D2709]

PTC SOP-00089 Aniline Point of Petroleum Products

[ASTM D611]

PTC SOP-00091 Electrical Conductivity of Aviation and Distillate Fuels

[ASTM D2624]

PTC SOP-00092 Free Water and Particulate Contamination in Distillate Fuels

(Visual Inspection Procedures)

[ASTM D4176]

PTC SOP-00093 Filterability of Diesel Fuels by Low Temperature Flow Test

(LTFT)

[ASTM D4539]

PTC SOP-00097 Determination of Bitumen, Water, Solids by Dean Stark Method

[Alberta Research Council Oil Sands Analytical Method Manual,

Chapter 1, Method 1.00]

PTC SOP-00099 Density and Relative Density of Liquids by Digital Density Meter

[ASTM D4052]

PTC SOP-00100 Density and Relative Density of Crude Oils by Digital Density

Analyzer

[ASTM D5002]

PTC SOP-00103 Total Acid Number of Petroleum Products by Potentiometric

Titration

[ASTM D664]

PTC SOP-00105 Water in Petroleum Products by Coulometric Karl Fischer

Titration

[ASTM D4928]

PTC SOP-00107 Standard Test Method for Determination of Carbon Residue

(Micro Method) [ASTM D4530]

PTC SOP-00111 Total Nitrogen Sulphur in Hydrocarbons by boat-inlet Antek

[ASTM D5453-S, ASTM D5762 – N2, ASTM D4629 – Trace

Nitrogen]

PTC SOP-00115 Sediment in Oil by Membrane Filtration [ASTM D4807]

PTC SOP-00116 Sulfur in Petroleum Products by Energy-Dispersive X-Ray

Fluorescence Spectroscopy [ASTM D4294]

PTC SOP-00120 Cetane Number of Diesel Fuel Oil [ASTM D613]

PTC SOP-00121 Heat of Combustion of Liquid Hydrocarbon Fuels by Bomb

Calorimeter [ASTM D240]

PTC SOP-00122 Lubricity of Diesel Fuels by High Frequency Reciprocating Rig

[ASTM D6079]

PTC SOP-00126 Acid Number by Color-Indicator Titration [ASTM D974]

PTC SOP-00175 Ash Content [ASTM D482]

PTC SOP-00204 High Temperature Stability of Distillate Fuels [ASTM D6468]

PTC SOP-00206 Metals Analysis in Organics by ICPOES [ASTM D5708]

PTC SOP-00209 Trace Hydrocarbon Analysis by GC

PTC SOP-00211 Light End Analysis in Stabilized Hydrocarbon Liquids

PTC SOP-00218 Boiling Range distribution by ASTM D7169

PTC SOP-00221 Oxidation Stability of FAME (Accelerated Oxidation Test) [EN14

112]

PTC SOP-00241 Ultimate Analysis of Coal and Coke (including Sulfur) [ASTM

D3176 / ASTM D4239]

PTC SOP-00242 Proximate Analysis of Coal and Coke and Loss on Ignition

Determination [ASTM D7582 / ASTM D7348]

PTC SOP-00250 Preparation of Coal Samples and Determination of Moisture in

Coal [ASTM D2013 / ASTM D3302]

PTC SOP-00254 Heating Value of Coal and Coke by Bomb Calorimeter [ASTM

D5865]

PTC SOP-00267 Viscosity by Stabinger [ASTM D7042]

PTC SOP-00275 Particle Size Distribution by Beckman Coulter Laser Analyzer

PTC SOP-00279 Total Mercury in Coal and Coal Combustion Residues [ASTM

D6722]

Notes:

ASTM: American Society for Testing and Materials ISO/IEC 17025: 2017: General Requirements for the Competence of Testing and Calibration Laboratories MSSMA: McKeague, Manual on Soil Sampling and Methods of Analysis SSMA: Carter, Soil Sampling and Methods of Analysis

Elias Rafoul, Vice President

Accreditation Services

Date: 2019-06-03

Number of Scope Listings: 142

SCC 1003-15/229

Partner File #0

Partner: SCC