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WATER QUALITY BASELINE REPORT DOVER COMMERCIAL PROJECT Submitted to: Dover Operating Company December 2010 09-1346-1011

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Page 1: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

WATER QUALITY BASELINE REPORT

DOVER COMMERCIAL PROJECT

Submitted to:

Dover Operating Company

December 2010 09-1346-1011

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- i - Water Quality Baseline Report December 2010

Golder Associates

EXECUTIVE SUMMARY EXECUTIVE SUMMARY

Dover Operating Corp. (Dover OPCO) proposes to develop and operate a commercial scheme for the recovery of bitumen from the McMurray formation approximately 95 km northwest of Fort McMurray, Alberta. This scheme will include the use of in situ steam assisted gravity drainage (SAGD) extraction, well pairs and two on-site steam generation and oil water treatment plants. The Project is submitted under the name of the Dover Commercial Project (the Project).

This report presents the baseline information on water quality conditions for the Project Aquatics Regional Study Area (RSA).

Water and sediment quality samples were collected within and near the LSA in 2009 and 2010, to characterize existing baseline water and sediment quality conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling program. A detailed analysis of the data is included in this section.

The Water Quality Baseline study results indicate that water and sediment quality within and near the LSA are similar to those documented by other studies in the Oil Sands Region.

Larger waterbodies and watercourses, (i.e., Namur and Gardiner lakes and the Ells River) are generally mesotrophic, while smaller waterbodies and watercourses are typically eutrophic. Most of the measured concentrations were below water quality guideline values, although concentrations of total phenolics, total iron and total manganese in water were frequently above water quality guidelines. Less frequent guideline exceedances were observed in concentrations of fluoride, sulphide and total arsenic, barium, chromium, copper, lead, mercury, selenium, silver and zinc. Water quality in the RSA and LSA is similar to that observed in the region and reflects local background conditions

Most bottom sediments contained higher proportions of sand than silt and clay. Arsenic, fluorene and phenanthrene concentrations were occasionally measured above sediment quality guidelines. Sediment quality in the LSA is similar to that observed in the region and reflects local background conditions.

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Dover Commercial Project - ii - Water Quality Baseline Report December 2010

Golder Associates

TABLE OF CONTENTS

SECTION PAGE

1  INTRODUCTION ......................................................................................................... 1 1.1  STUDY AREAS ............................................................................................................... 3 

1.1.1  Aquatics Regional Study Area ......................................................................... 3 1.1.2  Local Study Area .............................................................................................. 4 

1.2  STUDY OBJECTIVES ..................................................................................................... 4 

2  AVAILABLE DATA ...................................................................................................... 6 2.1  HISTORICAL DATA ......................................................................................................... 6 2.2  PROJECT DATA ............................................................................................................. 6 2.3  METHODS ....................................................................................................................... 9 

2.3.1  Field Sampling ................................................................................................. 9 2.3.2  Data Analysis ................................................................................................. 11 

3  RESULTS AND DISCUSSION .................................................................................. 17 3.1  WATER QUALITY ......................................................................................................... 17 

3.1.1  Namur Lake and Gardiner Lakes ................................................................... 17 3.1.2  Small Waterbodies Within and Near the Local Study Area ........................... 21 3.1.3  Ells River ........................................................................................................ 24 3.1.4  Other Watercourses Within and Near the Local Study Area ......................... 27 

3.2  SEDIMENT QUALITY .................................................................................................... 30 3.2.1  Waterbodies Within and Near the Local Study Area ..................................... 30 3.2.2  Watercourses Within and Near the Local Study Area ................................... 30 

4  SUMMARY ................................................................................................................ 32 

5  CLOSURE ................................................................................................................. 33 

6  REFERENCES .......................................................................................................... 34 

7  ABBREVIATIONS ..................................................................................................... 38 

8  GLOSSARY .............................................................................................................. 40 

LIST OF TABLES

Table 1  Details of the 2009/2010 Field Program .................................................................. 7 Table 2  Surface Water Quality Guidelines .......................................................................... 12 Table 3  Trophic Status Categories Based on Total Phosphorus Concentration ................ 14 Table 4  Trophic Status Categories Based on Chlorophyll a Concentration ....................... 15 Table 5  Canadian Sediment Quality Guidelines for the Protection of Freshwater

Aquatic Life ............................................................................................................ 16 Table 6  Seasonal Water Quality Summary for Namur Lake ............................................... 18 Table 7  Seasonal Water Quality Summary for Gardiner Lakes .......................................... 20 Table 8  Seasonal Water Quality Summary for Other Waterbodies Within and Near

the Local Study Area ............................................................................................. 22 

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Golder Associates

Table 9  Seasonal Water Quality Summary for the Ells River Within and Near the Local Study Area .................................................................................................... 25 

Table 10  Seasonal Water Quality Summary for Other Watercourses Within and Near the Local Study Area ..................................................................................... 28 

Table 11  Summary of Sediment Quality Data for Waterbodies and Watercourses Within and Near the Local Study Area .................................................................. 31 

LIST OF FIGURES

Figure 1  Project Location ....................................................................................................... 2 Figure 2  Aquatics Study Areas .............................................................................................. 5 Figure 3  2009/2010 Water and Sediment Quality Survey Locations ..................................... 8 

LIST OF ATTACHMENTS

Attachment A Individual Water Quality Sample Test Results for Project-Specific Sampling

Attachment B Individual Sediment Sample Test Results for Project-Specific Sampling Attachment C Quality Assurance/Quality Control Results Attachment D Regional Study Area Water Quality Summary Tables Attachment E Project-Specific Water Quality Summary Attachment F Project-Specific Sediment Quality Summary

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Dover Commercial Project - 1 - Water Quality Baseline Report December 2010

Golder Associates

1 INTRODUCTION

Dover Operating Corp. (Dover OPCO) proposes to develop and operate a commercial scheme for the recovery of bitumen from the McMurray Formation approximately 95 km northwest of Fort McMurray, Alberta. The project is located in Townships 92, 93, 94, 95 and 96, Ranges 15, 16, 17 and 18 West of the Fourth Meridian (W4M) as shown on Figure 1. This scheme will include the use of in situ Steam Assisted Gravity Drainage (SAGD) well pairs and two on-site steam generation and oil/water treatment plants. The project is submitted under the name of the Dover Commercial Project (the Project).

The Project is within a 170 section (43,500 ha) area of land called the Dover Leases. The Project will be developed in five phases with each phase having 50,000 barrels per day (bpd) of bitumen capacity. Phase 1 will consist of the Dover North Plant (DNP) and associated well pads and infrastructure generally to the north of the plant. The Initial Surface Development Area (ISDA) will include these Phase 1 facilities, the access corridor and the source water well system.

Currently, 11 well pads are planned for the Phase 1 development. The access corridor consists of a permanent 51-km-long access road and a 67-km-long utility Right-of-Way (ROW) extending southeast from the DNP to other projects currently proposed and under review by the regulators. The source water well system includes 12 well pads and 20 km of infield access corridor consisting of both a permanent road and a pipeline corridor. The majority of this access corridor will also be used for SAGD well pad development as the Project progresses.

Phase 2 will involve an expansion of the DNP to 100,000 bpd capacity and associated SAGD well pads and infrastructure. An additional 140 well pads are ultimately planned for the northern portion of the Project to support continued development of Phases 1 and 2 of the Project.

Phases 3 to 5 will include construction and progressive 50,000 bpd expansions of the Dover South Plant (DSP) along with production pads and associated infrastructure. A total of 375 SAGD well pads are planned in the southern portion of the Dover Leases.

Both the northern and southern portions of the Dover Leases will undergo progressive development wherein SAGD well pads will be constructed, operated for typically 8 to 12 years and then reclaimed. Materials recovered during reclamation of pads will be re-used for new well pads to the extent possible. This progressive development and reclamation will result in a likely scenario of 175 well pads being either in construction, operation, or reclamation at any one time when the Project is in full production.

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1.1 STUDY AREAS

1.1.1 Aquatics Regional Study Area

The Aquatics Regional Study Area (RSA) was based on potential effects from construction and operation of the Project on flows and water levels in watersheds in which the Project is located, including surface water/groundwater interactions. This RSA also contains other projects and activities that are considered in the Baseline and Planned Development Cases.

The Aquatics RSA is shown on Figure 2 and includes the following major watersheds and lakes:

Ells River basin (effective drainage area of 2,450 km2): The Ells River originates from Gardiner Lakes, and drains south (immediately east of the Project) and then to the east before discharging to the Athabasca River about 42 km east of the Project. The drainage for Joslyn Creek is within the Ells River basin but is 30 km to the east and it joins the Ells River very close to the mouth. Since this drainage is affected by proposed oil sands mining developments in its downstream reach, it was excluded from the RSA.

MacKay River basin (effective drainage area of 5,570 km2): The MacKay River basin drains the western and southern portions of the RSA. The MacKay River basin includes the Dover, Dunkirk, and MacKay sub-basins. The Dover River drains the majority of the southern Lease Area. The western of the Project area is drained by the Dunkirk River, a south-flowing tributary of the MacKay River at the upper MacKay River watershed. The MacKay River generally flows to the northeast before discharging into the Athabasca River about 45 km east of the Project. The Dover and Dunkirk rivers intersect at approximately 20 km and 90km upstream of the Athabasca River confluence, respectively.

Gardiner Lakes (Upper Gardiner Lake and Lower Gardiner Lake, total surface area of 50 km2): Gardiner Lakes are the headwaters for the Ells River, with the river originating at the outflow of Lower Gardiner Lake.

Namur Lake (surface area of 37 km2), Big Island Lake (surface area of 16 km2) and Sand Lake (surface area of 14 km2): These three large lakes are located in the headwaters of the Ells River system and all drain to the Gardiner Lakes.

The total area of the Aquatics RSA is approximately 796,000 ha. Namur Lake and Gardiner Lakes are considered to be regionally important as are the Ells and MacKay rivers (Westworth 1994).

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The northern portion of the RSA is comprised generally of uplands sloping to the northwest towards the Birch Mountains. This area is characterized by numerous small streams and drainages flowing to the southeast. A secondary direction for streams is along glacial striations that run from southwest to northeast. The southern portion of the RSA tends to have less variation in topography and a greater occurrence of wetlands. Many of the smaller unnamed streams tend to be poorly defined.

1.1.2 Local Study Area

The Local Study Area (LSA) covers approximately 62,000 ha and includes the Project footprint and the access corridor to the southeast (Figure 2). The LSA corresponds to that used for the terrestrial components.

These two study areas were used to define the level of detail of the baseline water and sediment quality study, with information collected and evaluated in detail for waterbodies and watercourses within and in the general vicinity of the LSA and compilation of historical water quality information compiled for the RSA.

1.2 STUDY OBJECTIVES

The following objectives were identified for the water quality and sediment quality components of this study:

compile existing information on water quality within the RSA;

compile existing information on sediment quality within and near the LSA;

describe and discuss existing water and sediment quality within and near the LSA;

where possible, discuss seasonal variation in water quality; and

compare existing water and sediment quality in the LSA with relevant guidelines for the protection of aquatic life, human health and wildlife health.

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2 AVAILABLE DATA

Data included in this report are from historical sources and recent (2009/2010) field programs designed to support the Environmental Impact Assessment for the Project.

2.1 HISTORICAL DATA

Publicly available, historical water quality data for the RSA were compiled from:

the Alberta Environment (AENV) Water Data System (AENV 2010); and

the Regional Aquatics Monitoring Program (Golder 1999, 2000, 2001, 2002, 2003; RAMP 2004, 2005, 2006, 2007, 2008, 2009, 2010).

Additional water quality data within the RSA and sediment quality data within and near the LSA were obtained from:

Athabasca Oil Sands Corporation (AOSC) for water and sediment samples collected in support of the MacKay River Commercial Project Environmental Impact Assessment (AOSC 2009);

Southern Pacific Resource Corp. Application for the Southern Pacific Resource Corp. (STP) McKay SAGD Project (Southern Pacific 2009); and

Sunshine Oil Sands Ltd. Application for Sunshine Oil Sands Ltd. West Ells SAGD Project (Sunshine 2010).

2.2 PROJECT DATA

A baseline sampling program was completed to characterize general water and sediment quality in waterbodies and watercourses that may be directly affected by the Project. Water samples were collected during the summer and fall of 2009 and during the winter and spring of 2010. Sediment samples were collected in the fall of 2009. Water sampling was conducted seasonally to represent water quality conditions at important points in the hydrologic cycle. Details of the 2009/2010 field sampling program are provided in Table 1, and field sample locations are shown on Figure 3.

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Table 1 Details of the 2009/2010 Field Program

Drainage Basin

Watercourse or Waterbody Name

Site ID Location

(UTM Zone 12) Sampling Season

Samples Collected

Northing Easting Water Sediment

Ells River Watershed

Ells River WC-1 6347183 407633 Winter 2010 -

Spring 2010 -

Ells River WC-17 6361021 406178 Summer 2009 -

Fall 2009 -

Unnamed Tributary to Ells River

WC-6 6350047 405509 Winter 2010 -

Spring 2010 -(a) -

Unnamed Tributary to Ells River

WC-7 6358374 401691

Summer 2009 -

Fall 2009

Winter 2010 -(b) -

Spring 2010 -

Unnamed Waterbody WB-1 6347327 404208

Summer 2009 -

Fall 2009

Winter 2010 -

Spring 2010 -

Unnamed Waterbody WB-3 6358217 398576

Summer 2009 -

Fall 2009

Winter 2010 -

Spring 2010 -

Namur Lake WB-4 6360789 396732

Summer 2009 -

Fall 2009 -

Winter 2010 -(c) -

Spring 2010 -

MacKay River Watershed

(Dunkirk River Sub-basin)

Unnamed Tributary to Dunkirk River

WC-5 6332815 384357 Winter 2010 -(b) -

Spring 2010 -

Unnamed Tributary to Snipe Creek

WC-2 6348247 400459

Fall 2009

Winter 2010 -(b) -

Spring 2010 -

Unnamed Tributary to Snipe Creek

WC-21 6348579 388141 Summer 2009 -

Fall 2009

Unnamed Tributary to Snipe Creek

WC-22 6344291 387643 Fall 2009

Unnamed Tributary to Snipe Creek

WC-23 6339156 385928 Summer 2009 -

Fall 2009

Snipe Creek WC-24 6336842 388195 Summer 2009 -

Fall 2009

Unnamed Waterbody WB-2 6344534 395969 Winter 2010 -

Spring 2010 -

Unnamed Waterbody WB-5 6341322 391875

Summer 2009 -

Fall 2009

Spring 2010 -

Unnamed Waterbody WB-10 6356236 391242 Summer 2009 -

Fall 2009 -

(a) Sample not collected due to impoundment of water behind beaver dam, waters not representative of a watercourse.

(b) Sample not collected due to insufficient flow volume under ice.

(c) Sample not collected due to lack of access (i.e., thick brush at shoreline).

Notes: = Sample collected; - = No sample collected.

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92

94

Tp97

96

PHASE 1DEVELOPMENTAREA

WC-1

WC-17

WC-6

WC-7

WB-4

WC-5

WC-21

WC-22

WC-23

WC-24

WB-2

WB-5

WB-10

WB-3

WB-1

WC-3

WC-4

WC-2

PHASE 1 DEVELOPMENT AREA

2009/2010 WATER AND SEDIMENTQUALITY SURVEY LOCATIONS

DOVER COMMERCIAL PROJECT

FIGURE: 3

ALBERTA DIGITAL DATA OBTAINED FROM ALTALIS LTD. (SEPTEMBER 2004).USED UNDER LICENSE. DATUM: NAD83 PROJECTION: UTM ZONE 12

REFERENCE

LEGEND

DOVER LEASES

WATER AND SEDIMENT QUALITY SITE LOCATION6

360

000N

380000 400000 420000

634

000

0N6

320

000N

636

000

0N6

340

000N

632

000

0N

380000 400000 420000

PROPOSED MAIN ACCESS ROAD

PROPOSED UTILITY ROW

LOCAL STUDY AREA

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2.3 METHODS

This section outlines the methods used to characterize water and sediment quality in the study areas, including field sampling, data compilation and analysis.

2.3.1 Field Sampling

At each waterbody site, a composite sample was collected with a 1 L bottle which was used to collect six grab samples from each of three randomly selected locations, for a total of 18 L. All water collected at a waterbody was added to a clean 20 L pail and was mixed before filling sample bottles provided by the analytical laboratories.

At watercourse sites, individual grab samples were collected from just below the water surface, at approximately mid-channel.

Field parameters including dissolved oxygen, pH, specific conductivity and water temperature were measured at each water quality sampling site near the water surface. Single measurements were taken at stream sites and the median of measurements taken at each of the three random sites on each lake were assigned to the composite samples. Field measurements were made using a field-calibrated multi-meter (YSI 556 or equivalent).

Water samples were collected, preserved, stored and shipped in accordance with established technical procedures for water quality sample collection that are consistent with standard methods (APHA 1992; Environment Canada 1993). For dissolved parameter testing, 1 L water samples were collected and filtered on the same day. Preservatives were added to sample bottles as required by the analytical laboratories. Summer and fall 2009 water quality samples were submitted to ALS Environmental in Fort McMurray, Alberta for analysis of parameters described below.

Water quality samples collected in winter and spring 2010 were split into two parts and shipped to separate laboratories for analysis: one part to the Alberta Innovates – Technology Futures in Vegreville, Alberta, for ultra low detection analysis of methyl mercury; and one part to the Maxxam Analytics in Fort McMurray, Alberta, for analysis of all other parameters described below. These samples were analyzed for a suite of detailed chemical parameters, which provide a broad profile of in-stream water quality and are generally consistent with the parameter list used by the Regional Aquatics Monitoring Program (RAMP 2010). Individual water quality sample results from the program are provided in Attachment A.

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The analytical parameters analyzed for water quality include the following:

Conventional: pH, conductivity, Total Dissolved Solids (TDS), Total Suspended Solids (TSS), hardness, total alkalinity, Dissolved Organic Carbon (DOC), Total Organic Carbon (TOC) and colour.

Major ions: bicarbonate, calcium, carbonate, chloride, magnesium, potassium, sodium, sulphate and sulphide.

Nutrients and biological indicators: ammonia, nitrate, nitrite, Total Kjeldahl Nitrogen (TKN), total and dissolved phosphorus, Biochemical Oxygen Demand (BOD) and chlorophyll a.

Organics: naphthenic acids, total phenolics and total recoverable hydrocarbons.

Total and dissolved metals: aluminum, antimony, arsenic, barium, beryllium, boron, cadmium, chromium, cobalt, copper, iron, lead, lithium, manganese, mercury, methyl mercury, molybdenum, nickel, selenium, silver, strontium, thallium, titanium, uranium, vanadium and zinc.

Sediment samples were collected using an Ekman grab. Three grab samples were collected and mixed in a metal pan to prepare a composite sample. Sample jars and bags were filled and submitted to ALS Environmental in Fort McMurray, Alberta, for analysis of particle size, carbon and organic content, total metals, Polycyclic Aromatic Hydrocarbons (PAHs) and alkylated PAHs. These parameters are also generally consistent with those used by RAMP (2010). Individual sediment quality sample results from the program are provided in Attachment B.

Quality Control samples were also collected during each sampling period. Blanks were used to assess potential sample contamination during collection, shipping and analysis; duplicate samples were used to check intra-site variation and precision of field sampling methods; and split samples were used to test the precision of laboratory analyses. Details of the Quality Control program are provided in Attachment C.

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2.3.2 Data Analysis

2.3.2.1 Water Quality

Results of the 2009 to 2010 water quality sampling program were combined with available historical data, and the seasonal median, minimum and maximum values were calculated. Consistent with RAMP (2010), seasons were defined as winter (November through March), spring (April and May), summer (June through August) and fall (September and October). Historical metals data associated with high analytical detection limits relative to recent detectable results (e.g., mercury and silver prior to 2001) were removed from the data sets prior to this summary, as such results are not representative of baseline conditions and would not add value to the baseline analysis.

Water quality data were evaluated by comparing concentrations of individual parameters with published water quality guidelines for the protection of freshwater aquatic life, human health and wildlife health (AENV 1999; CCME 1999; Health Canada 2008; U.S. EPA 2002, 2003a,b). In cases where several guidelines were available for a parameter, the most stringent guideline was used, as recommended by Alberta Environment (AENV 1999), unless otherwise noted. A summary of the relevant water quality guidelines is provided in Table 2.

Water quality guidelines have been developed for many parameters, typically based on measured responses of standard test species (fish and invertebrates) to known concentrations of chemicals. Guidelines for nutrients (e.g., total phosphorus [TP] and total nitrogen [TN]), which are non-toxic, correspond to levels, below which the harmful effects of nutrient enrichment (e.g., algal blooms) are unlikely. Chronic guidelines provide protection from long-term, sub-lethal effects (e.g., reduced growth or impaired reproduction). Acute guidelines are intended to protect aquatic organisms from short-term, usually lethal effects.

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Table 2 Surface Water Quality Guidelines

Parameter Units Water Quality Guidelines

Aquatic Life Human Health(c)

Wildlife Health(d) Acute(a) Chronic(b)

Field Measured pH - 6.5 to 8.5 6.5 to 8.5 5 to 9 - dissolved oxygen mg/L 5(e) 6.5(f) - - Major Ions calcium mg/L - - - 1,000 chloride mg/L 860 230 -(g) - fluoride mg/L - 0.12 1.5 2 sodium mg/L - - -(g) - sulphate mg/L - - -(g) 1,000 sulphide mg/L - 0.014(h) -(g) - total dissolved solids mg/L - - - 3,000 Nutrients ammonia(i) mg/L 5.6 2.43 - - nitrate mg/L - 2.93 10 - nitrite mg/L - 0.06 1 10 nitrate and nitrite mg/L - - - 100 total nitrogen mg/L - 1 - - total phosphorus mg/L - 0.05 - - Total Metals aluminum mg/L 0.75 0.1 0.1 5 antimony mg/L - - 0.0055 - arsenic mg/L 0.34 0.005 0.01(j) 0.025 barium mg/L - - 1.0 - beryllium mg/L - - 0.004 0.1 boron mg/L 29 1.5 5 5 cadmium(k) mg/L 0.0021(l) 0.00027(l) 0.005 0.08 chromium mg/L 0.016(m) 0.001(m) 0.05(n) 0.05(n)

cobalt mg/L - - - 1 copper(o) mg/L 0.014(l) 0.002(l) 1.3 0.5 iron mg/L - 0.3 0.3 - lead mg/L 0.082(l) 0.0032(l) 0.01 0.1 manganese mg/L - - 0.05 - mercury(p) mg/L 0.000013 0.000005 0.001 0.003 methyl mercury(p) mg/L 0.000002 0.000001 - - molybdenum mg/L - 0.073 - 0.5 nickel mg/L 0.469(l) 0.052(l) 0.34 1 selenium mg/L - 0.001 0.01 0.05 silver mg/L 0.0041(l) 0.0001 - - thallium mg/L - 0.0008 0.00013 - uranium mg/L - - 0.02 0.2 vanadium mg/L - - - 0.1 zinc mg/L 0.12(l) 0.03 5.1 50 Organics phenolics mg/L - 0.004 - 0.002(q)

acenaphthene µg/L - 5.8 330 - anthracene µg/L - 0.012 6300 - benzo(a)anthracene µg/L - 0.018 0.0029 - benzo(a)pyrene µg/L - 0.015 0.0029 - benzo(b&k)fluoranthenes µg/L - - 0.0029 - chrysene µg/L - - 0.0029 - dibenzo(a,h)anthracene µg/L - - 0.0029 -

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Table 2 Surface Water Quality Guidelines (continued)

Golder Associates

Parameter Units Water Quality Guidelines

Aquatic Life Human Health(c)

Wildlife Health(d) Acute(a) Chronic(b)

fluoranthene µg/L - 0.04 50 - fluorene µg/L - 3 800 - indeno(c,d-123)pyrene µg/L - - 0.0029 - naphthalene µg/L - 1.1 - - phenanthrene µg/L - 0.4 - - pyrene µg/L - 0.025 5.1 -

(a) Based on the more conservative guideline of: AENV (1999) and U.S. EPA (2002), unless otherwise noted.

(b) Based on the more conservative guideline of: AENV (1999), CCME (1999) and U.S. EPA (2002), unless otherwise

noted. (c)

Based on the more conservative guideline of: Health Canada (2008), U.S. EPA (2003a) and U.S. EPA (2002, 2003b) using fish consumption rate of 45 g/d (Richardson 1997), unless otherwise noted.

(d) CCME (1999) - livestock watering guidelines.

(e) Instantaneous minimum.

(f) 7-day mean.

(g) Health Canada (2008) - Aesthetic objective guidelines exist for these parameters, but were not used in this study as they do not relate to toxic thresholds; human health guidelines without this superscript are the maximum acceptable concentrations and interim maximum acceptable concentrations.

(h) Guideline is pH dependent; value shown here corresponds to a pH value of 8; this guideline was altered based on-site-specific median conditions using the methods described in U.S. EPA (2002).

(i) Guidelines are pH (acute and chronic) and temperature (chronic) dependent; values shown here correspond to a pH and temperature value of 8 and 10C, respectively; these guidelines were calculated based on-site-specific median conditions using the methods described in AENV (1999) and U.S. EPA (2002).

(j) The Health Canada (2008) drinking water guideline for arsenic was used in place of the lower U.S. EPA (2002) human health guideline for surface waters, because the human health guideline is based on the consumption of oysters, a non-resident species in the Oil Sands Region.

(k) The U.S. EPA (2002) chronic cadmium guideline was used in place of the lower CCME (1999) chronic guideline, because, as noted by CCME (1999), most ambient waters contain cadmium levels in excess of the recommended CCME chronic cadmium guideline.

(l) Guidelines are hardness dependent; values shown here are based on a hardness of 100 mg/L; these guidelines

were calculated based on-site-specific median hardness levels using the methods described in AENV (1999) and U.S. EPA (2002).

(m) Chromium VI guideline.

(n) Chromium III guideline. (o) U.S. EPA (2002) acute and CCME (1999) chronic guidelines are shown, because Alberta copper guidelines apply to

acid extractable values (as opposed to total values). (p) Alberta draft guidelines for mercury and methyl mercury are shown. (q) Guideline for phenols.

- = Not applicable or no guideline.

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Concentrations of parameters measured to evaluate baseline water quality may be affected by several factors. Natural conditions associated with surficial geology, interactions between surface water and groundwater, physical features of the waterbody and its drainage basin, local weather and seasonal hydrological changes and many other factors can influence baseline water quality. For example, many elements can be tightly bound to suspended sediments during spring runoff, resulting in elevated concentrations of metals (e.g., aluminum, iron and manganese) and nutrients (e.g., TP) in surface water. Consequently, it is common to measure some water quality parameters above regulatory guidelines in remote areas that are not directly affected by human activities. However, these parameters are generally not bioavailable to aquatic organisms.

Parameter concentrations that are slightly higher than water quality guidelines under baseline conditions are generally not considered to be of concern to aquatic life. Guidelines based on laboratory toxicity testing tend to be conservative, because such guidelines frequently incorporate a safety factor. Moreover, aquatic species are adapted to the natural levels of chemicals present in the waters they inhabit. Therefore, concentrations of water quality parameters that are greater than guidelines do not necessarily indicate that water quality has been compromised by human activities or natural factors.

Three qualitative scales were used to categorize the trophic status of watercourses and waterbodies in the results section of the report. A total phosphorus scale developed by Vollenweider and Kerekes (2002) was used to categorize the trophic status of waterbodies (Table 3). This scale also defines Canadian Council of Ministers of the Environment (CCME [CCME 2004]) trigger ranges for management of freshwater systems. A total phosphorus scale developed by Dodds et al. (1998) was used to categorize the trophic status of watercourses. Finally a chlorophyll a scale developed by Mitchell and Prepas (1990) was used to also categorize the trophic status of waterbodies (Table 4).

Table 3 Trophic Status Categories Based on Total Phosphorus Concentration

Trophic Status Average Epilimnetic Total Phosphorus

[mg/L] Waterbodies(a) Watercourses(b)

ultra-oligotrophic (very nutrient-poor) <0.004 n/a oligotrophic (nutrient-poor) 0.004 to 0.01 <0.025 mesotrophic (containing a moderate level of nutrients) 0.01 to 0.02 0.025 to 0.075 meso-eutrophic (containing moderate to high level of nutrients) 0.02 to 0.035 n/a eutrophic (nutrient-rich) 0.035 to 0.1 >0.075 hypereutrophic (very nutrient-rich) >0.1 n/a

(a) Vollenweider and Kerekes (1982).

(b) Dodds et al. (1998).

n/a = Not applicable. Source: CCME (2004).

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Table 4 Trophic Status Categories Based on Chlorophyll a Concentration

Trophic Status Maximum Epilimnetic Chlorophyll a

[g/L]

oligotrophic <8

oligo-mesotrophic occasionally >8

mesotrophic 8 to 25

eutrophic 26 to 75

hypereutrophic >75

Source: Mitchell and Prepas (1990).

2.3.2.2 Sediment Quality

Sediment quality data were evaluated through a comparison of individual parameter concentrations to the CCME guidelines shown in Table 5. These guidelines include the CCME Interim Sediment Quality Guidelines (ISQG) and Probable Effects Levels (PEL) (CCME 1999).

Sediment quality can be influenced by a number of different factors. The surficial geology, physical features of the lake or stream, seasonal hydrological changes and biological factors can all influence sediment quality. This can result in concentrations of parameters exceeding guideline criteria under baseline conditions.

Parameter concentrations that are higher than sediment quality guidelines under baseline conditions are generally not considered to be of concern. As in the case of water quality guidelines, sediment quality guidelines based on laboratory testing tend to be conservative, because such guidelines frequently incorporate a safety factor. Moreover, aquatic species are adapted to the natural levels of chemicals present in the waters they inhabit, which, in the case of sediment quality, tend to reflect local geological conditions.

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Table 5 Canadian Sediment Quality Guidelines for the Protection of Freshwater Aquatic Life

Parameter Units

[dry wt] Interim Sediment Quality

Guideline(a) Probable Effects Level

Total Metals

arsenic µg/g 5.9 17

cadmium µg/g 0.6 3.5

chromium µg/g 37.3 90

copper µg/g 35.7 197

lead µg/g 35 91.3

mercury µg/g 0.17 0.486

zinc µg/g 123 315

Polycyclic Aromatic Hydrocarbons

acenaphthene µg/g 0.00671 0.0889

acenaphthylene µg/g 0.00587 0.128

anthracene µg/g 0.0469 0.245

benzo(a)anthracene µg/g 0.0317 0.385

benzo(a)pyrene µg/g 0.0319 0.782

chrysene µg/g 0.0571 0.862

dibenzo(a,h)anthracene µg/g 0.00622 0.135

fluoranthene µg/g 0.111 2.355

fluorene µg/g 0.0212 0.144

2-methylnaphthalene µg/g 0.0202 0.201

naphthalene µg/g 0.0346 0.391

phenanthrene µg/g 0.0419 0.515

pyrene µg/g 0.053 0.875

(a) Guidelines from CCME (1999).

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3 RESULTS AND DISCUSSION

3.1 WATER QUALITY

Baseline water quality within and near the LSA, and for two large waterbodies upstream of the LSA that are of traditional importance to stakeholders, is described in the following sections. A summary of the water quality data for waterbodies and watercourses within the RSA is provided in Attachment D. This data provides a historical overview that is used for comparison with data collected specific to this study.

3.1.1 Namur Lake and Gardiner Lakes

Namur Lake and Gardiner Lakes are large waterbodies in the headwaters of the Ells River watershed located near the northernmost extent of the LSA. The available water quality sample analyses for selected parameters in these lakes are summarized in Tables 6 and 7; a summary including all available water quality parameters is provided in Attachment E.

Namur Lake and Gardiner Lakes had pH values that were generally near-neutral to slightly alkaline, with maximum laboratory pH measurements of 8.7 in water samples collected in summer. However, there was a single fall field pH measurement in Namur Lake which was unusually high, and may reflect a measurement error. Dissolved Oxygen (DO) levels were observed below the acute or chronic guideline ranges for the protection of aquatic life in both lakes in spring, suggesting oxygen depletion under ice prior to spring break-up, and in Namur Lake in fall, which may indicate oxygen depletion due to stratification in late summer.

Some seasonal concentrations of fluoride were above the chronic aquatic life guideline in Namur Lake and Gardiner Lakes, while concentrations of other ions with water quality guidelines were below respective guideline values in all samples. Concentrations of TP in these lakes were observed above the chronic guideline for the protection of aquatic life in all seasons, with more frequent exceedances observed in Gardiner Lakes during winter and summer. Total nitrogen (TN) concentrations were above the chronic guideline in both lakes in winter, spring and summer. Chlorophyll a concentrations in the lakes were generally higher in summer than in winter, although high concentrations were observed in winter. Based on observed concentrations of chlorophyll a and median concentrations of TP, Namur Lake is mesotrophic to meso-eutrophic. The Gardiner Lakes are potentially eutrophic based on TP concentrations, but are mesotrophic based on chlorophyll a concentrations.

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Table 6 Seasonal Water Quality Summary for Namur Lake

Parameter Units Winter (1977 to 2002) Spring (1977 to 2010) Summer (1972 to 2009) Fall (1972 to 2009)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Field Measured pH - - 6.5 6.7 2 7.4 - - 1 7.2 7.2 7.2 7 7.2 6.8 9.9(A,C,H) 4 Temperature °C 0 0 3.1 6 4 1 11.8 5 15 10.7 20 14 9 6 11 6 Dissolved oxygen mg/L 11 - - 1 10.6 3.4(A,C) 11 3 9 7.8 9.9 10 9.3 5.8(C) 9.7 4 Conventional Parameters Specific conductance µS/cm 64 59 89 10 52 43 84 6 60 43 72 23 56 46 70 8 Dissolved organic carbon mg/L 7 6 14 8 8 5 20 6 8 5 14 14 7 6 9 5 Hardness mg/L 25 21 29 6 20 20 20 6 23 23 23 9 22 22 22 5 pH - 6.9 6.8 7.4 10 7.1 6.8 7.3 6 7.3 6.9 8.2 23 7.3 6.5 7.8 8 Total alkalinity mg/L 23 20 34 10 18 16 19 6 22 18 31 22 21 20 26 8 Total dissolved solids mg/L 40 23 45 10 29 26 96 6 35 26 47 15 35 29 47 7 Total organic carbon mg/L 7 6 14 7 8 5 20 6 8 3 10 9 8 6 16 6 Total suspended solids mg/L 2 0.4 6 9 3 <0.4 134 6 2 <0.05 5 12 3 0.4 11 7 Major Ions Calcium mg/L 7 5 8 10 5 5 8 6 6 5 10 21 6 5 7 8 Chloride mg/L 0.4 0.1 1.5 10 0.9 0.2 2 6 0.5 0.1 5 23 0.4 0.1 1 8 Fluoride mg/L 0.07 0.06 0.1 6 0.06 0.03 0.08 4 0.05 <0.05 0.14(C) 8 0.08 0.07 0.12 5 Sulphate mg/L 7 5 8 10 6 4 16 6 7 6 15 22 6 4 8 7 Sulphide mg/L - - - 0 <0.002 - - 1 - - - 0 - - - 0 Nutrients and Biological Indicators Nitrate mg-N/L 0.076 0.051 0.093 4 - 0.02 <0.1 2 0.05 <0.003 0.193 7 0.03 0.006 <0.1 5 Nitrate + nitrite mg-N/L 0.051 <0.01 0.093 10 <0.015 0.004 <0.1 6 0.039 <0.001 0.193 14 0.04 0.006 <0.1 7 Nitrite mg-N/L <0.003 <0.001 <0.003 5 - <0.003 <0.05 2 <0.003 <0.001 <0.1(D>C) 10 <0.003 <0.003 <0.05 5 Nitrogen - ammonia mg-N/L 0.02 <0.001 0.15 12 0.045 <0.01 0.4 6 0.022 0.005 0.311 20 0.036 <0.01 0.2 8 Nitrogen - total mg-N/L 0.67 0.34 1.32(C) 11 0.78 0.54 2.1(C) 5 0.46 0.31 1.01(C) 16 0.47 0.28 0.81 7 Phosphorus - total mg-P/L 0.027 0.02 0.1(C) 12 0.035 0.013 0.17(C) 6 0.023 0.012 0.7(C) 19 0.028 0.017 0.2(C) 8 Chlorophyll a µg/L 2 0.8 14.47 5 - 2.9 7 2 3.32 1.56 12.85 9 5 - - 1 General Organics Naphthenic acids mg/L - - - 0 - <1 <1 2 - <1 <1 2 - <1 <1 2 Total phenolics mg/L 0.003(W) <0.001 0.008(C,W) 7 0.002 <0.001 0.008(C,W) 6 0.003(W) <0.001 0.15(C,W) 12 0.002 <0.001 0.027(C,W) 5 Total recoverable hydrocarbons mg/L <0.1 <0.1 1.2 4 1.6 <0.1 2.1 5 1 <0.1 23.6 5 1.3 - - 1 Total Metals Aluminum mg/L - - - 0 - 0.0091 7.3(A,C,H,W) 2 0.0097 0.0047 0.04 6 - 0.036 0.06 2 Antimony mg/L - - - 0 - 0.00006 <0.0004 2 0.000068 0.000064 <0.0004 6 - <0.0004 <0.0004 2 Arsenic mg/L 0.0003 - - 1 - 0.00031 0.0031 2 0.00036 0.00031 0.0005 7 - <0.0004 0.0006 2 Barium mg/L 0.018 - - 1 - 0.018 1.4(H) 2 0.019 0.019 0.02 7 - 0.019 0.023 2 Beryllium mg/L - - - 0 - <0.00001 <0.001 2 0.000006 0.000001 <0.001 6 - <0.001 <0.001 2 Boron mg/L - - - 0 - 0.02 0.54 2 0.025 0.022 <0.05 6 - <0.05 <0.05 2 Cadmium mg/L - - - 0 - 0.000011 <0.0002(D>C) 2 0.000008 0.000004 <0.002(D>A,C) 6 - <0.00005 <0.0002(D>C) 2 Chromium mg/L <0.001 - - 1 - <0.0001 0.012(C) 2 <0.0001 <0.00003 <0.005(D>C) 7 - <0.005(D>C) <0.005(D>C) 2 Cobalt mg/L <0.001 - - 1 - 0.00005 0.002 2 0.00003 0.00002 <0.002 7 - <0.002 <0.002 2 Copper mg/L <0.001 - - 1 - 0.0003 0.007(A,C) 2 0.0006 0.0003 <0.001 7 - <0.001 0.001 2 Iron mg/L 0.02 - - 1 - 0.11 6.7(C,H) 2 0.02 0.009 0.11 11 0.15 0.03 0.3 3 Lead mg/L - - - 0 - 0.000057 0.0033(C) 2 0.0001 0.00002 0.00029 6 - 0.00011 0.0002 2 Manganese mg/L <0.008 - - 1 - 0.019 0.15(H) 2 0.009 0.005 0.014 7 - 0.029 0.033 2 Mercury mg/L - - - 0 - 0.000003 0.00004(A,C) 2 <0.00002(D>A,C) <0.00002(D>A,C) <0.0001(D>A,C) 3 - <0.00002(D>A,C) <0.0001(D>A,C) 2 Methyl mercury µg/L - - - 0 <0.00003 - - 1 - - - 0 - - - 0 Nickel mg/L <0.001 - - 1 - 0.00052 0.008 2 0.00066 0.00058 <0.002 7 - <0.002 <0.002 2 Selenium mg/L <0.0002 - - 1 - 0.00006 0.0009 2 0.0002 0.00006 <0.0004 7 - <0.0004 0.0004 2 Silver mg/L - - - 0 - <0.000005 <0.0004(D>A,C) 2 <0.000001 <0.0000005 <0.0004(D>A,C) 6 - <0.0001 <0.0004(D>A,C) 2 Thallium mg/L - - - 0 - <0.000002 0.0001 2 0.000001 <0.0000003 <0.0001 6 - <0.0001 <0.0001 2 Uranium mg/L - - - 0 - 0.000011 0.0005 2 0.00001 0.00001 <0.0001 6 - <0.0001 <0.0001 2 Vanadium mg/L 0.002 0.001 0.003 3 - 0.0002 0.026 2 <0.001 0.00006 <0.002 11 0.008 <0.001 0.015 4

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Table 6 Seasonal Water Quality Summary for Namur Lake (continued)

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Parameter Units Winter (1977 to 2002) Spring (1977 to 2010) Summer (1972 to 2009) Fall (1972 to 2009)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Zinc mg/L 0.002 - - 1 - 0.0012 0.77(A,C) 2 0.0017 0.0004 0.0103 7 - 0.0051 0.007 2 PAHs and Alkylated PAHs Acenaphthene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 Anthracene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 Benzo(a)anthracene µg/L - - - 0 <0.01(D>H) - - 1 - <0.01(D>H) <0.01(D>H) 2 - <0.01(D>H) <0.01(D>H) 2 Benzo(a)pyrene µg/L - - - 0 <0.01(D>H) - - 1 - <0.01(D>H) <0.01(D>H) 2 - <0.01(D>H) <0.01(D>H) 2 Benzo(b)fluoranthene µg/L - - - 0 <0.01(D>H) - - 1 - <0.01(D>H) <0.01(D>H) 2 - <0.01(D>H) <0.01(D>H) 2 Benzo(k)fluoranthene µg/L - - - 0 <0.01(D>H) - - 1 - <0.01(D>H) <0.01(D>H) 2 - <0.01(D>H) <0.01(D>H) 2 Chrysene µg/L - - - 0 <0.01(D>H) - - 1 - <0.01(D>H) <0.01(D>H) 2 - <0.01(D>H) <0.01(D>H) 2 Dibenzo(a,h)anthracene µg/L - - - 0 <0.01(D>H) - - 1 - <0.01(D>H) <0.01(D>H) 2 - <0.01(D>H) <0.01(D>H) 2 Fluoranthene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 Fluorene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 Indeno(c,d-123)pyrene µg/L - - - 0 <0.01(D>H) - - 1 - <0.01(D>H) <0.01(D>H) 2 - <0.01(D>H) <0.01(D>H) 2 Naphthalene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 Phenanthrene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 0.014 2 Pyrene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2

- = Not applicable or no data.

Notes: Bolded concentrations are higher than relevant water quality guidelines. A = Concentration higher than the relevant acute aquatic life guideline or beyond the recommended pH or DO concentration range.

C = Concentration higher than the relevant chronic aquatic life guideline or beyond the recommended pH or DO concentration range.

H = Concentration higher than the relevant human health guideline or beyond the recommended pH range.

W = Concentration higher than the relevant wildlife health guideline.

D> = Analytical detection limit was higher than the relevant water quality guideline(s).

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Table 7 Seasonal Water Quality Summary for Gardiner Lakes

Parameter Units Winter (1977 to 1988) Spring (1977 to 1978) Summer (1972 to 1993) Fall (1972 to 1977)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Field Measured pH - 6.7 - - 1 7.4 - - 1 8 7.6 8.3 4 - - - 0 Temperature °C 0 0 4 7 3 0 15 6 16 14 20 9 - 6 11 2 Dissolved oxygen mg/L 10.4 - - 1 6.5 5.3(C) 13 3 8.9 8.3 9.3 5 - - - 0 Conventional Parameters Specific conductance µS/cm 142 127 250 9 84 34 223 6 115 104 130 9 110 110 118 3 Dissolved organic carbon mg/L 14 8 21 9 9 2 32 6 11 10 15 4 - 9 13 2 Hardness mg/L 66 59 122 9 43 13 121 6 57 54 77 7 58 53 63 3 pH - 7.3 7 7.8 9 7.3 6.9 7.4 6 7.9 7.5 8.7(A,C) 9 7.7 7.5 7.9 3 Total alkalinity mg/L 60 56 122 9 40 14 122 6 54 49 71 9 56 50 61 3 Total dissolved solids mg/L 89 76 150 9 55 22 150 6 67 61 75 5 - 72 74 2 Total organic carbon mg/L 13 8 21 8 10 2 33 6 12 10 13 3 - 10 17 2 Total suspended solids mg/L 4 2 19 8 3 <0.4 23 6 5 0.8 8 3 - 2 5 2 Major Ions Calcium mg/L 18 16 33 9 11 4 32 6 16 7 17 7 15 15 17 3 Chloride mg/L 0.6 0.5 2.1 9 0.6 0.2 1.2 6 1 0.4 5 9 0.6 0.4 1 3 Fluoride mg/L 0.11 0.08 0.16(C) 9 0.1 0.05 0.27(C) 6 0.08 <0.05 0.15(C) 8 0.1 <0.05 0.1 3 Sulphate mg/L 7 5 9 9 5 0.5 8 6 7 4 25 7 7 5 15 3 Sulphide mg/L - - - 0 - - - 0 - - - 0 - - - 0 Nutrients and Biological Indicators Nitrate mg-N/L - 0.062 0.063 2 - - - 0 - - - 0 - - - 0 Nitrate + nitrite mg-N/L 0.11 0.05 0.24 9 0.053 <0.01 0.31 6 <0.1 0.002 0.43 9 0.067 0.058 <0.1 3 Nitrite mg-N/L 0.003 0.002 0.003 3 0.003 - - 1 <0.1(D>C) 0.002 <0.1(D>C) 5 0.014 - - 1 Nitrogen - ammonia mg-N/L 0.01 <0.01 1.04 9 0.03 <0.01 0.12 6 0.13 <0.01 1.3 8 0.03 <0.01 0.3 3 Nitrogen - total mg-N/L 1.22(C) 0.69 4.56(C) 9 1.2(C) 0.96 2.69(C) 6 0.73 0.58 2.02(C) 5 - 0.94 1 2 Phosphorus - total mg-P/L 0.1(C) 0.036 0.38(C) 10 0.047 0.02 0.16(C) 6 0.051(C) 0.03 0.7(C) 10 0.046 0.042 0.2(C) 3 Chlorophyll a µg/L 0.9 0.8 33 4 - 1 2 2 10 6 10.8 5 - - - 0 General Organics Naphthenic acids mg/L - - - 0 - - - 0 - - - 0 - - - 0 Total phenolics mg/L 0.003(W) <0.001 0.007(C,W) 7 <0.001 <0.001 0.001 4 0.003(W) <0.001 0.011(C,W) 8 0.002 - - 1 Total recoverable hydrocarbons mg/L <0.1 <0.1 1.4 6 0.4 <0.1 1 4 1.9 0.5 127 7 - 0.5 1.9 2 Total Metals Arsenic mg/L 0.0008 - - 1 - - - 0 0.0008 - - 1 - - - 0 Barium mg/L 0.025 - - 1 - - - 0 0.027 - - 1 - - - 0 Chromium mg/L <0.001 - - 1 - - - 0 <0.001 - - 1 - - - 0 Cobalt mg/L <0.001 - - 1 - - - 0 <0.001 - - 1 - - - 0 Copper mg/L <0.001 - - 1 - - - 0 <0.001 - - 1 - - - 0 Iron mg/L - - - 0 - - - 0 0.288 - - 1 - - - 0 Manganese mg/L <0.008 - - 1 - - - 0 0.102(H) - - 1 - - - 0 Nickel mg/L 0.002 - - 1 - - - 0 0.002 - - 1 - - - 0 Selenium mg/L <0.0002 - - 1 - - - 0 <0.0002 - - 1 - - - 0 Vanadium mg/L <0.002 - - 1 - - - 0 <0.002 - - 1 - - - 0 Zinc mg/L 0.002 - - 1 - - - 0 <0.001 - - 1 - - - 0

- = Not applicable or no data.

Notes: Bolded concentrations are higher than relevant water quality guidelines. A

= Concentration higher than the relevant acute aquatic life guideline or beyond the recommended pH range. C

= Concentration higher than the relevant chronic aquatic life guideline or beyond the recommended pH or DO concentration range. H = Concentration higher than the relevant human health guideline.

W = Concentration higher than the relevant wildlife health guideline.

D> = Analytical detection limit was higher than the relevant water quality guideline(s).

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Naphthenic acids concentrations were non-detectable in Namur Lake samples and were not analyzed in Gardiner Lakes samples. Total phenolics concentrations in Gardiner Lakes were above wildlife health or chronic aquatic guidelines in winter, spring and summer, and in all seasons in Namur Lake, with the highest concentrations observed in summer. Total aluminum, barium, chromium, copper, iron, lead, manganese, mercury and zinc were above one or more water quality guidelines in a sample collected during spring in Namur Lake, which is likely related to inputs of suspended sediments during spring freshet. Of the limited metals data available for Gardiner Lakes, total manganese was measured at a concentration above the human health guideline in one sample collected during summer. With one exception, concentrations of PAHs in Namur Lake samples were below detection limits. A single detectable concentration of phenanthrene was below the water quality guideline in a sample collected in fall.

3.1.2 Small Waterbodies Within and Near the Local Study Area

A summary of available water quality sample analyses for selected parameters are provided in Table 8 for other small waterbodies within and near the LSA; a summary including all available water quality parameters is provided in Attachment E.

Smaller waterbodies within and near the LSA vary from slightly acidic to alkaline, with field measured minimum and maximum pH values outside water quality guideline ranges. Concentrations of DO were observed below acute and chronic guidelines for the protection of aquatic life in winter and summer, suggesting oxygen depletion under ice in winter and high sediment oxygen demand in some waterbodies in summer.

Observed concentrations of fluoride and sulphide were often above the chronic aquatic life guideline, while concentrations of other ions with water quality guidelines were below respective guideline values in all samples. Concentrations of TP and TN were observed above the chronic guideline for the protection of aquatic life in all seasons. Observed chlorophyll a concentrations were higher in summer than in spring and winter. Based on observed concentrations of chlorophyll a and TP, most of these small waterbodies are eutrophic.

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Table 8 Seasonal Water Quality Summary for Other Waterbodies Within and Near the Local Study Area

Parameter Units Winter (1989 to 2010) Spring (2008 to 2010) Summer (1977 to 2009) Fall (2008 to 2009)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Field Measured pH - 7.1 6.5 8.5 10 7.8 7 10(A,C,H) 9 7.9 6.5(A,C) 10(A,C,H) 12 7.3 6.9 8 6 Temperature °C 1.5 0.1 4.6 11 12.7 7.6 14.1 10 19.6 12.6 21.3 21 7.9 6 9.2 10 Dissolved oxygen mg/L 2.4(A,C) 0(A,C) 7.5 11 10.1 9.6 12.9 10 6.1(C) 0.7(A,C) 14.1 21 10 7.2 12.3 10 Conventional Parameters Specific conductance µS/cm 222 110 500 11 171 46 270 10 170 46 273 21 160 46 300 10 Dissolved organic carbon mg/L 34 15 50 11 23 18 38 10 30 13 49 21 27 20 48 10 Hardness mg/L 97 53 247 11 78 25 121 10 79 30 121 21 69 24 130 10 pH - 7.5 6.9 8 11 7.8 7 8.1 10 7.9 6.9 9.7(A,C,H) 21 7.9 7.1 8.1 10 Total alkalinity mg/L 105 49 200 11 85 16 103 10 75 16 118 21 75 15 123 10 Total dissolved solids mg/L 169 81 360 11 93 21 190 10 133 21 190 21 95 19 164 10 Total organic carbon mg/L 41 27 54 6 22 17 42 10 33 11 50 20 27 18 50 10 Total suspended solids mg/L 9 <3 18 6 8 3 29 10 5 <3 23 20 5 <3 9 10 Major Ions Calcium mg/L 27 14 72 11 20 7 34 10 21 8 33 21 17 6 35 10 Chloride mg/L 1 <0.5 3 11 1 <1 2 10 1 <0.5 2 21 <1 <0.5 3 10 Fluoride mg/L 0.13(C) 0.1 0.16(C) 5 - - - 0 0.13(C) 0.1 0.15(C) 2 - - - 0 Sulphate mg/L 17 <1 87 11 6 <1 38 10 8 0.7 42 21 8 2 44 10 Sulphide mg/L 0.044(C) 0.008(C) 0.076(C) 3 0.013(C) 0.008 0.02(C) 4 0.012(C) <0.002 0.039(C) 9 - - - 0 Nutrients and Biological Indicators Nitrate mg-N/L 0.135 0.03 1.2 6 <0.1 <0.003 <0.1 10 <0.1 <0.05 <0.1 10 <0.1 <0.05 0.2 10 Nitrate + nitrite mg-N/L 0.1 0.006 0.48 11 <0.1 <0.003 <0.1 10 <0.1 <0.003 <0.1 21 <0.1 <0.071 0.2 10 Nitrite mg-N/L <0.003 0.002 <0.05 11 <0.05 <0.003 <0.05 10 <0.05 <0.001 <0.05 11 <0.05 <0.05 <0.05 10 Nitrogen - ammonia mg-N/L 0.43 0.016 1.39 11 <0.05 <0.05 0.73 10 <0.05 0.012 0.55 21 <0.05 <0.05 0.2 10 Nitrogen - total mg-N/L 1.98(C) 0.94 4.3(C) 11 1.55(C) 0.83 3.7(C) 10 1.6(C) 1.2(C) 3.3(C) 21 1.5(C) 1.12(C) 2.2(C) 10 Phosphorus - total mg-P/L 0.09(C) 0.019 0.37(C) 11 0.06(C) 0.02 0.21(C) 10 0.058(C) 0.024 1.32(C) 18 0.05 0.028 0.09(C) 10 Chlorophyll a µg/L 2.1 0.2 3.6 5 10.1 7 42 4 - 54.1 71.2 2 - - - 0 General Organics Naphthenic acids mg/L <1 <1 1 6 <1 <1 <1 7 <1 <1 1 16 <1 <1 1.4 7 Total phenolics mg/L 0.01(C,W) <0.002 0.022(C,W) 11 0.004(W) <0.002 0.011(C,W) 7 0.01(C,W) 0.002 0.019(C,W) 18 0.008(C,W) <0.001 0.014(C,W) 7 Total recoverable hydrocarbons mg/L <2 <2 <2 3 <2 <2 <2 4 <1 <1 1.6 10 - - - 0 Total Metals Aluminum mg/L 0.01 <0.002 0.199(C,H) 11 0.0395 0.0033 0.14(C,H) 7 0.014 0.0073 0.103(C,H) 16 0.033 <0.01 0.07 7 Antimony mg/L 0.00028 0.00005 <0.0004 6 <0.00007 <0.00002 <0.0004 7 0.000045 0.00002 0.00084 16 <0.0004 <0.0004 <0.0004 7 Arsenic mg/L 0.0008 0.0004 0.0057(C) 11 0.0005 0.00028 0.0016 7 0.00069 <0.0004 0.00228 17 0.0006 <0.0004 0.0163(C,H) 7 Barium mg/L 0.036 0.021 0.052 11 0.024 0.01 0.027 7 0.022 0.014 0.051 17 0.019 0.012 0.033 7 Beryllium mg/L 0.000515 0.00001 <0.001 6 <0.00001 <0.00001 <0.001 7 <0.000012 <0.001 <0.001 16 <0.001 <0.001 <0.001 7 Boron mg/L 0.08 <0.02 0.14 6 0.05 <0.02 0.07 7 0.05 0.04 0.145 16 0.05 <0.05 0.1 7 Cadmium mg/L 0.000162 0.000039 <0.0002 6 <0.000021 <0.000005 <0.0002 7 0.000008 <0.000002 <0.002(D>A,C) 16 <0.00005 <0.00005 <0.0002 7 Chromium(a) mg/L 0.0026(C) 0.001 <0.005(D>C) 11 <0.0001 <0.0001 <0.005(D>C) 7 <0.0002 <0.00004 <0.005(D>C) 17 <0.005(D>C) <0.005(D>C) <0.005(D>C) 7 Cobalt mg/L <0.001 0.00022 0.002 11 0.00015 0.00004 <0.002 7 0.0001 0.00004 <0.002 17 <0.002 <0.002 <0.002 7 Copper mg/L 0.0011 0.0007 0.007(C) 11 0.0006 0.00006 0.001 7 <0.001 <0.00005 0.0091(C) 17 <0.001 <0.001 <0.001 7 Iron mg/L 0.65(C,H) 0.02 4.48(C,H) 11 0.39(C,H) 0.07 0.81(C,H) 7 0.27 0.02 0.89(C,H) 17 0.29 0.03 0.89(C,H) 7 Lead mg/L 0.00017 <0.0001 0.00149 6 0.0001 0.00006 0.00057 7 0.00007 0.000003 0.00039 16 <0.0001 <0.0001 0.0001 7 Manganese mg/L 0.303(H) 0.007 0.746(H) 11 0.046 0.009 0.304(H) 7 0.042 0.008 0.118(H) 17 0.023 0.014 0.044 7 Mercury mg/L <0.0001(D>A,C) 0.000002 <0.0002(D>A,C) 6 0.000006(C) 0.000003 <0.0002(D>A,C) 7 <0.0000007 <0.0000006 <0.0001(D>A,C) 16 <0.0001(D>A,C) <0.00002(D>A,C) <0.0001(D>A,C) 7 Methyl mercury µg/L <0.00003 <0.00003 0.00041 3 0.00006 0.00003 0.0002 4 - - - 0 - - - 0 Nickel mg/L <0.002 <0.001 0.003 11 0.00107 0.00017 <0.002 7 0.00046 <0.000005 0.0023 17 <0.002 <0.002 <0.002 7 Selenium mg/L <0.00011 <0.0001 0.0007 11 <0.00009 <0.00004 <0.0004 7 <0.0001 <0.0001 <0.0004 17 <0.0004 <0.0004 <0.0004 7 Silver mg/L <0.0002(D>C) <0.000005 <0.0004(D>C) 6 <0.000005 <0.000005 <0.0004(D>C) 7 0.000004 0.0000007 <0.0004(D>C) 16 <0.0004(D>C) <0.0001 0.00048(C) 7 Thallium mg/L <0.00005 <0.000002 <0.0001 6 <0.000003 <0.000002 <0.0001 7 0.000002 0.0000005 <0.0001 16 <0.0001 <0.0001 <0.0001 7 Uranium mg/L 0.0001 0.00003 0.00081 6 0.0001 0.000007 0.00035 7 0.0001 0.00001 0.00134 16 <0.0001 <0.0001 0.00033 7 Vanadium mg/L <0.001 <0.0002 0.004 11 <0.0005 <0.0002 <0.001 7 0.00041 0.0001 0.003 17 <0.001 <0.001 <0.001 7

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Dover Commercial Project - 23 - Water Quality Baseline Report December 2010

Table 8 Seasonal Water Quality Summary for Other Waterbodies Within and Near the Local Study Area (continued)

Golder Associates

Parameter Units Winter (1989 to 2010) Spring (2008 to 2010) Summer (1977 to 2009) Fall (2008 to 2009)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Zinc mg/L 0.011 0.005 0.045(C) 11 0.0028 0.0012 0.028 7 0.0033 <0.0001 0.007 17 <0.004 <0.004 0.009 7 PAHs and Alkylated PAHs Acenaphthene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10(D>C) 7 <0.01 <0.01 <0.01 7 Anthracene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10(D>C) 7 <0.01 <0.01 <0.01 7 Benzo(a)anthracene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <10(D>C,H) 7 <0.01(D>H) <0.01(D>H) <0.01(D>H) 7 Benzo(a)pyrene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <10(D>C,H) 7 <0.01(D>H) <0.01(D>H) <0.01(D>H) 7 Benzo(b)fluoranthene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <10(D>H) <10(D>H) <10(D>H) 3 <0.01(D>H) <0.01(D>H) <10(D>H) 7 <0.01(D>H) <0.01(D>H) <0.01(D>H) 7 Benzo(k)fluoranthene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <10(D>H) 7 <0.01(D>H) <0.01(D>H) <0.01(D>H) 7 Chrysene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <10(D>H) 7 <0.01(D>H) <0.01(D>H) <0.01(D>H) 7 Dibenzo(a,h)anthracene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <10(D>H) 7 <0.01(D>H) <0.01(D>H) <0.01(D>H) 7 Fluoranthene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10(D>C) 7 <0.01 <0.01 <0.01 7 Fluorene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10(D>C) 7 <0.01 <0.01 <0.01 7 Indeno(c,d-123)pyrene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <0.01(D>H) 3 <0.01(D>H) <0.01(D>H) <10(D>H) 7 <0.01(D>H) <0.01(D>H) <0.01(D>H) 7 Naphthalene µg/L 0.03 <0.01 0.05 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10(D>C) 7 <0.01 <0.01 0.014 7 Phenanthrene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.029 <0.01 <10(D>C) 7 <0.01 <0.01 0.02 7 Pyrene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10(D>C) 7 <0.01 <0.01 <0.01 7

(a) Chromium results for samples collected in winter 2010 are suspect due to irregularities found in QC samples. Refer to Attachment C for additional information.

- = Not applicable or no data.

Notes: Bolded concentrations are higher than relevant water quality guidelines. A = Concentration higher than the relevant acute aquatic life guideline or beyond the recommended pH or DO concentration range.

C = Concentration higher than the relevant chronic aquatic life guideline or beyond the recommended pH or DO concentration range.

H = Concentration higher than the relevant human health guideline or beyond the recommended pH range.

W = Concentration higher than the relevant wildlife health guideline.

D> = Analytical detection limit was higher than the relevant water quality guideline(s).

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Dover Commercial Project - 24 - Water Quality Baseline Report December 2010

Golder Associates

Naphthenic acids concentrations were non-detectable in 24 of 27 samples and total phenolics concentrations were often above wildlife health or chronic aquatic guidelines in all seasons. Total aluminum, arsenic, chromium, copper, iron, manganese, mercury, silver and zinc were observed to be above one or more water quality guidelines in at least one season, and guideline exceedances appear to be more frequent in winter and spring than in summer and fall. However, the concentration associated with the chromium exceedance may have been a result of sample contamination and may not be representative of baseline conditions. Concentrations of PAHs were generally below detection limits, and detectable PAH concentrations were below water quality guideline values.

3.1.3 Ells River

Available water quality sample analyses for selected parameters for the Ells River within and near the LSA are summarized in Table 9. A summary including all available water quality parameters is provided in Attachment E.

The Ells River varies from slightly acidic to alkaline, with field-measured minimum and maximum pH values commonly outside water quality guideline ranges (Table 9). River water is generally well oxygenated, although DO levels were observed below acute or chronic guidelines for the protection of aquatic life in winter, spring and summer.

Observed seasonal maximum concentrations of fluoride were occasionally above the chronic aquatic life guideline, while concentrations of other ions with water quality guidelines were below respective guideline values in all samples. Maximum concentrations of TN were observed above the chronic guideline for the protection of aquatic life in all seasons, while TP concentrations were observed above the same chronic guideline in winter, spring and fall. Chlorophyll a concentrations were low, although data are limited. Based on observed concentrations of TP, the Ells River appears to be mesotrophic near the LSA.

Naphthenic acids concentrations were non-detectable in all samples and total phenolics concentrations were observed above wildlife health and chronic aquatic guidelines in all seasons. Total aluminum, chromium, iron, manganese and zinc were observed above one or more water quality guidelines in at least one season. However, the concentration associated with the chromium exceedance may have been a result of sample contamination and may not be representative of baseline conditions. Guideline exceedances generally appear to be more frequent in spring than in other seasons, likely reflecting suspended sediment input during spring freshet. Concentrations of PAHs were below detection limits in all Ells River samples.

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Golder Associates

Table 9 Seasonal Water Quality Summary for the Ells River Within and Near the Local Study Area

Parameter Units Winter (1976 to 2010) Spring (1977 to 2010) Summer (1977 to 2009) Fall (1976 to 2009)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Field Measured pH - 7.1 6.6 7.9 7 7.2 6.4(A,C) 8.7(A,C) 5 7.5 6(A,C) 8.5(A,C) 6 7.9 5.6(A,C) 8.3 5 Temperature °C 0 0 1 13 8.2 0 17.5 9 15.7 9.3 20.8 12 6.4 3 11 9 Dissolved oxygen mg/L 8 5.5(C) 12.9 6 10.4 2(A,C) 13.4 8 9.4 6.4(C) 10.9 7 12.8 11.7 14.3 5 Conventional Parameters Specific conductance µS/cm 146 115 400 15 134 70 145 9 123 96 177 12 131 90 186 10 Dissolved organic carbon mg/L 12 8 17 16 12 7 25 9 13 10 18 12 14 10 15 10 Hardness mg/L 70 61 111 11 60 39 66 9 61 51 83 11 63 55 84 8 pH - 7.3 7.1 7.9 15 7.7 6.9 8 9 7.8 7.2 8.3 12 7.7 7.3 8 10 Total alkalinity mg/L 66 56 212 15 60 38 65 9 61 50 78 12 59 48 88 10 Total dissolved solids mg/L 93 75 264 15 73 46 130 9 71 58 128 12 77 59 113 10 Total organic carbon mg/L 12 8 20 14 14 7 25 9 14 11 18 10 14 10 16 9 Total suspended solids mg/L 3 0.8 86 15 10 2 70 9 3 1 26 12 4 1 17 10 Major Ions Calcium mg/L 18 15 50 14 16 10 18 9 15 13 22 10 16 14 23 9 Chloride mg/L 0.7 0.4 5.4 15 1 0.3 2 9 1 0.3 1.8 12 0.8 0.3 1.8 10 Fluoride mg/L 0.09 <0.05 0.13(C) 13 0.09 0.07 0.1 4 0.1 0.05 0.14(C) 8 0.1 <0.05 0.11 6 Sulphate mg/L 7 3 16 15 7 4 11 9 6 4 10 12 8 5 13 10 Sulphide mg/L <0.01(D>C) <0.001 <0.01(D>C) 7 0.003 - - 1 <0.003 <0.001 <0.01(D>C) 4 <0.01 0.002 <0.01 3 Nutrients and Biological Indicators Nitrate mg-N/L 0.133 0.066 1.4 6 <0.1 0.02 <0.1 6 <0.1 0.008 <0.1 5 <0.1 <0.05 <0.1 4 Nitrate + nitrite mg-N/L 0.17 0.046 0.4 15 <0.1 0.005 0.102 9 0.012 <0.003 <0.1 12 0.064 0.003 0.122 10 Nitrite mg-N/L 0.003 0.002 <0.05 7 <0.05 <0.003 <0.05 6 <0.027 <0.001 <0.05 8 <0.05 0.005 <0.05 6 Nitrogen – ammonia mg-N/L 0.05 0.02 0.13 16 <0.05 0.01 0.06 9 0.043 0.007 0.11 12 <0.05 0.02 0.08 8 Nitrogen – total mg-N/L 0.84 0.28 7.99(C) 15 0.89 0.55 1.2(C) 9 0.77 0.5 1.14(C) 12 0.7 0.13 1.1(C) 10 Phosphorus – total mg-P/L 0.042 0.03 1.08(C) 15 0.06(C) 0.019 0.08(C) 9 0.038 0.031 0.05 11 0.037 0.023 0.07(C) 10 Chlorophyll a µg/L - <1 <1 2 - - - 0 - - - 0 2 - - 1 General Organics Naphthenic acids mg/L - <1 <1 2 <1 <1 <1 5 <1 <1 <1 3 <1 <1 <1 4 Total phenolics mg/L <0.002 <0.001 0.02(C,W) 9 0.005(C,W) <0.001 0.007(C,W) 7 <0.001 <0.001 0.007(C,W) 8 <0.001 <0.001 0.004(W) 7 Total recoverable hydrocarbons

mg/L <0.4 <0.1 <2 8 <0.3 <0.1 <2 3 0.5 <0.1 0.9 6 0.5 <0.1 1 3

Total Metals Aluminum mg/L 0.0309 <0.01 0.0594 4 0.28(C,H) 0.0352 0.7(C,H) 5 0.05 0.015 0.08 6 0.0288 0.02 0.07 5 Antimony mg/L 0.000061 0.000047 <0.0004 4 <0.0004 0.00005 <0.0004 5 0.0004 0.000049 0.0025 6 <0.0004 0.000073 <0.0004 5 Arsenic mg/L 0.00066 0.0006 0.00071 4 0.0009 0.00067 0.0012 5 0.001 0.0007 0.0011 6 0.0008 0.00068 0.001 5 Barium mg/L 0.04 0.034 0.047 4 0.033 0.03 0.039 5 0.028 0.024 0.032 6 0.028 0.027 0.033 5 Beryllium mg/L 0.000065 <0.00001 <0.001 4 <0.001 <0.00001 <0.001 5 <0.001 <0.00004 <0.001 6 <0.001 0.000081 <0.001 5 Boron mg/L 0.038 0.024 <0.05 4 <0.05 0.03 <0.05 5 <0.05 0.022 <0.05 6 <0.05 0.022 0.05 5 Cadmium mg/L <0.00002 <0.000005 <0.0002 4 <0.0002(D>C) 0.00001 <0.0002(D>C) 5 <0.001(D>C) <0.00002 <0.002(D>A,C) 6 <0.0002(D>C) <0.00002 <0.0002(D>C) 5 Chromium(a) mg/L 0.0011(C) 0.0001 <0.005(D>C) 4 <0.005(D>C) <0.0001 <0.005(D>C) 5 <0.005(D>C) <0.0001 <0.005(D>C) 6 <0.005(D>C) <0.0001 <0.005(D>C) 5 Cobalt mg/L 0.00011 0.0001 <0.002 4 <0.002 0.0001 <0.002 5 <0.002 0.00009 <0.002 6 <0.002 0.00011 <0.002 5 Copper mg/L 0.0006 <0.00008 <0.001 4 0.001 0.0005 0.002 5 <0.001 0.0004 <0.001 6 0.001 0.0005 0.002 5 Iron mg/L 0.26 0.06 0.5(C,H) 4 0.51(C,H) 0.27 1.57(C,H) 5 0.36(C,H) 0.25 0.53(C,H) 6 0.36(C,H) 0.18 0.69(C,H) 5 Lead mg/L 0.00006 <0.00001 <0.0001 4 0.0002 <0.0001 0.0008 5 0.0001 <0.00001 0.0002 6 0.0001 0.00004 0.0003 5 Manganese mg/L 0.026 0.014 0.057(H) 4 0.069(H) 0.029 0.073(H) 5 0.036 0.025 0.051(H) 6 0.025 0.018 0.043 5 Mercury mg/L <0.000005 0.000003 <0.0002(D>A,C) 3 <0.00002(D>A,C) 0.000003 <0.0002(D>A,C) 5 <0.00002(D>A,C) <0.00002(D>A,C) <0.0001(D>A,C) 4 <0.00002(D>A,C) <0.00002(D>A,C) <0.0001(D>A,C) 4 Methyl mercury µg/L <0.00003 - - 1 0.00005 - - 1 - - - 0 - - - 0 Nickel mg/L 0.00092 0.00034 <0.002 4 <0.002 0.00075 0.003 5 <0.002 0.0006 <0.002 6 <0.002 0.00062 0.002 5 Selenium mg/L 0.00045 0.00009 0.0008 4 <0.0004 0.00007 <0.0004 5 <0.0004 <0.0004 <0.0005 6 <0.0004 <0.0004 <0.0005 5 Silver mg/L <0.000005 <0.000005 <0.0004(D>C) 3 <0.0004(D>C) <0.000005 <0.0004(D>C) 5 <0.0004(D>C) 0.00014(C) <0.0004(D>C) 4 <0.0004(D>C) <0.0001 <0.0004(D>C) 4 Thallium mg/L 0.000003 0.000002 <0.0001 4 <0.0001 <0.000002 <0.0001 5 <0.0001 <0.000003 <0.0001 6 <0.0001 <0.000003 <0.0001 5 Uranium mg/L 0.0001 0.00006 0.00014 4 0.0001 0.00009 0.0002 5 <0.0001 0.00005 <0.0001 6 <0.0001 0.00006 0.0002 5

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Table 9 Seasonal Water Quality Summary for the Ells River Near the Local Study Area (continued)

Golder Associates

Parameter Units Winter (1976 to 2010) Spring (1977 to 2010) Summer (1977 to 2009) Fall (1976 to 2009)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Vanadium mg/L 0.00028 <0.0002 <0.001 4 <0.001 <0.0002 0.002 5 0.001 0.00024 0.05 6 <0.001 0.00022 <0.001 5 Zinc mg/L 0.0028 0.0016 0.018 4 0.019 0.0013 0.058(C) 5 0.004 0.001 0.005 6 <0.004 <0.004 0.011 5 PAHs and Alkylated PAHs Acenaphthene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 Anthracene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 Benzo(a)anthracene µg/L <0.01(D>H) - - 1 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 Benzo(a)pyrene µg/L <0.01(D>H) - - 1 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 Benzo(b)fluoranthene µg/L <0.01(D>H) - - 1 <10(D>H) <10(D>H) <10(D>H) 4 <5(D>H) <0.01(D>H) <10(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 Benzo(k)fluoranthene µg/L <0.01(D>H) - - 1 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 Chrysene µg/L <0.01(D>H) - - 1 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 Dibenzo(a,h)anthracene µg/L <0.01(D>H) - - 1 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 Fluoranthene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 Fluorene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 Indeno(c,d-123)pyrene µg/L <0.01(D>H) - - 1 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 <0.01(D>H) <0.01(D>H) <0.01(D>H) 4 Naphthalene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 Phenanthrene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 Pyrene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4

(a) Chromium results for samples collected in winter 2010 are suspect due to irregularities found in QC samples. Refer to Attachment C for additional information.

- = Not applicable or no data.

Notes: Bolded concentrations are higher than relevant water quality guidelines. A = Concentration higher than the relevant acute aquatic life guideline or beyond the recommended pH or DO concentration range.

C = Concentration higher than the relevant chronic aquatic life guideline or beyond the recommended pH or DO concentration range.

H = Concentration higher than the relevant human health guideline.

W = Concentration higher than the relevant wildlife health guideline.

D> = Analytical detection limit was higher than the relevant water quality guideline(s).

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3.1.4 Other Watercourses Within and Near the Local Study Area

Available water quality sample analyses for selected parameters in other watercourses within and near the LSA are summarized in Table 10; a summary including all available water quality parameters is provided in Attachment E.

Other watercourses within and near the LSA vary from slightly acidic to slightly alkaline, with field-measured minimum pH values below water quality guideline ranges in winter and summer (Table 10). These waters are generally well oxygenated, although DO levels were observed below acute and chronic guidelines for the protection of aquatic life in all seasons.

The limited amount of available sulphide concentrations were all above the chronic aquatic life guideline, while concentrations of other ions with water quality guidelines were below respective guideline values in all samples. Concentrations of TP and TN were observed above the chronic guideline for the protection of aquatic life in all seasons. Based on observed concentrations of TP, most of these smaller watercourses appear to be eutrophic.

Naphthenic acids concentrations were non-detectable in 44 of 49 samples and total phenolics concentrations were often above wildlife health and chronic aquatic guidelines in all seasons. Total aluminum, chromium, copper, iron, manganese, selenium and zinc were observed above one or more water quality guidelines in at least one season. However, the concentration associated with the chromium exceedance may have been a result of sample contamination and may not be representative of baseline conditions. Guideline exceedances by metals are generally more frequent in winter and spring than in summer and fall, with the exception of total iron which is elevated year-round. Concentrations of PAHs were generally below detection limits, and detectable PAH concentrations were below water quality guideline values.

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Table 10 Seasonal Water Quality Summary for Other Watercourses Within and Near the Local Study Area

Parameter Units Winter (2008 to 2010) Spring (2008 to 2010) Summer (2008 to 2009) Fall (2008 to 2009)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Field Measured pH - 6.7 5.9(A,C) 7.5 5 7.5 7.1 7.7 14 7.4 5.6(A,C) 7.9 14 7.6 7.1 8.1 15 Temperature °C 0.1 0 0.3 6 9.1 7.4 16.1 14 14.9 5.3 20.4 22 5 1.3 10.1 16 Dissolved oxygen mg/L 8.6 4.8(A,C) 11.7 6 9.7 4(A,C) 10.6 14 6.9 0.9(A,C) 10.9 22 9.5 4.5(A,C) 12.8 16 Conventional Parameters Specific conductance µS/cm 524 200 833 6 160 124 410 13 218 65 452 22 286 193 488 16 Dissolved organic carbon mg/L 27 16 47 6 30 18 39 13 37 21 47 22 34 15 41 16 Hardness mg/L 217 89 262 6 66 51 182 13 97 37 188 22 113 81 230 16 pH - 8 7.5 8.1 6 7.8 7.6 7.9 13 7.9 6.9 8.2 22 8 7.7 8.2 16 Total alkalinity mg/L 242 89 404 6 74 46 180 13 94 24 236 22 131 90 266 16 Total dissolved solids mg/L 302 180 477 6 89 70 310 13 133 85 370 22 159 106 276 16 Total organic carbon mg/L 28 16 47 6 30 18 40 13 36 20 48 21 35 15 49 16 Total suspended solids mg/L 9 <3 11 6 8 2 55 13 7 <3 42 22 6 <3 53 16 Major Ions Calcium mg/L 56 24 70 6 17 13 51 13 26 9 46 22 29 20 61 16 Chloride mg/L 2 2 3 6 2 2 4 13 2 <0.5 2 22 2 <0.5 3 16 Sulphate mg/L 33 6 52 6 14 4 49 13 13 3 98 22 17 4 50 16 Sulphide mg/L 0.037(C) - - 1 0.037(C) 0.01(C) 0.074(C) 3 0.032(c) 0.006(C) 0.185(C) 8 - - - 0 Nutrients and Biological Indicators Nitrate mg/L 0.3 0.02 0.8 6 <0.1 <0.003 <0.1 13 <0.1 <0.05 <0.1 14 <0.1 <0.05 <0.1 16 Nitrate + nitrite mg-N/L 0.3 0.005 0.8 6 <0.1 <0.003 0.1 13 <0.1 <0.071 <0.1 22 <0.1 <0.071 <0.1 16 Nitrite mg-N/L <0.05 <0.003 <0.05 6 <0.05 <0.003 <0.05 13 <0.05 <0.05 <0.05 14 <0.05 <0.05 <0.05 16 Nitrogen – ammonia mg-N/L 0.28 0.11 0.79 6 <0.05 <0.05 0.44 13 <0.05 <0.05 0.33 22 <0.05 <0.05 0.124 16 Nitrogen – total mg-N/L 1.6(C) 1.3(C) 2.71(C) 6 1.7(C) 0.79 4(C) 13 1.2(C) 0.6 2.2(C) 22 1.15(C) 0.69 3.89(C) 16 Phosphorus – total mg-N/L 0.155(C) 0.1(C) 0.17(C) 6 0.07(C) 0.04 0.2(C) 13 0.11(C) 0.019 0.17(C) 18 0.086(C) 0.04 0.595(C) 14 Chlorophyll a mg-P/L - - - 0 - - - 0 <2 <2 3 8 - - - 0 General Organics Naphthenic acids mg/L <1 <1 <1 6 <1 <1 2 13 <1 <1 1.3 14 <1 <1 1.1 16 Total phenolics mg/L 0.008(C,W) 0.005(C,W) 0.011(C,W) 6 0.012(C,W) 0.005(C,W) 0.015(C,W) 13 0.013(C,W) 0.002 0.017(C,W) 14 0.008(C,W) <0.001 0.017(C,W) 16 Total recoverable hydrocarbons mg/L <2 - - 1 <2 <2 <2 3 - - - 0 - - - 0 Total Metals Aluminum mg/L 0.0809 0.06 0.41(C,H) 6 0.22(C,H) 0.0122 1.72(A,C,H) 13 0.0625 0.02 1.72(A,C,H) 22 0.075 <0.01 0.21(C,H) 16 Antimony mg/L <0.0004 0.00005 <0.0004 6 <0.0004 0.00004 <0.0004 13 <0.0004 0.000019 0.0007 22 <0.0004 <0.0004 <0.0004 16 Arsenic mg/L 0.00115 0.0005 0.0016 6 0.0007 <0.0004 0.0023 13 0.00111 0.00027 0.00233 22 0.00107 0.0005 0.00151 16 Barium mg/L 0.044 0.033 0.05 6 0.021 0.013 0.077 13 0.024 0.012 0.044 22 0.025 0.015 0.036 16 Beryllium mg/L <0.001 0.00002 <0.001 6 <0.001 0.00001 <0.001 13 <0.001 <0.000003 <0.001 22 <0.001 <0.001 <0.001 16 Boron mg/L 0.16 0.07 0.47 6 0.07 <0.05 0.21 13 0.063 0.015 0.2 22 0.069 <0.05 0.18 16 Cadmium mg/L <0.0002 0.000005 <0.0002 6 <0.0002 <0.000005 <0.0002 13 <0.00005 0.000005 <0.002(D>C) 22 <0.0002 <0.00005 <0.0002 16 Chromium(a) mg/L <0.005(D>C) 0.0025(C) <0.005(D>C) 6 <0.005(D>C) <0.0001 <0.005(D>C) 13 <0.005(D>C) 0.0001 <0.005(D>C) 22 <0.005(D>C) <0.005(D>C) <0.005(D>C) 16 Cobalt mg/L <0.002 0.00068 <0.002 6 <0.002 0.00008 <0.002 13 <0.002 0.00008 <0.002 22 <0.002 <0.002 <0.002 16 Copper mg/L 0.001 0.0006 0.004 6 0.001 0.0002 0.005(C) 13 <0.001 <0.00005 0.0022(C) 22 <0.001 <0.001 0.002 16 Iron mg/L 2.16(C,H) 0.73(C,H) 5.76(C,H) 6 1.02(C,H) 0.25 2.06(C,H) 13 0.94(C,H) 0.25 2.6(C,H) 22 1.03(C,H) 0.49(C,H) 2.9(C,H) 16 Lead mg/L 0.00017 0.0001 0.0003 6 0.0002 0.00003 0.0006 13 0.0001 0.00001 0.00081 22 0.0001 <0.0001 0.0003 16 Manganese mg/L 0.234(H) 0.108(H) 1.16(H) 6 0.059(H) 0.016 0.246(H) 13 0.085(H) 0.017 0.294(H) 22 0.095(H) 0.034 0.4(H) 16 Mercury mg/L <0.0002(D>A,C) 0.000003 <0.0002(D>A,C) 6 <0.00002(D>A,C) 0.000003 <0.00002(D>A,C) 13 <0.00002(D>A,C) <0.0000006 <0.0001(D>A,C) 22 <0.00002(D>A,C) <0.00002(D>A,C) <0.0001(D>A,C) 14 Methyl mercury µg/L <0.00003 - - 1 0.00003 <0.00003 0.00008 3 - - - 0 - - - 0 Nickel mg/L 0.002 0.00125 0.004 6 <0.002 0.00101 0.00752 13 0.002 0.00015 0.003 22 <0.002 <0.002 0.003 16 Selenium mg/L 0.00085 0.00011 0.0012(C) 6 <0.0004 0.00005 0.0009 13 <0.0004 <0.0001 <0.0004 22 <0.0004 <0.0004 <0.0004 16 Silver mg/L <0.0004(D>C) <0.000005 <0.0004(D>C) 6 <0.0004(D>C) <0.000005 <0.0004(D>C) 13 <0.0001 <0.0000005 <0.0004(D>C) 22 <0.0004(D>C) <0.0001 <0.0004(D>C) 16 Thallium mg/L <0.0001 <0.000002 <0.0001 6 <0.0001 <0.000002 <0.0001 13 <0.0001 0.000001 <0.0001 22 <0.0001 <0.0001 <0.0001 16 Uranium mg/L 0.0002 0.00007 0.0008 6 0.0001 0.00006 0.00172 13 0.0001 0.000009 0.00039 22 0.0002 <0.0001 0.00039 16 Vanadium mg/L <0.001 0.0005 <0.001 6 0.001 <0.0002 0.005 13 0.001 0.00023 0.008 22 <0.001 <0.001 0.002 16 Zinc mg/L 0.009 0.0065 0.273(A,C) 6 0.014 0.001 0.145(A,C) 13 0.004 0.0014 0.021 22 <0.004 <0.004 0.053(C) 16

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Table 10 Seasonal Water Quality Summary for Other Watercourses Within and Near the Local Study Area (continued)

Golder Associates

Parameter Units Winter (2008 to 2010) Spring (2008 to 2010) Summer (2008 to 2009) Fall (2008 to 2009)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

PAHs and Alkylated PAHs Acenaphthene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10(D>C) 14 <0.01 <0.01 <0.01 16 Anthracene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10(D>C) 14 <0.01 <0.01 <0.01 16 Benzo(a)anthracene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 5 <0.01(D>H) <0.01(D>H) <0.01(D>H) 10 <0.01(D>H) <0.01(D>H) <10(D>C,H) 13 <0.01(D>H) <0.01(D>H) <0.01(D>H) 16 Benzo(a)pyrene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 5 <0.01(D>H) <0.01(D>H) <0.01(D>H) 10 <0.01(D>H) <0.01(D>H) <10(D>C,H) 13 <0.01(D>H) <0.01(D>H) <0.01(D>H) 16 Benzo(b)fluoranthene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 5 <10(D>H) <10(D>H) <10(D>H) 10 <0.01(D>H) <0.01(D>H) <10(D>H) 13 <0.01(D>H) <0.01(D>H) <0.01(D>H) 16 Benzo(k)fluoranthene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 5 <0.01(D>H) <0.01(D>H) <0.01(D>H) 10 <0.01(D>H) <0.01(D>H) <10(D>H) 13 <0.01(D>H) <0.01(D>H) <0.01(D>H) 16 Chrysene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 5 <0.01(D>H) <0.01(D>H) <0.01(D>H) 10 <0.01(D>H) <0.01(D>H) <10(D>H) 14 <0.01(D>H) <0.01(D>H) <0.01(D>H) 16 Dibenzo(a,h)anthracene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 5 <0.01(D>H) <0.01(D>H) <0.01(D>H) 10 <0.01(D>H) <0.01(D>H) <10(D>H) 14 <0.01(D>H) <0.01(D>H) <0.01(D>H) 16 Fluoranthene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10(D>C) 14 <0.01 <0.01 <0.01 16 Fluorene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10(D>C) 14 <0.01 <0.01 <0.01 16 Indeno(c,d-123)pyrene µg/L <0.01(D>H) <0.01(D>H) <0.01(D>H) 5 <0.01(D>H) <0.01(D>H) <0.01(D>H) 10 <0.01(D>H) <0.01(D>H) <10(D>H) 14 <0.01(D>H) <0.01(D>H) <0.01(D>H) 16 Naphthalene µg/L <0.01 <0.01 0.02 5 <0.01 <0.01 0.01 10 <0.01 <0.01 <10(D>C) 14 <0.01 <0.01 <0.025 16 Phenanthrene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10(D>C) 14 <0.01 <0.01 0.01 16 Pyrene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10(D>C) 14 <0.01 <0.01 0.012 16

(a) Chromium results for samples collected in winter 2010 are suspect due to irregularities found in QC samples. Refer to Attachment C for additional information.

- = Not applicable or no data.

Notes: Bolded concentrations are higher than relevant water quality guidelines. A = Concentration higher than the relevant acute aquatic life guideline or beyond the recommended pH or DO concentration range.

C = Concentration higher than the relevant chronic aquatic life guideline or beyond the recommended pH or DO concentration range.

H = Concentration higher than the relevant human health guideline.

W = Concentration higher than the relevant wildlife health guideline.

D> = Analytical detection limit was higher than the relevant water quality guideline(s).

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3.2 SEDIMENT QUALITY

Available sediment quality sample analyses for selected parameters in waterbodies and watercourses within and near the LSA are summarized in Table 11; a summary including all available sediment quality parameters is provided in Attachment F.

3.2.1 Waterbodies Within and Near the Local Study Area

Sediments in most waterbodies sampled within and near the LSA contained higher proportions of sand than silt and clay. Total organic carbon content was generally low, ranging from 0.5 to 3.5%. Naphthenic acids concentrations were below detection limits.

Total arsenic concentrations were above the ISQG in some samples, while concentrations of other metals, when detectable, were below the ISQG. Concentrations of PAHs were generally low or below detection limits, with some detectable concentrations of naphthalene, fluorene and phenanthrene above the ISQG. Concentrations were not observed above PEL values.

3.2.2 Watercourses Within and Near the Local Study Area

Sediments in most watercourses sampled within and near the LSA contained higher proportions of sand than silt and clay. Total organic carbon content ranged from less than 0.4 to 9.9%. Naphthenic acids concentrations were below detection limits.

Total arsenic concentrations were above the ISQG in some samples, while concentrations of other metals, when detectable, were below the ISQG. Concentrations of PAHs were generally low or below detection limits, with some detectable concentrations of naphthalene and phenanthrene greater than the ISQG. Concentrations were not observed above PEL values.

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Table 11 Summary of Sediment Quality Data for Waterbodies and Watercourses Within and Near the Local Study Area

Parameter Units

[dry wt]

Waterbodies (2008 to 2009) Watercourses (2008 to 2009)

Median Minimum Maximum n Median Minimum Maximum n

Physical and Aggregate Properties

Moisture content % 85 56 86 3 55 31 85 6

Organic matter % 6 0.9 71 7 2 0.5 17 19

Total organic carbon % 2.3 0.5 3.5 4 1.2 <0.4 9.9 17

Sand(a) % 76 8 90 7 77 8 96 19

Silt and clay(a) % 24 10 92 7 23 4 92 19

Nutrients

Nitrogen – Kjeldahl % 0.49 0.09 2.95 7 0.09 <0.02 1.8 19

Phosphorus – total µg-P/g 829 825 1,400 3 478 298 1,500 6

Phosphate – P available µg-P/g 7 3 37 7 6 1 18 19

General Organics

Naphthenic acids µg/g <5 <5 <5 4 <5 <5 <5 12

Phenols µg/g 0.55 <0.1 2.93 7 0.78 <0.1 7.03 18

Total Metals

Arsenic µg/g 2.3 0.5 11.2 (I) 7 2.7 0.8 11.5 (I) 19

Cadmium µg/g <0.5 <0.5 <1 (D>I) 7 <0.5 <0.5 <1 (D>I) 19

Chromium µg/g 5.1 2.3 16.3 7 6.1 1.4 19.5 19

Copper µg/g 6 <2 18.8 7 5 <2 33 19

Lead µg/g <5.1 <5 11.6 7 <5 <5 11 19

Mercury µg/g 0.06 <0.05 0.11 7 <0.05 <0.05 0.09 19

Zinc µg/g 73 <10 120 7 20 <10 90 19

Polycyclic Aromatic Hydrocarbons

Naphthalene µg/g 0.015 <0.01 0.054 (I) 6 <0.01 <0.01 0.07 (I) 17

2-Methylnaphthalene µg/g <0.03 (D>I) <0.01 <0.03 (D>I) 3 <0.01 <0.01 <0.03 (D>I) 6

Acenaphthene µg/g <0.015 (D>I) <0.01 (D>I) <0.03 (D>I) 6 <0.01 (D>I) <0.01 (D>I) <0.03 (D>I) 17

Acenaphthylene µg/g <0.015 (D>I) <0.01 (D>I) <0.03 (D>I) 6 <0.01 (D>I) <0.01 (D>I) <0.03 (D>I) 17

Anthracene µg/g <0.01 <0.005 <0.03 6 <0.005 <0.005 <0.03 17

Dibenzo(a,h)anthracene µg/g <0.015 (D>I) <0.01 (D>I) <0.03 (D>I) 6 <0.01 (D>I) <0.01 (D>I) <0.03 (D>I) 17

Benzo(a)anthracene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17

Benzo(a)pyrene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17

Chrysene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 0.04 17

Fluoranthene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17

Fluorene µg/g <0.02 <0.01 0.04 (I) 6 <0.01 <0.01 <0.03 (D>I) 17

Phenanthrene µg/g 0.025 <0.01 0.08 (I) 6 <0.01 <0.01 0.06 (I) 17

Pyrene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17

(a) Sand percentage based on sieve analysis with mesh diameter of 75 µm; silt and clay percentage = (100% - sand).

Notes: Bolded concentrations are higher than the relevant sediment quality guideline. I = Concentration higher than the interim sediment quality guideline (CCME 1999). D>I = Analytical detection limit was higher than the interim sediment quality guideline.

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4 SUMMARY

Water and sediment quality samples were collected within and near the LSA in 2009 and 2010. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling program.

Overall, the baseline study results indicate that water and sediment quality within and near the LSA are similar to those documented by other studies in the Athabasca Oil Sands Region. Most of the measured concentrations were below guideline values for both water and sediment samples. Larger waterbodies and watercourses, (i.e., Namur and Gardiner lakes and the Ells River) are generally mesotrophic, while smaller waterbodies and watercourses are typically eutrophic. Concentrations of total phenolics, total iron and total manganese in water were frequently above guidelines. In bottom sediments, concentrations above the ISQG were occasionally measured for arsenic, napthalene, fluorene and phenanthrene but likely reflect local geological conditions.

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5 CLOSURE

We trust the above meets your present requirements. If you have any questions or require additional details, please contact the undersigned.

GOLDER ASSOCIATES LTD.

Report prepared by:

Report reviewed by:

Jason Parviainen, M.Sc. Water Quality Specialist

Zsolt Kovats, M.Sc. Associate, Aquatic Ecologist

Shawn McKeown, P.Eng. Principal, Oil Sands Division Director

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6 REFERENCES

AENV (Alberta Environment). 1999. Surface Water Quality Guidelines for Use in Alberta. November 1999. Environmental Service, Environmental Sciences Division. Edmonton, AB.

AENV. 2010. AENV Water Data System. Environmental Service, Environmental Sciences Division. Edmonton, AB.

AOSC (Athabasca Oil Sands Corp.). 2009. Application for Approval of the MacKay River Commercial Project. Volumes 1 to 5. Submitted to Alberta Energy Resources Conservation Board and Alberta Environment. December 2009.

APHA (American Public Health Association). 1992. Standard Methods for the Examination of Waste and Wastewater. 18th Edition. American Public Health Association. Washington, D.C.

CCME (Canadian Council of Ministers of the Environment). 1999 with updates to 2010. Canadian Environmental Quality Guidelines. Winnipeg, MB.

CCME. 2004. Canadian Guidance Framework for the Management of Phosphorus in Freshwater Systems. Report No. 1-8, Ecosystem Health, Science-Based Solutions. National Guidelines and Standards Office, Environment Canada. Gatineau, QC.

Dodds, W.K., J.R. Jones and E.B. Welch. 1998. Suggested Classification of Stream Trophic State: Distributions of Temperate Stream Types by Chlorophyll, Total Nitrogen and Phosphorus. Water Research 32:1455–1462.

Environment Canada. 1993. Quality Assurance in Water Quality Monitoring. Ecosystem Sciences and Evaluation Directorate Conservation and Protection. Ottawa, ON.

Golder (Golder Associates Ltd.). 1999. Oil Sands Regional Aquatics Monitoring Program (RAMP) 1998. Prepared for Suncor Energy Inc., Shell Canada Limited, Mobil Oil and Syncrude Canada Ltd. Fort McMurray, AB.

Golder. 2000. Oil Sands Regional Aquatics Monitoring Program (RAMP) 1999. Final Report for the RAMP Steering Committee.

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Golder. 2001. Oil Sands Regional Aquatics Monitoring Program (RAMP) 2000. Volume I: Chemical and Biological Monitoring. Prepared for the RAMP Steering Committee, Fort McMurray, AB.

Golder. 2002. Oil Sands Regional Aquatics Monitoring Program (RAMP) 2001. Volume I: Chemical and Biological Monitoring. Submitted to RAMP Steering Committee. April 2002.

Golder. 2003. Oil Sands Regional Aquatics Monitoring Program (RAMP) 2002. Submitted to the RAMP Steering Committee. March 2003.

Health Canada. 2008. Summary of Guidelines for Canadian Drinking Water Quality. Prepared by the Federal-Provincial Subcommittee on Drinking Water of the Federal-Provincial-Territorial Committee on Environmental and Occupational Health.

Mitchell, P. And E. Prepas. 1990. Atlas of Alberta Lakes. The University of Alberta Press. Edmonton, AB.

RAMP (Regional Aquatics Monitoring Program). 2004. Regional Aquatics Monitoring Program (RAMP) 2003 Annual Report. Prepared for the RAMP Steering Committee. Submitted by the RAMP 2003 Implementation Team Consisting of Hatfield Consultants Ltd., Jacques Whitford Environment Ltd., Mack, Slack and Associates Inc. And Western Resource Solutions. Submitted March 2004. 618 pp.

RAMP. 2005. Regional Aquatics Monitoring Program (RAMP) 2004 Technical Report. Prepared for RAMP Steering Committee. Submitted by the RAMP 2004 Implementation Team Consisting of Hatfield Consultants Ltd., Jacques Whitford Environment Ltd. Mack, Slack & Associates Inc. And Western Resource Solutions. Submitted April 2005. 45 pp.

RAMP. 2006. Regional Aquatics Monitoring Program (RAMP) 2005 Technical Report. Prepared for the RAMP Steering Committee. Submitted by the RAMP 2005 Implementation Team consisting of Hatfield Consultants Ltd., Stantec Consulting Ltd., Mack, Slack and Associates Inc. And Western Resource Solutions. Submitted April 2006.

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RAMP. 2007. Regional Aquatics Monitoring Program (RAMP) 2006 Technical Report. Prepared for the RAMP Steering Committee. Submitted by the RAMP 2006 Implementation Team consisting of Hatfield Consultants Ltd., Stantec Consulting Ltd., Mack, Slack and Associates Inc. And Western Resource Solutions. Submitted April 2007.

RAMP. 2008. Regional Aquatics Monitoring Program (RAMP) 2007 Technical Report. Prepared for the RAMP Steering Committee. Submitted by the RAMP 2007 Implementation Team consisting of Hatfield Consultants Ltd., Stantec Consulting Ltd., Klohn Crippen Berger Ltd. And Western Resource Solutions. 43 pp.

RAMP. 2009. Regional Aquatics Monitoring Program (RAMP) 2008 Technical Report. Prepared for the RAMP Steering Committee. Submitted by the RAMP 2008 Implementation Team consisting of Hatfield Consultants Ltd., Kilgour and Associates Ltd., Klohn Crippen Berger Ltd. And Western Resource Solutions. April 2009.

RAMP. 2010. Regional Aquatics Monitoring Program (RAMP) 2009 Technical Report. Prepared for the RAMP Steering Committee. Prepared by the RAMP 2009 Implementation Team consisting of Hatfield Consultants, Kilgour and Associates Ltd. And Western Resource Solutions. April 2010.

Richardson, G.M. 1997. Compendium of Canadian Human Exposure Factors to Risk Assessment. O’Connor Associates Environmental Inc. Ottawa, ON.

Southern Pacific (Southern Pacific Resource Corp.). 2009. Application for the Southern Pacific Resource Corp. STP McKay SAGD Project. Submitted to the Alberta Energy Resources Conservation Board and Alberta Environment May 29, 2009.

Sunshine (Sunshine Oilsands Ltd.). 2010. Application for Sunshine Oil Sands Ltd. West Ells SAGD Project. Submitted March 31, 2 010.

U.S. EPA (United States Environmental Protection Agency). 2002. National Recommended Water Quality Criteria: 2002. Office of Water 4304T. United States Environmental Protection Agency. EPA 822-R-02-047.

U.S. EPA. 2003a. National Primary Drinking Water Standards. Office of Water (4606M). EPA-816-F-03-016.

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U.S. EPA. 2003b. National Recommended Water Quality Criteria for the Protection of Human Health. Notice of Availability. Federal Register: December 31, 2003, Vol. 68, No. 250. P. 75507-75515.

Vollenweider, R.A. and J. Kerekes. 2002. Eutrophication of Waters, Monitoring Assessment and Control. Organization for Economic Co-operation and Development (OECD). Paris, France.

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7 ABBREVIATIONS

% Percent

< Less than

> More than

C Degrees Celsius

AENV Alberta Environment

AOSC Athabasca Oil Sands Corporation

BOD Biochemical Oxygen Demand

bpd Barrels of oil per day

CCME Canadian Council of Ministers of the Environment

DNP Dover North Plant

DO Dissolved oxygen

DOC Dissolved organic carbon

Dover OPCO Dover Operating Corp.

Dry wt Dry weight

DSP Dover South Plant

ds/m Decisiemens per metre

e.g. For example

et al. Group of authors

g/d Grams per day

ha Hectares

i.e. That is

ISDA Initial Surface Development Area

ISQG Interim Sediment Quality Guideline

km Kilometre

L or l Litre

LSA Local Study Area

mg/L Milligrams per litre

mg-N/L Milligrams of nitrogen per litre

mg-P/L Milligrams of phosphorous per litre

n Sample size

PAH Polycyclic Aromatic Hydrocarbons

PEL Probable effects level

pH Potential of Hydrogen; provides measure of the acidity or alkalinity of a solution on a scale of 0 to 14

RAMP Regional Aquatics Monitoring Program

ROW Rights-of-way

RSA Regional Study Area

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SAGD Steam Assisted Gravity Drainage

SAR Sodium Adsorption Ratio

TCU True colour unit

TDS Total dissolved solids

TKN Total Kjeldahl nitrogen

TN Total nitrogen

TOC Total organic carbon

TP Total phosphorus

TSS Total suspended solids

UTM Universal Transverse Mercator

wt Weight

W4M West of the Fourth Meridian

µg/g Micrograms per gram

µg/L Micrograms per litre

µm Micron or Micrometre

µg-P/g Micrograms of phosphorous per gram

µS/cm MicroSiemens per centimetre

µg-S/g Micrograms of sulphur per gram

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8 GLOSSARY

Acute Acute refers to a stimulus severe enough to rapidly induce an effect; in aquatic toxicity tests, an effect observed in 96 hours or less is typically considered acute. When referring to aquatic toxicology or human health, an acute effect is not always measured in terms of lethality.

Alkalinity A measure of water’s capacity to neutralize an acid. It indicates the presence of carbonates, bicarbonates and hydroxides, borates, silicates, phosphates and organic substances. It is expressed as an equivalent of calcium carbonate. The composition of alkalinity is affected by pH, mineral composition, temperature and ionic strength. However, alkalinity is normally interpreted as a function of carbonates, bicarbonates and hydroxides. The sum of these three components is called total alkalinity.

Baseline A surveyed or predicted condition that serves as a reference point on which later surveys are coordinated or correlated.

Basin A geographic area drained by a single major stream; consists of a drainage system comprised of streams and often natural or artificial (constructed) lakes.

Bioavailability The amount of chemical that enters the general circulation of the body following administration or exposure.

Biochemical Oxygen Demand

An empirical test in which standardized laboratory procedures are used to determine the relative oxygen requirements of wastewaters, effluents and polluted waters.

Bitumen A highly viscous, tarry, black hydrocarbon material having an API gravity of about 9 (specific gravity about 1.0). It is a complex mixture of organic compounds. Carbon accounts for 80 to 85% of the elemental composition of bitumen, hydrogen 10%, sulphur 5%, and nitrogen, oxygen and trace elements form the remainder.

Chlorophyll a One of the green pigments in plants. It is a photo-sensitive pigment that is essential for the conversion of inorganic carbon (e.g., carbon dioxide) and water into organic carbon (e.g., sugar). The concentration of chlorophyll a in water is an indicator of algal concentration.

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Chronic The development of adverse effects after extended exposure to a given substance. In chronic toxicity tests, the measurement of a chronic effect can be reduced growth, reduced reproduction or other non-lethal effects, in addition to lethality. Chronic should be considered a relative term depending on the life span of the organism.

Concentration Quantifiable amount of a chemical in environmental media.

Conductivity A measure of the capacity of water to conduct an electrical current. It is the reciprocal of resistance. This measurement provides an estimate of the total concentration of dissolved ions in the water (specific conductance is normalized to 25°C).

Dissolved Organic Carbon (DOC)

The dissolved portion of organic carbon water; made up of humic substances and partly degraded plant and animal materials.

Dissolved Oxygen (DO)

Measurement of the concentration of dissolved (gaseous) oxygen in the water, usually expressed in milligrams per litre (mg/L).

Drainage Basin A region of land that eventually contributes water to a river or lake.

Ekman Grab Cube-shaped mechanical device with a spring-loaded opening that is lowered to the bottom of a waterbody and triggered to close as to collect a sample of the bottom substrate.

Environmental Impact Assessment

A review of the effects that a proposed development will have on the local and regional environment.

Epilimnetic Localized in the surface layer of a waterbody.

Eutrophic The nutrient-rich status (amount of nitrogen, phosphorus and potassium) of an ecosystem.

Grab Sample A single sample collected at a particular time and place that represents the composition of the water only at that time and place.

Groundwater That part of the subsurface water that occurs beneath the water table, in soils and geologic formations that are fully saturated.

Headwater The source and upper reaches of a stream; also the upper reaches of a reservoir. The water upstream from a structure or point on a stream. The small streams that come together to form a river. Also may be thought of as any and all parts of a river basin except the mainstem river and main tributaries.

Hydrology The science of waters of the earth, their occurrence, distribution, and circulation; their physical and chemical properties; and their reaction with the environment, including living beings.

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Hyper-Eutrophic Trophic state classification for lakes characterized by high primary productivity and high nutrient inputs (particularly total phosphorus). Hyper-eutrophic lakes are characterized by abundant plant growth, algal blooms and oxygen depletion.

Initial Surface Development Area

The surface area containing all of the facilities that will be required for access and initial development of the subsurface bitumen associated with Phase 1 of the Dover Commercial Project; including the Dover North Plant, Phase 1 well pads gathering corridors and associated infrastructure, the main Dover Access Road and Utility Corridor and the wells, pipelines and infrastructure required for the non-saline water well system.

Invertebrates Any animal lacking a backbone, including all species not classified as vertebrates.

ISQG (Interim Sediment Quality Guideline)

Recommended maximum concentration of a chemical in sediment, intended to be protective of aquatic organisms.

In Situ Also known as “in place”. Refers to methods of extracting deep deposits of oil sands without removing the groundcover. The in-situ technology in oil sands uses underground wells to recover the resources with less impact to the land, air and water than for oil sands mining.

Local Study Area Defines the spatial extent directly or indirectly affected by the project.

Mesotrophic Trophic state classification for lakes characterized by moderate productivity and nutrient inputs (particularly total phosphorus).

Naphthenic Acid Generic name used for all the organic acids present in crude oils.

Nutrients Environmental substances (elements or compounds) such as nitrogen or phosphorus, which are necessary for the growth and development of plants and animals.

pH The degree of acidity (or alkalinity) of soil or solution. The pH scale is generally presented from 1 (most acidic) to 14 (most alkaline). A difference of one pH unit represents a ten-fold change in hydrogen ion concentration.

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Polycyclic Aromatic Hydrocarbons

Polycyclic aromatic hydrocarbons are a large group of organic compounds comprised of two or more aromatic rings and by-products of combustion. They are found in crude oil and a variety of products such as bitumen, asphalt, coal tar pitch volatiles, and unrefined or mildly refined mineral oils. Polycyclic aromatic hydrocarbons (PAHs) are emitted into the Canadian environment from both natural and anthropogenic sources. Forest fires, which release approximately 2000 tonnes of PAHs per year, are the single most important natural source of PAHs in Canada. However, since releases from that source are generally widely separated in time and space across the country, they do not result in continuous exposure in any specific area. Anthropogenic sources are numerous and result in emissions of PAHs into all environmental compartments

Probable Effects Level (PEL)

Concentration of a chemical in sediment above which adverse effects on an aquatic organism are likely.

Runoff The portion of water from rain and snow that flows over land to streams, ponds or other surface waterbodies. It is the portion of water from precipitation that does not infiltrate into the ground, or evaporate.

Sediments Solid material that is transported by, suspended in, or deposited from water. It originates mostly from disintegrated rocks; it also includes chemical and biochemical precipitates and decomposed organic material, such as humus. The quantity, characteristics and cause of the occurrence of sediment in streams are influenced by environmental factors. Some major factors are degree of slope, length of slope soil characteristics, land usage and quantity and intensity of precipitation.

Specific Conductivity A measure of the capacity of water to conduct an electrical current. It is the reciprocal of resistance. This measurement provides an estimate of the total concentration of dissolved ions in the water (specific conductance is normalized to 25°C).

Spring Freshet A spring thaw event resulting from snow and ice melt in rivers.

Steam Assisted Gravity Drainage

An in-situ oil sands recovery technique that involves the use of two horizontal wells, one to inject steam and a second to produce the bitumen.

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Suspended Sediments Particles of matter suspended in the water. Measured as the oven dry weight of the solids, in mg/L, after filtration through a standard filter paper. Less than 25 mg/L would be considered clean water, while an extremely muddy river might have 200 mg/L of suspended sediments.

Total Dissolved Solids (TDS)

The total concentration of all dissolved compounds solids found in a water sample.

Total Kjeldahl Nitrogen (TKN)

The sum of organic nitrogen; ammonia, NH3 and ammonium, NH4+

Total Recoverable Hydrocarbons

A term that refers to groups of petroleum hydrocarbons recovered using a solvent-specific extraction procedure. Hydrocarbons may include a wide range of fuels, oils and greases.

Total Suspended Solids (TSS)

A measure of the total concentrations of suspended solids in water.

Toxic A substance, dose or concentration that is harmful to a living organism.

Trophic Pertaining to part of a food chain, for example, the primary producers are a trophic level just as tertiary consumers are another trophic level.

Waterbody A general term that refers to ponds, bays, lakes, estuaries and marine areas.

Watercourse A general term that refers to riverine systems such as creeks, brooks, streams and rivers.

Watershed The entire surface drainage area that contributes water to a lake or river.

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ATTACHMENT A

INDIVIDUAL WATER QUALITY SAMPLE TEST RESULTS FOR PROJECT-SPECIFIC SAMPLING

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Golder Associates

Table A-1 Water Quality Results for Samples Collected from Waterbodies During the 2009/2010 Field Program

Parameter Units WB-1 WB-2 WB-3 WB-4 WB-5 WB-10

18-Aug-2009

01-Oct-2009

25-Feb-2010

15-May-2010

25-Feb-2010

15-May-2010

13-Aug-2009

01-Oct-2009

25-Feb-2010

16-May-2010

11-Aug-2009

29-Sep-2009

17-May-2010

15-Aug-2009

01-Oct-2009

16-May-2010

13-Aug-2009

01-Oct-2009

Field Measured pH - 7.43 6.95 8.49 7.77 7.95 8.9 7.3 6.92 7.02 7.91 7.76 7.41 - 8.85 8.05 8.25 7.08 7.76 Specific conductance µS/cm 113 168 225 97 505 270 43 64 107 46 63 102 - 248 435 262 143 379 Temperature °C 17.39 9.01 2.59 12.76 1.42 12.93 13.13 7.48 0.24 12.63 17.1 9.18 - 17.36 8.03 14.05 12.58 5.96 Dissolved oxygen mg/L 5.15 7.225 0.73 9.55 0.97 12.88 6.05 9.15 1.15 9.98 8.39 5.75 - 5.17 11 10.13 3.35 12.28 Conventional Parameters Specific conductance µS/cm 116 115 210 100 500 270 45.7 45.5 110 46 63.3 70.3 58 273 300 260 183 261 Colour TCU 105 83 160 39 61 27 147 92 210 79 7 8 12 82 69 65 81 47 Dissolved organic carbon mg/L 35.4 32.1 47 21.4 34 17.9 30.1 23.1 44 19 9.7 7.2 5.8 24.1 24 18 23 20.2 Hardness mg/L 45.4 44.1 97.2 39 247 112 29.6 24 61.7 25.1 28.4 27.6 24.6 121 130 121 84.3 118 pH - 7.71 7.53 7.27 7.49 7.98 8.05 6.89 7.05 6.89 7.03 7.36 7.45 7.29 8.17 8.05 7.91 7.76 7.94 Total alkalinity mg/L 52.6 46.8 96 39 200 100 15.9 15.4 49 16 23.3 24.2 18 111 123 100 68.6 90.9 Total dissolved solids mg/L 58.1 58.1 210 88 360 190 20.5 19.2 130 21 35.1 36.2 96 154 164 170 99.4 143 Total organic carbon mg/L 16 31.2 50 21.9 36 17.4 11.1 23.1 44 19.1 2.9 7.2 6.1 24.9 23.9 19 14.9 18 Total suspended solids mg/L 3 <3 10 3 3 3 5 <3 18 6 <3 <3 4 5 <3 6 14 5 Major Ions Bicarbonate mg/L 64.1 57.1 120 47 250 130 19.4 18.8 59 20 28.4 29.5 21 136 150 130 83.7 111 Calcium mg/L 12.2 11.7 26.7 10.3 71.8 31.9 7.75 6.13 16.2 6.88 7.37 7.18 6.41 33.4 35.2 33.5 22.5 31.3 Carbonate mg/L <5 <5 <0.5 <0.5 <0.5 <0.5 <5 <5 <0.5 <0.5 <5 <5 <0.5 <5 <5 <0.5 <5 <5 Chloride mg/L <0.5 <0.5 2 1 3 1 <0.5 <0.5 3 <1 <0.5 <0.5 <1 <0.5 <0.5 <1 <0.5 <0.5 Magnesium mg/L 3.63 3.62 7.38 3.22 16.5 7.91 2.5 2.1 4.49 1.93 2.43 2.35 2.01 9.22 10.3 8.82 6.84 9.79 Potassium mg/L 1.77 1.93 3.75 1.58 3.98 2.1 <0.5 <0.5 1.75 0.72 1.17 1.15 1.04 1.43 1.54 2.93 0.55 0.84 Sodium mg/L 6.4 6.8 11.7 5.21 25.4 11.9 <1 <1 2.15 0.9 2.7 2.8 2.2 12.4 14.7 10.8 4.9 9 Sulphate mg/L 2.53 5.57 6 <1 66 38 0.74 1.72 <1 <1 7.41 8.23 9 30.7 28.6 36 23.4 37.6 Sulphide mg/L - - 0.044 0.016 0.008 0.02 - - 0.076 0.01 - - <0.002 - - 0.008 - -

Nutrients and Biological Indicators Nitrate mg-N/L <0.05 0.098 0.17 <0.003 1.2 <0.003 <0.05 <0.05 0.03 0.02 <0.05 <0.05 0.02 <0.05 <0.05 0.02 <0.05 <0.05 Nitrate + nitrite mg-N/L <0.071 0.098 0.038 <0.003 0.28 <0.003 <0.071 <0.071 0.006 0.004 <0.071 <0.071 0.004 <0.071 <0.071 0.004 <0.071 <0.071 Nitrite mg-N/L <0.05 <0.05 <0.003 <0.003 <0.003 <0.003 <0.05 <0.05 <0.003 <0.003 <0.05 <0.05 <0.003 <0.05 <0.05 <0.003 <0.05 <0.05 Nitrogen - ammonia mg-N/L 0.089 <0.05 0.86 <0.05 0.19 <0.05 <0.05 <0.05 0.43 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 Nitrogen - Kjeldahl mg-N/L 2.44 2.09 3.2 1.1 1.7 0.83 1.47 1.39 2.4 1.1 0.49 0.42 0.54 1.25 1.12 1 1.52 1.21 Nitrogen - total mg-N/L 2.44 2.19 3.238 1.1 1.98 0.83 1.47 1.39 2.406 1.104 0.49 0.42 0.544 1.25 1.12 1.004 1.52 1.21 Phosphorus - total mg-P/L - 0.032 0.22 0.043 0.042 0.023 - 0.028 0.28 0.023 - 0.023 0.013 - 0.081 0.059 - 0.066 Phosphorus - dissolved mg-P/L 0.023 <0.02 0.18 0.015 0.034 0.008 <0.02 <0.02 0.022 0.006 <0.02 <0.02 0.007 0.035 0.045 0.03 0.027 <0.02 Biochemical oxygen demand mg/L - - - <6 - <6 - - - - - - - - - - - - Chlorophyll a µg/L - - - 42 - 7 - - - 12 - - 2.9 - - 8.2 - - General Organics Naphthenic acids mg/L <1 1.4 <1 <1 <1 <1 <1 1.1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 Total phenolics mg/L 0.0092 0.008 0.003 0.004 <0.002 0.004 0.0079 0.0079 0.002 0.003 0.001 0.0023 <0.002 0.0044 0.0052 <0.002 0.005 0.0049 Total recoverable hydrocarbons

mg/L - - <2 <2 <2 <2 - - <2 <2 - - <2 - - <2 - -

Total Metals Aluminum mg/L <0.01 <0.01 0.0468 0.0033 0.0199 0.0043 0.103 0.06 0.199 0.0626 <0.01 0.036 0.0091 0.038 0.033 0.0395 0.064 0.041 Antimony mg/L 0.00084 <0.0004 0.00006 <0.00002 0.00016 0.00005 <0.0004 <0.0004 0.00005 <0.00002 <0.0004 <0.0004 0.00006 <0.0004 <0.0004 0.00007 <0.0004 <0.0004 Arsenic mg/L 0.00228 0.0163 0.00098 0.00035 0.00113 0.00053 <0.0004 <0.0004 0.00078 0.00028 <0.0004 <0.0004 0.00031 0.00206 0.00168 0.00128 0.00171 0.0009 Barium mg/L 0.0511 0.0158 0.0419 0.012 0.0521 0.0237 0.0135 0.0123 0.0422 0.0104 0.019 0.0189 0.0184 0.0275 0.0246 0.0261 0.0313 0.0303 Beryllium mg/L <0.001 <0.001 0.00002 <0.00001 0.00001 <0.00001 <0.001 <0.001 0.00003 <0.00001 <0.001 <0.001 <0.00001 <0.001 <0.001 <0.00001 <0.001 <0.001 Bismuth mg/L - - <0.000005 <0.000005 <0.000005 <0.000005 - - <0.000005 0.000007 - - <0.000005 - - 0.000009 - - Boron mg/L 0.145 <0.05 0.08 0.04 0.14 0.07 <0.05 <0.05 <0.02 <0.02 <0.05 <0.05 0.02 0.08 0.06 0.06 <0.05 <0.05 Cadmium mg/L <0.00005 <0.00005 0.000123 <0.000005 0.000051 <0.000005 <0.00005 <0.00005 0.000039 0.000021 <0.00005 <0.00005 0.000011 <0.00005 <0.00005 0.000019 <0.00005 <0.00005 Chromium mg/L <0.005 <0.005 0.0024(a) <0.0001 0.0025(a) <0.0001 <0.005 <0.005 0.0026 0.0001 <0.005 <0.005 <0.0001 <0.005 <0.005 <0.0001 <0.005 <0.005 Cobalt mg/L <0.002 <0.002 0.000222 0.00004 0.000412 0.000055 <0.002 <0.002 0.00116 0.000084 <0.002 <0.002 0.000046 <0.002 <0.002 0.000148 <0.002 <0.002 Copper mg/L 0.0012 <0.001 0.0007 0.00006 0.00105 0.00023 <0.001 <0.001 0.00075 0.00027 <0.001 <0.001 0.00033 <0.001 <0.001 0.00061 <0.001 <0.001 Iron mg/L 0.535 0.14 1.63 0.072 0.7 0.157 0.374 0.29 3.66 0.676 <0.01 0.149 0.11 0.592 0.889 0.809 0.892 0.64 Lead mg/L 0.00022 <0.0001 0.000248 0.000224 0.00149 0.000058 0.00011 <0.0001 0.000485 0.000172 <0.0001 0.00011 0.000057 <0.0001 <0.0001 0.000572 <0.0001 <0.0001 Lithium mg/L 0.049 <0.01 0.0182 0.008 0.0363 0.0189 <0.01 <0.01 0.0063 0.0027 <0.01 <0.01 0.0063 0.022 0.024 0.022 0.017 0.02 Manganese mg/L 0.118 0.014 0.368 0.00901 0.746 0.0192 0.0151 0.0191 0.383 0.0141 <0.005 0.0294 0.0193 0.0424 0.0444 0.0473 0.0412 0.0338 Mercury mg/L <0.0001 <0.0001 0.000003 0.000005 0.000002 0.000003 <0.0001 <0.0001 0.000004 0.000006 <0.0001 <0.0001 0.000003 <0.0001 <0.0001 0.000004 <0.0001 <0.0001 Methyl mercury µg/L - - 0.00041 0.0002 <0.00003 0.00004 - - <0.00003 0.00007 - - <0.00003 - - 0.00003 - - Molybdenum mg/L <0.005 <0.005 0.00026 0.00011 0.00147 0.00067 <0.005 <0.005 0.00006 <0.00005 <0.005 <0.005 0.0002 <0.005 <0.005 0.00121 <0.005 <0.005

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Dover Commercial Project A-2 Water Quality Baseline Report December 2010

Table A-1 Summary Water Quality Results for Samples Collected from Waterbodies During the 2009/2010 Field Program (continued)

Golder Associates

Parameter Units WB-1 WB-2 WB-3 WB-4 WB-5 WB-10

18-Aug-2009

01-Oct-2009

25-Feb-2010

15-May-2010

25-Feb-2010

15-May-2010

13-Aug-2009

01-Oct-2009

25-Feb-2010

16-May-2010

11-Aug-2009

29-Sep-2009

17-May-2010

15-Aug-2009

01-Oct-2009

16-May-2010

13-Aug-2009

01-Oct-2009

Nickel mg/L <0.002 <0.002 0.00102 0.00017 0.00206 0.0006 <0.002 <0.002 0.00114 0.00039 <0.002 <0.002 0.00052 0.0023 <0.002 0.00107 <0.002 <0.002 Selenium mg/L <0.0004 <0.0004 0.00011 <0.00004 0.00018 0.00007 <0.0004 <0.0004 0.00011 0.00004 <0.0004 <0.0004 0.00006 <0.0004 <0.0004 0.00009 <0.0004 <0.0004 Silver mg/L <0.0001 0.00048 <0.000005 <0.000005 <0.000005 <0.000005 <0.0001 <0.0001 <0.000005 <0.000005 <0.0001 <0.0001 <0.000005 <0.0001 <0.0001 <0.000005 0.00032 <0.0001 Strontium mg/L - - 0.125 0.0484 0.342 0.162 - - 0.0644 0.026 - - 0.0361 - - 0.167 - - Thallium mg/L <0.0001 <0.0001 <0.000002 <0.000002 0.000003 <0.000002 <0.0001 <0.0001 0.000003 <0.000002 <0.0001 <0.0001 <0.000002 <0.0001 <0.0001 0.000003 <0.0001 <0.0001 Titanium mg/L <0.001 <0.001 0.0012 <0.0005 <0.0005 <0.0005 <0.001 <0.001 0.0009 <0.0005 <0.001 0.0012 <0.0005 0.0014 0.0016 0.001 0.0014 <0.001 Uranium mg/L 0.00134 <0.0001 0.000033 0.000007 0.000814 0.000293 <0.0001 <0.0001 0.00003 0.000008 <0.0001 <0.0001 0.000011 0.00039 0.00033 0.000353 0.00017 0.0003 Vanadium mg/L <0.001 <0.001 0.0003 <0.0002 <0.0002 <0.0002 0.0027 <0.001 0.0006 <0.0002 <0.001 <0.001 0.0002 <0.001 <0.001 0.0005 <0.001 <0.001 Zinc mg/L 0.0044 <0.004 0.0142 0.0012 0.0238 0.0012 0.0044 <0.004 0.0203 0.0024 <0.004 0.0051 0.0012 <0.004 <0.004 0.0028 <0.004 0.0057 Dissolved Metals Aluminum mg/L <0.01 0.013 0.0224 0.0022 0.0048 0.0141 0.085 0.063 0.12 0.047 <0.01 <0.01 0.0025 <0.01 <0.01 0.0084 0.031 0.012 Antimony mg/L <0.0004 <0.0004 0.00007 0.00002 0.00017 0.00005 <0.0004 <0.0004 0.00005 <0.00002 <0.0004 <0.0004 0.00006 <0.0004 <0.0004 0.00006 <0.0004 <0.0004 Arsenic mg/L 0.00051 0.00048 0.00105 0.00037 0.00111 0.00053 <0.0004 <0.0004 0.00078 0.00027 <0.0004 <0.0004 0.00031 0.00177 0.00144 0.00099 0.00095 0.00063 Barium mg/L 0.0211 0.0152 0.0375 0.011 0.0473 0.0235 0.0119 0.0113 0.0347 0.00971 0.019 0.0174 0.0175 0.0248 0.0229 0.0239 0.0248 0.0281 Beryllium mg/L <0.001 <0.001 0.00001 <0.00001 0.00001 <0.00001 <0.001 <0.001 0.00002 0.00001 <0.001 <0.001 <0.00001 <0.001 <0.001 <0.00001 <0.001 <0.001 Bismuth mg/L - - <0.000005 <0.000005 <0.000005 <0.000005 - - <0.000005 <0.000005 - - <0.000005 - - <0.000005 - - Boron mg/L 0.05 0.052 0.08 0.04 0.15 0.08 <0.05 <0.05 <0.02 <0.02 <0.05 <0.05 0.02 0.082 0.068 0.06 <0.05 <0.05 Cadmium mg/L <0.00005 <0.00005 0.00022 <0.000005 0.000196 0.000011 <0.00005 <0.00005 0.000052 0.000007 <0.00005 <0.00005 0.000007 <0.00005 <0.00005 0.00001 <0.00005 <0.00005 Chromium mg/L <0.005 <0.005 0.0022(a) <0.0001 0.0025(a) <0.0001 <0.005 <0.005 0.0024 <0.0001 <0.005 <0.005 <0.0001 <0.005 <0.005 <0.0001 <0.005 <0.005 Cobalt mg/L <0.002 <0.002 0.000221 0.000034 0.000374 0.000101 <0.002 <0.002 0.00106 0.000037 <0.002 <0.002 0.000015 <0.002 <0.002 0.000078 <0.002 <0.002 Copper mg/L <0.001 <0.001 0.00068 0.00015 0.00105 0.00056 <0.001 0.0015 0.00063 0.00007 <0.001 <0.001 0.00019 <0.001 <0.001 0.00037 <0.001 0.003 Iron mg/L 0.363 0.086 1.07 0.055 0.364 0.278 0.331 0.159 2.54 0.458 <0.01 <0.01 0.045 0.389 0.43 0.419 0.323 0.104 Lead mg/L 0.00016 <0.0001 0.000244 0.000091 0.000555 0.000176 <0.0001 <0.0001 0.0002 0.000067 <0.0001 <0.0001 0.000022 <0.0001 <0.0001 0.000147 <0.0001 <0.0001 Lithium mg/L 0.0086 0.0096 0.0187 0.0082 0.0373 0.0196 <0.003 <0.003 0.0062 0.0024 0.0069 0.0067 0.0062 0.0215 0.0236 0.0211 0.0138 0.0201 Manganese mg/L 0.1 0.009 0.376 0.00085 0.752 0.0351 0.0107 0.0042 0.368 0.00097 0.0024 <0.002 0.00317 0.0222 0.0344 0.0016 0.0093 0.0037 Mercury mg/L <0.0001 <0.0001 0.000002 0.000003 0.000001 0.000003 <0.0001 <0.0001 0.000003 <0.000002 <0.0001 <0.0001 <0.000002 <0.0001 <0.0001 <0.000002 <0.0001 <0.0001 Molybdenum mg/L <0.005 <0.005 0.00031 0.00012 0.00155 0.00084 <0.005 <0.005 0.00006 <0.00005 <0.005 <0.005 0.00022 <0.005 <0.005 0.00124 <0.005 <0.005 Nickel mg/L <0.002 <0.002 0.00082 0.0002 0.00162 0.0007 <0.002 <0.002 0.00097 0.00026 <0.002 <0.002 0.00051 <0.002 0.0024 0.00092 <0.002 <0.002 Selenium mg/L <0.0004 <0.0004 0.00012 <0.00004 0.0002 0.00008 <0.0004 <0.0004 0.00011 <0.00004 <0.0004 <0.0004 0.00006 <0.0004 <0.0004 0.00008 <0.0004 <0.0004 Silver mg/L <0.0001 <0.0001 <0.000005 <0.000005 <0.000005 <0.000005 <0.0001 <0.0001 <0.000005 <0.000005 <0.0001 <0.0001 <0.000005 <0.0001 <0.0001 <0.000005 <0.0001 <0.0001 Strontium mg/L - - 0.121 0.0495 0.341 0.157 - - 0.0608 0.0251 - - 0.0351 - - 0.163 - - Thallium mg/L <0.0001 <0.0001 <0.000002 <0.000002 0.000002 <0.000002 <0.0001 <0.0001 0.000002 <0.000002 <0.0001 <0.0001 <0.000002 <0.0001 <0.0001 0.000003 <0.0001 <0.0001 Titanium mg/L <0.001 <0.001 <0.0005 <0.0005 <0.0005 0.0006 <0.001 <0.001 0.0006 <0.0005 <0.001 <0.001 <0.0005 <0.001 <0.001 <0.0005 <0.001 <0.001 Uranium mg/L <0.0001 <0.0001 0.000028 0.000006 0.000805 0.000297 <0.0001 <0.0001 0.000022 0.000007 <0.0001 <0.0001 0.000008 0.00038 0.00029 0.000343 0.00013 0.00032 Vanadium mg/L <0.001 <0.001 <0.0002 <0.0002 <0.0002 <0.0002 <0.001 <0.001 0.0003 0.0002 <0.001 <0.001 0.0003 <0.001 <0.001 0.0004 <0.001 <0.001 Zinc mg/L <0.002 <0.002 0.0155 0.0015 0.025 0.0036 0.0041 0.0029 0.0134 0.0004 <0.002 0.005 0.0005 <0.002 <0.002 0.0006 <0.002 <0.002 Polycyclic Aromatic Hydrocarbons Naphthalene µg/L <0.01 0.014 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - 0.029 0.011 Acenaphthene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - 0.013 <0.01 Anthracene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - <0.01 <0.01 Dibenzo(a,h)anthracene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - <0.01 <0.01 Benzo(a)anthracene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - <0.01 <0.01 Benzo(a)pyrene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - <0.01 <0.01 Benzo(b)fluoranthene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - <0.01 <0.01 Benzo(k)fluoranthene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - <0.01 <0.01 Chrysene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - <0.01 <0.01 Fluoranthene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - <0.01 <0.01 Fluorene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - 0.036 <0.01 Indeno(c,d-123)pyrene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - <0.01 <0.01 Phenanthrene µg/L <0.01 <0.01 - - - - 0.029 <0.01 - - <0.01 0.014 - <0.01 <0.01 - 0.066 0.02 Pyrene µg/L <0.01 <0.01 - - - - <0.01 <0.01 - - <0.01 <0.01 - <0.01 <0.01 - <0.01 <0.01

(a) Chromium results for samples collected in winter 2010 are suspect due to irregularities found in QC samples. Refer to Attachment C for additional information.

- = Not applicable or no data.

Page 52: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project A-3 Water Quality Baseline Report December 2010

Golder Associates

Table A-2 Water Quality Results for Samples Collected from Watercourses During the 2009/2010 Field Program

Parameter Units WC-1 WC-2 WC-5 WC-6 WC-7 WC-17 WC-21 WC-22 WC-23 WC-24

24-Feb-2010

14-May-2010

04-Oct-2009

13-May-2010

13-May-2010

25-Feb-2010

14-Aug-2009

03-Oct-2009

13-May-2010

14-Aug-2009

03-Oct-2009

15-Aug-2009

05-Oct-2009

05-Oct-2009

16-Aug-2009

06-Oct-2009

16-Aug-2009

06-Oct-2009

Field Measured pH - 7.5 8.7 7.05 7.56 7.71 7.53 7.36 7.42 7.53 7.35 8.03 7.35 7.33 7.61 7.69 7.45 7.91 7.49 Specific conductance µS/cm 212 137 575 414 234 205 156 306 161 125 195 335 656 497 286 479 239 437 Temperature °C 0.01 9.6 5.12 7.55 8.04 0.09 12.74 4.3 7.38 13.65 6.17 5.32 1.31 3.77 9.73 3.29 15.54 4.53 Dissolved oxygen mg/L 11.75 13.4 5.06 4.03 6.04 5.17 8.74 7.46 9.92 7.51 11.72 7 10.29 9.88 7.58 10.08 4.91 9.27 Conventional Parameters Specific conductance µS/cm 230 140 393 410 230 200 162 212 160 131 133 350 460 339 304 334 254 303 Colour TCU 25 28 155 100 67 180 116 100 61 48 32 81 43 105 99 71 92 81 Dissolved organic carbon mg/L 12.2 11.1 39.8 38.8 21.1 47 22 19.1 17.5 15.8 13.3 21 14.6 25.8 24.2 21.9 27.6 26.6 Hardness mg/L 111 63.8 177 182 71.3 88.6 83.8 96 75.7 61.4 57.6 172 230 164 159 163 138 127 pH - 7.43 7.66 7.72 7.77 7.62 7.47 7.88 7.87 7.8 7.87 7.79 8.08 8.03 7.97 8.09 8.2 8.09 8.12 Total alkalinity mg/L 100 60 179 180 69 89 81.6 101 68 62.4 59 156 195 156 128 148 104 128 Total dissolved solids mg/L 140 130 219 310 160 180 85.3 106 120 68 67.3 193 261 183 172 182 148 162 Total organic carbon mg/L 12.4 11.2 49.3 39.7 21.2 47 19.9 19.1 18.2 13.9 13 32.9 14.5 25.2 27.9 20.7 23 24 Total suspended solids mg/L 5 10 53 7 2 10 <3 3 15 <3 5 10 <3 <3 6 4 7 8 Major Ions Bicarbonate mg/L 120 73 219 210 84 110 99.6 124 83 76.1 72 190 237 191 156 180 126 156 Calcium mg/L 29.6 17.3 48.6 50.8 20 23.8 22.8 25.8 20.9 16.3 15.5 45.5 60.8 43.3 41.6 43.6 36.3 34.8 Carbonate mg/L <0.5 <0.5 <5 <0.5 <0.5 <0.5 <5 <5 <0.5 <5 <5 <5 <5 <5 <5 <5 <5 <5 Chloride mg/L 2 <1 <0.5 4 2 2 <0.5 <0.5 2 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 0.71 <0.5 Magnesium mg/L 8.03 4.99 13.5 13.5 6.57 7.02 6.52 7.66 6.27 5.03 4.58 14.1 18.9 13.5 13.5 13.2 11.6 9.82 Potassium mg/L 1.46 1.03 1.56 2.97 2.27 3.3 0.72 1.03 1.5 0.93 0.95 1.71 2.38 1.53 1.54 1.73 1.24 1.3 Sodium mg/L 6.25 3.59 23.6 20.5 20.6 12 3.1 4.1 3.59 3.2 3.4 8 12.1 11 7.2 7.8 8.9 13.7 Sulphate mg/L 16 11 23.9 44 49 6 3.16 6.72 13 4.73 7.49 29.6 49.5 20.5 31.5 26.5 26.9 25.2 Sulphide mg/L <0.002 0.003 - 0.074 0.037 0.037 - - 0.01 - - - - - - - - - Nutrients and Biological Indicators Nitrate mg-N/L 1.4 0.02 <0.05 <0.003 <0.003 0.02 <0.05 <0.05 0.07 0.08 <0.05 0.088 0.088 <0.05 0.057 <0.05 <0.05 <0.05 Nitrate + nitrite mg-N/L 0.32 0.005 <0.071 <0.003 <0.003 0.005 <0.071 <0.071 0.015 0.08 <0.071 0.088 0.088 <0.071 <0.071 <0.071 <0.071 <0.071 Nitrite mg-N/L <0.003 <0.003 <0.05 <0.003 <0.003 <0.003 <0.05 <0.05 <0.003 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 <0.05 Nitrogen - ammonia mg-N/L <0.05 <0.05 0.124 0.44 <0.05 0.74 <0.05 0.053 0.08 0.089 <0.05 <0.05 0.06 <0.05 <0.05 <0.05 <0.05 <0.05 Nitrogen - Kjeldahl mg-N/L 0.74 0.71 3.89 4 0.94 2.7 1.03 1.08 0.77 1.06 1.1 1.01 0.72 0.93 1.03 0.69 1.2 0.87 Nitrogen - total mg-N/L 1.06 0.715 3.89 4 0.94 2.705 1.03 1.08 0.785 1.14 1.1 1.098 0.81 0.93 1.03 0.69 1.2 0.87 Phosphorus - total mg-P/L 0.033 0.019 0.595 0.2 0.06 0.16 - 0.081 0.064 - 0.032 - 0.044 0.092 - - - - Phosphorus - dissolved mg-P/L 0.019 0.011 0.051 0.1 0.032 0.11 0.051 0.048 0.031 0.022 <0.02 0.043 0.034 0.065 0.058 <0.02 0.055 0.042 Biochemical oxygen demand mg/L - - - <6 <6 - - - <6 - - - - - - - - - General Organics Naphthenic acids mg/L <1 <1 1.1 <1 <1 <1 1.1 <1 <1 <1 <1 <1 <1 <1 1.1 <1 1.3 <1 Total phenolics mg/L <0.002 0.005 0.0174 0.008 0.005 0.006 0.0043 0.0054 0.006 0.0036 0.0042 0.0022 0.0025 0.0055 0.0024 0.0059 0.0044 0.0077 Total recoverable hydrocarbons mg/L <2 <2 - <2 <2 <2 - - <2 - - - - - - - - - Total Metals Aluminum mg/L 0.0247 0.0352 0.062 0.125 0.0122 0.0818 0.102 0.029 0.154 0.015 0.025 0.028 <0.01 0.038 0.047 0.036 0.062 0.091 Antimony mg/L 0.00007 0.00005 <0.0004 0.00011 0.00004 0.00005 <0.0004 <0.0004 0.00004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 Arsenic mg/L 0.00063 0.00067 0.00074 0.0015 0.00059 0.00109 0.00166 0.00122 0.00106 0.0011 0.00068 0.00079 0.00104 0.00119 0.00167 0.00129 0.00192 0.00151 Barium mg/L 0.0473 0.0301 0.0343 0.0772 0.0176 0.0491 0.0368 0.0362 0.0407 0.0285 0.0276 0.0348 0.0308 0.0258 0.0256 0.0252 0.0257 0.0244 Beryllium mg/L <0.00001 <0.00001 <0.001 0.00003 0.00001 0.00002 <0.001 <0.001 0.00002 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 Bismuth mg/L <0.000005 0.000025 - <0.000005 0.000015 <0.000005 - - 0.000006 - - - - - - - - - Boron mg/L 0.04 0.03 0.09 0.1 0.1 0.07 <0.05 <0.05 <0.05 <0.05 <0.05 0.066 0.073 <0.05 0.059 <0.05 0.072 0.068 Cadmium mg/L <0.000005 0.00001 <0.00005 <0.000005 <0.000005 0.000005 <0.00005 <0.00005 0.00001 <0.00005 <0.00005 <0.00005 <0.00005 <0.00005 <0.00005 <0.00005 <0.00005 <0.00005 Chromium mg/L 0.002(a) <0.0001 <0.005 0.0001 <0.0001 0.0025(a) <0.005 <0.005 0.0002 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 Cobalt mg/L 0.000116 0.000102 <0.002 0.000327 0.000078 0.000683 <0.002 <0.002 0.000433 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 Copper mg/L 0.00069 0.00048 <0.001 0.00065 0.00019 0.00062 <0.001 <0.001 0.0005 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 Iron mg/L 0.503 0.275 0.58 1.03 0.62 3.35 1.87 2.9 1.86 0.273 0.364 0.836 0.605 1.89 1.64 1.19 0.705 0.943 Lead mg/L 0.000069 0.000125 0.00022 0.000186 0.000027 0.000145 0.00013 <0.0001 0.00023 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 0.00014 0.00013 Lithium mg/L 0.0159 0.0099 0.027 0.0284 0.0261 0.0178 <0.01 0.011 0.01 <0.01 <0.01 0.028 0.035 0.023 0.021 0.024 0.023 0.025 Manganese mg/L 0.0572 0.0294 0.255 0.237 0.0305 0.225 0.0914 0.316 0.246 0.0254 0.0433 0.072 0.102 0.223 0.0711 0.0986 0.03 0.0464 Mercury mg/L 0.000003 0.000003 <0.0001 0.000004 0.000003 0.000003 <0.0001 <0.0001 0.000003 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.00002 <0.00002 <0.00002 <0.00002

Page 53: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project A-4 Water Quality Baseline Report December 2010

Table A-2 Water Quality Results for Samples Collected from Watercourses During the 2009/2010 Field Program (continued)

Golder Associates

Parameter Units WC-1 WC-2 WC-5 WC-6 WC-7 WC-17 WC-21 WC-22 WC-23 WC-24

24-Feb-2010

14-May-2010

04-Oct-2009

13-May-2010

13-May-2010

25-Feb-2010

14-Aug-2009

03-Oct-2009

13-May-2010

14-Aug-2009

03-Oct-2009

15-Aug-2009

05-Oct-2009

05-Oct-2009

16-Aug-2009

06-Oct-2009

16-Aug-2009

06-Oct-2009

Methyl mercury µg/L <0.00003 0.00005 - 0.00008 0.00003 <0.00003 - - <0.00003 - - - - - - - - - Molybdenum mg/L 0.00076 0.00061 <0.005 0.00099 0.00075 0.00032 <0.005 <0.005 0.00044 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 Nickel mg/L 0.00098 0.00075 <0.002 0.00157 0.00752 0.00125 <0.002 <0.002 0.00101 <0.002 <0.002 <0.002 <0.002 <0.002 0.002 0.003 0.002 0.003 Selenium mg/L 0.00009 0.00007 <0.0004 0.00015 0.00006 0.00011 <0.0004 <0.0004 0.00005 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 Silver mg/L <0.000005 <0.000005 <0.0001 <0.000005 <0.000005 <0.000005 <0.0001 <0.0001 <0.000005 0.00014 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 Strontium mg/L 0.122 0.073 - 0.255 0.109 0.117 - - 0.0823 - - - - - - - - - Thallium mg/L 0.000002 <0.000002 <0.0001 0.000002 <0.000002 <0.000002 <0.0001 <0.0001 0.000004 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 Titanium mg/L 0.0006 0.0009 0.0018 0.0011 <0.0005 0.0016 0.0027 0.0014 0.0035 <0.001 0.0011 0.0013 0.001 0.0017 0.0026 0.0019 0.0016 0.0021 Uranium mg/L 0.000141 0.000094 0.00034 0.00172 0.000061 0.000069 0.0001 <0.0001 0.000137 <0.0001 <0.0001 0.00039 0.00035 0.00028 0.00024 0.00028 0.00038 0.00039 Vanadium mg/L <0.0002 <0.0002 <0.001 0.0009 <0.0002 0.0005 0.0017 <0.001 0.0006 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 Zinc mg/L 0.002 0.0013 0.0106 0.0091 0.001 0.0065 <0.004 <0.004 0.0023 <0.004 <0.004 <0.004 0.0042 0.0046 <0.004 <0.004 <0.004 <0.004 Dissolved Metals Aluminum mg/L 0.0025 0.0055 0.038 0.0668 0.0173 0.0416 0.013 0.012 0.184 <0.01 <0.01 0.018 <0.01 0.016 0.015 <0.01 0.012 <0.01 Antimony mg/L 0.00007 0.00006 <0.0004 0.0001 0.00004 0.00005 <0.0004 <0.0004 0.00003 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 Arsenic mg/L 0.00055 0.00059 0.00075 0.00134 0.00066 0.00097 0.00128 0.00095 0.00111 0.001 0.00059 0.00073 0.00097 0.00103 0.00143 0.00085 0.00142 0.00124 Barium mg/L 0.0444 0.0267 0.0297 0.039 0.0185 0.0438 0.0311 0.0323 0.0395 0.0261 0.0244 0.0347 0.0303 0.0224 0.0229 0.0224 0.0208 0.0225 Beryllium mg/L <0.00001 <0.00001 <0.001 0.00001 0.00001 0.00002 <0.001 <0.001 0.00003 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 Bismuth mg/L <0.000005 <0.000005 - 0.000036 0.000007 <0.000005 - - 0.000015 - - - - - - - - - Boron mg/L 0.05 0.03 0.076 0.09 0.09 0.07 <0.05 <0.05 <0.05 <0.05 <0.05 0.067 0.078 <0.05 0.061 <0.05 0.065 0.065 Cadmium mg/L 0.000079 <0.000005 <0.00005 <0.000005 <0.000005 0.000154 <0.00005 <0.00005 <0.000005 <0.00005 <0.00005 <0.00005 <0.00005 <0.00005 <0.00005 <0.00005 <0.00005 <0.00005 Chromium mg/L 0.0023(a) <0.0001 <0.005 0.0002 0.0001 0.0024(a) <0.005 <0.005 0.0003 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 Cobalt mg/L 0.000106 0.000057 <0.002 0.000236 0.000153 0.00064 <0.002 <0.002 0.000435 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 Copper mg/L 0.00069 0.0003 <0.001 0.00088 0.00036 0.00064 <0.001 <0.001 0.00071 <0.001 0.0021 <0.001 <0.001 0.0019 0.002 <0.001 <0.001 <0.001 Iron mg/L 0.252 0.126 0.305 0.725 0.87 2.31 1.41 1.19 1.99 0.151 0.119 0.622 0.522 1.02 1.2 0.353 0.816 0.535 Lead mg/L 0.000063 0.000017 <0.0001 0.00014 0.000098 0.000132 <0.0001 <0.0001 0.000297 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 Lithium mg/L 0.0165 0.0093 0.0278 0.0251 0.024 0.0183 0.0084 0.0104 0.0093 0.0078 0.0083 0.0273 0.0351 0.0235 0.0216 0.0214 0.0208 0.0224 Manganese mg/L 0.0529 0.00499 0.177 0.197 0.0851 0.218 0.0591 0.234 0.246 0.0052 0.0135 0.0639 0.108 0.188 0.0508 0.0885 0.0298 0.0404 Mercury mg/L 0.000002 0.000003 <0.0001 <0.000002 <0.000002 0.000002 <0.0001 <0.0001 <0.000002 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.00002 <0.0001 <0.00002 Molybdenum mg/L 0.00078 0.00059 <0.005 0.00114 0.00075 0.00032 <0.005 <0.005 0.00046 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 Nickel mg/L 0.00088 0.0007 0.0025 0.0013 0.00083 0.00123 <0.002 <0.002 0.00109 <0.002 <0.002 <0.002 0.0028 0.0028 <0.002 <0.002 <0.002 <0.002 Selenium mg/L 0.00009 0.00008 <0.0004 0.00016 0.00006 0.00011 <0.0004 <0.0004 0.00004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 <0.0004 Silver mg/L <0.000005 <0.000005 <0.0001 <0.000005 <0.000005 <0.000005 <0.0001 <0.0001 <0.000005 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 Strontium mg/L 0.121 0.074 - 0.241 0.116 0.112 - - 0.0823 - - - - - - - - - Thallium mg/L <0.000002 0.000003 <0.0001 <0.000002 <0.000002 <0.000002 <0.0001 <0.0001 0.000005 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 <0.0001 Titanium mg/L <0.0005 <0.0005 0.0011 <0.0005 <0.0005 0.0009 <0.001 <0.001 0.0074 <0.001 <0.001 0.001 0.0012 0.0012 <0.001 <0.001 <0.001 <0.001 Uranium mg/L 0.000143 0.000091 0.00035 0.00148 0.000061 0.000055 <0.0001 <0.0001 0.000135 <0.0001 <0.0001 0.00037 0.00036 0.00028 0.00023 0.00028 0.00027 0.00038 Vanadium mg/L <0.0002 <0.0002 <0.001 0.0008 0.0003 0.0003 <0.001 <0.001 0.0007 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 Zinc mg/L 0.0021 0.0005 0.0054 0.0116 0.0023 0.0062 <0.002 <0.002 0.0032 <0.002 0.0024 <0.002 <0.002 0.003 0.0031 <0.002 <0.002 0.0061 Polycyclic Aromatic Hydrocarbons and Alkylated Polycyclic Aromatic Hydrocarbons Naphthalene µg/L - - <0.01 - - - 0.025 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.025 <0.01 <0.025 C1 substituted naphthalenes µg/L - - - - - - - - - - - - - - - <0.01 - <0.01 C2 substituted naphthalenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 C3 substituted naphthalenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 C4 substituted naphthalenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 Acenaphthene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 C1 substituted acenaphthenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 Acenaphthylene µg/L - - - - - - - - - - - - - - - <0.01 - <0.01 Anthracene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 Dibenzo(a,h)anthracene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 Benzo(a)anthracene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 C1 substituted benzo(a)anthracenes / chrysenes

µg/L - - - - - - - - - - - - - - - <0.04 - <0.04

C2 substituted benzo(a)anthracenes / chrysenes

µg/L - - - - - - - - - - - - - - - <0.04 - <0.04

C3 substituted benzo(a)anthracenes / chrysenes

µg/L - - - - - - - - - - - - - - - <0.04 - <0.04

Page 54: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project A-5 Water Quality Baseline Report December 2010

Table A-2 Water Quality Results for Samples Collected from Watercourses During the 2009/2010 Field Program (continued)

Golder Associates

Parameter Units WC-1 WC-2 WC-5 WC-6 WC-7 WC-17 WC-21 WC-22 WC-23 WC-24

24-Feb-2010

14-May-2010

04-Oct-2009

13-May-2010

13-May-2010

25-Feb-2010

14-Aug-2009

03-Oct-2009

13-May-2010

14-Aug-2009

03-Oct-2009

15-Aug-2009

05-Oct-2009

05-Oct-2009

16-Aug-2009

06-Oct-2009

16-Aug-2009

06-Oct-2009

C4 substituted benzo(a)anthracenes / chrysenes

µg/L - - - - - - - - - - - - - - - <0.01 - <0.01

Benzo(a)pyrene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 Benzo(b)fluoranthene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 Benzo(k)fluoranthene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 C1 substituted benzofluoranthenes / benzopyrenes

µg/L - - - - - - - - - - - - - - - <0.04 - <0.04

C2 substituted benzofluoranthenes / benzopyrenes

µg/L - - - - - - - - - - - - - - - <0.04 - <0.04

Benzo(g,h,i)perylene µg/L - - - - - - - - - - - - - - - <0.01 - <0.01 Biphenyl µg/L - - - - - - - - - - - - - - - <0.01 - <0.01 C1 substituted biphenyls µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 C2 substituted biphenyls µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 Chrysene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 Dibenzothiophene µg/L - - - - - - - - - - - - - - - <0.01 - <0.01 C1 substituted dibenzothiophenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 C2 substituted dibenzothiophenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 C3 substituted dibenzothiophenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 C4 substituted dibenzothiophenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 Fluoranthene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 C1 substituted fluoranthenes / pyrenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 C2 substituted fluoranthenes / pyrenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 C3 substituted fluoranthenes / pyrenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 Fluorene µg/L - - <0.01 - - - 0.022 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 C1 substituted fluorenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 C2 substituted fluorenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 C3 substituted fluorenes µg/L - - - - - - - - - - - - - - - <0.04 - <0.04 Indeno(c,d-123)pyrene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 Perylene µg/L - - - - - - - - - - - - - - - <0.01 - <0.01 Phenanthrene µg/L - - <0.01 - - - 0.052 <0.01 - <0.01 <0.01 0.012 <0.01 0.01 <0.01 <0.01 <0.01 <0.01 C1 substituted phenanthrenes / anthracenes

µg/L - - - - - - - - - - - - - - - <0.04 - <0.04

C2 substituted phenanthrenes / anthracenes

µg/L - - - - - - - - - - - - - - - <0.04 - <0.04

C3 substituted phenanthrenes / anthracenes

µg/L - - - - - - - - - - - - - - - <0.04 - <0.04

C4 substituted phenanthrenes / anthracenes

µg/L - - - - - - - - - - - - - - - <0.04 - <0.04

Pyrene µg/L - - <0.01 - - - <0.01 <0.01 - <0.01 <0.01 <0.01 <0.01 0.012 <0.01 <0.01 <0.01 <0.01 Retene µg/L - - - - - - - - - - - - - - - <0.01 - <0.01

(a) Chromium results for samples collected in winter 2010 are suspect due to irregularities found in QC samples. Refer to Attachment C for additional information.

- = Not applicable or no data.

Page 55: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

ATTACHMENT B

INDIVIDUAL SEDIMENT SAMPLE TEST RESULTS FOR PROJECT-SPECIFIC SAMPLING

Page 56: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project B-1 Water Quality Baseline Report December 2010

Golder Associates

Table B-1 Sediment Quality Results for Samples Collected During the 2009/2010 Field Program

Parameter Units

[dry wt]

Waterbody Sites Watercourse Sites WB-1 WB-3 WB-5 WC-2 WC-7 WC-21 WC-22 WC-23 WC-24

01-Oct-2009 01-Oct-2009 01-Oct-2009 04-Oct-2009 03-Oct-2009 05-Oct-2009 05-Oct-2009 06-Oct-2009 06-Oct-2009

Physical and Aggregate Properties pH - 6.07 5.84 6.17 6.26 6.04 7.58 6.66 7.02 7.2 Electric conductivity ds/m 0.63 0.13 0.79 1.5 0.47 0.45 0.47 1.48 1.14 Moisture content % 85.3 85.6 55.5 84.8 78.6 30.6 55.2 41 54.2 Organic matter % 60.2 52.1 5.96 <1 15.9 0.54 1.75 1.99 1.21 Total organic carbon % 3.5 <0.4 1 1.2 0.7 Sand(a) % 62.3 58.1 8.3 28.3 37.3 88.5 88.6 77 80 Silt and clay(a) % 37.7 41.9 91.7 71.7 62.7 11.5 11.4 23 20 Salinity and Soluble Ions Sodium adsorption ratio SAR 0.73 0.47 0.53 0.66 0.4 0.61 0.76 2.08 0.89 Theoretical gypsum requirements

tons/acre <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1

Sodium mg/L 25.3 7.1 21 41.6 12 19.5 23 38.6 11.6 Calcium mg/L 63.2 11.7 86.5 212 50.9 52.3 47.4 49.2 32.9 Magnesium mg/L 16.9 3.3 20.2 56.1 11.2 16.1 13.4 43.6 32.8 Potassium mg/L 8.4 4.7 8.8 10.1 5.1 5.5 6.4 9.7 14.2 Chloride mg/L <20 <20 30 46 <20 <20 84 33 133 Sulphate mg/L 207 19.5 287 743 143 97.9 171 548 386 Saturation % 585 550 130 489 153 27 27 35 27 Nutrients Nitrate + nitrite mg-N/L <1 <1 <1 <1 <1 2.1 <1 <1 <1 Nitrogen - ammonia mg-N/L 120 33.9 93.6 47.7 50.8 2.18 5.81 37 28.8 Nitrogen - Kjeldahl % 2.54 1.67 0.488 1.8 0.537 0.029 0.049 0.088 0.043 Phosphorus - total µg-P/g 829 825 1400 1100 1500 450 298 505 368 Phosphate - available µg-P/g 8.6 2.9 2.9 6.1 <2 13.3 10.6 7.8 5.1 Sulphur - total % 2.27 0.38 0.26 2 0.17 <0.1 <0.1 <0.1 0.13 Sulphide µg-S/g 8.26 10.8 38.4 183 48.2 1.06 165 1.06 <0.2 General Organics Phenols µg/g <0.1 <0.1 <0.1 5.1 <0.1 <0.1 <0.1 0.11 0.38 Total Metals Antimony µg/g 0.23 <0.4 0.48 <0.4 <0.4 <0.2 <0.2 <0.2 <0.2 Arsenic µg/g 1.94 1.14 11.2 4.38 11.5 4.76 1.51 8.38 2.67 Barium µg/g 91.1 85 209 110 197 30.4 33.4 117 43 Beryllium µg/g <1 <2 <1 <2 <2 <1 <1 <1 <1 Boron µg/g 4.12 1.41 3.54 19.6 3.46 0.36 0.72 1.46 0.63 Cadmium µg/g 0.5 <1 0.61 <1 <1 <0.5 <0.5 <0.5 <0.5

Page 57: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project B-2 Water Quality Baseline Report December 2010 Table B-1 Sediment Quality Results for Samples Collected During the 2009/2010 Field Program (continued)

Golder Associates

Parameter Units

[dry wt]

Waterbody Sites Watercourse Sites WB-1 WB-3 WB-5 WC-2 WC-7 WC-21 WC-22 WC-23 WC-24

01-Oct-2009 01-Oct-2009 01-Oct-2009 04-Oct-2009 03-Oct-2009 05-Oct-2009 05-Oct-2009 06-Oct-2009 06-Oct-2009

Chromium µg/g 6.87 6.7 16.3 11.4 10.7 2.28 2.97 5.57 6.1 Cobalt µg/g 4.4 4 8.6 7.4 7.4 1.7 1.6 5.3 2.9 Copper µg/g 11.1 10.2 18.8 21.8 8.3 <2 <2 5.8 4.6 Lead µg/g 5.1 <10 11.6 <10 <10 <5 <5 <5 <5 Mercury µg/g 0.059 0.072 0.061 0.081 <0.05 <0.05 <0.05 <0.05 <0.05 Methyl mercury µg/g 0.000332 0.00164 0.00233 0.0013 0.000745 0.000159 0.000197 0.000327 0.000397 Molybdenum µg/g <1 <2 2.1 2.3 <2 <1 <1 1.2 <1 Nickel µg/g 18.7 10.4 22.8 24.2 11.1 2.4 2.8 8.1 6 Selenium µg/g 1.37 0.89 1.34 2.02 0.64 <0.2 0.25 0.43 <0.2 Silver µg/g <1 <2 <1 <2 <2 <1 <1 <1 <1 Thallium µg/g <1 <2 <1 <2 <2 <1 <1 <1 <1 Tin µg/g <5 <10 <5 <10 <10 <5 <5 <5 <5 Uranium µg/g <2 <4 <2 6.9 <4 <2 <2 <2 <2 Vanadium µg/g 10.8 8.1 25 22.1 20.5 3.8 4.3 13 9 Zinc µg/g 91 120 73 74 53 13 11 28 17 Polycyclic Aromatic Hydrocarbons and Alkylated Polycyclic Aromatic Hydrocarbons Naphthalene µg/g 0.054 0.052 0.01 0.07 0.032 <0.01 0.016 0.01 0.017 1-Methylnaphthalene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 2-Methylnaphthalene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 C2 substituted naphthalenes

µg/g <0.12 <0.12 <0.04 0.18 <0.12 <0.04 <0.04 <0.04 <0.04

C3 substituted naphthalenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C4 substituted naphthalenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

Acenaphthene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 C1 substituted acenaphthenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

Acenaphthylene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Anthracene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Dibenzo(a,h)anthracene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Benzo(a)anthracene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 C1 substituted benzo(a)anthracenes / chrysenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

Page 58: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project B-3 Water Quality Baseline Report December 2010 Table B-1 Sediment Quality Results for Samples Collected During the 2009/2010 Field Program (continued)

Golder Associates

Parameter Units

[dry wt]

Waterbody Sites Watercourse Sites WB-1 WB-3 WB-5 WC-2 WC-7 WC-21 WC-22 WC-23 WC-24

01-Oct-2009 01-Oct-2009 01-Oct-2009 04-Oct-2009 03-Oct-2009 05-Oct-2009 05-Oct-2009 06-Oct-2009 06-Oct-2009

C2 substituted benzo(a)anthracenes / chrysenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C3 substituted benzo(a)anthracenes / chrysenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C4 substituted benzo(a)anthracenes / chrysenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

Benzo(a)pyrene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 C1 substituted benzofluoranthenes / benzopyrenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C2 substituted benzofluoranthenes / benzopyrenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

Benzo(e)pyrene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Benzo(k)fluoranthene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Benzo(b&j)fluoranthene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Benzo(g,h,i)perylene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Biphenyl µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 C1 substituted biphenyls µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04 C2 substituted biphenyls µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04 Chrysene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Dibenzothiophene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 C1 substituted dibenzothiophenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C2 substituted dibenzothiophenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C3 substituted dibenzothiophenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C4 substituted dibenzothiophenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

Fluoranthene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 C1 substituted fluoranthenes / pyrenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C2 substituted fluoranthenes / pyrenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

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Dover Commercial Project B-4 Water Quality Baseline Report December 2010 Table B-1 Sediment Quality Results for Samples Collected During the 2009/2010 Field Program (continued)

Golder Associates

Parameter Units

[dry wt]

Waterbody Sites Watercourse Sites WB-1 WB-3 WB-5 WC-2 WC-7 WC-21 WC-22 WC-23 WC-24

01-Oct-2009 01-Oct-2009 01-Oct-2009 04-Oct-2009 03-Oct-2009 05-Oct-2009 05-Oct-2009 06-Oct-2009 06-Oct-2009

C3 substituted fluoranthenes / pyrenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

Fluorene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 C1 substituted fluorenes µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04 C2 substituted fluorenes µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04 C3 substituted fluorenes µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04 Indeno(1,2,3-cd)pyrene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Perylene µg/g <0.03 <0.03 0.068 0.03 0.033 <0.01 0.012 <0.01 0.038 Phenanthrene µg/g 0.03 <0.03 <0.01 0.054 <0.03 <0.01 0.01 <0.01 <0.01 C1 substituted phenanthrenes / anthracenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C2 substituted phenanthrenes / anthracenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C3 substituted phenanthrenes / anthracenes

µg/g <0.12 <0.12 <0.04 <0.12 <0.12 <0.04 <0.04 <0.04 <0.04

C4 substituted phenanthrenes / anthracenes

µg/g 0.29 0.59 0.175 0.19 <0.12 <0.04 <0.04 <0.04 <0.04

Pyrene µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Retene µg/g 0.289 0.588 0.175 0.191 0.053 <0.01 0.02 <0.01 0.029 Polycyclic Aromatic Nitrogen Heterocycles Acridine µg/g <0.03 <0.03 <0.01 <0.03 <0.03 <0.01 <0.01 <0.01 <0.01 Quinoline µg/g <0.03 <0.01 0.047 0.04 <0.03 <0.01 <0.01 <0.01 <0.01 (a)

Sand percentage based on sieve analysis with mesh diameter of 75 µm; silt and clay percentage = (100% - sand).

- = Not applicable.

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ATTACHMENT C

QUALITY ASSURANCE/QUALITY CONTROL RESULTS

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Dover Commercial Project C-1 Quality Assurance/Quality Control December 2010

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1 QUALITY ASSURANCE/QUALITY CONTROL

1.1 INTRODUCTION

Quality Assurance and Quality Control (QA/QC) practices determine data integrity and are relevant to all aspects of a study, from sample collection to data analysis and reporting. Quality Assurance encompasses management and technical practices designed to ensure that the data generated are of consistent high quality. Quality Control is an aspect of QA and includes the procedures used to measure and evaluate data quality, and the corrective actions to be taken when data quality objectives are not met. This appendix describes QA/QC practices applied during this study, evaluates QC data, and describes the implications of QC results to the interpretation of study results.

1.2 QUALITY CONTROL/QUALITY ASSURANCE PRACTICES

1.2.1 Quality Assurance

Quality Assurance applicable to this study cover three areas of internal and external management, as described below.

1.2.1.1 Field Staff Guidance

Field work was completed according to approved specific work instructions (SWIs) and established technical procedures (TPs). SWIs are standardized forms that describe exact sampling locations and provide specific sampling instructions, equipment needs and calibration requirements, required technical procedures, sample labelling and shipping protocols and laboratory contacts. They also provide specific guidelines for field record keeping and sample tracking. TPs are consistent with standard field methods described in the relevant scientific literature (e.g., Environment Canada 1993; American Public Health Association [APHA] 1992), and outline sample collection, preservation, handling, storage and shipping protocols.

During field work, field data were recorded on standardized field data sheets or in a bound field book, according to established field record-keeping procedures. Samples were documented and tracked using chain-of-custody forms and receipt of samples by the analytical laboratory was confirmed.

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One field crew member was responsible for managing the sample shipping process to ensure that:

all required samples were collected;

chain-of-custody and analytical request forms were completed and correct;

proper labelling and documentation procedures were followed; and

samples were delivered to the appropriate locations in a timely manner.

1.2.1.2 Laboratory

One member of the project team was designated as the lab liaison. To ensure that high quality data were generated, laboratories used for the sample analysis are accredited by the Canadian Association for Laboratory Accreditation Inc. (CALA). Under CALA’s accreditation program, performance evaluation assessments are conducted annually for laboratory procedures, methods and internal quality control.

1.2.1.3 Office Operations

Office-related QA included use of appropriately trained personnel for each task and senior review of work products at appropriate milestones, use of standardized data manipulation/summary tools, filing of data and project information according to standardized protocols and establishment of a data management system to ensure an organized consistent system of data storage, QC and retrieval.

1.2.2 Quality Control

1.2.2.1 Field Quality Control Procedures

The water quality field QC program consisted of the collection and analysis of field blanks, and duplicate and split samples. Each QC sample type is described below:

Field blanks consist of de-ionized water provided by the analytical laboratory, which is exposed to the sampling environment at the sample site and handled in the same manner as the surface water samples collected during the field program (e.g., preserved, filtered). Field blanks are used to detect potential sample contamination during sample collection, handling, shipping and analysis.

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Dover Commercial Project C-3 Quality Assurance/Quality Control December 2010

Golder Associates

Travel blanks consist of de-ionized water provided by the analytical laboratory in a set of sample bottles that is the same as would be used for a field sample, which is brought to the sample site but is not exposed to the sampling environment (i.e., travel blank sample bottles are neither opened in the field nor preserved/filtered) and shipped in the same manner as the surface water samples collected during the field program. Travel blanks are used to detect potential sample contamination during sample shipping, handling and analysis without influence of direct exposure to the sampling environment.

Duplicate samples are additional samples collected at the same time and location as surface water samples collected during a field program, using the same sampling methods. They are used to check within-site variation.

Quality Control samples collected during the field program accounted for approximately 10% of the total number of samples submitted for analysis. These samples were handled, stored and shipped along with field-collected surface water samples, and were submitted “blind” to the analytical laboratories, with the exception of travel blanks. Quality Control samples were analyzed for the same set of parameters as the samples collected from surface waters.

1.2.2.2 Office Quality Control Procedures

Key elements of office QC procedures included the following:

comparing sample data entered into the project database and data in report tables against final laboratory reports;

creating backup files before each major operation as data were being manipulated; and

verifying the accuracy of calculations performed to generate summary statistics.

Initial Data Screening

Upon receipt of water quality data from the analytical laboratory, a series of standard checks were performed to screen for potential data quality issues. These allowed potential re-analysis of samples to verify questionable data, or generate data for missing parameters. The following data checks were performed:

verification that all required parameters and samples were analyzed;

verification that data are reported using the appropriate units;

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Golder Associates

logic checks: presence of zero values, comparisons of TDS and conductivity, hardness and alkalinity, total and dissolved phosphorus, total and dissolved metals, measured and calculated TDS;

checking blanks for evidence of contamination (see next section);

checking duplicate samples for evidence of unacceptable variation (see next section); and

checking field-collected data for completeness, and unexpected values and trends.

If results of initial data screening indicated that there were deficiencies or potential data quality issues, the analytical laboratory was contacted and re-analysis of the parameters in question in the affected samples was requested. If data were verified by the analytical laboratory, but remained questionable based on the above evaluation, qualifiers were added to affected concentrations in the project data set and they were excluded for consideration during data summary and analysis.

Similarly, historic data were assessed to identify data points that were associated with high analytical detection limits relative to recent detectable results. These data were flagged and removed from the data summary reports produced for the baseline report. Laboratories were not contacted regarding historical data as laboratory hold times for reanalysis would be exceeded.

Quality Control Data Evaluation

Field Blanks and Travel Blanks

Concentrations in field and travel blanks were considered notable if they were greater than or equal to five times the corresponding Method Detection Limit (MDL). This threshold is based on the Practical Quantitation Limit defined by the United States Environmental Protection Agency (U.S. EPA 1985), and takes into account the potential for reduced accuracy when concentrations approach or are below MDLs. This criterion was not applied to pH and conductance, which is expected to be above the laboratory-reported MDL in the deionized water used to prepare blanks.

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Dover Commercial Project C-5 Quality Assurance/Quality Control December 2010

Golder Associates

The implications of notable results in blanks to data quality were evaluated relative to concentrations observed in surface waters sampled during the field program. The aim of this evaluation was to determine whether contamination was limited to a blank or was apparent in the corresponding water samples as well and whether it was severe enough to warrant qualifying the affected data. To address these questions, notable concentrations in blanks were interpreted as follows:

If the blank had a detectable concentration of a parameter that was higher than those in the corresponding surface water samples, it was assumed that the concentration in the blank was the result of an isolated field or lab error. In this case, the corresponding water samples were considered uncontaminated.

If the detectable concentration in the blank was less than 20% of the typical surface water concentration, the data for the corresponding water samples were considered acceptable for the parameter in question.

If the detectable concentration in a single blank was greater than 20% of the typical surface water concentration, but below those in the corresponding water samples, the water samples were considered potentially contaminated and the constituent results in question were compared to other available data to determine the significance of the potential contamination.

Duplicate Samples

Differences between concentrations measured in duplicate water samples were calculated as the relative percent difference (RPD) for each parameter. Before calculating the RPD, concentrations below the MDL were replaced with the MDL value in cases when only one of the concentrations for a given parameter was detectable. The RPD was calculated using the following formula:

RPD = (difference in concentration between duplicate samples/mean concentration) x 100

The RPD value for a given parameter was considered notable if:

it was greater than 20%; and

concentrations in one or both samples were greater than or equal to five times the MDL.

These criteria are consistent with those used by analytical laboratories for their internal QC procedures and take into account the potential for data accuracy error as parameter concentrations approach MDLs. The number of parameters with

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Golder Associates

exceedances of the assessment criteria was compared with the total number of parameters analyzed to evaluate and rate within-site variation as follows:

low, if less than 10% of the total number of parameters were notably different from one another;

moderate, if 10 to 30% of the total number of parameters were notably different from one another; or

high, if more than 30% of the total number of parameters were notably different from one another.

1.3 QUALITY CONTROL RESULTS

1.3.1 Field and Travel Blanks

Concentrations in the summer 2009 field and travel blanks were generally non-detectable or less than five times the MDL, with the exception of naphthalene in the field blank prepared August 19, 2009 (Table C-1). However, the observed naphthalene concentration in the field blank was greater than those observed in the corresponding surface water samples. The surface water samples collected in August 2009 are, therefore, considered free of contamination. No concentrations in the fall 2009 field and travel blanks were greater than five times the MDL, indicating that the corresponding field samples were free of contamination.

Concentrations of total mercury and total and dissolved chromium, copper, lead and zinc were greater than five times the MDL in the field blank prepared on February 25, 2010. However, the observed mercury concentration in the field blank was greater than those observed in the corresponding surface water samples and the observed total and dissolved lead and zinc concentrations were less than 20% of the typical surface water concentrations observed in the corresponding surface water samples. The analytical results for surface water samples collected in February 2010 are therefore unaffected by contamination for total mercury and are considered of acceptable quality for total and dissolved lead and zinc.

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Dover Commercial Project C-7 Quality Assurance/Quality Control December 2010

Table C-1 Results for Travel and Field Blank Samples

Parameter Unit

Method Detection

Limit (MDL)

Travel Blank

Field BlankTravel Blank

Field Blank Method Detection

Limit (MDL)

Field Blank Field Blank

18-Aug-09 19-Aug-09 29-Sep-09 06-Oct-09 25-Feb-10 17-May-10

Conventional Parameters

Conductance µS/cm 0.2 <0.2 <0.2 0.69 1.14 1 1 1

Colour TCU 2 <2 <2 <2 <2 2 <2 <2

Dissolved organic carbon mg/L 1 <1 1.3 <1 <1 0.5 <0.5 <0.5

Hardness mg/L 1 <1 <1 <1 <1 0.5 <0.5 <0.5

pH - - 5.65 5.41 5.69 6.12 n/a 5.41 5.31

Total alkalinity mg/L 5 <5 <5 <5 <5 0.5 <0.5 <0.5

Total dissolved solids mg/L 1 <1 <1 <1 <1 10 <10 76

Total organic carbon mg/L 1 <1 <1 <1 <1 0.5 <0.5 <0.5

Total suspended solids mg/L 3 <3 <3 <3 3 1 <1 1

Major Ions

Bicarbonate mg/L 5 <5 <5 <5 <5 0.5 <0.5 <0.5

Calcium mg/L 5 <5 <5 <5 <5 0.05 <0.05 <0.05

Carbonate mg/L 0.5 <0.5 <0.5 <0.5 <0.5 0.5 <0.5 <0.5

Chloride mg/L 0.5 <0.5 <0.5 <0.5 <0.5 1 <1 <1

Magnesium mg/L 0.1 <0.1 <0.1 <0.1 <0.1 0.05 <0.05 <0.05

Potassium mg/L 0.5 <0.5 <0.5 <0.5 <0.5 0.05 <0.05 <0.05

Sodium mg/L 1 <1 <1 <1 <1 0.05 <0.05 <0.05

Sulphate mg/L 0.5 <0.5 <0.5 <0.5 <0.5 1 <1 <1

Sulphide mg/L - - - - - 0.002 <0.002 <0.002

Nutrients and Biological Indicators

Nitrate mg-N/L 0.05 <0.05 <0.05 <0.05 <0.05 - - -

Nitrite mg-N/L 0.05 <0.05 <0.05 <0.05 <0.05 - - -

Nitrate + nitrite mg-N/L 0.071 <0.071 <0.071 <0.071 <0.071 0.003 <0.003 0.004

Nitrogen - ammonia mg-N/L 0.05 <0.05 <0.05 <0.05 <0.05 0.05 <0.05 <0.05

Nitrogen - Kjeldahl mg-N/L 0.2 <0.2 <0.2 <0.2 <0.2 0.05 <0.05 <0.05

Phosphorus - dissolved mg-P/L 0.02 <0.02 <0.02 <0.02 <0.02 0.001 0.003 <0.001

Phosphorus - total mg-P/L 0.02 - - <0.02 - 0.001 0.003 0.001

Chlorophyll a µg/L - - - - - 0.5 - 0.7

General Organics

Naphthenic acids mg/L 1 <1 <1 <1 <1 1 <1 <1

Phenols mg/L 0.001 <0.001 <0.001 <0.001 <0.001 0.002 <0.002 0.002

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Dover Commercial Project C-8 Quality Assurance/Quality Control December 2010

Table C-1 Results for Travel and Field Blank Samples (continued)

Golder Associates

Parameter Unit

Method Detection

Limit (MDL)

Travel Blank

Field BlankTravel Blank

Field Blank Method Detection

Limit (MDL)

Field Blank Field Blank

18-Aug-09 19-Aug-09 29-Sep-09 06-Oct-09 25-Feb-10 17-May-10

Total recoverable hydrocarbons mg/L - - - - - 2 <2 <2

Total Metals

Aluminum (Al) µg/L 10 <10 <10 <10 <10 0.2 0.3 0.6

Antimony (Sb) µg/L 0.4 <0.4 <0.4 <0.4 <0.4 0.02 <0.02 <0.02

Arsenic (As) µg/L 0.4 <0.4 <0.4 <0.4 <0.4 0.02 <0.02 <0.02

Barium (Ba) µg/L 3 <3 <3 <3 <3 0.02 0.02 0.03

Beryllium (Be) µg/L 1 <1 <1 <1 <1 0.01 <0.01 <0.01

Bismuth (Bi) µg/L - - - - - 0.005 <0.005 0.043

Boron (B) µg/L 50 <50 <50 <50 <50 20 <20 <20

Cadmium (Cd) µg/L 0.05 <0.05 <0.05 <0.05 <0.05 0.005 <0.005 0.005

Chromium (Cr) µg/L 5 <5 <5 <5 <5 0.1 2 <0.1

Cobalt (Co) µg/L 2 <2 <2 <2 <2 0.005 <0.005 <0.005

Copper (Cu) µg/L 1 <1 <1 <1 <1 0.05 0.32 0.14

Iron (Fe) µg/L 10 <10 <10 <10 <10 1 3 1

Lead (Pb) µg/L 0.1 <0.1 <0.1 <0.1 <0.1 0.005 0.032 0.299

Lithium (Li) µg/L 10 <10 <10 <10 <10 0.5 <0.5 <0.5

Manganese (Mn) µg/L 5 <5 <2 <2 <2 0.05 <0.05 0.06

Mercury (Hg) µg/L 0.1 / 0.02 <0.1 <0.1 <0.1 <0.02 0.001 0.013 0.003

Methyl mercury µg/L - - - - - 0.00003 <0.00003 0.00004

Molybdenum (Mo) µg/L 5 <5 <5 <5 <5 0.05 <0.05 <0.05

Nickel (Ni) µg/L 2 <2 <2 <2 <2 0.02 <0.02 <0.02

Selenium (Se) µg/L 0.4 <0.4 <0.4 <0.4 <0.4 0.04 <0.04 <0.04

Silver (Ag) µg/L 0.1 <0.1 <0.1 <0.1 <0.1 0.005 <0.005 <0.005

Strontium (Sr) µg/L - - - - - 0.05 <0.05 0.06

Thallium (Tl) µg/L 0.1 <0.1 <0.1 <0.1 <0.1 0.002 <0.002 <0.002

Tin (Sn) µg/L 50 <50 <50 <50 <50 0.01 <0.01 <0.01

Titanium (Ti) µg/L 1 <1 <1 <1 <1 0.5 <0.5 <0.5

Uranium (U) µg/L 0.1 <0.1 <0.1 <0.1 <0.1 0.002 <0.002 <0.002

Vanadium (V) µg/L 1 <1 <1 <1 <1 0.2 <0.2 <0.2

Zinc (Zn) µg/L 4 <4 <4 <4 <4 0.1 1.3 0.7

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Dover Commercial Project C-9 Quality Assurance/Quality Control December 2010

Table C-1 Results for Travel and Field Blank Samples (continued)

Golder Associates

Parameter Unit

Method Detection

Limit (MDL)

Travel Blank

Field BlankTravel Blank

Field Blank Method Detection

Limit (MDL)

Field Blank Field Blank

18-Aug-09 19-Aug-09 29-Sep-09 06-Oct-09 25-Feb-10 17-May-10

Dissolved Metals

Aluminum (Al) µg/L 10 <10 <10 <10 <10 0.2 0.3 0.3

Antimony (Sb) µg/L 0.4 <0.4 <0.4 <0.4 - 0.02 <0.02 <0.02

Arsenic (As) µg/L 0.4 <0.4 <0.4 <0.4 <0.4 0.02 <0.02 <0.02

Barium (Ba) µg/L 3 <3 <3 <3 <3 0.02 <0.02 <0.02

Beryllium (Be) µg/L 1 <1 <1 <1 <1 0.01 <0.01 <0.01

Bismuth (Bi) µg/L - - - - - 0.005 <0.005 <0.005

Boron (B) µg/L 50 <50 <50 <50 <50 20 <20 <20

Cadmium (Cd) µg/L 0.05 <0.05 <0.05 <0.05 <0.05 0.005 <0.005 0.006

Chromium (Cr) µg/L 5 <5 <5 <5 <5 0.1 1.5 <0.1

Cobalt (Co) µg/L 2 <2 <2 <2 <2 0.005 <0.005 <0.005

Copper (Cu) µg/L 1 <1 <1 <1 <1 0.05 0.43 <0.05

Iron (Fe) µg/L 10 <10 <10 <10 <10 1 3 <1

Lead (Pb) µg/L 0.1 <0.1 <0.1 <0.1 <0.1 0.005 0.039 <0.005

Lithium (Li) µg/L 3 <3 <3 <3 <3 0.5 <0.5 <0.5

Manganese (Mn) µg/L 2 <2 <2 <2 <2 0.05 0.08 <0.05

Mercury (Hg) µg/L 0.1 <0.1 <0.1 <0.1 <0.02 0.001 <0.001 <0.002

Molybdenum (Mo) µg/L 5 <5 <5 <5 <5 0.05 <0.05 <0.05

Nickel (Ni) µg/L 2 <2 <2 <2 <2 0.02 0.04 <0.02

Selenium (Se) µg/L 0.4 <0.4 <0.4 <0.4 <0.4 0.04 <0.04 <0.04

Silver (Ag) µg/L 0.1 <0.1 <0.1 <0.1 <0.1 0.005 <0.005 <0.005

Strontium (Sr) µg/L - - - - - 0.05 0.07 <0.05

Thallium (Tl) µg/L 0.1 <0.1 <0.1 <0.1 <0.1 0.002 <0.002 <0.002

Tin (Sn) µg/L 50 <50 <50 <50 <50 0.01 <0.01 <0.01

Titanium (Ti) µg/L 1 <1 <1 <1 <1 0.5 <0.5 <0.5

Uranium (U) µg/L 0.1 <0.1 <0.1 <0.1 <0.1 0.002 <0.002 <0.002

Vanadium (V) µg/L 1 <1 <1 <1 <1 0.2 <0.2 0.3

Zinc (Zn) µg/L 2 <2 <2 <2 <2 0.1 1.7 <0.1

Polycyclic Aromatic Hydrocarbons

Acenaphthene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Acenaphthylene µg/L 0.01 - - - <0.01 - - -

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Dover Commercial Project C-10 Quality Assurance/Quality Control December 2010

Table C-1 Results for Travel and Field Blank Samples (continued)

Golder Associates

Parameter Unit

Method Detection

Limit (MDL)

Travel Blank

Field BlankTravel Blank

Field Blank Method Detection

Limit (MDL)

Field Blank Field Blank

18-Aug-09 19-Aug-09 29-Sep-09 06-Oct-09 25-Feb-10 17-May-10

Acridine µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Anthracene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Benz[a]anthracene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Benzo[b]fluoranthene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Benzo[e] Pyrene µg/L 0.01 - - - <0.01 - - -

Benzo[g,h,i] perylene µg/L 0.01 - - - <0.01 - - -

Benzo[k]fluoranthene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Benzo[a]pyrene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Biphenyl µg/L 0.01 - - - <0.01 - - -

Chrysene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Dibenz[a,h]anthracene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Dibenzothiophene µg/L 0.01 - - - <0.01 - - -

Fluoranthene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Fluorene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Indeno[1,2,3-cd]pyrene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Naphthalene µg/L 0.01 / 0.025 <0.01 0.09 0.01 <0.025 - - -

Perylene µg/L 0.01 - - - <0.01 - - -

Phenanthrene µg/L 0.01 <0.01 <0.01 0.02 <0.01 - - -

Pyrene µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Quinoline µg/L 0.01 <0.01 <0.01 <0.01 <0.01 - - -

Retene µg/L 0.01 - - - <0.01 - - -

Alkylated Polycyclic Aromatic Hydrocarbons

C1 acenapthenes µg/L 0.04 - - - <0.04 - - -

C1 benzo(a)anthracenes/chrysenes µg/L 0.04 - - - <0.04 - - -

C1 benzofluoranthenes/benzopyrenes µg/L 0.04 - - - <0.04 - - -

C1 biphenyl µg/L 0.04 - - - <0.04 - - -

C1 dibenzothiophene µg/L 0.04 - - - <0.04 - - -

C1 fluoranthenes/pyrenes µg/L 0.04 - - - <0.04 - - -

C1 fluorenes µg/L 0.04 - - - <0.04 - - -

C1 phenanthrene/anthracene µg/L 0.04 - - - <0.04 - - -

C2 benzo(a)anthracenes/chrysenes µg/L 0.04 - - - <0.04 - - -

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Dover Commercial Project C-11 Quality Assurance/Quality Control December 2010

Table C-1 Results for Travel and Field Blank Samples (continued)

Golder Associates

Parameter Unit

Method Detection

Limit (MDL)

Travel Blank

Field BlankTravel Blank

Field Blank Method Detection

Limit (MDL)

Field Blank Field Blank

18-Aug-09 19-Aug-09 29-Sep-09 06-Oct-09 25-Feb-10 17-May-10

C2 benzofluoranthenes/benzopyrenes µg/L 0.04 - - - <0.04 - - -

C2 biphenyl µg/L 0.04 - - - <0.04 - - -

C2 dibenzothiophene µg/L 0.04 - - - <0.04 - - -

C2 fluoranthenes/pyrenes µg/L 0.04 - - - <0.04 - - -

C2 fluorene µg/L 0.04 - - - <0.04 - - -

C2 naphthalenes µg/L 0.04 - - - <0.04 - - -

C2 phenanthrene/anthracenes µg/L 0.04 - - - <0.04 - - -

C3 benzanthracenes/chrysenes µg/L 0.04 - - - <0.04 - - -

C3 Dibenzothiophenes µg/L 0.04 - - - <0.04 - - -

C3 Fluoranthenes/Pyrenes µg/L 0.04 - - - <0.04 - - -

C3 Fluorenes µg/L 0.04 - - - <0.04 - - -

C3 naphthalenes µg/L 0.04 - - - <0.04 - - -

C3 phenanthrenes/anthracenes µg/L 0.04 - - - <0.04 - - -

C4 benzanthracenes/chrysenes µg/L 0.04 - - - <0.01 - - -

C4 dibenzothiophenes µg/L 0.04 - - - <0.04 - - -

C4 naphthalenes µg/L 0.04 - - - <0.04 - - -

C4 phenanthrenes/anthracenes µg/L 0.04 - - - <0.04 - - -

1-Methylnaphthalene µg/L 0.01 - - - <0.01 - - -

2-Methylnaphthalene µg/L 0.01 - - - <0.01 - - -

- = No data or not applicable.

Note: Values in bold were more than 5 times the MDL.

Page 72: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project C-12 Quality Assurance/Quality Control December 2010

Golder Associates

The total and dissolved chromium and copper concentrations observed in the February 25, 2010 field blank were greater than 20% of the typical surface water concentrations observed in the corresponding surface water samples, indicating that the surface water sample concentrations for these constituents may be affected by contamination up to the level observed in the field blank. The observed concentrations of chromium in the spring 2010 surface water samples were higher than those detectable in surface waters in the region and above water quality guideline values, indicating that the potential contamination was notable. Total and dissolved chromium results potentially affected by this contamination were flagged and interpreted with this limitation in mind. The observed concentrations of copper in the spring 2010 surface water samples were comparable to those detectable in surface waters in the region and below water quality guideline values, indicating that the potential contamination was of limited significance.

Concentrations of total bismuth and lead were greater than five times the MDL in the field blank prepared on May 17, 2010. However, the observed total bismuth and lead concentrations in the field blank were greater than those observed in the corresponding surface water samples. The surface water samples collected in spring 2010 are, therefore, considered free of contamination.

1.3.2 Duplicate Samples

Duplicate samples were collected in summer and fall 2009 and spring 2010. A duplicate sample was not collected in winter 2010 due to the limited number of accessible sampling stations with sufficient water available for collection. Based on the RPDs, notable variations observed between concentrations in duplicate samples were as follows (Table C-2):

August 14, 2009 duplicate samples at Site WC-7: none.

September 29, 2009 duplicate samples at Site WB-4: total iron.

May 19, 2010 duplicate samples at Site LC4: total aluminum.

The two parameters with notable differences account for about 1% of the total number of parameters analyzed. Based on these results, within-site variability was rated low for the 2009/2010 water quality baseline monitoring program.

Page 73: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project C-13 Quality Assurance/Quality Control December 2010

Table C-2 Duplicate Sample Results

Parameter Units

Method Detection

Limit (MDL)

WC-7 Duplicates Relative Percent

Difference

WB-4 Duplicates Relative Percent

Difference

Method Detection

Limit (MDL)

WC-1 Duplicates Relative Percent

Difference Sample 1 Sample 2 Sample 1 Sample 2 Sample 1 Sample 2

14-Aug-09 14-Aug-09 29-Sep-09 29-Sep-09 14-May-10 14-May-10

Conventional Parameters

Conductance µS/cm 0.2 162 162 0.0% 70.3 70.4 0.1% 1 140 140 0.0%

Colour TCU 2 116 116 0.0% 8 10 - 2 28 28 0.0%

Dissolved organic carbon mg/L 1 22 21.9 0.5% 7.2 8.8 20.0% 0.5 10.6 11.1 4.6%

Hardness mg/L 1 83.8 84.5 0.8% 27.6 28.2 2.2% 0.5 61 61.8 1.3%

pH - - 7.88 7.87 0.1% 7.45 7.38 0.9% - 7.66 7.66 0.0%

Total alkalinity mg/L 5 81.6 81.8 0.2% 24.2 25.4 - 0.5 59 60 1.7%

Total dissolved solids mg/L 1 85.3 85.7 0.5% 36.2 37 2.2% 10 130 120 8.0%

Total organic carbon mg/L 1 19.9 21.3 6.8% 7.2 8.2 13.0% 0.5 10.8 11.2 3.6%

Total suspended solids mg/L 3 <3 <3 - <3 <3 - 1 10 9 10.5%

Major Ions

Bicarbonate mg/L 5 99.6 99.8 0.2% 29.5 31 5.0% 0.5 72 73 1.4%

Calcium mg/L 5 22.8 23 - 7.18 7.34 - 0.05 17.2 17.3 0.6%

Carbonate mg/L 0.5 <5 <5 - <5 <5 - 0.5 <0.5 <0.5 -

Chloride mg/L 0.5 <0.5 <0.5 - <0.5 <0.5 - 1 <1 <1 -

Magnesium mg/L 0.1 6.52 6.58 0.9% 2.35 2.39 1.7% 0.05 4.91 4.99 1.6%

Potassium mg/L 0.5 0.72 0.72 - 1.15 1.13 - 0.05 1.03 1.03 0.0%

Sodium mg/L 1 3.1 3.1 - 2.8 2.8 - 0.05 3.54 3.59 1.4%

Sulphate mg/L 0.5 3.16 3.2 1.3% 8.23 8.12 1.3% 1 11 11 0.0%

Sulphide mg/L 0.002 <0.002 0.003 -

Nutrients

Nitrate mg-N/L 0.05 <0.05 <0.05 - <0.05 <0.05 - - - - -

Nitrite mg-N/L 0.05 <0.05 <0.05 - <0.05 <0.05 - - - - -

Nitrate + nitrite mg-N/L 0.071 <0.071 <0.071 - <0.071 <0.071 - 0.003 0.005 0.004 -

Nitrogen - ammonia mg-N/L 0.05 <0.05 <0.05 - <0.05 <0.05 - 0.05 <0.05 <0.05 -

Nitrogen - Kjeldahl mg-N/L 0.2 1.03 1.09 5.7% 0.42 0.42 - 0.05 0.67 0.71 5.8%

Phosphorus - total mg-P/L 0.02 - - - 0.023 <0.02 - 0.001 0.017 0.019 11.1%

Phosphorus - dissolved mg-P/L 0.02 0.051 0.051 - <0.02 <0.02 - 0.001 0.011 0.011 0.0%

General Organics

Naphthenic acids mg/L 1 1.1 <1 - <1 <1 - 1 <1 <1 -

Phenols mg/L 0.001 0.0043 0.0054 - 0.0023 0.0036 - 0.002 0.005 0.003 -

Total recoverable hydrocarbons mg/L 2 <2 <2 -

Page 74: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project C-14 Quality Assurance/Quality Control December 2010

Table C-2 Duplicate Sample Results (continued)

Golder Associates

Parameter Units

Method Detection

Limit (MDL)

WC-7 Duplicates Relative Percent

Difference

WB-4 Duplicates Relative Percent

Difference

Method Detection

Limit (MDL)

WC-1 Duplicates Relative Percent

Difference Sample 1 Sample 2 Sample 1 Sample 2 Sample 1 Sample 2

14-Aug-09 14-Aug-09 29-Sep-09 29-Sep-09 14-May-10 14-May-10

Total Metals

Aluminum (Al) µg/L 10 102 38 - 36 <10 - 0.2 26.1 35.2 29.7%

Antimony (Sb) µg/L 0.4 <0.4 <0.4 - <0.4 <0.4 - 0.02 0.05 0.05 -

Arsenic (As) µg/L 0.4 1.66 1.52 - <0.4 0.41 - 0.02 0.65 0.67 3.0%

Barium (Ba) µg/L 3 36.8 33.5 9.4% 18.9 17.8 6.0% 0.02 28.8 30.1 4.4%

Beryllium (Be) µg/L 1 <1 <1 - <1 <1 - 0.01 <0.01 <0.01 -

Bismuth µg/L - - - - - - - 0.005 0.025 0.022 -

Boron (B) µg/L 50 <50 <50 - <50 <50 - 20 30 30 -

Cadmium (Cd) µg/L 0.05 <0.05 <0.05 - <0.05 <0.05 - 0.005 0.008 0.01 -

Chromium (Cr) µg/L 5 <5 <5 - <5 <5 - 0.1 <0.1 <0.1 -

Cobalt (Co) µg/L 2 <2 <2 - <2 <2 - 0.005 0.096 0.102 6.1%

Copper (Cu) µg/L 1 <1 <1 - <1 <1 - 0.05 0.43 0.48 11.0%

Iron (Fe) µg/L 10 1,870 1,700 9.5% 149 52 96.5% 1 273 275 0.7%

Lead (Pb) µg/L 0.1 0.13 <0.1 - 0.11 <0.1 - 0.005 0.125 0.118 5.8%

Lithium (Li) µg/L 10 <10 <10 - <10 <10 - 0.5 9.7 9.9 2.0%

Manganese (Mn) µg/L 5 91.4 92.6 1.3% 29.4 23.7 - 0.05 29.3 29.4 0.3%

Mercury (Hg) µg/L 0.1 <0.1 <0.1 - <0.1 <0.1 - 0.002 0.003 <0.002 -

Methyl mercury µg/L - - - - - - - 0.00003 <0.00003 0.00005 -

Molybdenum (Mo) µg/L 5 <5 <5 - <5 <5 - 0.05 0.61 0.61 0.0%

Nickel (Ni) µg/L 2 <2 <2 - <2 <2 - 0.02 0.75 0.75 0.0%

Selenium (Se) µg/L 0.4 <0.4 <0.4 - <0.4 <0.4 - 0.04 0.07 0.07 -

Silver (Ag) µg/L 0.1 <0.1 <0.1 - <0.1 <0.1 - 0.005 <0.005 <0.005 -

Strontium µg/L - - - - - - - 0.05 71.6 73 1.9%

Thallium (Tl) µg/L 0.1 <0.1 <0.1 - <0.1 <0.1 - 0.002 <0.002 <0.002 -

Tin (Sn) µg/L 50 <50 <50 - <50 <50 - 0.01 0.01 0.01 -

Titanium (Ti) µg/L 1 2.7 1.6 - 1.2 <1 - 0.5 0.6 0.9 -

Uranium (U) µg/L 0.1 0.1 <0.1 - <0.1 <0.1 - 0.002 0.094 0.093 1.1%

Vanadium (V) µg/L 1 1.7 <1 - <1 <1 - 0.2 <0.2 <0.2 -

Zinc (Zn) µg/L 4 <4 <4 - 5.1 <4 - 0.1 1.2 1.3 8.0%

Dissolved Metals

Aluminum (Al) µg/L 10 13 13 - <10 <10 - 0.2 5.1 5.5 7.5%

Antimony (Sb) µg/L 0.4 <0.4 <0.4 - <0.4 <0.4 - 0.02 0.06 0.05 -

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Dover Commercial Project C-15 Quality Assurance/Quality Control December 2010

Table C-2 Duplicate Sample Results (continued)

Golder Associates

Parameter Units

Method Detection

Limit (MDL)

WC-7 Duplicates Relative Percent

Difference

WB-4 Duplicates Relative Percent

Difference

Method Detection

Limit (MDL)

WC-1 Duplicates Relative Percent

Difference Sample 1 Sample 2 Sample 1 Sample 2 Sample 1 Sample 2

14-Aug-09 14-Aug-09 29-Sep-09 29-Sep-09 14-May-10 14-May-10

Arsenic (As) µg/L 0.4 1.28 1.32 - <0.4 <0.4 - 0.02 0.54 0.59 8.8%

Barium (Ba) µg/L 3 31.1 31.2 0.3% 17.4 17.3 0.6% 0.02 26.7 26.6 0.4%

Beryllium (Be) µg/L 1 <1 <1 - <1 <1 - 0.01 <0.01 <0.01 -

Bismuth µg/L - - - - - - - 0.005 <0.005 <0.005 -

Boron (B) µg/L 50 <50 <50 - <50 <50 - 20 30 30 -

Cadmium (Cd) µg/L 0.05 <0.05 <0.05 - <0.05 <0.05 - 0.005 <0.005 <0.005 -

Chromium (Cr) µg/L 5 <5 <5 - <5 <5 - 0.1 <0.1 <0.1 -

Cobalt (Co) µg/L 2 <2 <2 - <2 <2 - 0.005 0.052 0.057 9.2%

Copper (Cu) µg/L 1 <1 <1 - <1 <1 - 0.05 0.3 0.29 3.4%

Iron (Fe) µg/L 10 1,410 1,500 6.2% <10 <10 - 1 126 123 2.4%

Lead (Pb) µg/L 0.1 <0.1 <0.1 - <0.1 <0.1 - 0.005 0.017 0.009 -

Lithium (Li) µg/L 3 8.4 8.4 - 6.7 6.9 - 0.5 9.2 9.3 1.1%

Manganese (Mn) µg/L 2 59.1 68 14.0% <2 <2 - 0.05 4.63 4.99 7.5%

Mercury (Hg) µg/L 0.1 <0.1 <0.1 - <0.1 <0.1 - 0.002 <0.002 0.003 -

Molybdenum (Mo) µg/L 5 <5 <5 - <5 <5 - 0.05 0.58 0.59 1.7%

Nickel (Ni) µg/L 2 <2 <2 - <2 <2 - 0.02 0.68 0.7 2.9%

Selenium (Se) µg/L 0.4 <0.4 <0.4 - <0.4 <0.4 - 0.04 0.08 0.07 -

Silver (Ag) µg/L 0.1 <0.1 <0.1 - <0.1 <0.1 - 0.005 <0.005 <0.005 -

Strontium µg/L - - - - - - - 0.05 73.6 74 0.5%

Thallium (Tl) µg/L 0.1 <0.1 <0.1 - <0.1 <0.1 - 0.002 <0.002 0.003 -

Tin (Sn) µg/L 50 <50 <50 - <50 <50 - 0.01 0.01 <0.01 -

Titanium (Ti) µg/L 1 <1 <1 - <1 <1 - 0.5 <0.5 <0.5 -

Uranium (U) µg/L 0.1 <0.1 <0.1 - <0.1 <0.1 - 0.002 0.087 0.091 4.5%

Vanadium (V) µg/L 1 <1 <1 - <1 <1 - 0.2 <0.2 <0.2 -

Zinc (Zn) µg/L 2 <2 <2 - 5 3.2 - 0.1 0.3 0.5 -

Polycyclic Aromatic Hydrocarbons

Acenaphthene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Acridine µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Anthracene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Benz[a]anthracene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Benzo[b]fluoranthene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Benzo[k]fluoranthene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

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Dover Commercial Project C-16 Quality Assurance/Quality Control December 2010

Table C-2 Duplicate Sample Results (continued)

Golder Associates

Parameter Units

Method Detection

Limit (MDL)

WC-7 Duplicates Relative Percent

Difference

WB-4 Duplicates Relative Percent

Difference

Method Detection

Limit (MDL)

WC-1 Duplicates Relative Percent

Difference Sample 1 Sample 2 Sample 1 Sample 2 Sample 1 Sample 2

14-Aug-09 14-Aug-09 29-Sep-09 29-Sep-09 14-May-10 14-May-10

Benzo[a]pyrene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Chrysene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Dibenz[a,h]anthracene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Fluoranthene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Fluorene µg/L 0.01 0.022 <0.01 - <0.01 <0.01 - - - - -

Indeno[1,2,3-cd]pyrene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Naphthalene µg/L 0.01 0.025 <0.01 - <0.01 <0.01 - - - - -

Phenanthrene µg/L 0.01 0.052 0.01 - 0.014 <0.01 - - - - -

Pyrene µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

Quinoline µg/L 0.01 <0.01 <0.01 - <0.01 <0.01 - - - - -

- = No data or not applicable.

Note: Values in bold had relative percent difference greater than 20%.

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Dover Commercial Project C-17 Quality Assurance/Quality Control December 2010

2 REFERENCES

APHA (American Public Health Association). 1992. Standard Methods for the Examination of Waste and Wastewater. 18th Edition. American Public Health Association. Washington, D.C.

Environment Canada. 1993. Quality Assurance in Water Quality Monitoring Ecosystem Sciences and Evaluation Directorate Conservation and Protection. Ottawa. ON.

U.S. EPA (United States Environmental Protection Agency). 1985. National Primary Drinking Water Regulations; Volatile Synthetic Organic Chemicals; Proposed Rule; Recommendations for and Documentation of Biological Values for Use in Risk Assessment. U.S. EPA, Environmental Criteria and Assessment Office. Federal Register: 50;EPA/600/6-87/008. Volume 50. Cincinnati, OH. Submitted November 13, 1985.

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ATTACHMENT D

REGIONAL STUDY AREA WATER QUALITY SUMMARY TABLES

Page 79: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project D-1 Water Quality Baseline Report December 2010

Golder Associates

Table D-1 Summary of Available Water Quality Data for Waterbodies in the Regional Study Area

Parameter Units Winter (1975 to 2010) Spring (1977 to 2010) Summer (1972 to 2009) Fall (1972 to 2009) All Seasons (1972 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximu

m n

Field Measured

pH - 7 3.9 8.7 28 7.8 7 10 20 7.6 6.3 10 54 7.3 6.8 9.9 13 7.5 3.9 10 115 Specific conductance µS/cm 194 2 940 34 120 30 340 25 125 40 530 55 102 49 480 19 130 2 940 133 Temperature °C 0.5 0 4.6 45 11.8 0 15 35 18.2 7.8 21.4 78 8.5 3 12.2 32 10.5 0 21.4 190 Dissolved oxygen mg/L 2.8 0 11 28 10 3.4 13 27 8.3 0.7 14.1 68 9.7 5.8 12.5 23 8.6 0 14.1 146 Conventional Parameters Specific conductance µS/cm 134 51 559 62 100 34 383 41 107 43 375 97 100 46 376 35 111 34 559 235 Colour TCU 95 12 230 31 71 12 276 26 88 7 684 58 63 8 230 23 79 7 684 138 Dissolved organic carbon mg/L 22 6 63 60 20 2 52 41 29 <0.4 57 81 23 6 49 31 24 <0.4 63 213 Hardness mg/L 74 74 74 50 51 51 51 38 57 56 56 67 55 21 160 30 59 13 301 185 pH - 7.4 6.3 8.3 63 7.4 6.8 8.2 41 7.6 6.8 9.7 97 7.6 6.5 8.3 35 7.5 6.3 9.7 236 Total alkalinity mg/L 60 12 806 63 48 13 199 41 48 16 653 92 50 15 197 35 52 12 806 231 Total dissolved solids mg/L 94 23 360 61 67 21 221 41 70 21 240 75 60 19 220 33 76 19 360 210 Total organic carbon mg/L 16 6 58 36 20 2 50 37 29 3 58 52 24 6 50 32 22 2 58 157 Total suspended solids mg/L 3 0.4 352 44 6 <0.4 134 41 4 <0.05 42 58 3 0.4 16 33 4 <0.05 352 176 Major Ions Bicarbonate mg/L 72 15 359 41 56 16 242 26 56 19 212 72 62 19 235 23 62 15 359 162 Calcium mg/L 17 5 81 63 12 4 45 41 13 5 46 93 14 5 42 35 14 4 81 232 Carbonate mg/L <5 <0.5 <5 14 <5 <0.5 <5 23 <5 <1 31 40 <5 <5 <5 22 <5 <0.5 31 99 Chloride mg/L 1 0.1 3 63 1 0.07 2 40 1 0.09 5 97 1 0.1 4.5 35 1 0.07 5 235 Fluoride mg/L 0.12 <0.05 0.22 36 0.1 0.03 0.27 15 0.08 <0.05 0.19 33 0.08 <0.05 0.12 12 0.1 0.03 0.27 96 Magnesium mg/L 5 1 24 63 4 0.9 14 41 4 1 14 96 5 1 13 35 5 0.9 24 235 Potassium mg/L 1.1 0.4 5.3 63 0.9 0.2 3.8 41 0.9 0.1 4.8 97 0.9 0.1 3.5 35 1 0.1 5.3 236 Sodium mg/L 4 0.8 40 63 3 0.5 24 41 3 0.8 30 97 3 <1 26 35 3 0.5 40 236 Sulphate mg/L 7 0.7 87 62 5 0.5 38 41 7 0.7 42 91 5 <0.5 44 34 6 <0.5 87 228 Sulphide mg/L 0.027 0.008 0.076 4 0.01 <0.002 0.02 5 0.015 <0.002 0.046 17 <0.01 <0.01 <0.01 2 0.012 <0.002 0.076 28 Nutrients and Biological Indicators Nitrate mg-N/L 0.1 0.03 4.7 23 <0.1 <0.003 <0.1 23 <0.1 <0.003 0.193 27 <0.1 0.006 0.3 25 <0.1 <0.003 4.7 98 Nitrate + nitrite mg-N/L 0.1 <0.001 0.48 52 <0.097 0.0005 0.64 41 <0.1 <0.001 0.43 80 <0.1 0.006 0.3 34 <0.1 0.0005 0.64 207 Nitrite mg-N/L <0.004 <0.001 <0.05 38 <0.05 <0.003 <0.05 24 <0.05 <0.001 <0.1 48 <0.05 <0.003 <0.05 27 <0.05 <0.001 <0.1 137 Nitrogen - ammonia mg-N/L 0.11 <0.001 1.39 62 0.05 0.008 0.73 41 0.05 0.005 1.3 95 <0.05 <0.01 0.4 33 0.05 <0.001 1.39 231 Nitrogen - Kjeldahl mg-N/L 1.31 0.28 6.55 60 1.43 0.39 17 41 1.37 0.31 4.35 82 1.2 0.28 2.7 33 1.34 0.28 17 216 Nitrogen - total mg-N/L 1.47 0.34 6.55 60 1.43 0.4 17 41 1.38 0.31 4.35 82 1.39 0.28 2.7 33 1.4 0.28 17 216 Phosphorus - total mg-P/L 0.07 0.019 0.58 63 0.05 0.013 0.21 41 0.056 0.012 1.32 94 0.04 0.017 0.2 35 0.051 0.012 1.32 233 Phosphorus - dissolved mg-P/L 0.03 0.008 0.307 34 0.02 0.006 0.08 26 0.02 0.004 0.99 71 <0.02 0.011 0.05 23 0.02 0.004 0.99 154 Biochemical oxygen demand mg/L - - - 0 <6 <6 <6 3 2 <2 12 9 - - - 0 3 <2 12 12 Chlorophyll a µg/L 2.1 0.2 130.37 31 6.87 <1 69.95 12 11.66 1.56 135.65 38 9 5 13 3 7.05 0.2 135.65 84 General Organics

Naphthenic acids mg/L <1 <1 1 13 <1 <1 <1 18 <1 <1 1 33 <1 <1 1.4 17 <1 <1 1.4 81 Total phenolics mg/L 0.007 <0.001 0.035 43 0.006 <0.001 0.013 28 0.009 <0.001 0.15 66 0.005 <0.001 0.027 21 0.008 <0.001 0.15 158 Total recoverable hydrocarbons mg/L <0.1 <0.1 <2 15 2 <0.1 3.3 15 <1 <0.1 127 34 1.3 0.5 1.9 3 <1 <0.1 127 67 Total Metals

Aluminum mg/L 0.02 <0.002 0.199 25 0.025 0.0033 7.32 18 0.02 0.0047 0.876 47 0.03 <0.01 0.07 17 0.02 <0.002 7.32 107 Antimony mg/L <0.0004 0.000016 <0.0004 15 <0.0004 <0.00002 <0.0004 18 0.000057 0.000012 0.00084 47 <0.0004 <0.0004 <0.0004 17 <0.0004 0.000012 0.00084 97 Arsenic mg/L 0.00065 0.0003 0.0083 31 0.0004 0.00028 0.0031 18 0.0005 0.00027 0.0028 59 0.0005 <0.0004 0.0163 17 0.0005 0.00027 0.0163 125 Barium mg/L 0.033 0.011 0.114 31 0.017 0.009 1.41 18 0.019 0.001 0.055 59 0.019 0.009 0.051 17 0.021 0.001 1.41 125 Beryllium mg/L <0.001 0.000007 <0.001 15 <0.001 <0.00001 <0.001 18 0.000013 0.000001 <0.001 47 <0.001 <0.001 <0.001 17 <0.001 0.000001 <0.001 97 Bismuth mg/L <0.000005 0.000002 0.000012 5 <0.000005 <0.000005 0.000009 5 0.000005 <0.000001 0.000019 26 - - - 0 0.000005 <0.000001 0.000019 36 Boron mg/L <0.05 <0.02 0.14 15 <0.05 <0.02 0.54 18 0.05 0.006 0.145 47 <0.05 <0.05 0.13 17 0.05 0.006 0.54 97 Cadmium mg/L <0.0002 0.000006 <0.0002 15 <0.0002 <0.000005 <0.0002 18 0.000016 <0.000002 <0.002 47 <0.0002 <0.00005 <0.0002 17 <0.000098 <0.000002 <0.002 97 Chromium mg/L 0.003 0.0003 0.006 31 <0.005 <0.0001 0.012 18 <0.001 <0.00003 <0.005 59 <0.005 <0.005 <0.005 17 <0.003 <0.00003 0.012 125 Cobalt mg/L <0.00116 0.00007 0.007 31 <0.002 0.00004 0.002 18 0.001 0.00002 <0.002 59 <0.002 <0.002 <0.002 17 <0.00172 0.00002 0.007 125 Copper mg/L <0.001 0.0002 0.014 31 0.001 0.00006 0.007 18 <0.001 <0.00005 0.0167 59 <0.001 <0.001 0.001 17 <0.001 <0.00005 0.0167 125 Iron mg/L 0.28 0.02 9.73 32 0.15 0.03 6.72 21 0.12 0.005 3.29 69 0.14 0.02 1.02 18 0.15 0.005 9.73 140 Lead mg/L 0.0001 0.00009 0.00149 15 0.0001 0.00006 0.0033 18 0.0001 0.000003 0.00126 47 <0.0001 <0.0001 0.0008 17 0.0001 0.000003 0.0033 97 Lithium mg/L 0.01 0.0063 0.0363 15 0.01 0.0027 0.03 18 0.01 0.0025 0.049 47 <0.01 <0.01 0.024 17 0.01 0.0025 0.049 97 Manganese mg/L 0.212 0.007 1.294 31 0.038 0.009 0.304 18 0.046 0.005 0.778 59 0.029 0.005 0.199 17 0.046 0.005 1.294 125 Mercury mg/L <0.00002 0.000002 <0.0002 14 <0.00002 0.000003 <0.0002 18 <0.00002 <0.0000006 <0.0001 39 <0.00002 <0.00002 <0.0001 17 <0.00002 <0.0000006 <0.0002 88 Methyl mercury µg/L <0.00003 <0.00003 0.00041 3 0.00004 <0.00003 0.0002 5 - - - 0 - - - 0 0.00004 <0.00003 0.00041 8 Molybdenum mg/L <0.002 0.00003 <0.005 31 <0.005 <0.00005 <0.005 18 0.00062 0.00001 <0.005 59 <0.005 <0.005 <0.005 17 <0.002 0.00001 <0.005 125 Nickel mg/L <0.002 0.00011 0.007 31 <0.002 0.00017 0.008 18 0.001 <0.000005 0.004 59 <0.002 <0.002 <0.002 17 <0.002 <0.000005 0.008 125 Selenium mg/L <0.0002 <0.0001 0.0007 31 <0.0004 <0.00004 0.0009 18 <0.0002 0.00006 <0.0004 59 <0.0004 <0.0004 0.0005 17 <0.00023 <0.00004 0.0009 125 Silver mg/L <0.0004 0.000001 <0.0004 15 <0.0004 <0.000005 <0.0004 18 0.000005 <0.0000005 0.00488 47 <0.0004 <0.0001 0.00048 17 <0.0004 <0.0000005 0.00488 97

Page 80: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project D-2 Water Quality Baseline Report December 2010

Table D-1 Summary of Available Water Quality Data for Waterbodies in the Regional Study Area (continued)

Golder Associates

Parameter Units Winter (1975 to 2010) Spring (1977 to 2010) Summer (1972 to 2009) Fall (1972 to 2009) All Seasons (1972 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximu

m n

Strontium mg/L 0.09 0.064 0.342 5 0.048 0.026 0.167 5 0.076 0.029 0.159 30 - - - 0 0.0758 0.026 0.342 40 Thallium mg/L <0.0001 0.0000007 <0.0001 15 <0.0001 <0.000002 0.0001 18 0.000003 <0.0000003 <0.0001 47 <0.0001 <0.0001 <0.0001 17 <0.0001 <0.0000003 0.0001 97 Titanium mg/L <0.001 <0.0005 0.0021 15 0.001 <0.0005 0.083 18 0.001 0.0002 0.0283 47 <0.001 <0.001 0.002 17 0.001 0.0002 0.083 97 Uranium mg/L <0.0001 0.00001 0.00081 15 <0.0001 0.000007 0.0005 18 0.00006 0.000005 0.00134 47 <0.0001 <0.0001 0.00033 17 0.0001 0.000005 0.00134 97 Vanadium mg/L <0.002 <0.0002 0.007 33 <0.001 <0.0002 0.026 18 0.001 0.00006 0.004 63 <0.001 <0.001 0.015 19 <0.001 0.00006 0.026 133 Zinc mg/L 0.007 <0.001 0.045 31 0.018 0.0012 0.769 18 0.003 <0.0001 0.013 59 <0.004 <0.004 0.009 17 0.004 <0.0001 0.769 125 Dissolved Metals

Aluminum mg/L 0.0125 0.0048 0.12 17 0.01 0.0022 0.11 21 0.01 0.0002 0.085 44 0.01 <0.01 0.063 17 0.01 0.0002 0.12 99 Antimony mg/L <0.0004 0.00005 <0.0004 13 <0.0004 <0.00002 <0.0004 18 <0.0004 0.00002 <0.0004 30 <0.0004 <0.0004 <0.0004 17 <0.0004 0.00002 <0.0004 78 Arsenic mg/L 0.0007 0.0005 0.0027 15 0.0004 0.0003 0.0012 18 0.0005 0.0002 0.0018 34 <0.0004 0.0002 0.0014 19 0.0005 0.0002 0.0027 86 Barium mg/L 0.027 0.009 0.047 13 0.012 0.006 0.042 18 0.018 0.001 0.053 30 0.015 0.008 0.047 17 0.017 0.001 0.053 78 Beryllium mg/L <0.001 0.00001 <0.001 29 <0.001 <0.00001 <0.001 18 <0.001 <0.000003 <0.001 42 <0.001 <0.001 <0.001 17 <0.001 <0.000003 <0.001 106 Bismuth mg/L <0.000005 <0.000005 <0.000005 3 <0.000005 <0.000005 <0.000005 5 0.000002 <0.000001 0.000006 9 - - - 0 <0.000005 0.000006 0.000006 17 Boron mg/L <0.05 <0.02 0.15 13 <0.05 <0.02 0.11 18 0.05 0.006 0.14 30 <0.05 <0.05 0.13 17 <0.05 0.006 0.15 78 Cadmium mg/L <0.0001 0.000052 0.00022 13 <0.0001 <0.000005 <0.0001 18 <0.00005 <0.000002 <0.0001 30 <0.0001 <0.00005 <0.0001 17 <0.0001 <0.000002 0.00022 78 Chromium mg/L <0.005 0.0022 <0.005 13 <0.005 <0.0001 <0.005 18 <0.005 <0.00004 <0.005 30 <0.005 <0.005 <0.005 17 <0.005 <0.00004 <0.005 78 Chromium - hexavalent mg/L - - - 0 - - - 0 <0.001 <0.001 <0.001 6 - - - 0 <0.001 <0.001 <0.001 6 Cobalt mg/L <0.002 0.00022 <0.002 13 <0.002 0.00002 <0.002 18 <0.002 0.00001 <0.002 30 <0.002 <0.002 <0.002 17 <0.002 0.00001 <0.002 78 Copper mg/L <0.001 0.0006 0.002 13 <0.001 0.00007 0.001 18 <0.001 <0.00005 0.002 30 <0.001 <0.001 0.003 17 <0.001 <0.00005 0.003 78 Iron mg/L 0.34 0.05 2.54 13 0.09 0.007 1.3 19 0.06 0.003 1.02 30 0.09 <0.005 0.47 17 0.1 0.003 2.54 79 Lead mg/L <0.0001 <0.0001 0.00056 13 <0.0001 0.00002 0.00018 18 <0.0001 <0.000001 0.00032 30 <0.0001 <0.0001 <0.0001 17 <0.0001 <0.000001 0.00056 78 Lithium mg/L 0.009 <0.003 0.037 13 0.007 0.002 0.026 18 0.01 <0.003 0.024 30 0.008 <0.003 0.026 17 0.009 0.002 0.037 78 Manganese mg/L 0.278 0.026 0.752 13 0.004 0.0009 0.223 19 0.007 0.0005 0.1 30 0.004 <0.001 0.034 17 0.006 0.0005 0.752 79 Mercury mg/L <0.0001 0.000001 <0.0001 13 <0.00002 <0.000002 <0.00002 18 <0.0001 <0.00001 <0.0001 26 <0.0001 <0.0001 <0.0001 17 <0.0001 0.000001 <0.0001 74 Molybdenum mg/L <0.005 0.00006 <0.005 13 <0.005 <0.00005 <0.005 18 <0.005 <0.000001 <0.005 30 <0.005 <0.005 <0.005 17 <0.005 <0.000001 <0.005 78 Nickel mg/L <0.002 0.0008 <0.002 13 <0.002 0.0002 0.003 18 <0.002 <0.000005 <0.002 30 <0.002 <0.002 0.0024 17 <0.002 <0.000005 0.003 78

Selenium mg/L <0.0004 0.00011 0.0008 15 <0.0004 <0.00004 <0.0004 18 <0.0003

0.00006 <0.0004

34 <0.0004 <0.0002 0.0007 19 <0.0004 <0.00004 0.0008

86 Silver mg/L <0.0001 <0.000005 0.0002 13 <0.0001 <0.000005 <0.0001 18 <0.0001 <0.0000005 <0.0001 30 <0.0001 <0.0001 <0.0001 17 <0.0001 <0.0000005 0.0002 78 Strontium mg/L 0.121 0.061 0.341 3 0.05 0.025 0.163 5 0.093 0.027 0.149 13 - - - 0 0.0931 0.025 0.341 21 Thallium mg/L <0.0001 <0.000002 <0.0001 13 <0.0001 <0.000002 <0.0001 18 <0.0001 <0.0000003 <0.0001 30 <0.0001 <0.0001 0.0001 17 <0.0001 <0.0000003 0.0001 78 Titanium mg/L <0.001 <0.0005 <0.001 13 <0.001 <0.0005 0.002 18 0.001 <0.00004 0.002 30 <0.001 <0.001 <0.001 17 <0.001 <0.00004 0.002 78 Uranium mg/L <0.0001 0.00002 0.00081 13 <0.0001 0.000006 0.00034 18 0.0001 0.000004 0.00038 30 <0.0001 <0.0001 0.00032 17 <0.0001 0.000004 0.00081 78 Vanadium mg/L <0.001 <0.0002 0.002 13 <0.001 <0.0002 <0.001 18 0.001 0.00005 0.002 30 <0.001 <0.001 <0.001 17 <0.001 0.00005 0.002 78 Zinc mg/L 0.009 <0.002 0.051 13 0.009 0.0004 0.173 18 0.002 0.00005 0.006 30 <0.002 <0.002 0.005 17 0.003 0.00005 0.173 78 Polycyclic Aromatic Hydrocarbons and Alkylated Polycyclic Aromatic Hydrocarbons

Naphthalene µg/L <0.01 <0.01 0.05 10 <0.01 <0.01 0.01 13 <10 <0.01 20 17 <0.01 <0.01 0.014 17 <0.01 <0.01 20 57 C1 substituted naphthalenes µg/L 0.02 <0.01 0.04 4 <0.01 <0.01 <0.01 13 <0.01 - - 1 - - - 0 <0.01 <0.01 0.04 18 C4 substituted naphthalenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 Acenaphthene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 C1 substituted acenaphthenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 Acenaphthylene µg/L <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 <0.01 - - 1 - - - 0 <0.01 <0.01 <0.01 18 Anthracene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 Dibenzo(a,h)anthracene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 Benzo(a)anthracene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 C1 substituted benzo(a)anthracenes / chrysenes

µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18

C2 substituted benzo(a)anthracenes / chrysenes

µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18

Benzo(a)pyrene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 Benzo(b)fluoranthene µg/L <0.01 <0.01 <0.01 10 <10 <10 <10 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 Benzo(k)fluoranthene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 C1 substituted benzofluoranthenes / benzopyrenes

µg/L <0.04 <0.04 <0.04 4 <0.04 <0.01 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.01 <0.04 18

Benzo(g,h,i)perylene µg/L <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 <0.01 - - 1 - - - 0 <0.01 <0.01 <0.01 18 Biphenyl µg/L <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 <0.01 - - 1 - - - 0 <0.01 <0.01 <0.01 18 C1 substituted biphenyls µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 C2 substituted biphenyls µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 Chrysene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 Dibenzothiophene µg/L <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 <0.01 - - 1 - - - 0 <0.01 <0.01 <0.01 18 C1 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 C2 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 C3 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18

Page 81: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project D-3 Water Quality Baseline Report December 2010

Table D-1 Summary of Available Water Quality Data for Waterbodies in the Regional Study Area (continued)

Golder Associates

Parameter Units Winter (1975 to 2010) Spring (1977 to 2010) Summer (1972 to 2009) Fall (1972 to 2009) All Seasons (1972 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximu

m n

C4 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 Fluoranthene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 C1 substituted fluoranthenes / pyrenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 Fluorene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 C1 substituted fluorenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 C2 substituted fluorenes µg/L <0.04 <0.04 0.1 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 0.1 18 Indeno(c,d-123)pyrene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57 Phenanthrene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 10 17 <0.01 <0.01 0.02 17 <0.01 <0.01 10 57 C1 substituted phenanthrenes / anthracenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 C2 substituted phenanthrenes / anthracenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 C3 substituted phenanthrenes / anthracenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 C4 substituted phenanthrenes / anthracenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 13 <0.04 - - 1 - - - 0 <0.04 <0.04 <0.04 18 Pyrene µg/L <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 13 <10 <0.01 <10 17 <0.01 <0.01 <0.01 17 <0.01 <0.01 <10 57

- = Not applicable or no data.

Sources: Water quality data from samples collected in 2009 and 2010, AOSC (2009), Golder (2000, 2001, 2002, 2003), RAMP (2004, 2005, 2006, 2007, 2008, 2009, 2010) Southern Pacific (2009), Sunshine (2009) and Alberta Environment (AENV 2010) WDS Stations AB07DA1850, 1860, 1870, 1880, 1890, 1900, 1910, 1920, 1930, 1940, 1950, 1960, 2030, 2040, 2060, 2070, 2080, 2230, 2240, 2250, 2260, 2270, 2280, 2360, 2370, 2380, 2390, 2910, AB07DB0160, 0170, 0200, 0210, 0220, 0230, 0240, 0250, 0260, 0270, 0280 and 0290.

Page 82: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project D-4 Water Quality Baseline Report December 2010

Golder Associates

Table D-2 Summary of Available Water Quality Data for Watercourses in the Regional Study Area

Parameter Units Winter (1976 to 2010) Spring (1976 to 2010) Summer (1972 to 2009) Fall (1972 to 2009) All Seasons (1972 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Field Measured

pH - 7.6 5.9 8.8 43 7.5 6.4 8.7 42 7.7 4.8 8.52 60 7.9 5.6 9.7 47 7.6 4.8 9.7 192 Specific conductance µS/cm 310 4 5300 48 150 10 950 49 152 37 530 64 236 60 1222 62 195 4 5300 223 Temperature °C 0 0 9 71 9.3 0 14.4 59 16 5.3 24 90 7.6 0.4 19.1 72 9 0 24 292 Dissolved oxygen mg/L 9.7 0.8 12.9 29 9.8 2 14.4 54 7.8 0.9 11.8 70 9.8 4.5 14.3 58 9 0.8 14.4 211 Conventional Parameters

Specific conductance µS/cm 411 93 1370 90 143 32 840 63 183 65 581 108 212 59 903 89 200 32 1370 350 Colour TCU 90 22 220 27 140 28 190 39 190 36 300 53 135 25 230 54 140 22 300 173 Dissolved organic carbon mg/L 25 8 47 94 25 7 39 63 28 8 58 95 26 8 41 86 26 7 58 338 Hardness mg/L 182 45 493 77 60 19 315 62 88 37 223 98 99 31 356 84 93 19 493 321 pH - 7.6 6.7 8.5 92 7.7 6.8 8.4 64 7.9 6.9 8.6 108 8 7 8.6 92 7.8 6.7 8.6 356 Total alkalinity mg/L 175 13 577 92 62 11 409 64 82 24 271 107 100 27 422 91 91 11 577 354 Total dissolved solids mg/L 250 45 862 90 85 17 521 63 130 54 450 104 139 28 630 88 139 17 862 345 Total organic carbon mg/L 26 8 66 88 25 7 44 63 31 8 59 86 28 10 49 84 28 7 66 321 Total suspended solids mg/L 5 <0.4 124 94 12 2 547 64 6 <0.4 210 97 5 1 91 88 7 <0.4 547 343 Major Ions

Bicarbonate mg/L 261 54 578 29 75 13 210 39 96 29 288 59 123 32 325 58 105 13 578 185 Calcium mg/L 47 12 120 89 16 5 75 64 24 9 51 94 26 8 68 89 25 5 120 336 Carbonate mg/L <5 <0.5 <5 26 <5 <0.5 <5 39 <5 <0.5 <5 55 <5 <0.5 6 56 <5 <0.5 6 176 Chloride mg/L 2 0.4 149 92 2 0.2 13.7 64 2 0.3 16 104 2 0.3 41.2 92 2 0.2 149 352 Fluoride mg/L 0.13 <0.05 0.33 64 0.09 0.03 0.35 24 0.11 <0.05 0.21 43 0.09 0.04 0.37 31 0.1 0.03 0.37 162 Magnesium mg/L 16 4 47 89 5 2 31 63 7 3 19 98 8 3 19 88 8 2 47 338 Potassium mg/L 2 0.4 10.6 92 1.4 0.4 5 64 0.8 0.07 3.3 108 1 0.2 34.2 92 1.1 0.07 34.2 356 Sodium mg/L 24 <1 140 92 8 <1 88 64 9 2 51 108 12 <1 88 92 11 <1 140 356 Sulphate mg/L 27 1 159 93 11 <0.5 75 64 12 0.8 170 106 13 <0.5 109 92 14 <0.5 170 355 Sulphide mg/L <0.01 <0.001 0.037 29 0.01 <0.003 0.074 14 0.01 <0.001 0.185 44 0.01 0.002 0.032 37 0.01 <0.001 0.185 124 Nutrients and Biological Indicators

Nitrate mg-N/L 0.3 0.02 1.4 29 <0.1 <0.003 0.172 35 <0.1 <0.003 <0.1 30 <0.1 <0.05 0.3 30 <0.1 <0.003 1.4 124 Nitrate + nitrite mg-N/L 0.27 0.005 1 93 <0.1 <0.003 0.43 64 <0.1 <0.003 0.43 108 <0.1 <0.001 0.3 92 <0.1 <0.001 1 357 Nitrite mg-N/L 0.01 0.002 <0.05 39 <0.05 <0.003 <0.05 38 <0.05 <0.001 <0.1 51 <0.05 <0.003 <0.05 43 <0.05 <0.001 <0.1 171 Nitrogen - ammonia mg-N/L 0.086 <0.01 1.29 92 <0.05 <0.002 0.44 63 0.05 0.007 3.5 105 <0.05 0.007 0.8 87 0.05 <0.002 3.5 347 Nitrogen - Kjeldahl mg-N/L 1.11 0.1 7.85 90 1.2 0.55 4 63 1.1 0.31 2.41 98 0.98 0.11 4.2 88 1.1 0.1 7.85 339 Nitrogen - total mg-N/L 1.48 0.28 7.99 90 1.23 0.55 4 63 1.1 0.35 2.41 98 1 0.13 4.21 88 1.11 0.13 7.99 339 Phosphorus - total mg-P/L 0.1 0.009 1.08 92 0.06 0.016 0.78 64 0.074 0.013 4 101 0.05 0.01 2.3 90 0.064 0.009 4 347 Phosphorus - dissolved mg-P/L 0.035 0.008 0.15 30 0.03 0.011 0.1 39 0.041 0.006 0.11 64 0.03 0.004 0.07 60 0.03 0.004 0.15 193 Biochemical oxygen demand mg/L 2 0.8 8 11 <2 <2 <6 11 <2 0.9 3 23 <2 <0.1 177 28 <2 <0.1 177 73 Chlorophyll a µg/L <1 <0.1 2 17 3.5 2 26 4 <1 <1 29.7 7 1 <1 7 17 <1 <0.1 29.7 45 General Organics Naphthenic acids mg/L <1 <1 2 25 <1 <1 2 39 <1 <1 2 57 <1 <1 1.1 57 <1 <1 2 178 Total phenolics mg/L 0.002 <0.001 0.028 73 0.007 <0.001 0.015 54 0.004 <0.001 0.034 97 0.004 <0.001 0.02 81 0.005 <0.001 0.034 305 Total recoverable hydrocarbons mg/L <0.5 <0.1 2.5 53 <0.6 <0.1 4.4 26 1 <0.1 300 65 <0.6 <0.1 8.2 48 <0.6 <0.1 300 192 Total Metals Aluminum mg/L 0.086 <0.01 1.66 30 0.4 0.012 13.4 40 0.0963 0.015 4.799 65 0.14 <0.01 2.83 61 0.13 <0.01 13.4 196 Antimony mg/L <0.0004 0.000037 0.0006 27 <0.0004 0.00003 0.0013 40 0.000103 0.000016 0.0025 63 <0.0004 0.00001 <0.0008 58 <0.0004 0.00001 0.0025 188 Arsenic mg/L 0.00095 0.0004 0.00226 31 0.0009 <0.0004 0.0067 40 0.00106 0.00027 0.00313 65 0.00088 <0.0004 0.00247 61 0.00095 0.00027 0.0067 197 Barium mg/L 0.043 0.022 0.109 31 0.028 0.007 0.135 40 0.027 0.011 0.109 65 0.025 0.01 0.088 61 0.028 0.007 0.135 197 Beryllium mg/L <0.001 0.000005 0.001 30 <0.001 <0.00001 0.001 40 <0.000165 <0.000003 0.002 65 <0.001 0.000004 0.005 61 <0.001 <0.000003 0.005 196 Bismuth mg/L 0.00001 0.000003 0.000028 11 0.000017 <0.000005 0.000051 12 0.00001 0.000003 0.000037 29 0.00001 0.000001 0.00002 23 0.00001 0.000001 0.000051 75 Boron mg/L 0.086 0.024 0.47 30 0.05 0.03 0.21 40 0.05 0.015 0.211 65 0.059 0.022 0.189 61 0.05 0.015 0.47 196 Cadmium mg/L <0.0002 <0.000005 0.0002 27 <0.0002 <0.000005 0.0002 40 <0.000049 0.000002 <0.002 64 <0.00005 0.000002 <0.0002 57 <0.000097 0.000002 <0.002 188 Chromium mg/L <0.005 0.0001 0.007 30 <0.005 <0.0001 0.017 40 0.0032 <0.0001 0.013 65 <0.005 <0.0001 0.011 61 <0.005 <0.0001 0.0167 196 Cobalt mg/L <0.002 0.0001 0.003 29 <0.002 0.00008 0.00415 39 0.002 0.00008 0.00294 59 <0.002 0.00011 0.0026 59 <0.002 0.00008 0.00415 186 Copper mg/L 0.001 <0.00008 0.0087 30 0.001 0.0002 0.009 40 0.001 <0.00005 0.005 65 0.001 0.0002 0.012 61 0.001 <0.00005 0.012 196 Iron mg/L 1.95 0.06 8.29 31 1.18 0.14 12.3 40 1.01 0.25 9.36 65 0.92 0.18 23.3 61 1.01 0.06 23.3 197 Lead mg/L 0.0002 <0.00001 0.03 30 0.0003 0.00003 0.006 40 0.00019 <0.00001 0.00274 65 0.00016 0.00004 0.0036 61 0.0002 <0.00001 0.0295 196 Lithium mg/L 0.03 <0.01 0.09 29 0.01 0.00878 0.03 39 0.0108 0.00307 0.05 64 0.015 0.0084 0.05 61 0.0127 0.00307 0.09 193 Manganese mg/L 0.074 0.008 4.03 31 0.059 0.006 0.246 40 0.072 0.017 2.17 65 0.041 0.006 0.59 61 0.057 0.006 4.03 197 Mercury mg/L <0.00002 <0.0000006 <0.0002 27 <0.00002 <0.0000012 <0.0002 39 <0.00002 <6E-07 <0.0001 54 <0.00002 <0.0000006 <0.0001 54 <0.00002 <0.0000006 <0.0002 174 Methyl mercury µg/L - <0.00003 <0.00003 2 0.00004 <0.00003 0.00008 4 - - - 0 - - - 0 0.00003 <0.00003 0.00008 6 Molybdenum mg/L 0.004 0.00014 <0.005 30 <0.005 0.00019 <0.005 40 0.00086 0.00002 <0.005 63 0.00349 0.00013 <0.005 60 <0.005 0.00002 <0.005 193 Nickel mg/L 0.002 0.00034 0.0101 31 0.002 0.0007 0.0105 40 0.002 0.00015 0.1 65 0.002 <0.0005 0.0207 61 0.002 0.00015 0.1 197 Selenium mg/L 0.00046 0.00009 0.0038 31 <0.0004 0.00005 0.0014 40 <0.0004 <0.0001 <0.0005 65 <0.0004 0.00014 <0.0008 61 <0.0004 0.00005 0.0038 197 Silver mg/L <0.0004 0.000002 0.0004 28 <0.0004 <0.000005 0.0004 40 <0.0001 <5E-07 0.0004 59 <0.0001 0.000001 <0.0004 56 <0.000294 <0.0000005 0.0004 183 Strontium mg/L 0.145 0.079 0.562 15 0.096 0.064 0.255 13 0.112 0.048 0.431 37 0.14 0.066 0.807 31 0.115 0.048 0.807 96

Page 83: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project D-5 Water Quality Baseline Report December 2010 Table D-2 Summary of Available Water Quality Data for Watercourses in the Regional Study Area (continued)

Golder Associates

Parameter Units Winter (1976 to 2010) Spring (1976 to 2010) Summer (1972 to 2009) Fall (1972 to 2009) All Seasons (1972 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Thallium mg/L <0.0001 <0.000002 0.0005 28 <0.0001 <0.000002 0.00012 39 <0.00006 0.000001 <0.0001 57 <0.0001 0.0000007 <0.0001 57 <0.0001 0.0000007 0.0005 181 Titanium mg/L 0.004 0.0006 0.0459 28 0.008 <0.0005 0.0897 39 0.002 0.0006 0.0935 57 0.003 0.0009 0.094 58 0.003 <0.0005 0.094 182 Uranium mg/L 0.0002 0.00006 0.001 28 0.0001 0.00006 0.0017 39 0.0001 0.000009 0.00063 57 0.00014 0.00006 0.0014 58 0.00012 0.000009 0.00172 182 Vanadium mg/L 0.001 0.00013 0.005 33 0.001 <0.0002 0.035 40 0.001 0.0002 0.05 65 0.001 <0.0002 0.008 61 0.001 0.00013 0.05 199 Zinc mg/L 0.011 0.0015 0.27 30 0.016 0.001 0.15 40 0.004 0.0002 0.021 63 0.004 0.0008 0.067 60 0.0046 0.0002 0.273 193 Dissolved Metals

Aluminum mg/L 0.01 0.0025 0.05 23 0.03 0.0055 0.184 39 0.02 0.007 0.0963 44 0.02 <0.0002 0.038 52 0.02 <0.0002 0.184 158 Antimony mg/L <0.0004 0.00004 <0.0008 23 <0.0004 0.00003 0.01 39 <0.0004 0.00002 <0.0004 44 <0.0004 0.00001 <0.0008 52 <0.0004 0.00001 0.01 158 Arsenic mg/L 0.0007 <0.0004 0.0014 23 0.0006 <0.0004 0.0013 39 0.001 0.0003 0.002 44 0.0007 <0.0004 0.0012 52 0.0007 0.0003 0.002 158 Barium mg/L 0.036 0.018 0.097 23 0.018 0.006 0.04 39 0.022 0.011 0.036 44 0.02 0.009 0.047 52 0.022 0.006 0.097 158 Beryllium mg/L <0.001 0.000007 <0.001 24 <0.001 0.000004 <0.001 39 <0.001 <0.000003 <0.001 44 <0.001 0.000003 <0.001 52 <0.001 <0.000003 <0.001 159 Bismuth mg/L <0.000008 0.000002 <0.00001 6 0.00001 <0.000005 0.000036 12 0.000004 0.000002 0.000017 16 <0.00001 <0.000001 0.00002 17 <0.00001 <0.000001 0.000036 51 Boron mg/L 0.09 <0.05 0.48 23 0.05 0.03 0.22 39 0.05 0.01 0.2 44 0.06 0.04 0.18 52 0.05 0.01 0.48 158 Cadmium mg/L <0.0001 0.000005 0.000154 23 <0.0001 0.000002 <0.0001 39 <0.0001 0.000003 <0.0001 44 <0.000075 0.000002 <0.0001 52 <0.0001 0.000002 0.000154 158 Chromium mg/L <0.005 0.00009 0.006 23 <0.005 <0.0001 <0.005 39 <0.005 0.0001 <0.005 44 <0.005 0.00007 <0.005 52 <0.005 0.00007 0.006 158 Cobalt mg/L <0.002 0.00006 0.003 23 <0.002 0.00006 <0.002 39 <0.002 0.00005 <0.002 44 <0.002 0.00008 <0.002 52 <0.002 0.00005 0.003 158 Copper mg/L <0.001 0.0006 0.005 23 <0.001 0.0003 0.006 39 0.001 0.00006 0.139 44 0.001 0.0003 0.0021 52 <0.001 0.00006 0.139 158 Iron mg/L 0.57 0.04 2.89 25 0.42 0.08 1.99 39 0.59 0.13 2 44 0.5 0.12 1.2 52 0.52 0.04 2.89 160 Lead mg/L <0.0001 0.00004 0.0004 23 <0.0001 0.00002 0.004 39 0.0001 0.000009 0.008 44 0.0001 0.00002 0.0002 52 <0.0001 0.000009 0.008 158 Lithium mg/L 0.035 <0.003 0.101 23 0.01 <0.003 0.036 39 0.012 <0.003 0.356 44 0.016 <0.003 0.048 52 0.013 <0.003 0.356 158 Manganese mg/L 0.102 0.007 3.87 25 0.017 0.001 0.246 39 0.03 0.002 0.366 44 0.018 0.001 0.383 52 0.025 0.001 3.87 160 Mercury mg/L <0.0001 0.000002 <0.0001 21 <0.00002 <0.000002 <0.00005 39 <0.0001 <0.00001 <0.0001 44 <0.0001 <0.00001 <0.0001 49 <0.00005 <0.000002 <0.0001 153 Molybdenum mg/L <0.005 0.0003 <0.005 23 <0.005 0.0002 <0.005 39 <0.005 0.00002 <0.005 44 <0.005 0.0001 <0.005 52 <0.005 0.00002 <0.005 158 Nickel mg/L 0.002 0.0003 0.003 23 <0.002 0.0006 0.006 39 <0.002 0.0001 0.0996 44 <0.002 0.0004 0.0028 52 <0.002 0.0001 0.0996 158 Selenium mg/L <0.0004 0.00009 0.0013 23 <0.0004 0.00004 <0.0005 39 <0.0004 <0.0001 <0.0005 44 <0.0004 <0.0001 0.0005 52 <0.0004 0.00004 0.0013 158 Silver mg/L <0.0001 0.000001 0.0002 21 <0.0001 <0.0000005 <0.0001 39 <0.0001 <5E-07 0.0002 44 <0.0001 <0.0000005 <0.0001 49 <0.0001 <0.0000005 0.0002 153 Strontium mg/L 0.377 0.112 0.58 8 0.093 0.059 0.241 12 0.112 0.047 0.209 16 0.134 0.094 0.275 22 0.122 0.047 0.58 58 Thallium mg/L <0.0001 <0.000002 <0.0001 23 <0.0001 <0.000002 0.0001 39 <0.0001 0.0000007 0.0001 44 <0.0001 0.0000007 0.0001 51 <0.0001 0.0000007 0.0001 157 Titanium mg/L 0.001 <0.0005 0.0034 23 <0.001 <0.0005 0.008 39 <0.001 0.0006 0.0038 44 <0.001 <0.0003 0.0024 52 <0.001 <0.0003 0.008 158 Uranium mg/L 0.0003 0.00006 0.001 23 <0.0001 0.00006 0.00148 39 0.00011 0.000007 0.00037 44 0.00011 0.00007 0.00038 52 0.0001 0.000007 0.00148 158 Vanadium mg/L 0.001 0.00004 0.002 23 <0.001 <0.0002 <0.001 39 <0.001 0.0002 0.002 44 <0.001 0.0002 <0.001 52 <0.001 0.00004 0.002 158 Zinc mg/L 0.009 0.001 0.031 23 0.01 0.0005 0.178 39 0.002 0.0005 0.03 44 0.002 0.0008 0.05 52 0.003 0.0005 0.178 158 Polycyclic Aromatic Hydrocarbons and Alkylated Polycyclic Aromatic Hydrocarbons Naphthalene µg/L <0.01 <0.01 0.06 15 <0.01 <0.01 0.01 27 <0.01 <0.01 <10 28 <0.01 <0.01 <0.025 30 <0.01 <0.01 <10 100 C1 substituted naphthalenes µg/L <0.01 <0.01 0.02 9 <0.01 <0.01 0.01 27 <0.01 <0.01 <0.01 4 - <0.01 <0.01 2 <0.01 <0.01 0.02 42 C2 substituted naphthalenes µg/L - - - 0 - - - 0 - - - 0 - <0.04 <0.04 2 - <0.04 <0.04 2 C3 substituted naphthalenes µg/L - - - 0 - - - 0 - - - 0 - <0.04 <0.04 2 - <0.04 <0.04 2 C4 substituted naphthalenes µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 Acenaphthene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.01 <0.01 <10 28 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 100 C1 substituted acenaphthenes µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 Acenaphthylene µg/L <0.01 <0.01 <0.01 9 <0.01 <0.01 <0.01 27 <0.01 <0.01 <0.01 4 - <0.01 <0.01 2 <0.01 <0.01 <0.01 42 Anthracene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.01 <0.01 <10 28 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 100 Dibenzo(a,h)anthracene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.01 <0.01 <10 28 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 100 Benzo(a)anthracene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.01 <0.01 <10 27 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 99 C1 substituted benzo(a)anthracenes / chrysenes

µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42

C2 substituted benzo(a)anthracenes / chrysenes

µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42

C3 substituted benzo(a)anthracenes / chrysenes

µg/L - - - 0 - - - 0 - - - 0 - <0.04 <0.04 2 - <0.04 <0.04 2

C4 substituted benzo(a)anthracenes / chrysenes

µg/L - - - 0 - - - 0 - - - 0 - <0.01 <0.01 2 - <0.01 <0.01 2

Benzo(a)pyrene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.01 <0.01 <10 27 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 99 Benzo(b)fluoranthene µg/L <0.01 <0.01 <0.01 15 <10 <10 <10 27 <10 <0.01 <10 27 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 99 Benzo(k)fluoranthene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.01 <0.01 <10 27 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 99 C1 substituted benzofluoranthenes / benzopyrenes

µg/L <0.04 <0.04 <0.04 9 <0.04 <0.01 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.01 <0.04 42

C2 substituted benzofluoranthenes / benzopyrenes

µg/L - - - 0 - - - 0 - - - 0 - <0.04 <0.04 2 - <0.04 <0.04 2

Benzo(g,h,i)perylene µg/L <0.01 <0.01 <0.01 9 <0.01 <0.01 <0.01 27 <0.01 <0.01 <0.01 4 - <0.01 <0.01 2 <0.01 <0.01 <0.01 42 Biphenyl µg/L <0.01 <0.01 <0.01 9 <0.01 <0.01 <0.01 27 <0.01 <0.01 <0.01 4 - <0.01 <0.01 2 <0.01 <0.01 <0.01 42 C1 substituted biphenyls µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 C2 substituted biphenyls µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 Chrysene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.01 <0.01 <10 28 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 100 Dibenzothiophene µg/L <0.01 <0.01 <0.01 9 <0.01 <0.01 <0.01 27 <0.01 <0.01 <0.01 4 - <0.01 <0.01 2 <0.01 <0.01 <0.01 42

Page 84: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project D-6 Water Quality Baseline Report December 2010 Table D-2 Summary of Available Water Quality Data for Watercourses in the Regional Study Area (continued)

Golder Associates

Parameter Units Winter (1976 to 2010) Spring (1976 to 2010) Summer (1972 to 2009) Fall (1972 to 2009) All Seasons (1972 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

C1 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 C2 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 C3 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 C4 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 Fluoranthene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.01 <0.01 <10 28 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 100 C1 substituted fluoranthenes / pyrenes µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 C2 substituted fluoranthenes / pyrenes µg/L - - - 0 - - - 0 - - - 0 - <0.04 <0.04 2 - <0.04 <0.04 2 C3 substituted fluoranthenes / pyrenes µg/L - - - 0 - - - 0 - - - 0 - <0.04 <0.04 2 - <0.04 <0.04 2 Fluorene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.016 <0.01 <10 28 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 100 C1 substituted fluorenes µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 C2 substituted fluorenes µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42 C3 substituted fluorenes µg/L - - - 0 - - - 0 - - - 0 - <0.04 <0.04 2 - <0.04 <0.04 2 Indeno(c,d-123)pyrene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.01 <0.01 <10 28 <0.01 <0.01 <0.01 30 <0.01 <0.01 <10 100 Perylene µg/L - - - 0 - - - 0 - - - 0 - <0.01 <0.01 2 - <0.01 <0.01 2 Phenanthrene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.016 <0.01 <10 28 <0.01 <0.01 0.01 30 <0.01 <0.01 <10 100 C1 substituted phenanthrenes / anthracenes

µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42

C2 substituted phenanthrenes / anthracenes

µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42

C3 substituted phenanthrenes / anthracenes

µg/L <0.04 <0.04 <0.04 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 <0.04 42

C4 substituted phenanthrenes / anthracenes

µg/L <0.04 <0.04 0.09 9 <0.04 <0.04 <0.04 27 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 <0.04 <0.04 0.09 42

Pyrene µg/L <0.01 <0.01 <0.01 15 <0.01 <0.01 <0.01 27 <0.01 <0.01 <10 28 <0.01 <0.01 0.012 30 <0.01 <0.01 <10 100 Retene µg/L - - - 0 - - - 0 - - - 0 - <0.01 <0.01 2 - <0.01 <0.01 2

- = Not applicable or no data.

Sources: Water quality data from samples collected in 2009 and 2010, AOSC (2009), Golder (1999, 2001, 2002, 2003), RAMP (2004, 2005, 2006, 2007, 2008, 2009) Southern Pacific (2009), Sunshine (2009) and and Alberta Environment (AENV 2010) WDS Stations AB07DA1260, 1400, 3000, 3005, AB07DB0030, 0050, 0060, 0070, 0100, 0110, 0120 and 0300.

Page 85: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

ATTACHMENT E

PROJECT-SPECIFIC WATER QUALITY SUMMARY

Page 86: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-1 Water Quality Baseline Report December 2010

Golder Associates

Table E-1 Summary of Available Water Quality Data for Namur Lake

Parameter Units Winter (1977 to 2002) Spring (1977 to 2010) Summer (1972 to 2009) Fall (1972 to 2009) All Seasons (1972 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Field Measured pH - - 6.5 6.7 2 7.4 - - 1 7.2 7.2 7.2 7 7.2 6.8 9.9 4 7.2 6.5 9.9 14 Specific conductance µS/cm 56 51 87 3 - 60 110 2 56 40 90 10 60 49 102 4 56 40 110 19 Temperature °C 0 0 3.1 6 4 1 11.8 5 15 10.7 20 14 9 6 11 6 10.7 0 20 31 Dissolved oxygen mg/L 11 - - 1 10.6 3.4 11 3 9 7.8 9.9 10 9.3 5.8 9.7 4 9.2 3.4 11 18 Conventional Parameters Specific conductance µS/cm 64 59 89 10 52 43 84 6 60 43 72 23 56 46 70 8 61 43 89 47 Colour TCU - 12 13 2 - 12 150 2 12 7 14 10 11 8 14 3 12 7 150 17 Dissolved organic carbon mg/L 7 6 14 8 8 5 20 6 8 5 14 14 7 6 9 5 8 5 20 33 Hardness mg/L 25 21 29 6 20 20 20 6 23 23 23 9 22 22 22 5 24 24 24 26 pH - 6.9 6.8 7.4 10 7.1 6.8 7.3 6 7.3 6.9 8.2 23 7.3 6.5 7.8 8 7.3 6.5 8.2 47 Total alkalinity mg/L 23 20 34 10 18 16 19 6 22 18 31 21 21 20 26 8 21 16 34 45 Total dissolved solids mg/L 40 23 45 10 29 26 96 6 35 26 47 15 35 29 47 7 37 23 96 38 Total organic carbon mg/L 7 6 14 7 8 5 20 6 8 3 10 9 8 6 16 6 8 3 20 28 Total suspended solids mg/L 2 0.4 6 9 3 <0.4 134 6 2 <0.05 5 12 3 0.4 11 7 2 <0.05 134 34 Major Ions Bicarbonate mg/L 26 24 37 3 20 19 21 2 27 24 30 11 30 25 31 3 27 19 37 19 Calcium mg/L 7 5 8 10 5 5 8 6 6 5 10 21 6 5 7 8 6 5 10 45 Carbonate mg/L - - - 0 - <0.5 <5 2 - <5 <5 2 - <5 <5 2 <5 <0.5 <5 6 Chloride mg/L 0.4 0.1 1.5 10 0.9 0.2 2 6 0.5 0.1 5 23 0.4 0.1 1 8 0.4 0.1 5 47 Fluoride mg/L 0.07 0.06 0.1 6 0.06 0.03 0.08 4 0.05 <0.05 0.14 8 0.08 0.07 0.12 5 0.07 0.03 0.14 23 Magnesium mg/L 2 2 2 10 2 1 3 6 2 1 3 22 2 1 3 8 2 1 3 46 Potassium mg/L 1 0.9 1.4 10 0.8 0.6 1 6 1 0.1 1.3 23 0.9 0.1 1.4 8 1 0.1 1.4 47 Sodium mg/L 2 <1 8 10 2 2 4 6 2 1 7 23 2 <1 3 8 2 <1 8 47 Sulphate mg/L 7 5 8 10 6 4 16 6 7 6 15 22 6 4 8 7 7 4 16 45 Sulphide mg/L - - - 0 <0.002 - - 1 - - - 0 - - - 0 <0.002 - - 1 Nutrients and Biological Indicators Nitrate mg-N/L 0.076 0.051 0.093 4 - 0.02 <0.1 2 0.05 <0.003 0.193 7 0.03 0.006 <0.1 5 0.051 <0.003 0.193 18 Nitrate + nitrite mg-N/L 0.051 <0.01 0.093 10 <0.015 0.004 <0.1 6 0.039 <0.001 0.193 14 0.04 0.006 <0.1 7 0.04 <0.001 0.193 37 Nitrite mg-N/L <0.003 <0.001 <0.003 5 - <0.003 <0.05 2 <0.003 <0.001 <0.1 10 <0.003 <0.003 <0.05 5 <0.003 <0.001 <0.1 22 Nitrogen - ammonia mg-N/L 0.02 <0.001 0.15 12 0.045 <0.01 0.4 6 0.022 0.005 0.311 20 0.036 <0.01 0.2 8 0.023 <0.001 0.4 46 Nitrogen - Kjeldahl mg-N/L 0.62 0.28 1.25 11 0.76 0.54 2.1 5 0.42 0.31 0.93 16 0.46 0.28 0.8 7 0.49 0.28 2.1 39 Nitrogen - total mg-N/L 0.67 0.34 1.32 11 0.78 0.54 2.1 5 0.46 0.31 1.01 16 0.47 0.28 0.81 7 0.54 0.28 2.1 39 Phosphorus - total mg-P/L 0.027 0.02 0.1 12 0.035 0.013 0.17 6 0.023 0.012 0.7 19 0.028 0.017 0.2 8 0.026 0.012 0.7 45 Phosphorus - dissolved mg-P/L - 0.008 0.012 2 - 0.007 0.04 2 0.008 0.004 <0.02 11 <0.02 0.011 <0.02 3 0.01 0.004 0.04 18 Chlorophyll a µg/L 2 0.8 14.47 5 - 2.9 7 2 3.32 1.56 12.85 9 5 - - 1 3.32 0.8 14.47 17 General Organics Naphthenic acids mg/L - - - 0 - <1 <1 2 - <1 <1 2 - <1 <1 2 <1 <1 <1 6 Total phenolics mg/L 0.003 <0.001 0.008 7 0.002 <0.001 0.008 6 0.003 <0.001 0.15 12 0.002 <0.001 0.027 5 0.003 <0.001 0.15 30 Total recoverable hydrocarbons mg/L <0.1 <0.1 1.2 4 1.6 <0.1 2.1 5 1 <0.1 23.6 5 1.3 - - 1 1 <0.1 23.6 15 Total Metals Aluminum mg/L - - - 0 - 0.0091 7.3 2 0.0097 0.0047 0.04 6 - 0.036 0.06 2 0.0126 0.0047 7.3 10 Antimony mg/L - - - 0 - 0.00006 <0.0004 2 0.000068 0.000064 <0.0004 6 - <0.0004 <0.0004 2 0.000234 0.00006 <0.0004 10 Arsenic mg/L 0.0003 - - 1 - 0.00031 0.0031 2 0.00036 0.00031 0.0005 7 - <0.0004 0.0006 2 0.00038 0.0003 0.0031 12 Barium mg/L 0.018 - - 1 - 0.018 1.4 2 0.019 0.019 0.02 7 - 0.019 0.023 2 0.019 0.018 1.4 12 Beryllium mg/L - - - 0 - <0.00001 <0.001 2 0.000006 0.000001 <0.001 6 - <0.001 <0.001 2 <0.0005 0.000001 <0.001 10 Bismuth mg/L - - - 0 <0.000005 - - 1 0.000002 0.000002 0.000006 3 - - - 0 0.0000035 0.000002 0.000006 4 Boron mg/L - - - 0 - 0.02 0.54 2 0.025 0.022 <0.05 6 - <0.05 <0.05 2 0.037 0.02 0.54 10 Cadmium mg/L - - - 0 - 0.000011 <0.0002 2 0.000008 0.000004 <0.002 6 - <0.00005 <0.0002 2 0.00003 0.000004 <0.002 10 Chromium mg/L <0.001 - - 1 - <0.0001 0.012 2 <0.0001 <0.00003 <0.005 7 - <0.005 <0.005 2 <0.001 <0.00003 0.012 12 Cobalt mg/L <0.001 - - 1 - 0.00005 0.002 2 0.00003 0.00002 <0.002 7 - <0.002 <0.002 2 0.001 0.00002 0.002 12 Copper mg/L <0.001 - - 1 - 0.0003 0.007 2 0.0006 0.0003 <0.001 7 - <0.001 0.001 2 0.001 0.0003 0.007 12 Iron mg/L 0.02 - - 1 - 0.11 6.7 2 0.02 0.009 0.11 11 0.15 0.03 0.3 3 0.02 0.009 6.7 17 Lead mg/L - - - 0 - 0.000057 0.0033 2 0.0001 0.00002 0.00029 6 - 0.00011 0.0002 2 0.00011 0.00002 0.0033 10

Page 87: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-2 Water Quality Baseline Report December 2010

Table E-1 Summary of Available Water Quality Data for Namur Lake (continued)

Golder Associates

Parameter Units Winter (1977 to 2002) Spring (1977 to 2010) Summer (1972 to 2009) Fall (1972 to 2009) All Seasons (1972 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Lithium mg/L - - - 0 - 0.0063 0.02 2 0.00776 0.0061 <0.01 6 - <0.01 <0.01 2 0.00907 0.0061 0.02 10 Manganese mg/L <0.008 - - 1 - 0.019 0.15 2 0.009 0.005 0.014 7 - 0.029 0.033 2 0.011 0.005 0.15 12 Mercury mg/L - - - 0 - 0.000003 0.00004 2 <0.00002 <0.00002 <0.0001 3 - <0.00002 <0.0001 2 <0.00002 0.000003 <0.0001 7 Methyl mercury µg/L - - - 0 <0.00003 - - 1 - - - 0 - - - 0 <0.00003 - - 1 Molybdenum mg/L <0.001 - - 1 - 0.0002 <0.005 2 0.00024 0.00022 <0.005 7 - <0.005 <0.005 2 <0.001 0.0002 <0.005 12 Nickel mg/L <0.001 - - 1 - 0.00052 0.008 2 0.00066 0.00058 <0.002 7 - <0.002 <0.002 2 0.001 0.00052 0.008 12 Selenium mg/L <0.0002 - - 1 - 0.00006 0.0009 2 0.0002 0.00006 <0.0004 7 - <0.0004 0.0004 2 0.00025 0.00006 0.0009 12 Silver mg/L - - - 0 - <0.000005 <0.0004 2 <0.000001 <0.0000005 <0.0004 6 - <0.0001 <0.0004 2 <0.00005 <0.0000005 <0.0004 10 Strontium mg/L - - - 0 0.0361 - - 1 0.041 0.04 0.043 4 - - - 0 0.0404 0.036 0.043 5 Thallium mg/L - - - 0 - <0.000002 0.0001 2 0.000001 <0.0000003 <0.0001 6 - <0.0001 <0.0001 2 <0.00005 <0.0000003 0.0001 10 Titanium mg/L - - - 0 - <0.0005 0.083 2 0.0005 0.0002 <0.001 6 - 0.0012 0.002 2 0.0008 0.0002 0.083 10 Uranium mg/L - - - 0 - 0.000011 0.0005 2 0.00001 0.00001 <0.0001 6 - <0.0001 <0.0001 2 0.00006 0.00001 0.0005 10 Vanadium mg/L 0.002 0.001 0.003 3 - 0.0002 0.026 2 <0.001 0.00006 <0.002 11 0.008 <0.001 0.015 4 0.001 0.00006 0.026 20 Zinc mg/L 0.002 - - 1 - 0.0012 0.77 2 0.0017 0.0004 0.0103 7 - 0.0051 0.007 2 0.003 0.0004 0.77 12 Dissolved Metals Aluminum mg/L - - - 0 - 0.0025 0.11 2 0.001 0.0002 <0.01 9 - <0.01 0.01 2 0.0016 0.0002 0.11 13 Antimony mg/L - - - 0 - 0.00006 <0.0004 2 <0.0004 0.00006 <0.0004 3 - <0.0004 <0.0004 2 <0.0004 0.00006 <0.0004 7 Arsenic mg/L - 0.0007 0.0027 2 - 0.0003 0.0008 2 0.0004 0.0002 0.0016 7 0.0004 0.0002 0.0004 4 0.0004 0.0002 0.0027 15 Barium mg/L - - - 0 - 0.0175 0.021 2 0.018 0.018 0.019 3 - 0.017 0.019 2 0.018 0.017 0.021 7 Beryllium mg/L <0.001 - - 1 - <0.00001 <0.001 2 <0.001 <0.000003 <0.001 4 - <0.001 <0.001 2 <0.001 <0.000003 <0.001 9 Bismuth mg/L - - - 0 <0.000005 - - 1 - - - 0 - - - 0 <0.000005 - - 1 Boron mg/L - - - 0 - 0.02 <0.05 2 <0.05 0.02 <0.05 3 - <0.05 <0.05 2 <0.05 0.02 <0.05 7 Cadmium mg/L - - - 0 - 0.000007 <0.0001 2 <0.00005 <0.000002 <0.0001 3 - <0.00005 <0.0001 2 <0.00005 <0.000002 <0.0001 7 Chromium mg/L - - - 0 - <0.0001 <0.005 2 <0.005 <0.00004 <0.005 3 - <0.005 <0.005 2 <0.005 <0.00004 <0.005 7 Cobalt mg/L - - - 0 - 0.000015 <0.002 2 <0.002 0.00001 <0.002 3 - <0.002 <0.002 2 <0.002 0.00001 <0.002 7 Copper mg/L - - - 0 - 0.00019 0.001 2 <0.001 0.0003 <0.001 3 - <0.001 <0.001 2 <0.001 0.0002 0.001 7 Iron mg/L - - - 0 - 0.045 0.96 2 0.01 0.003 0.02 3 - <0.01 0.02 2 0.02 0.003 0.96 7 Lead mg/L - - - 0 - 0.000022 0.0001 2 <0.0001 0.000007 <0.0001 3 - <0.0001 <0.0001 2 <0.0001 0.000007 0.0001 7 Lithium mg/L - - - 0 - 0.0062 0.015 2 0.008 0.007 0.009 3 - 0.007 0.007 2 0.007 0.006 0.015 7 Manganese mg/L - - - 0 - 0.00317 0.098 2 0.002 0.0006 0.006 3 - <0.002 0.008 2 0.003 0.0006 0.098 7 Mercury mg/L - - - 0 - <0.000002 <0.00002 2 - <0.0001 <0.0001 2 - <0.0001 <0.0001 2 <0.0001 <0.000002 <0.0001 6 Molybdenum mg/L - - - 0 - 0.00022 <0.005 2 <0.005 0.0002 <0.005 3 - <0.005 <0.005 2 <0.005 0.0002 <0.005 7 Nickel mg/L - - - 0 - 0.00051 0.003 2 <0.002 0.0006 <0.002 3 - <0.002 <0.002 2 <0.002 0.0005 0.003 7 Selenium mg/L <0.0002 <0.0002 <0.0002 2 - 0.00006 <0.0004 2 <0.0002 0.00006 <0.0004 7 <0.0003 <0.0002 <0.0004 4 <0.0002 0.00006 <0.0004 15 Silver mg/L - - - 0 - <0.000005 <0.0001 2 <0.0001 <0.0000005 <0.0001 3 - <0.0001 <0.0001 2 <0.0001 <0.0000005 <0.0001 7 Strontium mg/L - - - 0 0.035 - - 1 0.039 - - 1 - - - 0 - 0.035 0.039 2 Thallium mg/L - - - 0 - <0.000002 <0.0001 2 <0.0001 <0.0000003 <0.0001 3 - <0.0001 <0.0001 2 <0.0001 <0.0000003 <0.0001 7 Titanium mg/L - - - 0 - <0.0005 0.002 2 <0.001 0.00009 <0.001 3 - <0.001 <0.001 2 <0.001 0.00009 0.002 7 Uranium mg/L - - - 0 - 0.000008 <0.0001 2 <0.0001 0.000009 <0.0001 3 - <0.0001 <0.0001 2 <0.0001 0.000008 <0.0001 7 Vanadium mg/L - - - 0 - 0.0003 <0.001 2 <0.001 0.00005 <0.001 3 - <0.001 <0.001 2 <0.001 0.00005 <0.001 7 Zinc mg/L - - - 0 - 0.0005 0.031 2 <0.002 0.0004 <0.002 3 - <0.002 0.005 2 0.002 0.0004 0.031 7 Polycyclic Aromatic Hydrocarbons and Alkylated Polycyclic Aromatic Hydrocarbons Naphthalene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 C1 substituted naphthalenes µg/L - - - 0 <0.01 - - 1 <0.01 - - 1 - - - 0 - <0.01 <0.01 2 C4 substituted naphthalenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 Acenaphthene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 C1 substituted acenaphthenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 Acenaphthylene µg/L - - - 0 <0.01 - - 1 <0.01 - - 1 - - - 0 - <0.01 <0.01 2 Anthracene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 Dibenzo(a,h)anthracene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 Benzo(a)anthracene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 C1 substituted benzo(a)anthracenes / chrysenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 C2 substituted benzo(a)anthracenes / chrysenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2

Page 88: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-3 Water Quality Baseline Report December 2010

Table E-1 Summary of Available Water Quality Data for Namur Lake (continued)

Golder Associates

Parameter Units Winter (1977 to 2002) Spring (1977 to 2010) Summer (1972 to 2009) Fall (1972 to 2009) All Seasons (1972 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Benzo(a)pyrene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 Benzo(b)fluoranthene µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 Benzo(k)fluoranthene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 C1 substituted benzofluoranthenes / benzopyrenes µg/L - - - 0 <0.01 - - 1 <0.01 <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 Benzo(g,h,i)perylene µg/L - - - 0 <0.01 - - 1 <0.01 - - 1 - - - 0 - <0.01 <0.01 2 Biphenyl µg/L - - - 0 <0.01 - - 1 <0.01 - - 1 - - - 0 - <0.01 <0.01 2 C1 substituted biphenyls µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 C2 substituted biphenyls µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 Chrysene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 Dibenzothiophene µg/L - - - 0 <0.01 - - 1 <0.01 - - 1 - - - 0 - <0.01 <0.01 2 C1 substituted dibenzothiophenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 C2 substituted dibenzothiophenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 C3 substituted dibenzothiophenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 C4 substituted dibenzothiophenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 Fluoranthene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 C1 substituted fluoranthenes / pyrenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 Fluorene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 C1 substituted fluorenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 C2 substituted fluorenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 Indeno(c,d-123)pyrene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5 Phenanthrene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 0.014 2 <0.01 <0.01 0.014 5 C1 substituted phenanthrenes / anthracenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 C2 substituted phenanthrenes / anthracenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 C3 substituted phenanthrenes / anthracenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 C4 substituted phenanthrenes / anthracenes µg/L - - - 0 <0.04 - - 1 <0.04 - - 1 - - - 0 - <0.04 <0.04 2 Pyrene µg/L - - - 0 <0.01 - - 1 - <0.01 <0.01 2 - <0.01 <0.01 2 <0.01 <0.01 <0.01 5

- = Not applicable or no data.

Sources: Water quality data from samples collected in 2009 and 2010, AOSC (2009), Golder (2000, 2001, 2002, 2003), RAMP (2004, 2005, 2006, 2007, 2008, 2009, 2010) and Alberta Environment (AENV 2010) WDS Stations AB07DA1850, 1860, 1870, 1880, 1890, and 1900.

Page 89: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-4 Water Quality Baseline Report December 2010

Golder Associates

Table E-2 Summary of Available Water Quality Data for Gardiner Lakes

Parameter Units Winter (1977 to 1988) Spring (1977 to 1978) Summer (1972 to 1993) Fall (1972 to 1977) All Seasons (1972 to 1993)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Field Measured pH - 6.7 - - 1 7.4 - - 1 8 7.6 8.3 4 - - - 0 7.7 6.7 8.3 6 Specific conductance µS/cm - 93 186 2 - 30 50 2 120 112 128 4 - - - 0 116 30 186 8 Temperature °C 0 0 4 7 3 0 15 6 16 14 20 9 - 6 11 2 8 0 20 24 Dissolved oxygen mg/L 10.4 - - 1 6.5 5.3 13 3 8.9 8.3 9.3 5 - - - 0 8.93 5.3 13 9 Conventional Parameters Specific conductance µS/cm 142 127 250 9 84 34 223 6 115 104 130 9 110 110 118 3 119 34 250 27 Dissolved organic carbon mg/L 14 8 21 9 9 2 32 6 11 10 15 4 - 9 13 2 12 2 32 21 Hardness mg/L 66 59 122 9 43 13 121 6 57 54 77 7 58 53 63 3 61 13 122 25 pH - 7.3 7 7.8 9 7.3 6.9 7.4 6 7.9 7.5 8.7 9 7.7 7.5 7.9 3 7.5 7.5 7.5 27 Total alkalinity mg/L 60 56 122 9 40 14 122 6 54 49 71 9 56 50 61 3 56 14 122 27 Total dissolved solids mg/L 89 76 150 9 55 22 150 6 67 61 75 5 - 72 74 2 77 22 150 22 Total organic carbon mg/L 13 8 21 8 10 2 33 6 12 10 13 3 - 10 17 2 12 2 33 19 Total suspended solids mg/L 4 2 19 8 3 <0.4 23 6 5 0.8 8 3 - 2 5 2 4 <0.4 23 19 Major Ions Bicarbonate mg/L 82 - - 1 - - - 0 66 - - 1 - - - 0 - 66 82 2 Calcium mg/L 18 16 33 9 11 4 32 6 16 7 17 7 15 15 17 3 16 4 33 25 Chloride mg/L 0.6 0.5 2.1 9 0.6 0.2 1.2 6 1 0.4 5 9 0.6 0.4 1 3 0.6 0.2 5 27 Fluoride mg/L 0.11 0.08 0.16 9 0.1 0.05 0.27 6 0.08 <0.05 0.15 8 0.1 <0.05 0.1 3 0.1 <0.05 0.27 26 Magnesium mg/L 6 5 10 9 3 0.9 10 6 5 3 6 9 5 4 5 3 5 0.9 10 27 Potassium mg/L 1 0.8 1.5 9 0.7 0.2 2 6 0.9 0.6 1.3 9 0.9 0.9 1 3 0.9 0.2 2 27 Sodium mg/L 3 2 4 9 2 0.5 4 6 3 2 11 9 3 2 3 3 3 0.5 11 27 Sulphate mg/L 7 5 9 9 5 0.5 8 6 7 4 25 7 7 5 15 3 7 0.5 25 25 Nutrients and Biological Indicators Nitrate mg-N/L - 0.062 0.063 2 - - - 0 - - - 0 - - - 0 - 0.062 0.063 2 Nitrate + nitrite mg-N/L 0.11 0.05 0.24 9 0.053 <0.01 0.31 6 <0.1 0.002 0.43 9 0.067 0.058 <0.1 3 0.086 0.002 0.43 27 Nitrite mg-N/L 0.003 0.002 0.003 3 0.003 - - 1 <0.1 0.002 <0.1 5 0.014 - - 1 0.003 0.002 <0.1 10 Nitrogen - ammonia mg-N/L 0.01 <0.01 1.04 9 0.03 <0.01 0.12 6 0.13 <0.01 1.3 8 0.03 <0.01 0.3 3 0.03 <0.01 1.3 26 Nitrogen - Kjeldahl mg-N/L 0.99 0.52 4.51 9 1.18 0.66 2.6 6 0.7 0.57 1.59 5 - 0.88 0.93 2 0.91 0.52 4.51 22 Nitrogen - total mg-N/L 1.22 0.69 4.56 9 1.2 0.96 2.69 6 0.73 0.58 2.02 5 - 0.94 1 2 0.98 0.58 4.56 22 Phosphorus - total mg-P/L 0.1 0.036 0.38 10 0.047 0.02 0.16 6 0.051 0.03 0.7 10 0.046 0.042 0.2 3 0.051 0.02 0.7 29 Phosphorus - dissolved mg-P/L - - - 0 - - - 0 0.026 - - 1 - - - 0 0.026 - - 1 Chlorophyll a µg/L 0.9 0.8 33 4 - 1 2 2 10 6 10.8 5 - - - 0 6 0.8 33 11 General Organics Total phenolics mg/L 0.003 <0.001 0.007 7 <0.001 <0.001 0.001 4 0.003 <0.001 0.011 8 0.002 - - 1 0.002 <0.001 0.011 20 Total recoverable hydrocarbons mg/L <0.1 <0.1 1.4 6 0.4 <0.1 1 4 1.9 0.5 127 7 - 0.5 1.9 2 1 <0.1 127 19 Total Metals Arsenic mg/L 0.0008 - - 1 - - - 0 0.0008 - - 1 - - - 0 - 0.0008 0.0008 2 Barium mg/L 0.025 - - 1 - - - 0 0.027 - - 1 - - - 0 - 0.025 0.027 2 Chromium mg/L <0.001 - - 1 - - - 0 <0.001 - - 1 - - - 0 - <0.001 <0.001 2 Cobalt mg/L <0.001 - - 1 - - - 0 <0.001 - - 1 - - - 0 - <0.001 <0.001 2 Copper mg/L <0.001 - - 1 - - - 0 <0.001 - - 1 - - - 0 - <0.001 <0.001 2 Iron mg/L - - - 0 - - - 0 0.288 - - 1 - - - 0 0.288 - - 1 Manganese mg/L <0.008 - - 1 - - - 0 0.102 - - 1 - - - 0 - <0.008 0.102 2 Molybdenum mg/L <0.001 - - 1 - - - 0 <0.001 - - 1 - - - 0 - <0.001 <0.001 2 Nickel mg/L 0.002 - - 1 - - - 0 0.002 - - 1 - - - 0 - 0.002 0.002 2 Selenium mg/L <0.0002 - - 1 - - - 0 <0.0002 - - 1 - - - 0 - <0.0002 <0.0002 2 Vanadium mg/L <0.002 - - 1 - - - 0 <0.002 - - 1 - - - 0 - <0.002 <0.002 2 Zinc mg/L 0.002 - - 1 - - - 0 <0.001 - - 1 - - - 0 - <0.001 0.002 2 Dissolved Metals Beryllium mg/L <0.001 - - 1 - - - 0 <0.001 - - 1 - - - 0 - <0.001 <0.001 2

- = Not applicable or no data.

Sources: Water quality data from Alberta Environment (AENV 2010) WDS Stations AB07DA2030, 2040, 2060, 2070, 2080 and 2380.

Page 90: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-5 Water Quality Baseline Report December 2010

Golder Associates

Table E-3 Summary of Available Water Quality Data for Other Waterbodies Within and Near the Local Study Area

Parameter Units Winter (1989 to 2010) Spring (2008 to 2010) Summer (1977 to 2009) Fall (2008 to 2009) All Seasons (2008 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Field Measured pH - 7.1 6.5 8.5 10 7.8 7 10 9 7.9 6.5 10 12 7.3 6.9 8 6 7.4 6.5 10 37 Specific conductance µS/cm 225 2 505 11 150 46 270 10 186 43 330 12 170 64 435 8 190 2 505 41 Temperature °C 1.5 0.1 4.6 11 12.7 7.6 14.1 10 19.6 12.6 21.3 21 7.9 6 9.2 10 12.6 0.1 21.3 52 Dissolved oxygen mg/L 2.4 0 7.5 11 10.1 9.6 12.9 10 6.1 0.7 14.1 21 10 7.2 12.3 10 7.7 0 14.1 52 Conventional Parameters Specific conductance µS/cm 222 110 500 11 171 46 270 10 170 46 273 21 160 46 300 10 174 46 500 52 Colour TCU 61 23 210 11 49 22 98 10 75 21 240 20 65 21 140 10 65 21 240 51 Dissolved organic carbon mg/L 34 15 50 11 23 18 38 10 30 13 49 21 27 20 48 10 29 13 50 52 Hardness mg/L 97 53 247 11 78 25 121 10 79 30 121 21 69 24 130 10 79 24 247 52 pH - 7.5 6.9 8 11 7.8 7 8.1 10 7.9 6.9 9.7 21 7.9 7.1 8.1 10 7.8 6.9 9.7 52 Total alkalinity mg/L 105 49 200 11 85 16 103 10 75 16 118 21 75 15 123 10 79 15 200 52 Total dissolved solids mg/L 169 81 360 11 93 21 190 10 133 21 190 21 95 19 164 10 114 19 360 52 Total organic carbon mg/L 41 27 54 6 22 17 42 10 33 11 50 20 27 18 50 10 31 11 54 46 Total suspended solids mg/L 9 <3 18 6 8 3 29 10 5 <3 23 20 5 <3 9 10 5 <3 29 46 Major Ions Bicarbonate mg/L 128 59 250 11 103 20 130 10 88 19 144 20 92 19 150 10 93 19 250 51 Calcium mg/L 27 14 72 11 20 7 34 10 21 8 33 21 17 6 35 10 21 6 72 52 Carbonate mg/L <3 <0.5 <5 6 <5 <0.5 <5 10 <5 <5 31 19 <5 <5 <5 10 <5 <0.5 31 45 Chloride mg/L 1 <0.5 3 11 1 <1 2 10 1 <0.5 2 21 <1 <0.5 3 10 1 <0.5 3 52 Fluoride mg/L 0.13 0.1 0.16 5 - - - 0 - 0.1 0.15 2 - - - 0 0.13 0.1 0.16 7 Magnesium mg/L 7 4 17 11 7 2 9 10 7 3 10 21 6 2 10 10 7 2 17 52 Potassium mg/L 2.7 1.5 4 11 2.2 0.7 2.9 10 1.3 <0.5 2.7 21 1.5 <0.5 2.7 10 1.6 <0.5 4 52 Sodium mg/L 12 2 25 11 8 0.9 12 10 8 <1 24 21 8 <1 15 10 9 0.9 25 52 Sulphate mg/L 17 <1 87 11 6 <1 38 10 8 0.7 42 21 8 2 44 10 9 0.7 87 52 Sulphide mg/L 0.044 0.008 0.076 3 0.013 0.008 0.02 4 0.012 <0.002 0.039 9 - - - 0 0.014 <0.002 0.076 16 Nutrients and Biological Indicators Nitrate mg-N/L 0.135 0.03 1.2 6 <0.1 <0.003 <0.1 10 <0.1 <0.05 <0.1 10 <0.1 <0.05 0.2 10 <0.1 <0.003 1.2 36 Nitrate + nitrite mg-N/L 0.1 0.006 0.48 11 <0.1 <0.003 <0.1 10 <0.1 <0.003 <0.1 21 <0.1 <0.071 0.2 10 <0.1 <0.003 0.48 52 Nitrite mg-N/L <0.003 0.002 <0.05 11 <0.05 <0.003 <0.05 10 <0.05 <0.001 <0.05 11 <0.05 <0.05 <0.05 10 <0.05 <0.001 <0.05 42 Nitrogen - ammonia mg-N/L 0.43 0.016 1.39 11 <0.05 <0.05 0.73 10 <0.05 0.012 0.55 21 <0.05 <0.05 0.2 10 <0.05 0.012 1.39 52 Nitrogen - Kjeldahl mg-N/L 1.7 0.68 4.3 11 1.55 0.83 3.7 10 1.6 1.2 3.3 21 1.5 1.12 2.2 10 1.6 0.68 4.3 52 Nitrogen - total mg-N/L 1.98 0.94 4.3 11 1.55 0.83 3.7 10 1.6 1.2 3.3 21 1.5 1.12 2.2 10 1.6 0.83 4.3 52 Phosphorus - total mg-P/L 0.09 0.019 0.372 11 0.06 0.02 0.21 10 0.058 0.024 1.32 18 0.05 0.028 0.09 10 0.06 0.019 1.32 49 Phosphorus - dissolved mg-P/L 0.032 0.015 0.208 11 0.02 0.006 0.08 10 0.02 0.01 0.99 21 <0.02 <0.02 0.05 10 0.02 0.006 0.99 52 Biochemical oxygen demand mg/L - - - 0 - <6 <6 2 2 <2 12 9 - - - 0 3 <2 12 11 Chlorophyll a µg/L 2.1 0.2 3.6 5 10.1 7 42 4 - 54.1 71.2 2 - - - 0 7 0.2 71.2 11 General Organics Naphthenic acids mg/L <1 <1 1 6 <1 <1 <1 7 <1 <1 1 16 <1 <1 1.4 7 <1 <1 1.4 36 Total phenolics mg/L 0.01 <0.002 0.022 11 0.004 <0.002 0.011 7 0.01 0.002 0.019 18 0.008 <0.001 0.014 7 0.009 <0.001 0.022 43 Total recoverable hydrocarbons mg/L <2 <2 <2 3 <2 <2 <2 4 <1 <1 1.6 10 - - - 0 <1 <1 <2 17 Total Metals Aluminum mg/L 0.01 <0.002 0.199 11 0.0395 0.0033 0.14 7 0.014 0.0073 0.103 16 0.033 <0.01 0.07 7 0.0199 <0.002 0.199 41 Antimony mg/L 0.00028 0.00005 <0.0004 6 <0.00007 <0.00002 <0.0004 7 0.000045 0.00002 0.00084 16 <0.0004 <0.0004 <0.0004 7 <0.0004 0.00002 0.00084 36 Arsenic mg/L 0.0008 0.0004 0.0057 11 0.0005 0.00028 0.0016 7 0.00069 <0.0004 0.00228 17 0.0006 <0.0004 0.0163 7 0.00069 0.00028 0.0163 42 Barium mg/L 0.036 0.021 0.052 11 0.024 0.01 0.027 7 0.022 0.01 0.051 17 0.019 0.012 0.033 7 0.025 0.01 0.052 42 Beryllium mg/L 0.000515 0.00001 <0.001 6 <0.00001 <0.00001 <0.001 7 <0.000012 <0.000003 <0.001 16 <0.001 <0.001 <0.001 7 <0.001 <0.000003 <0.001 36 Bismuth mg/L <0.000005 <0.000005 <0.000005 3 0.000006 <0.000005 0.000009 4 0.000003 <0.000001 0.000006 9 - - - 0 0.00000435 <0.000001 0.000009 16 Boron mg/L 0.08 <0.02 0.14 6 0.05 <0.02 0.07 7 0.05 0.04 0.145 16 0.05 <0.05 0.1 7 0.05 <0.02 0.145 36 Cadmium mg/L 0.000162 0.000039 <0.0002 6 <0.000021 <0.000005 <0.0002 7 0.000008 <0.000002 <0.002 16 <0.00005 <0.00005 <0.0002 7 <0.00005 <0.000002 <0.002 36 Chromium mg/L 0.0026(a) 0.001 <0.005 11 <0.0001 <0.0001 <0.005 7 <0.0002 <0.00004 <0.005 17 <0.005 <0.005 <0.005 7 <0.003 <0.00004 <0.005 42 Cobalt mg/L <0.001 0.00022 0.002 11 0.00015 0.00004 <0.002 7 0.0001 0.00004 <0.002 17 <0.002 <0.002 <0.002 7 <0.00158 0.00004 0.002 42 Copper mg/L 0.0011 0.0007 0.007 11 0.0006 0.00006 0.001 7 <0.001 <0.00005 0.0091 17 <0.001 <0.001 <0.001 7 <0.001 <0.00005 0.0091 42 Iron mg/L 0.65 0.02 4.48 11 0.39 0.07 0.81 7 0.27 0.02 0.89 17 0.29 0.03 0.89 7 0.32 0.02 4.48 42 Lead mg/L 0.00017 <0.0001 0.00149 6 0.0001 0.00006 0.00057 7 0.00007 0.000003 0.00039 16 <0.0001 <0.0001 0.0001 7 0.0001 0.000003 0.00149 36 Lithium mg/L 0.02 0.0063 0.0363 6 0.01 0.0027 0.022 7 0.01465 <0.01 0.049 16 0.01 <0.01 0.024 7 0.01465 0.0027 0.049 36 Manganese mg/L 0.303 0.007 0.746 11 0.046 0.009 0.304 7 0.042 0.008 0.118 17 0.023 0.014 0.044 7 0.044 0.007 0.746 42 Mercury mg/L 0.000102 0.000002 <0.0002 6 0.000006 0.000003 <0.0002 7 <0.0000007 <0.0000006 <0.0001 16 <0.0001 <0.00002 <0.0001 7 <0.00002 <0.0000006 <0.0002 36 Methyl mercury µg/L <0.00003 <0.00003 0.00041 3 0.00006 0.00003 0.0002 4 - - - 0 - - - 0 0.00004 <0.00003 0.00041 7 Molybdenum mg/L <0.00147 0.00006 <0.005 11 <0.00121 <0.00005 <0.005 7 0.00062 0.00001 <0.005 17 <0.005 <0.005 <0.005 7 <0.002 0.00001 <0.005 42

Page 91: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-6 Water Quality Baseline Report December 2010

Table E-3 Summary of Available Water Quality Data for Other Waterbodies Within and Near the Local Study Area (continued)

Golder Associates

Parameter Units Winter (1989 to 2010) Spring (2008 to 2010) Summer (1977 to 2009) Fall (2008 to 2009) All Seasons (2008 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Nickel mg/L <0.002 <0.001 0.003 11 0.00107 0.00017 <0.002 7 0.00046 <0.000005 0.0023 17 <0.002 <0.002 <0.002 7 <0.002 <0.000005 0.003 42 Selenium mg/L <0.00011 <0.0001 0.0007 11 <0.00009 <0.00004 <0.0004 7 <0.0001 <0.0001 <0.0004 17 <0.0004 <0.0004 <0.0004 7 <0.00016 <0.00004 0.0007 42 Silver mg/L <0.000203 <0.000005 <0.0004 6 <0.000005 <0.000005 <0.0004 7 0.000004 0.0000007 <0.0004 16 <0.0004 <0.0001 0.00048 7 <0.0001 0.0000007 0.00048 36 Strontium mg/L 0.125 0.064 0.342 3 0.105 0.026 0.167 4 0.097 0.081 0.152 9 - - - 0 0.1108 0.026 0.342 16 Thallium mg/L <0.00005 <0.000002 <0.0001 6 <0.000003 <0.000002 <0.0001 7 0.000002 0.0000005 <0.0001 16 <0.0001 <0.0001 <0.0001 7 <0.0001 0.0000005 <0.0001 36 Titanium mg/L 0.0011 <0.0005 0.002 6 0.001 <0.0005 0.006 7 0.0009 0.0004 0.0017 16 <0.001 <0.001 0.002 7 0.001 0.0004 0.006 36 Uranium mg/L 0.0001 0.00003 0.00081 6 0.0001 0.000007 0.00035 7 0.0001 0.00001 0.00134 16 <0.0001 <0.0001 0.00033 7 0.0001 0.000007 0.00134 36 Vanadium mg/L <0.001 <0.0002 0.004 11 <0.0005 <0.0002 <0.001 7 0.00041 0.0001 0.003 17 <0.001 <0.001 <0.001 7 <0.001 0.0001 0.004 42 Zinc mg/L 0.011 0.005 0.045 11 0.0028 0.0012 0.028 7 0.0033 <0.0001 0.007 17 <0.004 <0.004 0.009 7 0.0042 <0.0001 0.045 42 Dissolved Metals Aluminum mg/L 0.01 0.0048 0.12 6 0.01 0.0022 0.047 7 0.0083 0.0005 0.085 16 0.012 <0.01 0.063 7 0.01 0.0005 0.12 36 Antimony mg/L 0.0003 0.00005 <0.0004 6 <0.00006 <0.00002 <0.0004 7 0.00004 0.00002 <0.0004 16 <0.0004 <0.0004 <0.0004 7 <0.0004 0.00002 <0.0004 36 Arsenic mg/L 0.001 0.0007 0.0019 6 0.0004 0.0003 0.0012 7 0.0007 <0.0004 0.0018 16 0.0005 <0.0004 0.0014 7 0.0006 0.0003 0.0019 36 Barium mg/L 0.036 0.027 0.047 6 0.021 0.01 0.024 7 0.02 0.01 0.026 16 0.017 0.011 0.032 7 0.021 0.01 0.047 36 Beryllium mg/L <0.001 0.00001 <0.001 11 <0.00001 <0.00001 <0.001 7 <0.000004 <0.000003 <0.001 17 <0.001 <0.001 <0.001 7 <0.001 <0.000003 <0.001 42 Bismuth mg/L <0.000005 <0.000005 <0.000005 3 <0.000005 <0.000005 <0.000005 4 0.000002 <0.000001 0.000006 9 - - - 0 0.00000435 <0.000001 0.000006 16 Boron mg/L 0.08 <0.02 0.15 6 0.05 <0.02 0.08 7 0.05 0.04 0.08 16 <0.05 <0.05 0.09 7 0.05 <0.02 0.15 36 Cadmium mg/L 0.0001 0.000052 0.00022 6 <0.000011 <0.000005 <0.0001 7 <0.000006 <0.000002 <0.0001 16 <0.00005 <0.00005 <0.0001 7 <0.00005 <0.000002 0.00022 36 Chromium mg/L 0.0038(a) 0.0022(a) <0.005 6 <0.0001 <0.0001 <0.005 7 <0.0001 <0.00004 <0.005 16 <0.005 <0.005 <0.005 7 <0.005 <0.00004 <0.005 36 Chromium - hexavalent mg/L - - - 0 - - - 0 <0.001 - - 1 - - - 0 <0.001 - - 1 Cobalt mg/L 0.00153 0.00022 <0.002 6 0.0001 0.00003 <0.002 7 0.00008 0.00004 <0.002 16 <0.002 <0.002 <0.002 7 <0.002 0.00003 <0.002 36 Copper mg/L 0.001 0.0006 0.0011 6 0.0006 0.00007 <0.001 7 <0.001 <0.00005 0.0016 16 <0.001 <0.001 0.003 7 <0.001 <0.00005 0.003 36 Iron mg/L 0.72 0.1 2.54 6 0.25 0.04 0.46 7 0.17 0.006 0.47 16 0.09 0.03 0.43 7 0.2 0.006 2.54 36 Lead mg/L 0.00015 <0.0001 0.00056 6 0.0001 0.00007 0.00018 7 0.00004 <0.000001 0.00016 16 <0.0001 <0.0001 <0.0001 7 <0.0001 <0.000001 0.00056 36 Lithium mg/L 0.02 0.006 0.037 6 0.011 0.002 0.021 7 0.014 <0.003 0.022 16 0.012 <0.003 0.024 7 0.014 0.002 0.037 36 Manganese mg/L 0.334 0.207 0.752 6 0.005 0.0009 0.223 7 0.01 0.0005 0.1 16 0.005 <0.001 0.034 7 0.01 0.0005 0.752 36 Mercury mg/L 0.0000515 0.000001 <0.0001 6 <0.000003 <0.000002 <0.00002 7 <0.0000109 <0.00001 <0.0001 16 <0.0001 <0.0001 <0.0001 7 <0.00002 0.000001 <0.0001 36 Molybdenum mg/L 0.0033 0.00006 <0.005 6 <0.0012 <0.00005 <0.005 7 0.0003 0.00001 <0.005 16 <0.005 <0.005 <0.005 7 <0.005 0.00001 <0.005 36 Nickel mg/L 0.0018 0.0008 <0.002 6 0.0009 0.0002 <0.002 7 <0.0003 <0.000005 <0.002 16 <0.002 <0.002 0.0024 7 <0.002 <0.000005 0.0024 36 Selenium mg/L 0.0003 0.00011 0.0008 6 <0.00008 <0.00004 <0.0004 7 <0.0001 0.0001 <0.0004 16 <0.0004 <0.0004 <0.0004 7 <0.0004 <0.00004 0.0008 36 Silver mg/L <0.000053 <0.000005 0.0002 6 <0.000005 <0.000005 <0.0001 7 <0.0000005 <0.0000005 <0.0001 16 <0.0001 <0.0001 <0.0001 7 <0.0001 <0.0000005 0.0002 36 Strontium mg/L 0.121 0.061 0.341 3 0.103 0.025 0.163 4 0.093 0.079 0.149 9 - - - 0 0.10715 0.025 0.341 16 Thallium mg/L <0.00005 <0.000002 <0.0001 6 <0.000003 <0.000002 <0.0001 7 0.000002 0.0000005 <0.0001 16 <0.0001 <0.0001 <0.0001 7 <0.0001 0.0000005 <0.0001 36 Titanium mg/L <0.0008 <0.0005 <0.001 6 <0.0006 <0.0005 <0.001 7 0.0008 0.0002 <0.001 16 <0.001 <0.001 <0.001 7 <0.001 0.0002 <0.001 36 Uranium mg/L 0.0001 0.00002 0.00081 6 0.0001 0.000006 0.00034 7 0.0001 0.000008 0.00038 16 <0.0001 <0.0001 0.00032 7 0.0001 0.000006 0.00081 36 Vanadium mg/L 0.0007 <0.0002 0.002 6 <0.0004 <0.0002 <0.001 7 0.0003 0.00005 <0.001 16 <0.001 <0.001 <0.001 7 <0.001 0.00005 0.002 36 Zinc mg/L 0.014 <0.002 0.051 6 0.004 0.0004 0.011 7 0.002 0.00005 0.004 16 <0.002 <0.002 0.005 7 0.002 0.00005 0.051 36 PAHs and Alkylated PAHs Naphthalene µg/L 0.03 <0.01 0.05 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 0.014 7 <0.01 <0.01 <10 20 C1 substituted naphthalenes µg/L 0.03 <0.01 0.04 3 <0.01 <0.01 <0.01 3 - - - 0 - - - 0 <0.01 <0.01 0.04 6 C4 substituted naphthalenes µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6 Acenaphthene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 C1 substituted acenaphthenes µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6 Acenaphthylene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 - - - 0 - - - 0 <0.01 <0.01 <0.01 6 Anthracene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 Dibenzo(a,h)anthracene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 Benzo(a)anthracene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 C1 substituted benzo(a)anthracenes / chrysenes

µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6

C2 substituted benzo(a)anthracenes / chrysenes

µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6

Benzo(a)pyrene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 Benzo(b)fluoranthene µg/L <0.01 <0.01 <0.01 3 <10 <10 <10 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 Benzo(k)fluoranthene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 C1 substituted benzofluoranthenes / benzopyrenes

µg/L <0.04 <0.04 <0.04 3 <0.01 <0.01 <0.01 3 - - - 0 - - - 0 <0.025 <0.01 <0.04 6

Benzo(g,h,i)perylene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 - - - 0 - - - 0 <0.01 <0.01 <0.01 6 Biphenyl µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 - - - 0 - - - 0 <0.01 <0.01 <0.01 6 C1 substituted biphenyls µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6 C2 substituted biphenyls µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6

Page 92: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-7 Water Quality Baseline Report December 2010

Table E-3 Summary of Available Water Quality Data for Other Waterbodies Within and Near the Local Study Area (continued)

Golder Associates

Parameter Units Winter (1989 to 2010) Spring (2008 to 2010) Summer (1977 to 2009) Fall (2008 to 2009) All Seasons (2008 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Chrysene µg/L <0.01 <0.01 <0.01 3 <0.01 �ז���0>ז. <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 Dibenzothiophene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 - - - 0 - - - 0 <0.01 <0.01 <0.01 6 C1 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6 C2 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6 C3 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6 C4 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6 Fluoranthene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 C1 substituted fluoranthenes / pyrenes µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6 Fluorene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 C1 substituted fluorenes µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6 C2 substituted fluorenes µg/L <0.04 <0.04 0.1 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 0.1 6 Indeno(c,d-123)pyrene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20 Phenanthrene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.029 <0.01 <10 7 <0.01 <0.01 0.02 7 <0.01 <0.01 <10 20 C1 substituted phenanthrenes / anthracenes

µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6

C2 substituted phenanthrenes / anthracenes

µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6

C3 substituted phenanthrenes / anthracenes

µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6

C4 substituted phenanthrenes / anthracenes

µg/L <0.04 <0.04 <0.04 3 <0.04 <0.04 <0.04 3 - - - 0 - - - 0 <0.04 <0.04 <0.04 6

Pyrene µg/L <0.01 <0.01 <0.01 3 <0.01 <0.01 <0.01 3 <0.01 <0.01 <10 7 <0.01 <0.01 <0.01 7 <0.01 <0.01 <10 20

(a) Chromium results for samples collected in winter 2010 are suspect due to irregularities found in QC samples. Refer to Attachment C for additional information.

- = Not applicable or no data.

Sources: Water quality data from samples collected in 2009 and 2010, AOSC (2009), Sunshine (2009) and Alberta Environment (AENV 2010) WDS Stations AB07DA0200, 0210, 0220, 0230, 0240, 0250, 0260 and 0290.

Page 93: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-8 Water Quality Baseline Report December 2010

Golder Associates

Table E-4 Summary of Available Water Quality Data for the Ells River Within and Near the Local Study Area

Parameter Units Winter (1976 to 2010) Spring (1977 to 2010) Summer (1977 to 2009) All Seasons (1976 to 2009) Annual (1976 to 2010)

Median Min Max n Median Min Max n Median Min Max n Median Min Max n Median Min Max n

Field Measured pH - 7.1 6.6 7.9 7 7.2 6.4 8.7 5 7.5 6 8.5 6 7.9 5.6 8.3 5 7.5 5.6 8.7 23 Specific conductance µS/cm 161 80 5300 10 132 90 160 6 126 43 220 8 195 70 1222 7 151 43 5300 31 Temperature °C 0 0 1 13 8.2 0 17.5 9 15.7 9.3 20.8 12 6.4 3 11 9 7.5 0 20.8 43 Dissolved oxygen mg/L 8 5.5 12.9 6 10.4 2 13.4 8 9.4 6.4 10.9 7 12.8 11.7 14.3 5 10.2 2 14.3 26 Conventional Parameters Specific conductance µS/cm 146 115 400 15 134 70 145 9 123 96 177 12 131 90 186 10 134 70 400 46 Colour TCU - 25 25 2 37 28 43 5 49 36 51 4 38 32 45 4 37 25 51 15 Dissolved organic carbon mg/L 12 8 17 16 12 7 25 9 13 10 18 12 14 10 15 10 13 7 25 47 Hardness mg/L 70 61 111 11 60 39 66 9 61 51 83 11 63 55 84 8 65 39 111 39 pH - 7.3 7.1 7.9 15 7.7 6.9 8 9 7.8 7.2 8.3 12 7.7 7.3 8 10 7.5 6.9 8.3 46 Total alkalinity mg/L 66 56 212 15 60 38 65 9 61 50 78 12 59 48 88 10 61 38 212 46 Total dissolved solids mg/L 93 75 264 15 73 46 130 9 71 58 128 12 77 59 113 10 79 46 264 46 Total organic carbon mg/L 12 8 20 14 14 7 25 9 14 11 18 10 14 10 16 9 14 7 25 42 Total suspended solids mg/L 3 0.8 86 15 10 2 70 9 3 1 26 12 4 1 17 10 4 0.8 86 46 Major Ions Bicarbonate mg/L 105 83 120 3 76 73 79 5 79 76 95 6 84 72 108 5 79 72 120 19 Calcium mg/L 18 15 50 14 16 10 18 9 15 13 22 10 16 14 23 9 17 10 50 42 Carbonate mg/L - <0.5 <5 2 <5 <0.5 <5 5 <5 <5 <5 4 <5 <5 <5 4 <5 <0.5 <5 15 Chloride mg/L 0.7 0.4 5.4 15 1 0.3 2 9 1 0.3 1.8 12 0.8 0.3 1.8 10 0.9 0.3 5.4 46 Fluoride mg/L 0.09 <0.05 0.13 13 0.09 0.07 0.1 4 0.1 0.05 0.14 8 0.1 <0.05 0.11 6 0.09 <0.05 0.14 31 Magnesium mg/L 6 5 16 14 5 4 6 9 5 4 7 10 5 4 7 9 5 4 16 42 Potassium mg/L 1 0.7 2.4 15 0.9 0.6 1.3 9 0.9 0.07 1.1 12 0.9 0.4 1.2 10 0.9 0.07 2.4 46 Sodium mg/L 4 3 15 15 3 2 4 9 3 2 6 12 3 1 8 10 4 1 15 46 Sulphate mg/L 7 3 16 15 7 4 11 9 6 4 10 12 8 5 13 10 7 3 16 46 Sulphide mg/L <0.01 <0.001 <0.01 7 0.003 - - 1 <0.003 <0.001 <0.01 4 <0.01 0.002 <0.01 3 <0.003 <0.001 <0.01 15 Nutrients and Biological Indicators Nitrate mg-N/L 0.133 0.066 1.4 6 <0.1 0.02 <0.1 6 <0.1 0.008 <0.1 5 <0.1 <0.05 <0.1 4 <0.1 0.008 1.4 21 Nitrate + nitrite mg-N/L 0.17 0.046 0.4 15 <0.1 0.005 0.102 9 0.012 <0.003 <0.1 12 0.064 0.003 0.122 10 0.1 <0.003 0.4 46 Nitrite mg-N/L 0.003 0.002 <0.05 7 <0.05 <0.003 <0.05 6 <0.027 <0.001 <0.05 8 <0.05 0.005 <0.05 6 <0.011 <0.001 <0.05 27 Nitrogen - ammonia mg-N/L 0.05 0.02 0.13 16 <0.05 0.01 0.06 9 0.043 0.007 0.11 12 <0.05 0.02 0.08 8 0.05 0.007 0.13 45 Nitrogen - Kjeldahl mg-N/L 0.7 0.1 7.85 15 0.82 0.55 1.2 9 0.77 0.5 1.09 12 0.69 0.11 1.1 10 0.73 0.1 7.85 46 Nitrogen - total mg-N/L 0.84 0.28 7.99 15 0.89 0.55 1.2 9 0.77 0.5 1.14 12 0.7 0.13 1.1 10 0.79 0.13 7.99 46 Phosphorus - total mg-P/L 0.042 0.03 1.08 15 0.06 0.019 0.08 9 0.038 0.031 0.05 11 0.037 0.023 0.07 10 0.038 0.019 1.08 45 Phosphorus - dissolved mg-P/L 0.02 0.019 0.029 3 <0.02 0.011 <0.02 5 0.021 0.014 0.03 6 <0.02 0.011 <0.02 5 0.02 0.011 0.03 19 Chlorophyll a µg/L - <1 <1 2 - - - 0 - - - 0 2 - - 1 <1 <1 2 3 General Organics Naphthenic acids mg/L - <1 <1 2 <1 <1 <1 5 <1 <1 <1 3 <1 <1 <1 4 <1 <1 <1 14 Total phenolics mg/L <0.002 <0.001 0.02 9 0.005 <0.001 0.007 7 <0.001 <0.001 0.007 8 <0.001 <0.001 0.004 7 <0.001 <0.001 0.02 31 Total recoverable hydrocarbons mg/L <0.4 <0.1 <2 8 <0.3 <0.1 <2 3 0.5 <0.1 0.9 6 0.5 <0.1 1 3 0.5 <0.1 <2 20 Total Metals Aluminum mg/L 0.0309 <0.01 0.0594 4 0.28 0.0352 0.7 5 0.05 0.015 0.08 6 0.0288 0.02 0.07 5 0.05 <0.01 0.7 20 Antimony mg/L 0.000061 0.000047 <0.0004 4 <0.0004 0.00005 <0.0004 5 0.0004 0.000049 0.0025 6 <0.0004 0.000073 <0.0004 5 <0.0004 0.000047 0.0025 20 Arsenic mg/L 0.00066 0.0006 0.00071 4 0.0009 0.00067 0.0012 5 0.001 0.0007 0.0011 6 0.0008 0.00068 0.001 5 0.0008 0.0006 0.0012 20 Barium mg/L 0.04 0.034 0.047 4 0.033 0.03 0.039 5 0.028 0.024 0.032 6 0.028 0.027 0.033 5 0.031 0.024 0.047 20 Beryllium mg/L 0.000065 <0.00001 <0.001 4 <0.001 <0.00001 <0.001 5 <0.001 <0.00004 <0.001 6 <0.001 0.000081 <0.001 5 <0.001 <0.00001 <0.001 20 Bismuth mg/L <0.000005 <0.000005 0.000018 3 0.000025 - - 1 0.000007 <0.000005 0.000008 2 0.00001 - - 1 0.000008 <0.000005 0.000025 7 Boron mg/L 0.038 0.024 <0.05 4 <0.05 0.03 <0.05 5 <0.05 0.022 <0.05 6 <0.05 0.022 0.05 5 <0.05 0.022 0.05 20 Cadmium mg/L <0.00002 <0.000005 <0.0002 4 <0.0002 0.00001 <0.0002 5 <0.001025 <0.00002 <0.002 6 <0.0002 <0.00002 <0.0002 5 <0.0002 <0.000005 <0.002 20 Chromium mg/L 0.0011(a) 0.0001 <0.005 4 <0.005 <0.0001 <0.005 5 <0.005 <0.0001 <0.005 6 <0.005 <0.0001 <0.005 5 <0.005 <0.0001 <0.005 20 Cobalt mg/L 0.00011 0.0001 <0.002 4 <0.002 0.0001 <0.002 5 <0.002 0.00009 <0.002 6 <0.002 0.00011 <0.002 5 <0.002 0.00009 <0.002 20 Copper mg/L 0.0006 <0.00008 <0.001 4 0.001 0.0005 0.002 5 <0.001 0.0004 <0.001 6 0.001 0.0005 0.002 5 0.001 <0.00008 0.002 20 Iron mg/L 0.26 0.06 0.5 4 0.51 0.27 1.57 5 0.36 0.25 0.53 6 0.36 0.18 0.69 5 0.34 0.06 1.57 20 Lead mg/L 0.00006 <0.00001 <0.0001 4 0.0002 <0.0001 0.0008 5 0.0001 <0.00001 0.0002 6 0.0001 0.00004 0.0003 5 0.0001 <0.00001 0.0008 20

Page 94: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-9 Water Quality Baseline Report December 2010

Table E-4 Summary of Available Water Quality Data for the Ells River Within and Near the Local Study Area (continued)

Golder Associates

Parameter Units Winter (1976 to 2010) Spring (1977 to 2010) Summer (1977 to 2009) All Seasons (1976 to 2009) Annual (1976 to 2010)

Median Min Max n Median Min Max n Median Min Max n Median Min Max n Median Min Max n

Lithium mg/L 0.01085 0.01 0.0159 4 <0.01 0.0099 0.01 5 0.01 0.00656 0.01 6 0.01 0.0084 0.01 5 0.01 0.00656 0.0159 20 Manganese mg/L 0.026 0.014 0.057 4 0.069 0.029 0.073 5 0.036 0.025 0.051 6 0.025 0.018 0.043 5 0.036 0.014 0.073 20 Mercury mg/L <0.000005 0.000003 <0.0002 3 <0.00002 0.000003 <0.0002 5 <0.00002 <0.00002 <0.0001 4 <0.00002 <0.00002 <0.0001 4 <0.00002 0.000003 <0.0002 16 Methyl mercury µg/L <0.00003 - - 1 0.00005 - - 1 - - - 0 - - - 0 - <0.00003 0.00005 2 Molybdenum mg/L 0.00074 0.00054 <0.005 4 <0.005 0.00061 <0.005 5 <0.005 0.00056 <0.005 6 <0.005 0.0006 <0.005 5 <0.005 0.00054 <0.005 20 Nickel mg/L 0.00092 0.00034 <0.002 4 <0.002 0.00075 0.003 5 <0.002 0.0006 <0.002 6 <0.002 0.00062 0.002 5 <0.002 0.00034 0.003 20 Selenium mg/L 0.00045 0.00009 0.0008 4 <0.0004 0.00007 <0.0004 5 <0.0004 <0.0004 <0.0005 6 <0.0004 <0.0004 <0.0005 5 <0.0004 0.00007 0.0008 20 Silver mg/L <0.000005 <0.000005 <0.0004 3 <0.0004 <0.000005 <0.0004 5 <0.0004 0.00014 <0.0004 4 <0.0004 <0.0001 <0.0004 4 <0.0004 <0.000005 <0.0004 16 Strontium mg/L 0.101 0.079 0.122 3 0.073 - - 1 0.071 0.071 0.072 2 0.066 - - 1 0.073 0.066 0.122 7 Thallium mg/L 0.000003 0.000002 <0.0001 4 <0.0001 <0.000002 <0.0001 5 <0.0001 <0.000003 <0.0001 6 <0.0001 <0.000003 <0.0001 5 <0.0001 <0.000002 <0.0001 20 Titanium mg/L 0.0012 0.0006 0.002 4 0.006 0.0009 0.014 5 0.001 0.0007 0.0019 6 0.001 <0.001 0.0012 5 0.001 0.0006 0.014 20 Uranium mg/L 0.0001 0.00006 0.00014 4 0.0001 0.00009 0.0002 5 <0.0001 0.00005 <0.0001 6 <0.0001 0.00006 0.0002 5 0.0001 0.00005 0.0002 20 Vanadium mg/L 0.00028 <0.0002 <0.001 4 <0.001 <0.0002 0.002 5 0.001 0.00024 0.05 6 <0.001 0.00022 <0.001 5 <0.001 <0.0002 0.05 20 Zinc mg/L 0.0028 0.0016 0.018 4 0.019 0.0013 0.058 5 0.004 0.001 0.005 6 <0.004 <0.004 0.011 5 0.004 0.001 0.058 20 Dissolved Metals Aluminum mg/L - 0.0025 0.04 2 0.01 0.0055 0.02 5 <0.01 <0.01 <0.01 4 0.01 <0.01 0.01 4 0.01 0.0025 0.04 15 Antimony mg/L - 0.00007 <0.0004 2 <0.0004 0.00006 <0.0004 5 <0.0004 <0.0004 <0.0004 4 <0.0004 <0.0004 <0.0004 4 <0.0004 0.00006 <0.0004 15 Arsenic mg/L - 0.0006 0.0007 2 0.0006 0.0005 0.0006 5 0.001 0.0008 0.0011 4 0.0006 0.0006 0.0007 4 0.0006 0.0005 0.0011 15 Barium mg/L - 0.035 0.044 2 0.026 0.025 0.027 5 0.026 0.025 0.026 4 0.026 0.024 0.029 4 0.026 0.024 0.044 15 Beryllium mg/L - <0.00001 <0.001 2 <0.001 <0.00001 <0.001 5 <0.001 <0.001 <0.001 4 <0.001 <0.001 <0.001 4 <0.001 <0.00001 <0.001 15 Bismuth mg/L <0.000005 - - 1 <0.000005 - - 1 - - - 0 - - - 0 <0.000005 <0.000005 <0.000005 2 Boron mg/L - <0.05 0.05 2 <0.05 0.03 <0.05 5 <0.05 <0.05 <0.05 4 <0.05 <0.05 <0.05 4 <0.05 0.03 0.05 15 Cadmium mg/L - 0.000079 <0.0001 2 <0.0001 <0.000005 <0.0001 5 <0.0001 <0.00005 <0.0001 4 <0.0001 <0.00005 <0.0001 4 <0.0001 <0.000005 <0.0001 15 Chromium mg/L - 0.0023(a) <0.005 2 <0.005 <0.0001 <0.005 5 <0.005 <0.005 <0.005 4 <0.005 <0.005 <0.005 4 <0.005 <0.0001 <0.005 15 Cobalt mg/L - 0.00011 <0.002 2 <0.002 0.00006 <0.002 5 <0.002 <0.002 <0.002 4 <0.002 <0.002 <0.002 4 <0.002 0.00006 <0.002 15 Copper mg/L - 0.0007 <0.001 2 <0.001 0.0003 <0.001 5 <0.001 <0.001 <0.001 4 0.001 <0.001 0.0021 4 <0.001 0.0003 0.0021 15 Iron mg/L 0.25 0.08 0.33 3 0.13 0.08 0.54 5 0.19 0.15 0.25 4 0.24 0.12 0.28 4 0.18 0.08 0.54 16 Lead mg/L - 0.00006 <0.0001 2 <0.0001 0.00002 <0.0001 5 <0.0001 <0.0001 <0.0001 4 <0.0001 <0.0001 <0.0001 4 <0.0001 0.00002 <0.0001 15 Lithium mg/L - 0.011 0.017 2 0.009 0.007 0.012 5 0.009 0.008 0.011 4 0.009 0.008 0.013 4 0.009 0.007 0.017 15 Manganese mg/L 0.021 0.019 0.053 3 0.015 0.005 0.043 5 0.014 0.005 0.019 4 0.015 0.01 0.019 4 0.016 0.005 0.053 16 Mercury mg/L - 0.000002 <0.0001 2 <0.00002 0.000003 <0.00002 5 <0.0001 <0.0001 <0.0001 4 <0.0001 <0.0001 <0.0001 4 <0.0001 0.000002 <0.0001 15 Molybdenum mg/L - 0.0008 <0.005 2 <0.005 0.0006 <0.005 5 <0.005 <0.005 <0.005 4 <0.005 <0.005 <0.005 4 <0.005 0.0006 <0.005 15 Nickel mg/L - 0.0009 <0.002 2 <0.002 0.0007 <0.002 5 <0.002 <0.002 <0.002 4 <0.002 <0.002 <0.002 4 <0.002 0.0007 <0.002 15 Selenium mg/L - 0.00009 <0.0004 2 <0.0004 0.00008 <0.0004 5 <0.0004 <0.0004 <0.0004 4 <0.0004 <0.0004 <0.0004 4 <0.0004 0.00008 <0.0004 15 Silver mg/L - <0.000005 <0.0001 2 <0.0001 <0.000005 <0.0001 5 <0.0001 <0.0001 <0.0001 4 <0.0001 <0.0001 <0.0001 4 <0.0001 <0.000005 <0.0001 15 Strontium mg/L 0.121 - - 1 0.074 - - 1 - - - 0 - - - 0 - 0.074 0.121 2 Thallium mg/L - <0.000002 <0.0001 2 <0.0001 0.000003 <0.0001 5 <0.0001 <0.0001 <0.0001 4 <0.0001 <0.0001 <0.0001 4 <0.0001 <0.000002 <0.0001 15 Titanium mg/L - <0.0005 0.002 2 <0.001 <0.0005 <0.001 5 <0.001 <0.001 <0.001 4 <0.001 <0.001 <0.001 4 <0.001 <0.0005 0.002 15 Uranium mg/L - <0.0001 0.00014 2 0.0001 0.00009 0.0001 5 <0.0001 <0.0001 0.0001 4 0.0001 <0.0001 0.0001 4 <0.0001 0.00009 0.00014 15 Vanadium mg/L - <0.0002 0.002 2 <0.001 <0.0002 <0.001 5 <0.001 <0.001 <0.001 4 <0.001 <0.001 <0.001 4 <0.001 <0.0002 0.002 15 Zinc mg/L - 0.002 0.004 2 0.012 0.0005 0.144 5 <0.002 <0.002 <0.002 4 0.004 <0.002 0.019 4 0.002 0.0005 0.144 15 Polycyclic Aromatic Hydrocarbons and Alkylated Polycyclic Aromatic Hydrocarbons Naphthalene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 C1 substituted naphthalenes µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 - <0.01 <0.01 2 - - - 0 <0.01 <0.01 <0.01 7 C4 substituted naphthalenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 Acenaphthene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 C1 substituted acenaphthenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 Acenaphthylene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 - <0.01 <0.01 2 - - - 0 <0.01 <0.01 <0.01 7 Anthracene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 Dibenzo(a,h)anthracene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 Benzo(a)anthracene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 C1 substituted benzo(a)anthracenes / chrysenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 C2 substituted benzo(a)anthracenes / chrysenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7

Page 95: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-10 Water Quality Baseline Report December 2010

Table E-4 Summary of Available Water Quality Data for the Ells River Within and Near the Local Study Area (continued)

Golder Associates

Parameter Units Winter (1976 to 2010) Spring (1977 to 2010) Summer (1977 to 2009) All Seasons (1976 to 2009) Annual (1976 to 2010)

Median Min Max n Median Min Max n Median Min Max n Median Min Max n Median Min Max n

Benzo(a)pyrene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 Benzo(b)fluoranthene µg/L <0.01 - - 1 <10 <10 <10 4 <5 <0.01 <10 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <10 13 Benzo(k)fluoranthene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 C1 substituted benzofluoranthenes / benzopyrenes µg/L <0.04 - - 1 <0.025 <0.01 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.01 <0.04 7 Benzo(g,h,i)perylene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 - <0.01 <0.01 2 - - - 0 <0.01 <0.01 <0.01 7 Biphenyl µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 - <0.01 <0.01 2 - - - 0 <0.01 <0.01 <0.01 7 C1 substituted biphenyls µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 C2 substituted biphenyls µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 Chrysene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 Dibenzothiophene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 - <0.01 <0.01 2 - - - 0 <0.01 <0.01 <0.01 7 C1 substituted dibenzothiophenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 C2 substituted dibenzothiophenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 C3 substituted dibenzothiophenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 C4 substituted dibenzothiophenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 Fluoranthene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 C1 substituted fluoranthenes / pyrenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 Fluorene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 C1 substituted fluorenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 C2 substituted fluorenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 Indeno(c,d-123)pyrene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 Phenanthrene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13 C1 substituted phenanthrenes / anthracenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 C2 substituted phenanthrenes / anthracenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 C3 substituted phenanthrenes / anthracenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 C4 substituted phenanthrenes / anthracenes µg/L <0.04 - - 1 <0.04 <0.04 <0.04 4 - <0.04 <0.04 2 - - - 0 <0.04 <0.04 <0.04 7 Pyrene µg/L <0.01 - - 1 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 13

(a) Chromium results for samples collected in winter 2010 are suspect due to irregularities found in QC samples. Refer to Attachment C for additional information.

- = Not applicable or no data.

Sources: Water quality data from samples collected in 2009 and 2010, AOSC (2009) and Alberta Environment (AENV 2010) WDS Stations AB07DA1260 and 3000.

Page 96: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-11 Water Quality Baseline Report December 2010

Golder Associates

Table E-5 Summary of Available Water Quality Data for Other Watercourses Within and Near the LSA

Parameter Units Winter (2008 to 2010) Spring (2008 to 2010) Summer (2008 to 2009) All Seasons (2008 to 2009) Annual (2008 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Field Measured pH - 6.7 5.9 7.5 5 7.5 7.1 7.7 14 7.4 5.6 7.9 14 7.6 7.1 8.1 15 7.5 5.6 8.1 48 Specific conductance µS/cm 459 205 742 6 180 10 414 14 288 90 530 14 313 200 656 16 265 10 742 50 Temperature °C 0.1 0 0.3 6 9.1 7.4 16.1 14 15.6 5.3 20.4 14 5 1.3 10.1 16 8.7 0 20.4 50 Dissolved oxygen mg/L 8.6 4.8 11.7 6 9.7 4 10.6 14 7 2.4 8.7 14 9.5 4.5 12.8 16 8.5 2.4 12.8 50 Conventional Parameters Specific conductance µS/cm 524 200 833 6 160 124 410 13 248 162 452 14 286 193 488 16 245 124 833 49 Colour TCU 89 22 180 6 160 61 190 13 145 75 270 14 163 43 210 16 150 22 270 49 Dissolved organic carbon mg/L 27 16 47 6 30 18 39 13 37 21 44 14 34 15 41 16 30 15 47 49 Hardness mg/L 217 89 262 6 66 51 182 13 108 84 188 14 113 81 230 16 101 51 262 49 pH - 8 7.5 8.1 6 7.8 7.6 7.9 13 8 7.8 8.2 14 8 7.7 8.2 16 7.9 7.5 8.2 49 Total alkalinity mg/L 242 89 404 6 74 46 180 13 105 78 236 14 131 90 266 16 105 46 404 49 Total dissolved solids mg/L 302 180 477 6 89 70 310 13 140 85 255 14 159 106 276 16 145 70 477 49 Total organic carbon mg/L 28 16 47 6 30 18 40 13 36 20 41 13 35 15 49 16 32 15 49 48 Total suspended solids mg/L 9 <3 11 6 8 2 55 13 10 <3 26 14 6 <3 53 16 8 2 55 49 Major Ions Bicarbonate mg/L 295 110 493 6 90 56 210 13 128 95 288 14 160 110 325 16 128 56 493 49 Calcium mg/L 56 24 70 6 17 13 51 13 28 23 46 14 29 20 61 16 26 13 70 49 Carbonate mg/L <5 <0.5 <5 6 <5 <0.5 <5 13 <5 <5 <5 14 <5 <5 <5 16 <5 <0.5 <5 49 Chloride mg/L 2 2 3 6 2 2 4 13 1.5 <0.5 2 14 2 <0.5 3 16 2 <0.5 4 49 Magnesium mg/L 19 7 25 6 5 5 14 13 9 7 19 14 10 8 19 16 9 5 25 49 Potassium mg/L 3.1 2.5 4.3 6 1.4 0.6 3 13 0.7 <0.5 1.7 14 1.1 0.5 2.4 16 1.2 <0.5 4.3 49 Sodium mg/L 35 12 92 6 14 4 22 13 10 3 41 14 13 4 41 16 14 3 92 49 Sulphate mg/L 33 6 52 6 14 4 49 13 15 3 32 14 17 4 50 16 14 3 52 49 Sulphide mg/L 0.037 - - 1 0.037 0.01 0.074 3 - - - 0 - - - 0 0.037 0.01 0.074 4 Nutrients and Biological Indicators Nitrate mg-N/L 0.3 0.02 0.8 6 <0.1 <0.003 <0.1 13 <0.1 <0.05 <0.1 14 <0.1 <0.05 <0.1 16 <0.1 <0.003 0.8 49 Nitrate + nitrite mg-N/L 0.3 0.005 0.8 6 <0.1 <0.003 0.1 13 <0.1 <0.071 <0.1 14 <0.1 <0.071 <0.1 16 <0.1 <0.003 0.8 49 Nitrite mg-N/L <0.05 <0.003 <0.05 6 <0.05 <0.003 <0.05 13 <0.05 <0.05 <0.05 14 <0.05 <0.05 <0.05 16 <0.05 <0.003 <0.05 49 Nitrogen - ammonia mg-N/L 0.28 0.11 0.79 6 <0.05 <0.05 0.44 13 <0.05 <0.05 0.33 14 <0.05 <0.05 0.124 16 <0.05 <0.05 0.79 49 Nitrogen - Kjeldahl mg-N/L 1.4 0.7 2.7 6 1.7 0.77 4 13 1.2 1 2.2 14 1.15 0.69 3.89 16 1.3 0.69 4 49 Nitrogen - total mg-N/L 1.6 1.3 2.71 6 1.7 0.79 4 13 1.2 1 2.2 14 1.15 0.69 3.89 16 1.3 0.69 4 49 Phosphorus - total mg-P/L 0.155 0.1 0.17 6 0.07 0.04 0.2 13 0.12 0.05 0.17 10 0.086 0.04 0.595 14 0.09 0.04 0.595 43 Phosphorus - dissolved mg-P/L 0.045 <0.02 0.12 6 0.04 0.03 0.1 13 0.059 0.04 0.11 14 0.045 <0.02 0.07 16 0.048 <0.02 0.12 49 Biochemical oxygen demand mg/L - - - 0 <6 <6 <6 3 - - - 0 - - - 0 <6 <6 <6 3 General Organics Naphthenic acids mg/L <1 <1 <1 6 <1 <1 2 13 <1 <1 1.3 14 <1 <1 1.1 16 <1 <1 2 49 Total phenolics mg/L 0.008 0.005 0.011 6 0.012 0.005 0.015 13 0.013 0.002 0.017 14 0.008 <0.001 0.017 16 0.01 <0.001 0.017 49 Total recoverable hydrocarbons mg/L <2 - - 1 <2 <2 <2 3 - - - 0 - - - 0 <2 <2 <2 4 Total Metals Aluminum mg/L 0.0809 0.06 0.41 6 0.22 0.0122 1.72 13 0.076 0.02 0.19 14 0.075 <0.01 0.21 16 0.09 <0.01 1.72 49 Antimony mg/L <0.0004 0.00005 <0.0004 6 <0.0004 0.00004 <0.0004 13 <0.0004 <0.0004 0.0007 14 <0.0004 <0.0004 <0.0004 16 <0.0004 0.00004 0.0007 49 Arsenic mg/L 0.00115 0.0005 0.0016 6 0.0007 <0.0004 0.0023 13 0.00167 0.0006 0.0022 14 0.00107 0.0005 0.00151 16 0.00109 <0.0004 0.0023 49 Barium mg/L 0.044 0.033 0.05 6 0.021 0.013 0.077 13 0.026 0.014 0.037 14 0.025 0.015 0.036 16 0.026 0.013 0.077 49 Beryllium mg/L <0.001 0.00002 <0.001 6 <0.001 0.00001 <0.001 13 <0.001 <0.001 <0.001 14 <0.001 <0.001 <0.001 16 <0.001 0.00001 <0.001 49 Bismuth mg/L <0.000005 - - 1 0.000006 <0.000005 0.000015 3 - - - 0 - - - 0 0.0000055 <0.000005 0.000015 4 Boron mg/L 0.16 0.07 0.47 6 0.07 <0.05 0.21 13 0.076 <0.05 0.2 14 0.069 <0.05 0.18 16 0.073 <0.05 0.47 49 Cadmium mg/L <0.0002 0.000005 <0.0002 6 <0.0002 <0.000005 <0.0002 13 <0.0011 <0.00005 <0.002 14 <0.0002 <0.00005 <0.0002 16 <0.0002 <0.000005 <0.002 49 Chromium mg/L <0.005 0.0025(a) <0.005 6 <0.005 <0.0001 <0.005 13 <0.005 <0.005 <0.005 14 <0.005 <0.005 <0.005 16 <0.005 <0.0001 <0.005 49 Cobalt mg/L <0.002 0.00068 <0.002 6 <0.002 0.00008 <0.002 13 <0.002 <0.002 <0.002 14 <0.002 <0.002 <0.002 16 <0.002 0.00008 <0.002 49 Copper mg/L 0.001 0.0006 0.004 6 0.001 0.0002 0.005 13 <0.001 <0.001 0.001 14 <0.001 <0.001 0.002 16 <0.001 0.0002 0.005 49 Iron mg/L 2.16 0.73 5.76 6 1.02 0.25 2.06 13 1.2 0.57 2.6 14 1.03 0.49 2.9 16 1.04 0.25 5.76 49 Lead mg/L 0.00017 0.0001 0.0003 6 0.0002 0.00003 0.0006 13 0.00014 <0.0001 0.0004 14 0.0001 <0.0001 0.0003 16 0.00019 0.00003 0.0006 49 Lithium mg/L 0.045 0.0178 0.09 6 0.02 0.01 0.03 13 0.02 <0.01 0.05 14 0.0215 0.01 0.05 16 0.02 <0.01 0.09 49

Page 97: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-12 Water Quality Baseline Report December 2010

Table E-5 Summary of Available Water Quality Data for Other Watercourses Within and Near the LSA (continued)

Golder Associates

Parameter Units Winter (2008 to 2010) Spring (2008 to 2010) Summer (2008 to 2009) All Seasons (2008 to 2009) Annual (2008 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

Manganese mg/L 0.234 0.108 1.16 6 0.059 0.016 0.246 13 0.082 0.025 0.294 14 0.095 0.034 0.4 16 0.091 0.016 1.16 49 Mercury mg/L <0.0002 0.000003 <0.0002 6 <0.00002 0.000003 <0.00002 13 <0.00002 <0.00002 <0.0001 14 <0.00002 <0.00002 <0.0001 14 <0.00002 0.000003 <0.0002 47 Methyl mercury µg/L <0.00003 - - 1 0.00003 <0.00003 0.00008 3 - - - 0 - - - 0 0.00003 <0.00003 0.00008 4 Molybdenum mg/L <0.005 0.00032 <0.005 6 <0.005 0.00044 <0.005 13 <0.005 <0.005 <0.005 14 <0.005 <0.005 <0.005 16 <0.005 0.00032 <0.005 49 Nickel mg/L 0.002 0.00125 0.004 6 <0.002 0.00101 0.00752 13 <0.002 <0.002 0.003 14 <0.002 <0.002 0.003 16 <0.002 0.00101 0.00752 49 Selenium mg/L 0.00085 0.00011 0.0012 6 <0.0004 0.00005 0.0009 13 <0.0004 <0.0004 <0.0004 14 <0.0004 <0.0004 <0.0004 16 <0.0004 0.00005 0.0012 49 Silver mg/L <0.0004 <0.000005 <0.0004 6 <0.0004 <0.000005 <0.0004 13 <0.0004 <0.0001 <0.0004 14 <0.0004 <0.0001 <0.0004 16 <0.0004 <0.000005 <0.0004 49 Strontium mg/L 0.117 - - 1 0.109 0.082 0.255 3 - - - 0 - - - 0 0.113 0.082 0.255 4 Thallium mg/L <0.0001 <0.000002 <0.0001 6 <0.0001 <0.000002 <0.0001 13 <0.0001 <0.0001 <0.0001 14 <0.0001 <0.0001 <0.0001 16 <0.0001 <0.000002 <0.0001 49 Titanium mg/L 0.0025 0.0016 0.011 6 0.005 <0.0005 0.056 13 0.002 <0.001 0.003 14 0.002 <0.001 0.005 16 0.002 <0.0005 0.056 49 Uranium mg/L 0.0002 0.00007 0.0008 6 0.0001 0.00006 0.00172 13 0.0001 <0.0001 0.00039 14 0.0002 <0.0001 0.00039 16 0.00014 0.00006 0.00172 49 Vanadium mg/L <0.001 0.0005 <0.001 6 0.001 <0.0002 0.005 13 <0.001 <0.001 0.008 14 <0.001 <0.001 0.002 16 <0.001 <0.0002 0.008 49 Zinc mg/L 0.009 0.0065 0.273 6 0.014 0.001 0.145 13 <0.004 <0.004 0.021 14 <0.004 <0.004 0.053 16 0.0065 0.001 0.273 49 Dissolved Metals Aluminum mg/L 0.01 <0.01 0.0416 6 0.03 0.0173 0.184 13 0.014 <0.01 0.03 14 0.02 <0.01 0.038 16 0.02 <0.01 0.184 49 Antimony mg/L <0.0004 0.00005 <0.0004 6 <0.0004 0.00003 <0.0004 13 <0.0004 <0.0004 <0.0004 14 <0.0004 <0.0004 <0.0004 16 <0.0004 0.00003 <0.0004 49 Arsenic mg/L 0.0008 <0.0004 0.0014 6 0.0007 <0.0004 0.0013 13 0.0012 0.0005 0.002 14 0.0007 0.0004 0.0012 16 0.0008 <0.0004 0.002 49 Barium mg/L 0.034 0.028 0.044 6 0.018 0.01 0.04 13 0.021 0.013 0.035 14 0.02 0.013 0.032 16 0.021 0.01 0.044 49 Beryllium mg/L <0.001 0.00002 <0.001 6 <0.001 0.00001 <0.001 13 <0.001 <0.001 <0.001 14 <0.001 <0.001 <0.001 16 <0.001 0.00001 <0.001 49 Bismuth mg/L <0.000005 - - 1 0.000015 0.000007 0.000036 3 - - - 0 - - - 0 0.000011 <0.000005 0.000036 4 Boron mg/L 0.16 0.07 0.48 6 0.07 <0.05 0.22 13 0.07 <0.05 0.2 14 0.06 <0.05 0.18 16 0.07 <0.05 0.48 49 Cadmium mg/L <0.0001 <0.0001 0.000154 6 <0.0001 <0.000005 <0.0001 13 <0.0001 <0.00005 <0.0001 14 <0.0001 <0.00005 <0.0001 16 <0.0001 <0.000005 0.000154 49 Chromium mg/L 0.005 0.0024(a) 0.005 6 <0.005 0.0001 <0.005 13 <0.005 <0.005 <0.005 14 <0.005 <0.005 <0.005 16 <0.005 0.0001 0.005 49 Cobalt mg/L <0.002 0.00064 <0.002 6 <0.002 0.00015 <0.002 13 <0.002 <0.002 <0.002 14 <0.002 <0.002 <0.002 16 <0.002 0.00015 <0.002 49 Copper mg/L <0.001 0.0006 <0.001 6 <0.001 0.0004 <0.001 13 <0.001 <0.001 0.003 14 <0.001 <0.001 0.0019 16 <0.001 0.0004 0.003 49 Iron mg/L 0.73 0.04 2.31 6 0.61 0.21 1.99 13 0.87 0.24 1.41 14 0.66 0.31 1.2 16 0.7 0.04 2.31 49 Lead mg/L <0.0001 <0.0001 0.00013 6 <0.0001 0.0001 0.0003 13 <0.0001 <0.0001 0.0007 14 <0.0001 <0.0001 0.0001 16 <0.0001 0.0001 0.0007 49 Lithium mg/L 0.043 0.018 0.101 6 0.015 0.008 0.036 13 0.02 0.008 0.356 14 0.022 0.01 0.048 16 0.021 0.008 0.356 49 Manganese mg/L 0.231 0.102 1.13 6 0.034 0.003 0.246 13 0.055 0.02 0.289 14 0.065 0.025 0.383 16 0.062 0.003 1.13 49 Mercury mg/L <0.0001 0.000002 <0.0001 6 <0.00002 <0.000002 <0.00002 13 <0.0001 <0.0001 <0.0001 14 <0.0001 <0.00002 <0.0001 16 <0.0001 <0.000002 <0.0001 49 Molybdenum mg/L <0.005 0.0003 <0.005 6 <0.005 0.0005 <0.005 13 <0.005 <0.005 <0.005 14 <0.005 <0.005 <0.005 16 <0.005 0.0003 <0.005 49 Nickel mg/L 0.002 0.0012 0.003 6 <0.002 0.0008 <0.002 13 <0.002 <0.002 0.002 14 <0.002 <0.002 0.0028 16 <0.002 0.0008 0.003 49 Selenium mg/L <0.0004 0.00011 0.0009 6 <0.0004 0.00004 <0.0004 13 <0.0004 <0.0004 <0.0004 14 <0.0004 <0.0004 <0.0004 16 <0.0004 0.00004 0.0009 49 Silver mg/L <0.0001 <0.000005 0.0002 6 <0.0001 <0.000005 <0.0001 13 <0.0001 <0.0001 <0.0001 14 <0.0001 <0.0001 <0.0001 16 <0.0001 <0.000005 0.0002 49 Strontium mg/L 0.112 - - 1 0.116 0.082 0.241 3 - - - 0 - - - 0 0.114 0.082 0.241 4 Thallium mg/L <0.0001 <0.000002 <0.0001 6 <0.0001 <0.000002 <0.0001 13 <0.0001 <0.0001 0.0001 14 <0.0001 <0.0001 <0.0001 16 <0.0001 <0.000002 0.0001 49 Titanium mg/L 0.001 0.0009 0.001 6 <0.001 <0.0005 0.0074 13 <0.001 <0.001 0.001 14 <0.001 <0.001 0.0012 16 <0.001 <0.0005 0.0074 49 Uranium mg/L 0.00015 0.00006 0.0007 6 <0.0001 0.00006 0.00148 13 0.00015 <0.0001 0.00037 14 0.00015 <0.0001 0.00038 16 0.0001 0.00006 0.00148 49 Vanadium mg/L 0.0015 0.0003 0.002 6 <0.001 0.0003 <0.001 13 <0.001 <0.001 <0.001 14 <0.001 <0.001 <0.001 16 <0.001 0.0003 0.002 49 Zinc mg/L 0.011 0.006 0.026 6 0.012 0.002 0.178 13 <0.002 <0.002 0.03 14 0.003 <0.002 0.05 16 0.006 <0.002 0.178 49 Polycyclic Aromatic Hydrocarbons and Alkylated Polycyclic Aromatic Hydrocarbons Naphthalene µg/L <0.01 <0.01 0.02 5 <0.01 <0.01 0.01 10 <0.01 <0.01 <10 14 <0.01 <0.01 <0.025 16 <0.01 <0.01 <10 45 C1 substituted naphthalenes µg/L 0.01 <0.01 0.01 4 <0.01 <0.01 0.01 10 <0.01 <0.01 <0.01 2 <0.01 <0.01 <0.01 2 <0.01 <0.01 0.01 18 C2 substituted naphthalenes µg/L - - - 0 - - - 0 - - - 0 <0.04 <0.04 <0.04 2 - <0.04 <0.04 2 C3 substituted naphthalenes µg/L - - - 0 - - - 0 - - - 0 <0.04 <0.04 <0.04 2 - <0.04 <0.04 2 C4 substituted naphthalenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 Acenaphthene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 14 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 45 C1 substituted acenaphthenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 Acenaphthylene µg/L <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 2 <0.01 <0.01 <0.01 2 <0.01 <0.01 <0.01 18 Anthracene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 14 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 45 Dibenzo(a,h)anthracene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 14 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 45 Benzo(a)anthracene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 13 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 44 C1 substituted benzo(a)anthracenes / chrysenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18

Page 98: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project E-13 Water Quality Baseline Report December 2010

Table E-5 Summary of Available Water Quality Data for Other Watercourses Within and Near the LSA (continued)

Golder Associates

Parameter Units Winter (2008 to 2010) Spring (2008 to 2010) Summer (2008 to 2009) All Seasons (2008 to 2009) Annual (2008 to 2010)

Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n Median Minimum Maximum n

C2 substituted benzo(a)anthracenes / chrysenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C3 substituted benzo(a)anthracenes / chrysenes µg/L - - - 0 - - - 0 - - - 0 <0.04 <0.04 <0.04 2 - <0.04 <0.04 2 C4 substituted benzo(a)anthracenes / chrysenes µg/L - - - 0 - - - 0 - - - 0 <0.01 <0.01 <0.01 2 - <0.01 <0.01 2 Benzo(a)pyrene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 13 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 44 Benzo(b)fluoranthene µg/L <0.01 <0.01 <0.01 5 <10 <10 <10 10 <0.01 <0.01 <10 13 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 44 Benzo(k)fluoranthene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 13 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 44 C1 substituted benzofluoranthenes / benzopyrenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C2 substituted benzofluoranthenes / benzopyrenes µg/L - - - 0 - - - 0 - - - 0 <0.04 <0.04 <0.04 2 - <0.04 <0.04 2 Benzo(g,h,i)perylene µg/L <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 2 <0.01 <0.01 <0.01 2 <0.01 <0.01 <0.01 18 Biphenyl µg/L <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 2 <0.01 <0.01 <0.01 2 <0.01 <0.01 <0.01 18 C1 substituted biphenyls µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C2 substituted biphenyls µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 Chrysene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 14 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 45 Dibenzothiophene µg/L <0.01 <0.01 <0.01 4 <0.01 <0.01 <0.01 10 <0.01 <0.01 <0.01 2 <0.01 <0.01 <0.01 2 <0.01 <0.01 <0.01 18 C1 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C2 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C3 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C4 substituted dibenzothiophenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 Fluoranthene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 14 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 45 C1 substituted fluoranthenes / pyrenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C2 substituted fluoranthenes / pyrenes µg/L - - - 0 - - - 0 - - - 0 <0.04 <0.04 <0.04 2 - <0.04 <0.04 2 C3 substituted fluoranthenes / pyrenes µg/L - - - 0 - - - 0 - - - 0 <0.04 <0.04 <0.04 2 - <0.04 <0.04 2 Fluorene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 14 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 45 C1 substituted fluorenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C2 substituted fluorenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C3 substituted fluorenes µg/L - - - 0 - - - 0 - - - 0 <0.04 <0.04 <0.04 2 - <0.04 <0.04 2 Indeno(c,d-123)pyrene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 14 <0.01 <0.01 <0.01 16 <0.01 <0.01 <10 45 Perylene µg/L - - - 0 - - - 0 - - - 0 <0.01 <0.01 <0.01 2 - <0.01 <0.01 2 Phenanthrene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 14 <0.01 <0.01 0.01 16 <0.01 <0.01 <10 45 C1 substituted phenanthrenes / anthracenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C2 substituted phenanthrenes / anthracenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C3 substituted phenanthrenes / anthracenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 C4 substituted phenanthrenes / anthracenes µg/L <0.04 <0.04 <0.04 4 <0.04 <0.04 <0.04 10 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 2 <0.04 <0.04 <0.04 18 Pyrene µg/L <0.01 <0.01 <0.01 5 <0.01 <0.01 <0.01 10 <0.01 <0.01 <10 14 <0.01 <0.01 0.012 16 <0.01 <0.01 <10 45 Retene µg/L - - - 0 - - - 0 - - - 0 <0.01 <0.01 <0.01 2 - <0.01 <0.01 2

(a) Chromium results for samples collected in winter 2010 are suspect due to irregularities found in QC samples. Refer to Attachment C for additional information.

- = Not applicable or no data.

Sources: Water quality data from field surveys conducted in 2009 and 2010, AOSC (2009) and Sunshine (2009).

Page 99: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

ATTACHMENT F

PROJECT-SPECIFIC SEDIMENT QUALITY SUMMARY

Page 100: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project F-1 Water Quality Baseline Report December 2010

Golder Associates

Table F-1 Summary of Available Sediment Quality Data for Waterbodies and Watercourses Within and Near the Local Study Area

Sample Site Waterbodies (2008 to 2009) Watercourses (2008 to 2009) Parameter Units Median Minimum Maximum n Median Minimum Maximum n

Physical and Aggregate Properties pH - 6.2 5.8 6.5 7 6.6 5.2 7.6 19 Electrical conductivity ds/m 0.6 0.1 1.1 7 0.6 0.3 1.5 19 Moisture content % 85 56 86 3 55 31 85 6 Organic matter % 6 0.9 71 7 2 0.5 17 19 Total organic carbon % 2.3 0.5 3.5 4 1.2 <0.4 9.9 17 Sand(a) % 76 8 90 7 77 8 96 19 Silt and clay(a) % 24 10 92 7 23 4 92 19 Salinity and Soluble Ions Sodium adsorption ratio SAR 0.5 0.4 0.9 7 0.8 0.4 2.1 19 Theoretical gypsum requirement tons/acre <0.1 <0.1 <0.1 7 <0.1 <0.1 <0.1 19 Sodium mg/L 7.1 0.6 25.3 7 2.2 0.5 47.1 19 Calcium mg/L 11.7 3.2 86.5 7 6.2 1.6 212 19 Magnesium mg/L 3.4 1.6 20.2 7 3.1 0.7 56.1 19 Potassium mg/L 4.7 0.21 14.9 7 0.22 0.07 14.2 19 Chloride mg/L 20 0.4 30 7 1.3 0.4 133 19 Sulphate mg/L 19.5 3.4 786 7 10.3 2.5 743 19 Saturation % 130 45 585 7 45 27 489 19 Nutrients Nitrate + nitrite mg-N/L <1 <1 <1 3 <1 <1 2.1 6 Nitrogen - ammonia mg-N/L 93.6 33.9 120 3 32.9 2.2 50.8 6 Nitrogen - Kjeldahl % 0.49 0.09 2.95 7 0.09 <0.02 1.8 19 Phosphate - available µg-P/g 7 3 37 7 6 1 18 19 Phosphorus - total µg-P/g 829 825 1400 3 478 298 1500 6 Sulphur - total % 0.38 0.26 2.27 3 0.12 <0.1 2 6 Sulphide µg-S/g 10.8 8.26 38.4 3 24.63 <0.2 183 6 General Organics Naphthenic acids µg/g <5 <5 <5 4 <5 <5 <5 12 Phenols µg/g 0.55 <0.1 2.93 7 0.78 <0.1 7.03 18 Total Metals Antimony µg/g <0.23 <0.2 0.48 7 <0.2 <0.2 <0.4 19 Arsenic µg/g 2.3 0.5 11.2 7 2.67 0.8 11.5 19 Barium µg/g 85 23 209 7 62 21 197 19 Beryllium µg/g <1 <1 <2 7 <1 <1 <2 19 Boron µg/g 3.54 1.41 4.12 3 1.09 0.36 19.6 6 Cadmium µg/g <0.5 <0.5 <1 7 <0.5 <0.5 <1 19 Chromium µg/g 5.1 2.3 16.3 7 6.1 1.4 19.5 19

Page 101: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project F-2 Water Quality Baseline Report December 2010

Table F-1 Summary of Available Sediment Quality Data for Waterbodies and Watercourses Within and Near the Local Study Area (continued)

Golder Associates

Sample Site Waterbodies (2008 to 2009) Watercourses (2008 to 2009) Parameter Units Median Minimum Maximum n Median Minimum Maximum n

Cobalt µg/g 3 <1 8.6 7 4 <1 12 19 Copper µg/g 6 <2 18.8 7 5 <2 33 19 Lead µg/g <5.1 <5 11.6 7 <5 <5 11 19 Mercury µg/g 0.059 <0.05 0.11 7 <0.05 <0.05 0.09 19 Methyl mercury µg/g 0.00164 0.000332 0.00233 3 0.000362 0.000159 0.0013 6 Molybdenum µg/g <1 <1 2.1 7 <1 <1 2.3 19 Nickel µg/g 8 <2 22.8 7 7 <2 24.2 19 Selenium µg/g 0.89 <0.2 1.37 7 0.3 <0.2 2.02 19 Silver µg/g <1 <1 <2 7 <1 <1 <2 19 Thallium µg/g <1 <1 <2 7 <1 <1 <2 19 Tin µg/g <5 <5 <10 7 <5 <5 <10 19 Uranium µg/g <2 <2 <4 7 <2 <2 6.9 19 Vanadium µg/g 8.1 3 25 7 12 3 32 19 Zinc µg/g 73 <10 120 7 20 <10 90 19 Polycyclic Aromatic Hydrocarbons and Alkylated Polycyclic Aromatic Hydrocarbons Naphthalene µg/g 0.015 <0.01 0.054 6 <0.01 <0.01 0.07 17 1-Methylnaphthalene µg/g <0.03 <0.01 <0.03 3 <0.01 <0.01 <0.03 6 2-Methylnaphthalene µg/g <0.03 <0.01 <0.03 3 <0.01 <0.01 <0.03 6 C2 substituted naphthalenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 0.18 6 C3 substituted naphthalenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C4 substituted naphthalenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 Acenaphthene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17 C1 substituted acenaphthenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 Acenaphthylene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17 Anthracene µg/g <0.01 <0.005 <0.03 6 <0.005 <0.005 <0.03 17 Dibenzo(a,h)anthracene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17 Benzo(a)anthracene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17 C1 substituted benzo(a)anthracenes / chrysenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C2 substituted benzo(a)anthracenes / chrysenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C3 substituted benzo(a)anthracenes / chrysenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C4 substituted benzo(a)anthracenes / chrysenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 Benzo(a)pyrene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17 C1 substituted benzofluoranthenes / benzopyrenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C2 substituted benzofluoranthenes / benzopyrenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 Benzo(e)pyrene µg/g <0.03 <0.01 <0.03 3 <0.01 <0.01 <0.03 6 Benzo(b&j)fluoranthenes µg/g <0.025 <0.01 <0.04 6 <0.02 <0.01 <0.03 17

Page 102: WATER QUALITY BASELINE REPORT - Alberta · conditions. Historical baseline water and sediment quality data were compiled and summarized along with the results of the baseline sampling

Dover Commercial Project F-3 Water Quality Baseline Report December 2010

Table F-1 Summary of Available Sediment Quality Data for Waterbodies and Watercourses Within and Near the Local Study Area (continued)

Golder Associates

Sample Site Waterbodies (2008 to 2009) Watercourses (2008 to 2009) Parameter Units Median Minimum Maximum n Median Minimum Maximum n

Benzo(k)fluoranthene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17 Benzo(g,h,i)perylene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17 Biphenyl µg/g <0.03 <0.01 <0.03 3 <0.01 <0.01 <0.03 6 C1 substituted biphenyls µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C2 substituted biphenyls µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 Chrysene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 0.04 17 Dibenzothiophene µg/g <0.03 <0.01 <0.03 3 <0.01 <0.01 <0.03 6 C1 substituted dibenzothiophenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C2 substituted dibenzothiophenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C3 substituted dibenzothiophenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C4 substituted dibenzothiophenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 Fluoranthene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17 C1 substituted fluoranthenes / pyrenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C2 substituted fluoranthenes / pyrenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C3 substituted fluoranthenes / pyrenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 Fluorene µg/g <0.02 <0.01 0.04 6 <0.01 <0.01 <0.03 17 C1 substituted fluorenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C2 substituted fluorenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C3 substituted fluorenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 Indeno(1,2,3-cd)pyrene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17 Perylene µg/g <0.03 <0.03 0.068 3 0.021 <0.01 0.038 6 Phenanthrene µg/g 0.025 <0.01 0.08 6 <0.01 <0.01 0.06 17 C1 substituted phenanthrenes / anthracenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C2 substituted phenanthrenes / anthracenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C3 substituted phenanthrenes / anthracenes µg/g <0.12 <0.04 <0.12 3 <0.04 <0.04 <0.12 6 C4 substituted phenanthrenes / anthracenes µg/g 0.29 0.175 0.59 3 <0.04 <0.04 0.19 6 Pyrene µg/g <0.015 <0.01 <0.03 6 <0.01 <0.01 <0.03 17 Retene µg/g 0.289 0.175 0.588 3 0.0245 <0.01 0.191 6 Polycyclic Aromatic Nitrogen Heterocycles Acridine µg/g <0.03 <0.01 <0.03 3 <0.01 <0.01 <0.03 6 Quinoline µg/g <0.03 <0.01 0.047 3 <0.01 <0.01 0.04 6 (a)

Sand percentage based on sieve analysis with mesh diameter of 75 µm; silt and clay percentage = (100% - sand).

- = Not applicable.

Sources: Sediment quality data from samples collected in 2009 and 2010; AOSC (2009).