investigating for dry stack tailings facility closure ... · laboratory testing indicate that...

1
Investigating for Dry Stack Tailings Facility Closure: Multidisciplinary Evaluation at the Pogo Mine, Alaska * [email protected], Ph. +1-907-273-3604 Dan Neuffer and Christopher Stevens, SRK Consulting (U.S.) Inc., USA Russell Staines, SRK Consulting (Australasia) Pty Ltd., Australia Makoto Umedera and Sally McLeod, Sumitomo Metal Mining Pogo LLC, USA * Sumitomo Metal Mining Pogo LLC (Pogo) is the operator of the Pogo underground gold mine, located near Delta Junction, Alaska. The mine has been in operation since 2006 and produces between 380,000 and 400,000 ounces of gold annually. Filtered tailings from the flotation circuit and waste rock from the mine are placed in the dry stack tailings facility (DSTF). Expansion of the DSTF from 7 M tonnes to 18 M metric tonnes has prompted further evaluation of the facility for closure planning. This paper presents data from several components of a multidisciplinary DSTF closure study, including geotechnical and geochemical test results, in situ temperature and pore pressure measurements, and estimated freezing characteristics of tailings samples. Results of this study indicate the DSTF is physically stable and is comprised of materials that are non-potentially acid-generating; these findings support operational material placement practices and elements of the DSTF closure plan. Geotechnical field and laboratory testing indicate that effective friction angles and dry densities of in situ DSTF materials are consistent with previous slope stability analyses. Geotechnical borehole drilling, thermal monitoring, and analysis indicate the presence of permafrost within the DSTF. Pore pressure measurements and drilling observations indicate a phreatic surface near the base of the DSTF. This study narrows the focus of data collection for future closure planning and provides an example of physical and chemical conditions within a dry stack tailings facility in a continental, subarctic climate. These findings are pertinent for planning, design, permitting, operation, and closure of dry stacks in similar climates. Acid-generating Potential Subsurface Investigation The authors thank the following: Megan Miller, for geotechnical logging of drill core and installation of VWP sensors; Ben Green, for supporting design of the VWP program; and Ivan Clark and Dan Mackie for their discussion of hydrologic processes. Alaska Department of Natural Resources and Alaska Department of Environmental Conservation have provided and continue to provide valuable feedback for the DSTF closure study. The authors also thank Sumitomo Metal Mining Pogo LLC for supporting this study. Summary 0 10 20 30 40 50 60 0 10 20 30 40 50 60 NP (kg CaCO 3 /t) AP (kg CaCO 3 /t) GP-1, n=25 RR-1, n=24 SB-1, n=16 Tailings NP/AP = 1 NP/AP = 2 NP/AP = 3 7.0 7.5 8.0 8.5 9.0 9.5 0 10 20 30 40 50 Rinse pH Depth (m bgs) Geochemical characteristics of DSTF materials affect water quality associated with the facility Rinse pH values were in the range of pH 7 – 9 Nearly all samples were classified as non-potentially acid-generating (non-PAG) based on neutralization potential (NP) to acidification potential (AP) ratios greater than three (NP/AP > 3) Subsurface investigation to evaluate DSTF geotechnical, thermal, hydrogeological, and geochemical characteristics Major components of the facility include the starter and toe berms, shells, general placement area (GPA), and flow-through drain Three sonic boreholes were vertically drilled at SB-1, GP-1, and RR-1 (total depth of 107 m) Sonic core, standard penetration testing (SPT), and Shelby tube samples were collected Four Shelby tube, 38 modified California and 49 geotechnical grab samples Laboratory testing included grain size, Atterberg limits, natural moisture and density, consolidated-undrained triaxial shear, flexible wall permeability, and consolidation Vibrating wire piezometers (VWP) were installed at SB-1, GP-1, and RR-1 to measure ground temperature and pore pressure Dry Stack Tailings and Waste Rock Dry Moist Key Findings and Implications for DSTF Closure Tailings Freezing Characteristics Freezing characteristics of tailings estimated from grain size distribution Atterberg limits, estimated specific surface area Phase state of water in the DSTF affects physical stability, surface water runoff characteristics, permeability, and geochemical reactivity of materials in the stack Estimated unfrozen water content curves for DSTF tailings indicate liquid pore water is present at subfreezing temperatures The unfrozen water content at −1°C is estimated to range between 7 and 11% of the dry mass Presence of unfrozen tailings can be inferred from the relatively warm ground temperatures, the fine-grained nature of the tailings, observational evidence from the drill core, and the estimated freezing characteristics Summary of Measured DSTF Ground Temperature Geotechnical investigation, thermal monitoring, and analyses indicate the presence of both frozen and liquid water within the DSTF Pore pressure measurements and drilling observations indicate a phreatic surface near the base of the DSTF and isolated, perched saturated zones within the dry stack Density and shear strength of DSTF materials indicate static and pseudostatic slope stability of the stack and stability against liquefaction Geochemical analyses of DSTF materials show that acidic drainage from the stack is unlikely DSTF ground temperatures confirm the presence of permafrost, as thermally defined by temperatures at or below 0°C DSTF can be expected to thermally evolve as additional material is added and in relation to changes in local climate and microclimatic effects Monitoring of VWP and evaluation of surface water and groundwater from and adjacent to the DSTF may further constrain components of the DSTF water balance, including runoff, seepage, and flow-through drain flux. Evaluation of the long-term metals-leaching potential of DSTF materials through laboratory testing, comparison to operational monitoring data, and water quality modelling may inform selection and design of a closure cover system Ground Temperature and Pore Pressure Site Sensor descripon Sensor depth 1 (m b.g.s.) Elevaon 2 (m a.m.s.l.) Temperature (°C) Measurement date/period SB-1 Shallow 7.6 726.3 0.1 to 0.7 10/3/2012 to 10/22/2013 SB-1 Deep 31.9 702.0 0.7 10/22/2013 GP-1 Shallow 19.2 738.5 0.7 10/22/2013 GP-1 Deep 41.8 716.0 0.4 10/22/2013 RR-1 Shallow 0.6 764.1 9.1 to 6.2 10/1/2012 to 10/22/2013 RR-1 Mid 18.6 746.2 0.8 10/22/2013 RR-1 Deep 28.7 736.1 0.6 10/22/2013 Freezing point depression -10 -8 -6 -4 -2 0 0 5 10 15 20 25 30 Unfrozen water, % dry mass 10823 10859 10804b 10819 10849b 10853 10858 SSA - 21 m 2 g -1 Temperature ( o C) Sample ID Ice lens from 5.1 m b.g.s Acknowledgements SB-1 (14.3 to 15.8 m) SB-1 (23.5 to 25 m) This study contributes to further understanding of the geotechnical, thermal, hydrologic, and geochemical conditions of the Pogo Mine DSTF to support closure planning. Specifically, this study confirms specific aspects of the DSTF operational construction and closure plans while narrowing the focus of data collection for future closure planning. 2013 2012 Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov. 2013 2012 Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov. Pressure head (kpa) Temperature ( o C) -10 -8 -6 -4 -2 0 2 4 6 8 10 -60 -50 -40 -30 -20 -10 0 10 RR-1 Shallow (764.1 m amsl) RR-1 Deep (736.1 amsl) RR-1 Thermistor RR-1 VWP RR-1 Mid (746.2 m amsl) Water height above sensor (m) -6 -5 -4 -3 -2 -1 0 1 RR-1 Sonic drill rig used for recovery of core and installation of VWP at boreholes SB-1, GP-1, and RR-1 1. Sensor depth is based on the depth below ground surface (b.g.s.) at the time of sensor installation (October 2012). 2. Elevations are presented as metres above mean sea level (m a.m.s.l.). Elevation (m) Elevation (m) Distance in Metres LEGEND Compacted Tailings GPA Materials Rock Shell Flow-through Drain Starter Berm and Toe Berm Sand Silt Clay Gravel Cobble Cobble & Gravel Silt & Gravel Gravel & Sand Lithology Units: Vibrating Wire Piezometer / Thermistor Location Permeability Inferred Water Height Above Sensor Sample Testing Types: Consolidation Triaxial Cross-section Units NW SE 640 680 720 760 800 840 640 680 720 760 800 840 Flow-through drain Composite Shell (Shell 2) Composite Shell (Shell 3) Native Ground Rockfill Shell (Shell 1) GPA Materials 0+000 0+100 0+200 0+300 0+400 0+500 0+600 0+700 0+800 0+900 1+000 1+100 2012 DSTF Surface SB-1 GP-1 RR-1 18M Ton DSTF Surface VWP: 8.7 kpa Temp: -0.1 to -0.7 o C VWP: 41.7 kpa Temp: -0.7 o C VWP: 23.6 kpa Temp: -0.7 o C VWP: 10.1 kpa Temp: -0.4 o C VWP: -3.7 kpa Temp: 9.1 to -6.2 o C VWP: -29 to -40 kpa Temp: -0.8 o C VWP: 5.2 kpa Temp: -0.6 o C DSTF Cross-section A A’ 2013 2012 Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov. 2013 2012 Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov. Pressure head (kpa) -20 -10 0 10 20 30 40 50 -1.0 -0.8 -0.6 -0.4 -0.2 0.0 0.2 0.4 0.6 0.8 1.0 GP-1 Shallow (738.5 m amsl) GP-1 Deep (716.0 m amsl) GP-1 Thermistor GP-1 VWP -2 -1 0 1 2 3 4 5 Water height above sensor (m) GP-1 Temperature (o C) Compacted Tailings (typical) Non-mineralized Waste Rock (typical) GPA - Tailings 2012 Dry Stack Tailings Facility (DSTF) General Placement Area (GPA) - Waste Rock South Diversion Ditch North Diversion Ditch 1818000 E 1816000 E 1818000 E 3820000 N 3818000 N 3820000 N 800m 775m 750m 725m 675m 700m 775m 750m 800m 825m 850m 875m 925m 825m 850m 875m 900m 800m 825m 850m 875m 900m 850m A' A Old North Diversion Ditch (closed 2013) Old South Diversion Ditch (closed 2013) Flow Through Drain 18M Metric Tonne DSTF Extent Anchorage Fairbanks Pogo Mine Alaska Recycle Tailings Pond (RTP) Shell 3 Shell 2 Shell 1 2012 DSTF Extent New North Diversion Ditch for DSTF Expansion Pogo Mine is an underground gold mine operated by Sumitomo Metal Mining Pogo LLC (Pogo), located approximately 60 km northeast of Delta Junction, Alaska. The site is characterised by a continental climate with relatively low annual precipitation (~356 mm), relatively cool summers (mean of 10°C), and cold winters (mean of −13°C). Warm (>-2 °C) discontinuous permafrost is present beneath naturally vegetated terrain. DSTF History DSTF has been in operation since February 2006. Placement of approximately 5.3 M metric tonnes of tailings and waste rock through 2011 Original design capacity of approximately 6.8 M metric tonnes 2011 - DSTF material balance confirmed the need for expansion of the facility by 2013 2012 - Increase of the permitted DSTF storage capacity from 6.8 M tonnes to 18 M metric tonnes was approved 2012 - Update of DSTF closure study was initiated 2013 - Pogo completed expansion of the surface water diversion ditches and haul road Pogo Dry Stack Tailings Facility (DSTF) Ice lens Waste rock Unfrozen tailings Silt-size tailings were described in the field to be moist, with most intervals unfrozen (gravimetric moisture content from 13 to 22%) Sand and gravel waste rock were described in the field to be dry (gravimetric moisture content from 2 to 10%) Dry densities of tailings ranged from 1.68 to 1.97 g/cm 3 SPT blow counts corrected to (N 1 ) 60 in tailings averaged 13 for 10 samples (range from 2 to 21) Effective friction angles of tailings ranged from 34−35° Temperature Ground temperatures thermally equilibrated over a two- to three-month period following installation Shallow ground temperatures ranged from 9.1°C to −6.2°C in response to surface heating and cooling (VWP Sensor RR-1 Shallow) Deep ground temperatures below the depth of seasonal variation ranged from −0.4°C to −0.8°C Permafrost, as thermally defined, is present within the DSTF Pressure VWP recorded both positive and negative pore pressures Positive pore pressures recorded at the site may be caused by a phreatic water surface above the sensor Negative pressures may be caused by either soil matrix suction in unsaturated materials or cryosuction under freezing conditions SB-1 Deep sensor - maximum pressure of 41.7 kPa, equivalent to a water height of 4.3 m above the sensor New South Diversion Ditch for DSTF Expansion SB-1 Shallow (726.3 m amsl) SB-1 Deep (702.0 m amsl) 2013 2012 -20 -10 0 10 20 30 40 50 Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov. 2013 2012 Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov. Pressure head (kpa) -1.0 -0.8 -0.6 -0.4 -0.2 0.0 0.2 0.4 0.6 0.8 1.0 SB-1 Thermistor SB-1 VWP -2 -1 0 1 2 3 4 5 Water height above sensor (m) SB-1 4.3 m of water over sensor Temperature ( o C)

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Page 1: Investigating for Dry Stack Tailings Facility Closure ... · laboratory testing indicate that effective friction angles and dry densities of in situ DSTF materials are consistent

Investigating for Dry Stack Tailings Facility Closure: Multidisciplinary Evaluation at the Pogo Mine, Alaska

* [email protected], Ph. +1-907-273-3604

Dan Neuffer and Christopher Stevens, SRK Consulting (U.S.) Inc., USARussell Staines, SRK Consulting (Australasia) Pty Ltd., AustraliaMakoto Umedera and Sally McLeod, Sumitomo Metal Mining Pogo LLC, USA

*

Sumitomo Metal Mining Pogo LLC (Pogo) is the operator of the Pogo underground gold mine, located near Delta Junction, Alaska. The mine has been in operation since 2006 and produces between 380,000 and 400,000 ounces of gold annually. Filtered tailings from the flotation circuit and waste rock from the mine are placed in the dry stack tailings facility (DSTF). Expansion of the DSTF from 7 M tonnes to 18 M metric tonnes has prompted further evaluation of the facility for closure planning. This paper presents data from several components of a multidisciplinary DSTF closure study, including geotechnical and geochemical test results, in situ temperature and pore pressure measurements, and estimated freezing characteristics of tailings samples. Results of this study indicate the DSTF is physically stable and is comprised of materials that are non-potentially acid-generating; these findings support operational material placement practices and elements of the DSTF closure plan. Geotechnical field and laboratory testing indicate that effective friction angles and dry densities of in situ DSTF materials are consistent with previous slope stability analyses. Geotechnical borehole drilling, thermal monitoring, and analysis indicate the presence of permafrost within the DSTF. Pore pressure measurements and drilling observations indicate a phreatic surface near the base of the DSTF. This study narrows the focus of data collection for future closure planning and provides an example of physical and chemical conditions within a dry stack tailings facility in a continental, subarctic climate. These findings are pertinent for planning, design, permitting, operation, and closure of dry stacks in similar climates.

Acid-generating Potential

Subsurface Investigation

The authors thank the following: Megan Miller, for geotechnical logging of drill core and installation of VWP sensors; Ben Green, for supporting design of the VWP program; and Ivan Clark and Dan Mackie for their discussion of hydrologic processes. Alaska Department of Natural Resources and Alaska Department of Environmental Conservation have provided and continue to provide valuable feedback for the DSTF closure study. The authors also thank Sumitomo Metal Mining Pogo LLC for supporting this study.

Summary

0

10

20

30

40

50

60

0 10 20 30 40 50 60

NP

(kg

CaC

O3/t

)

AP (kg CaCO3/t)

GP-1, n=25RR-1, n=24SB-1, n=16TailingsNP/AP = 1NP/AP = 2NP/AP = 3

7.0

7.5

8.0

8.5

9.0

9.5

0 10 20 30 40 50

Rin

se p

H

Depth (m bgs)

• Geochemical characteristics of DSTF materials affect water quality associated with the facility

• Rinse pH values were in the range of pH 7 – 9

• Nearly all samples were classified as non-potentially acid-generating (non-PAG) based on neutralization potential (NP) to acidification potential (AP) ratios greater than three (NP/AP > 3)

• Subsurface investigation to evaluate DSTF geotechnical, thermal, hydrogeological, and geochemical characteristics

• Major components of the facility include the starter and toe berms, shells, general placement area (GPA), and flow-through drain

• Three sonic boreholes were vertically drilled at SB-1, GP-1, and RR-1 (total depth of 107 m)

• Sonic core, standard penetration testing (SPT), and Shelby tube samples were collected

• Four Shelby tube, 38 modified California and 49 geotechnical grab samples

• Laboratory testing included grain size, Atterberg limits, natural moisture and density, consolidated-undrained triaxial shear, flexible wall permeability, and consolidation

• Vibrating wire piezometers (VWP) were installed at SB-1, GP-1, and RR-1 to measure ground temperature and pore pressure

Dry Stack Tailings and Waste Rock

Dry

Moist

Key Findings and Implications for DSTF Closure

Tailings Freezing Characteristics

Freezing characteristics of tailings estimated from grain size distribution Atterberg limits, estimatedspecific surface area

• Phase state of water in the DSTF affects physical stability, surface water runoff characteristics, permeability, and geochemical reactivity of materials in the stack

• Estimated unfrozen water content curves for DSTF tailings indicate liquid pore water is present at subfreezing temperatures • The unfrozen water content at −1°C is estimated to range between 7 and 11% of the dry mass

• Presence of unfrozen tailings can be inferred from the relatively warm ground temperatures, the fine-grained nature of the tailings, observational evidence from the drill core, and the estimated freezing characteristics

Summary of Measured DSTF Ground Temperature

• Geotechnical investigation, thermal monitoring, and analyses indicate the presence of both frozen and liquid water within the DSTF

• Pore pressure measurements and drilling observations indicate a phreatic surface near the base of the DSTF and isolated, perched saturated zones within the dry stack

• Density and shear strength of DSTF materials indicate static and pseudostatic slope stability of the stack and stability against liquefaction

• Geochemical analyses of DSTF materials show that acidic drainage from the stack is unlikely

• DSTF ground temperatures confirm the presence of permafrost, as thermally defined by temperatures at or below 0°C • DSTF can be expected to thermally evolve as additional material is added and in relation to changes in local climate and microclimatic effects

• Monitoring of VWP and evaluation of surface water and groundwater from and adjacent to the DSTF may further constrain components of the DSTF water balance, including runoff, seepage, and flow-through drain flux.

• Evaluation of the long-term metals-leaching potential of DSTF materials through laboratory testing, comparison to operational monitoring data, and water quality modelling may inform selection and design of a closure cover system

Ground Temperature and Pore Pressure

Site Sensor description

Sensor depth 1

(m b.g.s.)

Elevation2 (m a.m.s.l.)

Temperature (°C)

Measurement date/period

SB-1 Shallow 7.6 726.3 −0.1 to −0.7 10/3/2012 to 10/22/2013

SB-1 Deep 31.9 702.0 −0.7 10/22/2013

GP-1 Shallow 19.2 738.5 −0.7 10/22/2013

GP-1 Deep 41.8 716.0 −0.4 10/22/2013

RR-1 Shallow 0.6 764.1 9.1 to −6.2 10/1/2012 to 10/22/2013

RR-1 Mid 18.6 746.2 −0.8 10/22/2013

RR-1 Deep 28.7 736.1 −0.6 10/22/2013

Free

zing

poi

nt d

epre

ssio

n

-10-8-6-4-200

5

10

15

20

25

30

Unf

roze

n w

ater

, % d

ry m

ass

108231085910804b

1081910849b1085310858

SSA - 21 m2 g-1

Temperature (oC)

Sample ID

Ice lens from 5.1 m b.g.s

Acknowledgements

SB-1 (14.3 to 15.8 m)

SB-1 (23.5 to 25 m)

This study contributes to further understanding of the geotechnical, thermal, hydrologic, and geochemical conditions of the Pogo Mine DSTF to support closure planning. Specifically, this study confirms specific aspects of the DSTF operational construction and closure plans while narrowing the focus of data collection for future closure planning.

20132012Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov.

20132012Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov.

Pres

sure

hea

d (k

pa)

Tem

pera

ture

(o C

)

-10

-8

-6

-4

-2

0

2

4

6

8

10

-60

-50

-40

-30

-20

-10

0

10

RR-1 Shallow (764.1 m amsl)

RR-1 Deep (736.1 amsl)

RR-1 Thermistor

RR-1 VWP

RR-1 Mid (746.2 m amsl)

Water height above sensor (m

)

-6

-5

-4

-3

-2

-1

0

1

RR-1

Sonic drill rig used for recovery of core and installation of VWP at boreholes SB-1, GP-1, and RR-1

1. Sensor depth is based on the depth below ground surface (b.g.s.) at the time of sensor installation (October 2012).2. Elevations are presented as metres above mean sea level (m a.m.s.l.).

Ele

vatio

n (m

)

Ele

vatio

n (m

)

Distance in Metres

LEGEND

Compacted Tailings

GPA Materials

Rock Shell

Flow-through Drain

Starter Berm and Toe Berm

Sand

Silt

Clay

Gravel

Cobble

Cobble & Gravel

Silt & Gravel

Gravel & Sand

Lithology Units:

Vibrating Wire Piezometer / Thermistor Location

Permeability

Inferred Water Height Above Sensor

Sample Testing Types:

Consolidation

Triaxial

Cross-section Units

NW SE

640

680

720

760

800

840

640

680

720

760

800

840

Flow-through drain

Composite Shell (Shell 2)

Composite Shell (Shell 3) Native Ground

Rockfill Shell (Shell 1)

GPA Materials

0+000 0+100 0+200 0+300 0+400 0+500 0+600 0+700 0+800 0+900 1+000 1+100

2012 DSTF Surface

SB-1GP-1 RR-1

18M Ton DSTF Surface

VWP: 8.7 kpaTemp: -0.1 to -0.7oC

VWP: 41.7 kpaTemp: -0.7oC

VWP: 23.6 kpaTemp: -0.7oC

VWP: 10.1 kpaTemp: -0.4oC

VWP: -3.7 kpaTemp: 9.1 to -6.2oC

VWP: -29 to -40 kpaTemp: -0.8oC

VWP: 5.2 kpaTemp: -0.6oC

DSTF Cross-sectionA A’

20132012Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov.

20132012

Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov.

Pres

sure

hea

d (k

pa)

-20

-10

0

10

20

30

40

50

-1.0

-0.8

-0.6

-0.4

-0.2

0.0

0.2

0.4

0.6

0.8

1.0GP-1 Shallow (738.5 m amsl)GP-1 Deep (716.0 m amsl)

GP-1 Thermistor

GP-1 VWP

-2

-1

0

1

2

3

4

5

Water height above sensor (m

)

GP-1

Tem

pera

ture

(o C

)

Compacted Tailings (typical)

Non-mineralized Waste Rock (typical)

GPA - Tailings

2012 Dry Stack Tailings Facility (DSTF)General Placement Area(GPA) - Waste Rock

South Diversion Ditch

North Diversion Ditch

1816

000

E

1818

000

E

1816

000

E

1818

000

E

3818000 N

3820000 N

3818000 N

3820000 N

800m

775m

750m

725m

675m

700m

775m

750m

800m

825m

850m 875m

925m

825m

850m

875m

900m

800m

825m

850m

875m

900m

925m

975m

950m

850m

A'

A

Old North Diversion Ditch (closed 2013)

Old South Diversion Ditch (closed 2013)

Flow ThroughDrain

18M Metric Tonne DSTF Extent

Anchorage

Fairbanks Pogo Mine

Alaska

Recycle Tailings Pond (RTP)

Shell 3

Shell 2

Shell 1

2012 DSTF Extent

New North Diversion Ditch for DSTF Expansion

Pogo Mine is an underground gold mine operated by Sumitomo Metal Mining Pogo LLC (Pogo), located approximately 60 km northeast of Delta Junction, Alaska.

The site is characterised by a continental climate with relatively low annual precipitation (~356 mm), relatively cool summers (mean of 10°C), and cold winters (mean of −13°C). Warm (>-2 °C) discontinuous permafrost is present beneath naturally vegetated terrain.

DSTF History

• DSTF has been in operation since February 2006. Placement of approximately 5.3 M metric tonnes of tailings and waste rock through 2011

• Original design capacity of approximately 6.8 M metric tonnes

• 2011 - DSTF material balance confirmed the need for expansion of the facility by 2013

• 2012 - Increase of the permitted DSTF storage capacity from 6.8 M tonnes to 18 M metric tonnes was approved

• 2012 - Update of DSTF closure study was initiated

• 2013 - Pogo completed expansion of the surface water diversion ditches and haul road

Pogo Dry Stack Tailings Facility (DSTF)

Ice lens Waste rock Unfrozen tailings

• Silt-size tailings were described in the field to be moist, with most intervals unfrozen (gravimetric moisture content from 13 to 22%)

• Sand and gravel waste rock were described in the field to be dry (gravimetric moisture content from 2 to 10%)

• Dry densities of tailings ranged from 1.68 to 1.97 g/cm3

• SPT blow counts corrected to (N1)60 in tailings averaged 13 for 10 samples (range from 2 to 21)

• Effective friction angles of tailings ranged from 34−35°

Temperature

• Ground temperatures thermally equilibrated over a two- to three-month period following installation

• Shallow ground temperatures ranged from 9.1°C to −6.2°C in response to surface heating and cooling (VWP Sensor RR-1 Shallow)

• Deep ground temperatures below the depth of seasonal variation ranged from −0.4°C to −0.8°C

• Permafrost, as thermally defined, is present within the DSTF

Pressure

• VWP recorded both positive and negative pore pressures

• Positive pore pressures recorded at the site may be caused by a phreatic water surface above the sensor

• Negative pressures may be caused by either soil matrix suction in unsaturated materials or cryosuction under freezing conditions

• SB-1 Deep sensor - maximum pressure of 41.7 kPa, equivalent to a water height of 4.3 m above the sensor

New South Diversion Ditch for DSTF Expansion

SB-1 Shallow (726.3 m amsl)

SB-1 Deep (702.0 m amsl)

20132012

-20

-10

0

10

20

30

40

50

Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov.

20132012Oct. Nov. Dec. Jan. Feb. Mar. Apr. May June July Aug. Sep. Oct. Nov.

Pres

sure

hea

d (k

pa)

-1.0

-0.8

-0.6

-0.4

-0.2

0.0

0.2

0.4

0.6

0.8

1.0SB-1 Thermistor

SB-1 VWP

-2

-1

0

1

2

3

4

5

Water height above sensor (m

)

SB-1

4.3 m of water over sensor

Tem

pera

ture

(o C

)