Corporate Presentation
Transcription
Corporate Presentation
technology diversity We deliver energy 2011 Confidential Performance Presentation Whitesands Pilot Project February 22, 2010 TSX : PBG Table of Contents Introduction Surface Facilities Measurement and Reporting Water and Waste Disposal H2S and Sulphur Recovery Drilling and Completions Environmental Monitoring Compliance Subsurface issues Introduction Geology 4‐D Seismic Scheme Performance Observations and Conclusions Future Plans TSX : PBG 2 Conklin Pilot Area‐ Oil sands asset base 62 sections of oil sands leases (46,240 acres ‐ 100%) 3P reserves of 77.7 mmbbls & contingent recoverable resource of up to 737.1 mmbbls (NPV 8% ‐ $3.6 billion) TSX : PBG 3 Conklin THAI® Pilot Project Production Pad & Facility P1B (THAI™) P2B (THAI™) P3B (CAPRI™) Injection Pad Injection Pad TSX : PBG 4 Whitesands THAI® Integrated injection & production facilities Air Toe Combustion Zone Mobile Oil Coke Zone Zone Cold Bitumen Heel TSX : PBG 5 THAI® technology benefits Current operations demonstrate key THAI® benefits Minimal natural gas and water use Higher recovery rates: 70‐80% of oil in place Improved economics The 70‐80% recovery factor comes from lab work and numerical modeling. Approximately 9% of the hydrocarbon (the heavy ends) is used to make coke which is ultimately the fuel for the combustion process. Combustion gases (see Slide 106), upgraded oil and water are produced. The rest of the hydrocarbon is left behind. Lower capital cost: 1 horizontal well, no steam or water handling facilities Lower operating cost: negligible natural gas & minimal water handling Higher netbacks for partially upgraded product Faster project execution time Able to generate power from produced gas Lower environmental impact 50% less greenhouse gas emissions Partially upgraded oil requires less refining CO2 capture‐ready Net useable water production Smaller surface footprint TSX : PBG 6 THAI® oil initial upgrading Native bitumen 8o API, 550,000 centipoise Consistent THAI® upgrading since start up Confirmed CAPRITM catalyst upgrading Recent P3B “CAPRITM oil” quality is up to 15º API In‐situ upgraded THAI® oil 12o API, 1,225 centipoise Produced THAI® condensate 36 O API TSX : PBG 7 Oil and water samples from the plant Sales Oil Condensate Sales Oil + Produced Water Produced Water Treater Oil TSX : PBG 8 Whitesands Project Operational status The wells have demonstrated the feasibility of THAI® (Toe‐to‐Heal Air Injection) and of the CAPRI™ catalyst enhancement Key expectations of the THAI® and CAPRI™ processes have been demonstrated Initiating communication of P1B continues to be challenging due to wellbore placement in the reservoir Abandoning P2B due to inability to replace instrumentation string Assessing options for Conklin pilot as a test facility for further technology enhancements TSX : PBG 9 Plot Plan TSX : PBG 10 Process Flow Diagram Start and End of 2010 TSX : PBG 11 Key Facilities Additions 2010 Sand knock‐out vessel modifications for V‐170 (P3‐B) Completed construction and commissioning of new incinerator (IS‐380) TSX : PBG 12 Water Withdrawal and Treatment Our process only requires treatment of fresh water that is softened through a conventional sodium zeolite system This boiler feed water (BFW) is only required if the wells are being steamed No other water treatment is required No brackish water is used No withdrawal from natural bodies of fresh water Source water well: 10‐12‐77‐09 W4 Water from source well is used for steam generation and utility water Source water is drawn from the Empress Channel Aquifer which occurs at the base of the buried Christina Channel The Empress Channel Aquifer occurs from 160.9 – 186.5 mbgs (meters below ground surface)* *Reference: Westwater Environmental Ltd., Annual Water Use Report – Whitesands Pilot Project. February 2011. TSX : PBG 13 Water Balance Total raw water flow is measured by a turbine meter with totalizer. The accuracy of the meter is +/‐ 0.5 % of rate. The meter is changed out annually with a new meter or a recalibrated meter. BFW flow is measured by a Vortex meter Injected steam is measured at each production well using a Vortex meter All with electronic verifications completed annually, and physical inspections pending shutdowns. The accuracy of the meters is +/‐ 1.35 % of rate. Utility water is estimated as ~2 m3/day 10‐12‐77‐09 W4M Jan‐10 Feb‐10 Mar‐10 Apr‐10 May‐10 Jun‐10 Jul‐10 Aug‐10 Sep‐10 Oct‐10 Nov‐10 Dec‐10 Total 4218.8 4217.5 4426 4882 4658.5 3435.3 174.3 2070 4347.4 3705 1574.1 3872.4 41581.1 TSX : PBG 14 Steam Generation and Power Consumption Steam is injected during the initial well start‐up and may be used periodically for assisting production in the wells Steam is generated onsite utilizing a 25 MMBTU/HR OTSG Steam Injection (m3) 1AW ‐ 15‐12‐077‐09 W4M 1 AV ‐ 15‐12‐077‐09 W4M 1 AX ‐ 15‐12‐077‐09 W4M Total Jan‐10 2017.2 1376.7 402.2 3796.1 Feb‐10 Mar‐10 Apr‐10 May‐10 Jun‐10 Jul‐10 Aug‐10 Sep‐10 Oct‐10 Nov‐10 Dec‐10 Total 1858.5 2425.3 2104.7 1773.3 1153.2 0.7 236.8 988.4 880.0 589.5 441.1 14468.7 1304.5 534.4 1413.9 1324.4 680.5 0.5 719.9 1271.4 634.9 0.0 0.0 9261.1 830.4 640.0 55.6 0.0 53.2 18.0 0.0 5.5 7.2 0.0 0.0 2012.1 3993.4 3599.7 3574.2 3097.7 1886.9 19.2 956.7 2265.3 1522.1 589.5 441.1 25741.9 Power usage based on bills from Valeo Power Corporation Power Usage ‐ MWh Jan‐10 Feb‐10 Mar‐10 Apr‐10 May‐10 Jun‐10 Jul‐10 Aug‐10 Sep‐10 Oct‐10 Nov‐10 Dec‐10 Total 2029.3 1641 1587.7 1303 1432.2 1803.6 2160 2300.1 1722.1 1457 830.5 1188 19454.6 TSX : PBG 15 Gas Production And Disposition All volumes in e3m3 Gas Imported Total Gas Production Gas Vented Gas Flared Jan‐10 766.7 4484.8 1356.6 3128.2 Feb‐10 799.5 1965.6 96.091 1869.509 Mar‐10 654.5 568.5 0 568.5 Apr‐10 694.1 1061 0 1061 May‐10 458.2 1371 0 1371 Jun‐10 465.4 2960.1 0 2960.1 Jul‐10 292.5 3858.6 0 3858.6 Aug‐10 334.1 3172.7 0 3172.7 Sep‐10 647.8 1107 0 1107 Oct‐10 546.8 863.4 0 863.4 Nov‐10 374.4 649.4 0 649.4 Dec‐10 464.6 520.3 0 520.3 Total 6498.6 22582.4 1452.691 21129.709 TSX : PBG 16 Greenhouse Gases CO2 Emissions (t) Based on complete combustion of all gases Produced Gas Fuel Gas Jan‐10 2416.7 1490.4 Feb‐10 1032.9 1554.2 Mar‐10 293.3 1272.3 Apr‐10 571.2 1349.3 May‐10 719.3 890.7 Jun‐10 1541.3 904.7 Jul‐10 2051.3 568.6 Aug‐10 1727.4 649.5 Sep‐10 598.5 1259.3 Oct‐10 460.0 1062.9 Nov‐10 360.3 727.8 Dec‐10 290.0 903.1 Total 3907.1 2587.1 1565.5 1920.5 1610.0 2445.9 2619.9 2376.8 1857.7 1522.9 1088.1 1193.1 TSX : PBG 17 Reporting Methodology to Petroleum Registry Each well has its own desand, separation and metering Produced oil for each well is prorated based on the individual well meters and oil cuts and reconciled against sales and tank inventory changes Produced water for each well is prorated based on the individual well meters and water cuts and reconciled against the disposal meter, water shipments to disposal facilities, and tank inventory changes Produced gas is metered individually per well train and reconciled against the total gas metered and measured through incineration / flaring. Injected steam is metered on a per well basis, total steam is measured via BFW consumption and results are reconciled with the disposal volumes from the blowdown tank and utility water usage. Injected air is metered on a per well basis MARP Discussions / Revisions TSX : PBG 18 Air injection wells A1/A3 are measured by differential pressure transmitter calibrated annually A2 is measured by a vortex meter that has had an electronic verification done annually. TSX : PBG 19 Well Flow Measurement Produced liquid measurement is taken at the outlet of the desand separator vessels through mass flow meters. The accuracy of these meters is +/‐ 0.2 % of rate. Produced gas measurement is done by vortex meters after cooling and secondary separation of condensed liquids. These meters are scheduled to be proven beginning of second quarter every year. This calibration was done in April 2010 and will be completed next in April 2011. TSX : PBG 20 Proration Factors Proration factors are based on the volumes measured in the plant versus the volumes as reconciled with inventory and shipments Proration Factors Oil Water Jan‐10 0.67 0.18 Feb‐10 0.64 0.30 Mar‐10 0.74 0.23 Apr‐10 1.00 0.43 May‐10 1.42 0.26 Jun‐10 0.91 0.44 Jul‐10 0.68 2.76 Aug‐10 2.18 1.00 Sep‐10 0.84 0.65 Oct‐10 1.03 1.04 Nov‐10 0.63 0.90 Dec‐10 0.88 1.32 2010 Average 0.97 0.79 TSX : PBG 21 Water Disposal Wells Two disposal wells: 00/08‐12‐77‐09 W4 (UWI 100081207709W400) (McMurray formation) 00/15‐12‐77‐09 W4 (UWI 100151207709W400) (McMurray formation) Produced water volumes are metered by orifice meters at the facility. Turbine meters were installed at both wellheads late in 2010. Boiler blowdown water is metered by truck gauge Disposal injection pressure at pump discharge is monitored on DCS Disposal injection pressure readings at the wellheads were not recorded in 2010 Disposal Pressure and Rates: 3000‐3500kPa at 150‐250 m³/d Disposal Volumes (m3) 8‐12‐77‐09 W4M 15‐12‐77‐09 W4M Injection Pressure Temperature (°C) Jan‐10 Feb‐10 Mar‐10 Apr‐10 May‐10 Jun‐10 Jul‐10 Aug‐10 Sep‐10 Oct‐10 Nov‐10 Dec‐10 Total 4194.4 4453.5 3530.6 4205 6004.5 5353.7 1351 2833.7 3589.8 2622 1006.2 0.8 39144.9 158.3 1723.3 1881.6 3178.2 3080.4 3101.8 3103 3270 3285.5 1893 3307.2 3079.9 3143.6 2808.3 2911.9 80 80 80 80 80 80 80 80 80 80 80 80 TSX : PBG 23 Water Disposal Pressures and Flows TSX : PBG 24 Offsite Waste Management Solid waste is disposed at CCS Janvier landfill (S1/2‐03‐81‐06 W4), volume is recorded on an ERCB Waste Manifest. Produced and blowdown water is trucked off‐site when we do not have disposal capacity. Locations of offsite disposal are: Facility Code AB CT 0000457/557 AB WP 0000671 AB WP 0000677 AB CT 0000458 AB WP 0000556 Company CCS Newalta Cancen CNRL Beartrap Palko Environmental Volume 4383.1 255.0 1047.8 0.4 2772.2 TSX : PBG 25 Quarterly Sulphur Emissions We manage our produced gas via well production to ensure we do not exceed 1.0 tonne per day of sulphur emissions A monthly sulphur balance is not included as we combust all of our produced gas so our sulphur inlet is equal to our sulphur outlet. The exception is January and the first few days of February of last year which are shown in the Q1 balance below. SO2 Emissions (t) Jan‐10 29.77 Feb‐10 12 Mar‐10 8.21 Apr‐10 16.61 May‐10 12.93 Jun‐10 Jul‐10 Aug‐10 Sep‐10 Oct‐10 Nov‐10 Dec‐10 Total 19.45 24.43 17.75 5.16 3.45 0.889 1.14 151.789 Sulphur Balance (t) S Removed by Total Quarter S Emissions SO2 Emissions Sweetener Sulphur Q1 24.99 49.98 7.30 32.29 Q2 24.50 48.99 24.50 Q3 23.67 47.34 23.67 Q4 2.74 5.48 2.74 TSX : PBG 26 2010 Chronology of events at the Whitesands Pilot P1B showing response and THAI® quality oil (up to 10o API oil) in late‐June to mid‐August and continually produced combustion gas that is associated with THAI® combustion P2B established communication with the combustion zone and later encountered instrument string failure P3B required to shut‐in for a minor casing vent flow and the remedial work is in progress Experimented with elevated air rates from July‐August to establish communication (maintain high air on A1 up to today) P2B and P3B down from October‐December TSX : PBG 27 Drilling and Completions 2010 OSE Drilling Program TSX : PBG 28 Drilling, Completions and Workover Update Producer Wells P1B (1AW/16‐12‐77‐9W4/00): no workovers P2B (1AX/16‐12‐77‐9W4/00): 4 workovers Two cleanouts Workover to inspect long string integrity Workover to replace coil tubing instrument string resulted in parted tubing and decision to abandon the well P3B (CAPRI™ liner) (1AV/16‐12‐77‐9W4/00) Three Cleanouts Remediating low‐flow surface casing vent flow (SCVF) TSX : PBG 29 Cleanout Details Cleanouts are done with coil tubing and nitrogen A P‐tank is used to collect the liquids, solids and gases Sources of plugged liner includes solids and bitumen Production tubing also suffers from bitumen plugs Cleanouts are complete when production is restored Range in duration from a few hours to several days TSX : PBG 30 P3B Surface Casing Vent Flow •Total volume released <100m3 •Composition consistent with combustion gas •Leak source is likely through ST&C casing connections •SCVF ceased when well was killed and has not resumed •Will remediate by cementing in a new full length slimhole casing string with premium connections TSX : PBG 31 P1‐B (With FacsRITE) TSX : PBG 32 P2‐B (With FacsRITE) TSX : PBG 33 P3‐B (With CAPRITM) TSX : PBG 34 FacsRiteTM Liner Design • Stronger liner integrity • Improved sand control with screens • Greater flow area (4 to 10%) • 2 wells at Whitesands (P1B & P2B) TSX : PBG 35 CAPRITM Liner (P3B) TSX : PBG 36 Drilling, Completions and Workover Update Air Injectors & Disposal Wells P1 (1AH/16‐12‐77‐9W4/00) Pumped viscous oil to stop cross‐flow to P1B A3 (1AQ) at 16‐12‐77‐9W4 Recompleted with packerless completion Monthly fluid shots have always shown annulus is completely purged Water Disposal Well (100/15‐12‐077‐09W4/03) Unsuccessful attempt to run a tracer log Granted temporary operation until April 30, 2011 Water Disposal Well (100/08‐12‐077‐09W4/00) During packer replacement, packer would not unset and parted tubing while trying to shear packer Washover mill wedged on fish top and exited casing Applying for abandonment TSX : PBG 37 A3 Injector Packer Removed Annulus Purged with N2 Monthly fluid shots confirm successfully purged casing annulus TSX : PBG 38 15‐12 Disposal Well 100/15-12-077-09W4/00 ERCB approved a packer setting depth between 350.0 – 355.0 (October 2009) Packer relocated to top of McMurray B because of casing distortion After workover to run tracer log, packer re-set at 355.36 mKB with same completion configuration TSX : PBG 39 100/15‐12 Disposal Well Video shows why tracer log tools could not enter the zone of interest TSX : PBG 40 Artificial Lift All producer wells rely on gas lift from combustion gas to provide lift to surface Water flashing to steam also helps to generate lift Steam circulation is sometimes required to initiate inflow of combustion gas TSX : PBG 41 Well Instrumentation 18 thermocouples (TC’s) per observation well (OB and TOB wells) cemented in place. From Clearwater shale to base of McMurray Approximately every 2.5 m through the McMurray TC’s along the length of the horizontal sections of the production wells, approximately 25 m spacing 20 TC’s in P1B 10 TC’s in P2B 18 TC’s in P3B Pressure observation well (POB well) with piezometer pressure sensors in Wabiskaw and in Clearwater TSX : PBG 42 Pressure Observation Well (POB) TSX : PBG 43 Environmental Monitoring Air Quality Passive and produced gas analysis of H2S and SO2 Run off Containment Ponds Regular monitoring, testing and pump off Groundwater monitoring 18 shallow groundwater monitoring wells (early detection of subsurface contamination) 2 source water wells Interim Reclamation Erosion, sedimentation and dust control; revegetation Full operational environmental compliance achieved in 2010 TSX : PBG 44 Sampling Points Passive monitors (4) Source Wells (2) Groundwater wells (18) TSX : PBG 45 Environment Ambient Air Quality Results 2010 Reporting Month H2S Max (ppb) AAOQO = 3 SO2 Max (ppb) AAOQO =23 January 0.66 2.5 February 0.66 2.4 March 0.46 1.6 April 0.97 1.1 May 0.73 0.7 June 0.82 0.9 July 2.36 0.9 August 0.84 1.0 September 0.31 0.8 October 0.31 1.0 November 0.38 1.3 December 0.68 1.8 All 2010 monitoring results are below the AAAQO TSX : PBG 46 Environmental Monitoring Regional Initiatives Lower Athabasca Regional Plan (LARP) NOx /SOx emission thresholds Groundwater project Regional monitoring programs (IMERF) Southern Athabasca Oil Sands Producers (SAOP) Regional wildlife project Insitu Oil Sands Association (IOSA) Regulatory reform discussions with AENV TSX : PBG 47 2010 Regulatory Compliance Summary ERCB Self disclosure - Cased hole blowout/master valve failure (Apr) ERCB Application Audit (Aug) Site inspections (Jul, Sept) Low Risk Non Compliance – Operational Inspection (Oct) AENV No compliance issues ASRD 1 winter drilling inspection (construction and creek crossings) 1 seismic field inspection (construction and creek crossings) 1 OSE aerial reclamation inspection ABSA No compliance issues TSX : PBG 48 Non‐Compliance Issues Cased hole blowout/Master valve failure ERCB received a self disclosure about a surface casing vent flow and requested additional information by May 10, 2010 Petrobank provided all requested information to the ERCB preliminary investigation identified human error as the cause of the incident physical evidence indicates that the valve was partially closed during operation, causing it to fail operating procedures had been amended and the procedures reviewed with all applicable personnel Well Licensing The new OB wells are currently licensed incorrectly, we are in the process of addressing this non‐compliance Detailed Operational Inspection The requirements outlined by the ERCB were successfully addressed TSX : PBG 49 Original Bitumen In Place (OBIP) THAITM pilot area 30 m 0 45 0 m Drainage Area Length Width (m) (m) 450 300 Area (m2) 135,000 Average Net Rock Pay Volume Thickness (m3) (m) 11.5 1,552,500 Porosity (%) Pore Volume (m3) Average Bitumen Saturation (%) Bitumen Volume In Place (m3) 34 527,850 80 422,280 Bitumen Volume In Place (mmbbl) 2.7 OBIP = Area * pay thickness * porosity * bitumen saturation TSX : PBG 50 McMurray net Basal bitumen pay isopach Contour Interval = 1m TSX : PBG 51 Structure of Basal bitumen pay top Contour Interval = 1m TSX : PBG 52 Structure of bitumen pay base Contour Interval = 1m TSX : PBG 53 Whitesands type log Clearwater Shale Wabiskaw Marker Approximate 20m of shale as the cap rock Wabiskaw C McMurray A McMurray A Shale McMurray B IHS top Basal Sand top Main target bitumen zone Oil/WaterContact McMurray C Paleozoic TSX : PBG 54 Whitesands Pilot: Well layout and cored wells Section 12 T77 R9 W4 Cored Cored Cored Cored Cored Legend Observation well Air injection well Cored Production well Exploration well TSX : PBG 55 Log‐core correlation Top OB1 Well Core Gamma Gamma Resistivity Wabiskaw C McMurray A2 Sequence C Shale McMurray B Channel IHS McMurray C Shale Paleozoic Mudstone Clast Breccia Basal B Sand B Silty Mudstone A Shale A Sand Paleozoic Limestone Bottom TSX : PBG 56 Petrographic analysis TSX : PBG 57 Petrographic analysis 383.46m Sample taken from 383.46m – 383.75m 3C 3E Q Z Clay 383.75m 3B 3D Burrows and bioturbation enhance the porosity and permeability in the IHS interval and make IHS exploitable with THAI®. TSX : PBG 58 Structural cross‐section along P1B well HEEL TOE TSX : PBG 59 P1B trajectory OB1 OB2 OB3 P1B A Sand IHS Basal Sand TSX : PBG 60 Structural cross‐section along P2B well HEEL TOE TSX : PBG 61 P2B trajectory OB4 P2B OB5 OB6 A Sand IHS Basal Sand TSX : PBG 62 Structural cross‐section along P3B well HEEL TOE TSX : PBG 63 P3B trajectory OB7 OB8 OB9 A Sand P3B IHS Basal Sand TSX : PBG 64 Geomechanical analysis = Has sonic log = Has density log 8-12-77-9-W4 Water Injection TSX : PBG 65 Geomechanical data analysis Where: z = vertical depth g = acceleration due to gravity ρ = density TSX : PBG 67 Geomechanical data analysis TSX : PBG 68 Geomechanical data analysis: density profiles TSX : PBG 69 Regional overburden analysis TSX : PBG 70 Greater May River area seismic McMurray channel continuous net bitumen (contours) existing 3Ds and 4Ds in green and orange 2010 3D merged seismic (2003, 2005, 2010 shoots) High‐Res 4D‐3C seismic 2003, 2008, 2009, 2010, 2011 TSX : PBG 71 time (ms) Paleozoic regional time structure = Well with compressional sonic = Well with shear sonic = 2011 OSE wells TSX : PBG 72 Seismic cross section through merged 3D Clearwater Wabiskaw Paleozoic TSX : PBG 73 What is time lapse seismic? Repeat seismic over time – like timelapse photography…. Monitors – 5X5m bins Baseline Interpolated to 5X5m bins Baseline – 15X20m bins ….then difference the Monitor Surveys from the Baseline TSX : PBG 74 Seismic velocities Temperature dependent Han et al., 2007 TSX : PBG 75 03‐10 Time lapse OB9 A3 A2 OB6 OB8 A1 OB5 OB3 TSX : PBG 76 Well instrumentation 18 thermocouples (TC’s) per observation well (OB and TOB wells) cemented in place. From Clearwater shale to base of McMurray Approximately every 2.5 m through the McMurray TC’s along the length of the horizontal sections of the production wells, approximately 25 m spacing 20 TC’s in P1B 10 TC’s in P2B 18 TC’s in P3B POB well with pressure sensor in Wabiskaw and in Clearwater TSX : PBG 77 Observation well map TSX : PBG 78 TOB1 temperature profile TSX : PBG 79 TOB1 temperature profile (2010) TSX : PBG 80 TOB2 temperature profile TSX : PBG 81 TOB2 temperature profile (2010) TSX : PBG 82 OB3 temperature profile TSX : PBG 83 OB3 temperature profile (2010) TSX : PBG 84 OB6 temperature profile TSX : PBG 85 OB6 temperature profile (2010) TSX : PBG 86 OB7 temperature profile TSX : PBG 87 OB7 temperature profile (2010) TSX : PBG 88 OB9 temperature profile TSX : PBG 89 OB9 temperature profile (2010) TSX : PBG 90 Air injection timelines Steam Injection (PIHC) Air Injection A2 air injector timeline October 2010 June 2006 March 2006 Steam Injection (PIHC) A3 air injector timeline December 2010 April 2007 November 2006 Steam Injection (PIHC) Air Injection Air Injection October 2010 January 2007 September 2006 A1 air injector timeline A2 and A3 shut down air for well operations in October TSX : PBG 91 McMurray A sand heating TSX : PBG 92 McMurray A gas production TSX : PBG 93 McMurray A sand isopach TSX : PBG 94 McMurray A sand temperature discussion This temporary heating of the McMurray A sand during start‐up at TOB1/2 and was due to the high injection pressures for steam injection. The steam injection pressure likely fractured the McMurray A2 shale and provided a communication conduit for steam heat at first and then hot combustion gas from the advancing front after the PIHC. From the profile at TOB1 and TOB2 this communication was decreasing dramatically before the thermocouples were lost in August of 2008. There is no evidence that these thermocouples failed due to excessively high temperatures. The following reasons could be the cause of the thermocouple failure: Surface lead issues – Rain, snow, and hot/cold thermal cycling. This also extends to any surface cable that may have been moved or cycled. Corrosion – if the metal sheath corrodes moisture gets in and shorts the thermocouple. This is the second most common problem after the surface problems Strain – in places where the thermocouple is spliced together, you can pull apart the splice. This often happens during installation but can also occur downhole. In addition, the heating of the McMurray A appears to be an extremely localized effect as OB6, which is only 42 meters away, shows very little heating in the time period of this apparent communication. OB3 more than likely had a similar scenario with steam heat being transferred during the PIHC at A1. There is no evidence that combustion gas, due to the time of the temperature increase, affected the McMurray A sand temperature at OB3. The OB3 profile shows that the McMurray A sand is now at native temp and has been for some time. In all of these profiles there is no evidence of a negative impact of the resource in the McMurray A sand. TSX : PBG 95 P1 temperature profile TSX : PBG 96 P1 temperature profile (2010) TSX : PBG 97 P1B temperature profile TSX : PBG 98 P2 temperature profile TSX : PBG 99 P2 temperature profile (2010) TSX : PBG 100 P2B temperature profile Thermocouple string down and pulled October 2010‐present TSX : PBG 101 P3B temperature profile Thermocouple string down and pulled October 2010‐present TSX : PBG 102 P3B temperature profile (2010) Thermocouple string down and pulled October 2010‐present TSX : PBG 103 POB1 pressure profile Clearwater Shale CAPROCK Wabiskaw Marker Wabiskaw C sand piezometer Wabiskaw C Sand top Clearwater sand piezometer Piezometers in Wabiskaw C sand and Clearwater Sandstone (above cap rock) TSX : PBG 104 Air injection wellhead pressures TSX : PBG 105 Combustion Gas Analyses TSX : PBG 106 H2 O2 CO Mar 2011 Jan2011 Nov 2010 Sep2010 Jul 2010 May 2010 Mar 2010 Jan2010 Nov 2009 Sep2009 Jul 2009 May 2009 Mar 2009 Jan2009 Nov 2008 Sep2008 Jul 2008 May 2008 Mar 2008 Jan2008 Nov 2007 Sep2007 Jul 2007 May 2007 Mar 2007 Jan2007 Nov 2006 Sep2006 20 20 18 18 16 16 14 14 12 12 10 10 8 8 6 6 4 4 2 2 0 0 TSX : PBG MOLE % Jul 2006 MOLE P1/P1B Well Combustion Gas Analyses P1 / P1B GAS DATE CO2 107 H2 O2 CO Mar 2011 Jan2011 Nov 2010 Sep2010 Jul 2010 May 2010 Mar 2010 Jan2010 Nov 2009 Sep2009 Jul 2009 May 2009 Mar 2009 Jan2009 Nov 2008 Sep2008 Jul 2008 May 2008 Mar 2008 Jan2008 Nov 2007 Sep2007 Jul 2007 May 2007 Mar 2007 Jan2007 Nov 2006 Sep2006 20 20 18 18 16 16 14 14 12 12 10 10 8 8 6 6 4 4 2 2 0 0 TSX : PBG MOLE % Jul 2006 MOLE P2/P2B Well Combustion Gas Analyses P2 / P2B GAS DATE CO2 108 H2 O2 CO Mar 2011 Jan2011 Nov 2010 Sep2010 Jul 2010 May 2010 Mar 2010 Jan2010 Nov 2009 Sep2009 Jul 2009 May 2009 8 Mar 2009 Jan2009 Nov 2008 Sep2008 Jul 2008 May 2008 Mar 2008 Jan2008 Nov 2007 Sep2007 Jul 2007 May 2007 Mar 2007 Jan2007 Nov 2006 Sep2006 20 20 18 18 16 16 14 14 12 12 10 10 P3BStart-up 6 6 4 4 2 2 0 0 TSX : PBG MOLE % Jul 2006 MOLE P3/P3B Well Combustion Gas Analyses P3 / P3B GAS 8 DATE CO2 109 THAI® Oil Partial Upgrading Bitumen Viscosity at 20 ºC, cP Oil sulphur content, wt % API Gravity “SARA ” ANALYSIS Volatile organics, 40 ºC, mass % Saturates Aromatics Resins Asphaltenes Source: Partially Upgraded Production 550,000 3.2 7.9 1225 2.6 12.3 21.1 12.7 30.3 19.0 16.9 25.5 23.5 22.6 17.2 11.2 Whitesands Bitumen & P1 Upgraded Oil Archon Technologies Ltd. Oil Analysis 2007 (Archon, a wholly owned technology subsidiary of Petrobank) TSX : PBG 110 Water Quality Whitesands Produced Water Whitesands Condensed Water Calculated Parameters Units Total Dissolved Solids mg/L pH 11,000 8.3 50 8.2 Anions Bicarbonate (HCO3) mg/L mg/L Carbonate (CO3) Dissolved Sulphate (SO4) mg/L Dissolved Chloride (Cl) mg/L 1610 <0.5 <0.5 5800 1600 N/D N/D 45 Elements Dissolved Sodium (Na) mg/L Dissolved Potassium (K) mg/L Dissolved Calcium (Ca) mg/L Dissolved Magnesium (Mg) mg/L 3800 17 55 30 10 0.5 0.4 0.1 TSX : PBG 111 A1‐P1 Well Pair Production & Injection History TSX : PBG 112 A1‐P1 Well Pair Liquids Production & Injection History TSX : PBG 113 A1‐P1 Well Pair Cumulative Oil Production & Air‐Oil Ratio TSX : PBG 114 A2‐P2 Well Pair Production & Injection History TSX : PBG 115 A2‐P2 Well Pair Liquids Production & Injection History TSX : PBG 116 A2‐P2 Well Pair Cumulative Oil Production & Air‐Oil Ratio TSX : PBG 117 A3‐P3 Well Pair Production & Injection History TSX : PBG 118 A3‐P3 Well Pair Liquids Production & Injection History TSX : PBG 119 A3‐P3 Well Pair Cumulative Oil Production & Air‐Oil Ratio TSX : PBG 120 A1‐P1B Well Pair Production & Injection History TSX : PBG 121 A1‐P1B Well Pair Liquids Production & Injection History TSX : PBG 122 A1‐P1B Well Pair Cumulative Oil Production & Air‐Oil Ratio TSX : PBG 123 A2‐P2B Well Pair Production & Injection History TSX : PBG 124 A2‐P2B Well Pair Liquids Production & Injection History TSX : PBG 125 A2‐P2B Well Pair Cumulative Oil Production & Air‐Oil Ratio TSX : PBG 126 A3‐P3B Well Pair Production & Injection History TSX : PBG 127 A3‐P3B Well Pair Liquids Production & Injection History TSX : PBG 128 A3‐P3B Well Pair Cumulative Oil Production & Air‐Oil Ratio TSX : PBG 129 Field Oil Production & Steam – Air Injection History TSX : PBG 130 Field Gas Production & Injection History TSX : PBG 131 Field Liquids Production & Injection History TSX : PBG 132 Field Oil Production & Air‐Oil Ratio (AOR) trends TSX : PBG 133 Field Cumulative Oil Production and Air‐Oil Ratio TSX : PBG 134 Well On‐Stream Factor: P1, P2 & P3 TSX : PBG 135 Well On‐Stream Factor: P1B, P2B & P3B TSX : PBG 136 Observations & Conclusions Fluid Quality Summary Oil Consistent API upgrade and viscosity reduction Significant increase in volatiles and saturates Notable reduction of resins and asphaltenes Increased carry over of lighter ends to the secondary separators as surface temperatures increase Early production from new wells does not show significant upgrading Overall a higher quality produced oil than SAGD Gas No issues with O2 in produced gas Free H2 production up to 8% Up to 9% of hydrocarbons (C1–C5) in the produced gas with a heating value 85‐120 Btu/scf, suitable for use in Low‐Btu steam generators CO2 and CO levels and ratios consistent with high temperature combustion H2S levels are stable in produced gas, off‐set by reduction of sulphur in produced oil TSX : PBG 137 Observations and Conclusions Successfully ran the CAPRITM well at temperatures between 350 to 450oC at the toe for catalytic cracking Bitumen upgrading was increased by an additional 3oAPI with CAPRITM Reservoir thickness and quality are the major contributors, along with low plant on‐stream times early on in the project, to the difference in approval capacity and actual production Wellbore trajectory also has a large impact on well performance and establishment of injector communication On stream factors are still problematic (cumulative on‐stream for all three wells is 55%) TSX : PBG 138 Key Learnings to date Conklin Pilot Reservoir quality constrains the initial production rates THAI® is the only known process that can produce in this quality of reservoir Wellbore placement toward bottom of the reservoir is optimal On stream factor of facilities is critical to advance production TSX : PBG 139 Future Plans Conklin plant will be used as a field testing site for: Enriched oxygen injection Sulphur removal (catalytic and chemical) Multi‐THAI® well configuration The following activities are proposed for 2011 Abandonment 8‐12 water disposal well Redrill water disposal well on the 15‐12 pad Evaluate existing 15‐12 disposal well Abandon P2B/Re‐drill Evaluate P3B Remediate or re‐drill Potential new injection well (Multi‐THAI® candidate) Evaluate P1B to potentially re‐drill the A1 closer to the heel Evaluate potential new producing wells TSX : PBG 140 technology diversity We deliver energy TSX: PBG www.petrobank.com TSX : PBG