Ev projectpresentation vrs meeting june12v1

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Errington-Vermilion Project June 2013


Deposit Location and Property


Errington-Vermilion: A rich history •

was shipped to Kidd Creek for processing in 1992.


Errington: Circa 1928


Original Shafts are still in good shape


Operations and Exploration in Canada


A strong record of corporate responsibility


The uses of metals


Errington-Vermilion Resources: Fact Sheet Errington

Vermilion

Size of orebody

5.8MT

2.5MT

Zinc

4.16%

4.7%

Copper

1.23%

1.46%

Lead

1.06%

1.46%

Silver

50.53g/t

53.77g/t

Gold

0.73

0.89g/t

Mining Rate

2900 tonnes/day

Employment

200-250 direct jobs (both mining and milling)

Yearly concentrate production

Zinc: 74,800 DMT, Copper: 44,500DMT, Lead: 12,150 DMT

Life of Mine

7-10 years

Total estimated capital cost

$350Million CDN


Errington-Vermilion: Location in Sudbury Basin


Sudbury Deposit Types


Errington Deposit – Oblique View Looking North-West

Ore Lenses Historical Development, circa 1930 Oblique section looking NE


Vermilion Deposit – Oblique Section looking North-West

Ore Lenses cut by diabase dyke. Historical Development, circa 1956 Oblique section looking NW


Errington-Vermilion Deposits Ore Types


Errington-Vermilion: Location in Sudbury Basin


Concentrator Process flow


A number of Baseline studies have been conducted at site including:

• • • • • • •

Hydrology Surface water Hydrogeology Fisheries Hydro geochemical Geochemical Species at risk assessment • Archeological, • Benthos, • Sediment


Surface Water Quality Overview of the Surface Water Quality Monitoring Program (2011 to 2013): • Surface Water Quality Data Collection (Fall 2011 to Spring 2013) • Whitson River, Vermilion River, Unnamed Pond at Vermilion Site • Samples collected seasonally (spring, summer, fall and winter) • 20 stations, 2 of which were added in 2012 (SW20 and SW21) • Reference, near field and far field samples • Samples collected using standard sampling protocols and sent to a CALA accredited Lab for analysis.



Hydrological Investigations Hydrological Investigations (2012 to 2013): • Program initiated March 2012, ongoing. • 2 sites o Whitson River o Vermilion River • Utilizing existing WSC data (Onaping River, Vermilion at Val Caron, and Whitson at Chelmsford.


Hydrogeological Investigations Overview of the Hydrogeological Characterization Program (2012 ongoing): • Objectives: o Determine groundwater flow patterns o Define phreatic surface (natural fluctuations) o Quantity • Packer Testing, response testing, water level measurements • Installation of vibrating wire piezometers (hydrostatic conditions)


Groundwater Data Collection Groundwater Quality Monitoring Program (2012 to 2013): • Objectives: o Determine baseline groundwater quality o Define Local groundwater/surface water interactions • 16 active wells, 12 new wells installed in spring 2012, 4 existing wells o Shallow (overburden and weathered bedrock) o Deep (competent bedrock)



Geochemical Characterization ARD/ML Predictions (2012): • Previous investigations were carried out in the early 2000’s • Results obtained agree with original predictions – majority of rock is acid generating and potentially Metal Leaching • ARD/ML material handling plan o Waste rock will be stored on lined facility and eventually utilized as cemented rock fill o Run-off coming into contact with the waste rock pile will be collected and treated o No waste rock will remain on surface at closure • There will be no crushing or processing at site, all ore will be trucked off site to the Strathcona Complex • As such, there will be no ARD/ML materials left on surface at closure

• Underground workings will be allowed to flood at closure, enhancing the geochemical stability of the cemented rock fill


Aquatics Assessment

Aquatics Field Program (Fall 2012): • Designed following the EEM protocols • Objectives: o Characterize local sediment quality o Characterize the benthic macroinvertabrate community o Define local fish community • Samples obtained using EEM protocols


Species at Risk Blanding’s Turtle and Whip-poor-will Surveys (2012): • Desktop studies and consultation with MNR • Studies were designed using MNR sampling protocols • No SAR detected at site.


Archaeological Assessments Stage 1 and 2 Assessments (2012): • Completed by Horizon Archaeology Inc. • Reports have been submitted to the Ministry of Tourism, Culture and Sport • Currently in review and awaiting reply from the Ministry • No archaeological remains were identified during the Stage 2 Assessment


Glencore Potable water / sanitary


Water Management: Three Key Elements Acid Mine Drainage Control: • The waste pad, ore pad and ditches will be lined with an impervious liner • All water (precipitation) falling on defined area of the site (that could come into contact with acid generating material) as well water pumped from the mine will be collected in lined water treatment pond Effluent treatment Plant: • Water from the water treatment pond will be treated in the effluent treatment plant and recycled to the process, any surplus not needed for the mining process will be discharged to the Vermilion River Sewage Treatment Plant: • Waste water from washroom facilities on site will be treated in a separate waste water/sewage treatment plant and discharged into the environment


Vermilion River: Water Use and Discharge Water Volumes: • Average flow in Vermilion River is 180,000 L/min • Fresh water for potable use and make up water for the process is pumped from the Vermillion River at an average rate of 150 L/min or 0.08% of flow • Excess water from effluent treatment plant discharged to Vermilion River 1,000 L/min Our discharge is roughly 0.56% of average flow of the Vermilion River. Water Quality: • End of pipe effluent quality must meet all Federal and Provincial Regulations (Municipal Industrial Strategy for Abatement and Metal Mining Effluent Regulations) • Must also meet Provincial Water Quality Objectives in Vermilion River • A monitoring program will be designed conforming to Environment Canada Aquatic Effects monitoring (in stream water quality, benthos, sediment and fish population) • The result of this monitoring will be publicly available.


Design for End of Pipe Water Quality to Meet PWQO

• A mass balance approach is taken to determine the maximum allowable effluent concentration for each wastewater constituent, by the equation: CE = QR/ QE * (CPWQO - CR) + CPWQO • The maximum allowable effluent quality (CE) that is acceptable for discharge is determined based on the following parameters: • Receiving water body (Vermilion River) and its expected flow rate (QR). • The effluent discharge flow rate (QE). • The concentrations that must be achieved in the receiving body after discharge (PWQO). • The background concentration of the receiving water body (CR). • Background Water Quality data taken from Knight Piésold Consulting Memorandum 2012 Fall Surface Water Quality Monitoring Program.


Potable Water System


Process Water


Sewage Treatment Plant


Closure Planning

• All waste rock will be used as back fill under ground • Ore and waste pads will be removed and placed under ground • All buildings will be removed from site • Water treatment plant and pond removed from site • Portal and raises capped • Site re-graded and vegetated


Required Permits Permit

For What purpose

Issued by Whom

Lakes & Rivers Improvement Act Approval

Construction of settling pond

Ministry of Natural Resources

Work Permit

Construction of outlet/inlet on Vermilion River

Ministry of Natural Resources

Environmental Compliance Approval

Release of noise, dust, treated water to the environment

Ministry of Environment

Permit to Take Water

Taking more than 50,000L/day

Ministry of Environment

Certificate of Approval Amendment

Changes to Onaping Complex Tailings Area

Ministry of Environment

Conservation Authorities Act Permit

Development of intake/outlet & other structures on Vermilion River shoreline

Nickel District Conservation Authority

Clean Water Act

Compliance with Source Water Protection Plan

Nickel District Conservation Authority

Mining Effluent Regulatory Compliance

Discharge of > 50m3/day of effluent to the environment

Environment Canada

Letter of Advice

Development of outlet/inlet on Vermilion River

Department of Fisheries & Oceans Canada

Navigable Waters Act Review/Approval

Development of outlet/inlet on Vermilion River

Transport Canada


Required Permits


Major project timelines

2012

2013

2012

• •

Exploration & Definition drilling for both deposits Started prefeasibility for both deposits Community & stakeholder Consultation

2014

2013

• •

Additional Exploration & Definition drilling for both deposits Completion of feasibility for both deposits Ongoing community & stakeholder consultation First Nation & Metis Consultation Permitting for Errington

2015

2014

Beginning of Construction on Errington and Strathcona

2016 2016

2015

Construction

Beginning of operations


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