application to renew water license n7l2-1645 public hearing - november 7-10, 2006 presentation by...
TRANSCRIPT
Application to Renew Water License N7L2-1645
• Public Hearing - November 7-10, 2006
• Presentation by Diavik Diamond Mines Inc.
Pictures for Mark
Lac de Gras
The Plant Site Today
Diesel power plant
Boiler plant
Permanent Accommodations
Administration / Maintenance Complex
Process Plant
Fuel Tanks
Sewage Treatment
Explosives Emulsion Plant
Water intake
Lac de Gras
Lac de Gras
Introduction
• Panel• Mr. Gord Macdonald – Lead DDMI Representative
• Mr. Scott Wytrychowski – DDMI Environment Manager
• Mr. Jeff Reinson – DDMI Manager of Infrastructure Construction
• Mr. Brad Armstrong and Ms. Melanie Smith - legal
• Experts• Mr. Geoff Beale – water management
• Mr. J.P. Bechtold – effluent quality criteria
• Dr. Alan Cameron – explosives management
• Mr. Don Chorley – hydrogeology
• Mr. Terry Eldridge – processed kimberlite storage and closure
• Ms. Amy Langhorne – aquatic effects monitoring
• Dr. Karsten Liber – aquatic toxicology
• Dr. Marcel Pineau – water treatment
• Mr. Erik Madsen – DDMI Northern Affairs Manager
Outline
• Overview of the Status of the Mine
• Renewal Application
• Status of Ammonia Management
• Status of Aquatic Effects Monitoring Plan
• Status of Closure and Reclamation Plan
• Term of Water License
• Other Issues
• Final Summary
Outline
• Overview of the Status of the Mine• Overview of Mine• Current Development• Environmental Performance• Socio-Economic Performance• Planned Development• Summary
• Renewal Application
• Status of Ammonia Management
• Status of Aquatic Effects Monitoring Plan
• Status of Closure and Reclamation Plan
• Term of Water License
• Other Issues
• Final Summary
Overview
Plan vs Current
A154 Dike & Pit Area
Diavik Diamond Mine Site
PKC Area
North Inlet Storage Facility
North Country Rock Area
North Inlet Water Treatment Plant &
Discharge
A418 Dike & Future Pit Area
Water Management Area
Diavik Diamond Mine SitePKC Area
PKC Area
Primary Containment Dams
Secondary Containment Dam
Final Containment Dams Secondary Containment Dam
Diavik Diamond Mine Site
North Country Rock Area
North Country Rock Area
Pond 2Pond 3
Pond 1
Diavik Diamond Mine Site
A154 Pit and North Inlet Area
A154N
A154S
What is a cubic metre per day (m3/d)
20,000 m3/d
250,000 m3/d
• Coppermine River at Lac de Gras• 1,750,000 m3/d
• Coppermine River at Kugluktuk• 25,000,000 m3/d
A154 Pit Area
20,000
>100
>100
20,000
Mine SeepageDike Seepage
Final EffluentTreatment Plant
North Inlet
20,000
22
23
27
2120
2425
26
33
3231
29
28
1. Surface Runoff and Groundwater Stations
Surveillance Network Program
22
23
27
2120
24
25
26
33
3231
29
28
1. Surface Runoff and Groundwater Stations2. Source Water Quality
47
46
45
42
15
12
13
1642a
4952
48
11
Surveillance Network Program
Surveillance Network Program
22
23
27
2120
24
25
26
33
3231
29
28
1. Surface Runoff and Groundwater Stations2. Source Water Quality3. Final Effluent 4. Mixing Zone -Lac de Gras
47
46
45
42
15
12
13
1642a
4952
48
11
19a19c19b
18
19a19c
19b18
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
Alum
inum
Amm
onia
Arsen
ic
Cadm
ium
Chrom
ium
CopperLea
d
Nicke
l
Phosphoru
sTSS
Zinc
Per
cen
t o
f E
ffec
t T
hre
sho
ldat
Mix
ing
Zo
ne
Bo
un
dar
y
Effect ThresholdDischargeBackground
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
Alum
inum
Amm
onia
Arsen
ic
Cadm
ium
Chrom
ium
CopperLea
d
Nicke
l
Phosphoru
sTSS
Turbid
ityZin
c
Pe
rce
nt
of
Ma
xim
um
Av
era
ge
Dis
ch
arg
e L
imit
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
Alum
inum
Amm
onia
Arsen
ic
Cadm
ium
Chrom
ium
CopperLea
d
Nicke
l
Phosphoru
sTSS
Turbid
ityZin
c
Per
cen
t o
f M
axim
um
Ave
rag
e D
isch
arg
e L
imit
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
Alum
inum
Amm
onia
Arsen
ic
Cadm
ium
Chrom
ium
CopperLea
d
Nicke
l
Phosphoru
sTSS
Zinc
Per
cen
t o
f E
ffec
t T
hre
sho
ldat
Mix
ing
Zo
ne
Bo
un
dar
y
Effect ThresholdDischargeBackground
Final discharge as percent ofLicense limit
Water quality at highest effluentexposure as a percent of effects threshold
Water and Waste Summary
Year Withdrawal from LDG Pumped from Mine Discharged from NIWTP
2000 0.01 - -
2001 0.18 - -
2002 0.46 - 4.1
2003 0.52 2.0 6.8
2004 1.16 4.0 4.7
2005 0.86 5.2 5.6
Annual Water Quantities (Mm3/y)
Water and Waste Summary
Annual Mine Waste Quantities
Process Kimberlite (Mt)
Waste Rock (Mm3)
Year Coarse Fine Type I Type II Type III
2002 - - - - -
2003 0.26 1.09 2.55 0.85 4.10
2004 0.38 1.60 3.64 1.57 5.63
2005 0.23 1.90 4.45 0.88 4.82
Environmental Performance
• Water Management and Monitoring
• Wasterock and PKC Management
• Compliance
• Effects less than EA Predictions
• No significant adverse effects on Lac de Gras
Socio-Economic PerformanceNorthern Commitments
C$1.2 billion
50% Aboriginal
80%Northern
73%Northern74%
Northern44%
Northern
ConstructionWorkforce
ConstructionContracts
OperationsWorkforce
Business Spending
20% Aboriginal
800 Workers
C$1.2 billion
50% Aboriginal
($600 m)
C$223 million (2005)
39% Aboriginal
35% Aboriginal
(256)
727 Workers
Source: Diavik 2005 SEMA Report
Aboriginal Business
Cumulative Total for All Aboriginal Business
$0
$200
$400
$600
$800
$1,000
$1,200
1999 2000 2001 2002 2003 2004 2005
C$
Mil
lio
ns
Min
ing
Op
erat
ion
s b
egin
Total Diavik Aboriginal Business Spend ~ $1 Billion
Diavik’s Growing Underground Future
Diavik Will Become an Underground Mine *
A154 Open-Pit A418 Open-Pit
A154/A418 Underground
* mine schedule subject to change due to market condictions, further resource evaluation, continued mine planning, etc.
Note: A21 pipe is pending further resource evaluation
2021 2022 20232017 2018 2019 20202013 2014 2015 20162009 2010 2011 20122005 2006 2007 2008
Full and Safe Closure Diavik Site - 2025
Full and Safe Closure Diavik Site - 2025
The Long Term Goal
Overview Summary
• Developed as planned.
• Proud of accomplishments.
• Proud of performance in Sustainable Development.
• Our challenge is to continue to improve into the future.
Outline
• Overview of the Status of the Mine
• Renewal Application• Overview of Application• Security Deposit• Renewal Workplan
• Status of Ammonia Management
• Status of Aquatic Effects Monitoring Plan
• Status of Closure and Reclamation Plan
• Term of Water License
• Other Issues
• Final Summary
Renewal Application
• Renewal of Water License N7L2-1645 filed on August 8, 2005.
• Application contains:• Part 1 - Application Form• Part 2 - Completed Mining Industry Questionaire with references on 3
CD’s• Part 3 – Consultation Summary• Part 4 – Overview and Status of N7L2-1645• Part 5 – Copy of Water License
• Application deemed complete – September 8, 2006.
• DDMI has not applied for any changes to Terms and conditions.
• Seek a 15 year term to coincide with expected duration of operations.
• With the Application, DDMI requested an exemption from Preliminary Screening.
• DDMI received exemption from Preliminary Screening – September 8, 2006.
Part B - Security
•Additional security amounts• Part B Item 2b
• Minister currently holds $153M in Security Deposits and this increases to $178M in 2007.
• The expected total Life of Project Closure Cost is $123M• Reference Schedule 1 - Environmental Agreement – Column (A)
• “Additional Security Deposit Amounts ” have been scheduled for the Life of Project
• Reference Schedule 1 - Environmental Agreement – Column (B)
Application cont’
Application cont’
• WLWB Renewal Workplan:• Renewal and Terms and Conditions• Progress with respect to ammonia and AEMP• Productive discussions at hearing
• DDMI written response to interventions submitted to WLWB October 30, 2006.
• DDMI Responded to specific intervener suggestions and recommendations with a focus on:• Changes to terms and conditions, including discharge
limit for total ammonia.• Ammonia Management Plan and proposed way forward.• AEMP and proposed way forward.
Outline
• Overview of the Status of the Mine
• The Application
• Status of Ammonia Management• Ammonia Overview• Draft Ammonia Management Plan• Total Ammonia Discharge Limit• Proposed Way Forward
• Status of Aquatic Effects Monitoring Plan
• Status of Closure and Reclamation Plan
• Term of Water License
• Other Issues
• Final Summary
Ammonia Management
Drilling
I&D Mgmt Services
Mixing & Placing Explosives
Western Denesoline Explosives
Blasting
Western Denesoline Explosives
Loading Holes
Western Denesoline
LoadingLoad & Haul
I&D Management Services
Ammonia Investigations
ADP
AMP
Terms of Reference
2004
2005
2006
Scope
Revised ADP
Addendum
other
Ammonia Management Plan
Ammonia Management Plan (AMP) - Objectives
1. To ensure that explosives are used and water is managed in such a way that ammonia losses do not result in a change in the trophic status of Lac de Gras or adverse environmental effects.
2. To continually work towards achieving the lowest practical ammonia levels in the mine water and final effluent discharge.
Additional Measures to Manage Ammonia
2006 2007 2008 2009
Explosives Management
Explosives Investigation
Explosives Implementation
A418 Water to PKC
Monitor A418
Decision on Water Use
Feasibility Engineering
Construction/Operations
Rock Wall Seepage
Phase I
Phase II
Treatment in North Inlet
Monitor NI
Quantify ammonia processing
Non-native Species Issue
Design Approval - NI Dams
Field Tests
Decision on Approach
Draft AMP - Content
• Additional measures to manage ammonia
• Management objectives
• Internal control levels
• Monitoring, controls and contingencies
• Additional monitoring requirements
• Review, reporting and corrective actions
Discharge Limit Total Ammonia
0
5
10
15
20
25
Level that is protective of the environment(Water-Quality based Approach)
Technology Limit(Technology Based Approach)
Estimated range of lowest practical level(Practically Achievable Approach)
To
tal A
mm
oni
a (
mg
/L)
Daily Maximum
Recommended Discharge Limit
• 20 mg/L daily maximum – water quality based approach• Protective of environment• Ensures no chronic toxicity• Ensures no acute toxicity with pH control• Consistent and recognized approach
• Ammonia Management Plan to achieve internal control levels.
Response to Interventions - Ammonia
• Round whitefish testing• Research on northern aquatic species
• Total ammonia discharge limit• Table 1 INAC Intervention
Water Source Sodium
(mg/L)
Potassium (mg/L)
pH Acute Toxicity
(mg/L NH3-N)
Chronic Toxicity
(mg/L NH3-N)
Lac de Gras 0.48 0.44 6.56 1.25 0.79
Effluent 50 14.1 7.2 132 83
Mixing zone 2.6 1.0 6.56 5.24 3.30
Borgmann and Borgmann (1997)
• Initial tests showing greater NH3 toxicity in softer water were run in artificial media diluted 90% with deionized water (no intermediate concentrations tested)
• Tests used to develop a model on the influence of Na+ and K+ on ammonia toxicity were only run in artificial media at two undocumented hardnesses
• The model slightly overestimated ammonia toxicity in Lake Ontario water
• The model substantially overestimated ammonia toxicity (by 6-9 fold) in Lake Superior water
• While Na+ and K+ can influence ammonia toxicity to Hyalella azteca in artificial media, there is no evidence that the Borgmann model is applicable to Lac de Gras conditions
Proposed Way Forward - Ammonia
• With discussions from these hearings:• submit that the Board will be in a position to approve
the AMP in accordance with Part H of the Water License, and
• the Board should be able to determine the long-term discharge limit for ammonia.
• DDMI proposes that the testing of round whitefish be developed as a research project with DDMI as a funding partner.
Summary Ammonia Presentation
• Provided information about Ammonia.
• Provided an overview of the draft AMP.• How it was developed• Management measures• Plan contents
• Proposed a way forward.• Approving the AMP• Setting an ammonia discharge limit• Round whitefish research
• Substantial progress has been made.
Outline
• Overview of the Status of the Mine
• The Application
• Status of Ammonia Management
• Status of Aquatic Effects Monitoring Plan• Aquatic monitoring
• Project-related effects pathways
• 2001 AEMP
• 2006 AEMP
• Terms and Conditions
• Proposed Way Forward
• Status of Closure and Reclamation Plan
• Term of Water License
• Other Issues
• Final Summary
Aquatic Effects Monitoring
Water QualityProject Activity (Location) Potential Change (Location)
Dikes(Lac de Gras)
Mine Water and Sewage Discharge
(Lac de Gras)
Infrastructure(Lac de Gras)
Durst and Air Emissions
(east island)
Increase in metals and nutrients through porewater release1
Increase in suspended sediment1
WQ-1
1=could occur during construction 2=could occur during operation3=could occur during closure 4=could occur during post-closureTSS = Total Suspended Solids TDS = Total Dissolved Solids
Environmental AssessmentPermitting
Fisheries Authorization· S35(2) Section 11/12
Aquatics Effects Monitoring Program· SNP Part B1-B13· Park K Item 6/7
· FA dissolved oxygen during construction S35(2) Section 10
Seepage Monitoring· SNP Part B14-15· Part F Item 11
Snow Quality Monitoring· Part K Item 7k
Mine Pit Dewatering and
Flooding(Lac de Gras)
Surveillance Network Program· SNP Part B21
Increase in sedimentation1
Leaching of metals and nutrients from the outside of the dikes1,2,3,4
Increase in suspended sediment due to breaching of dikes3
WQ-2
Introduction of metals, nutrients, TSS from mine water and sewage discharge1,2,3
WQ-3
Introduction of hydrocarbons, metals, nutrients, TSS through east island runoff1,2,3
WQ-4
Introduction of TSS through dust from transportation and air emissions1,2
WQ-5
Change in groundwater TDS1,2,3,4
Change in sedimentation due to introduction of TSS1,2
Water Quality
Water SupplyProject Activity (Location) Potential Change (Location)
Dikes and Mine Pits
(Lac de Gras)
Mine Water and Sewage Discharge
(Lac de Gras)
Water Withdrawal(Lac de Gras)
Infrastructure(east island)
Changes in surface area, water level and outflow of Lac de Gras due to dike construction1,2
Changes in surface area and outflow of Lac de Gras due to mine pit construction and dewatering1,2
Changes in Lac de Gras flow and water level due to discharge1,2
Changes in flow and water level in Lac de Gras due to changes in the hydrological conditions of the east island1,2,3,4
Changes in flow and water level due to removal of water from Lac de Gras1,2
1=could occur during construction 2=could occur during operation3=could occur during closure 4=could occur during post-closure
Environmental AssessmentPermitting
Water License· Part E, Item 8
Water License· Part B, Item E
Water License· Part B, Item 4· SNP Part C
Mine Pit Dewatering
(Lac de Gras)
Mine Pite Dewatering and
Flooding (Lac de Gras)
Changes in water level and outflow through interaction with groundwater1,2,3
Change in groundwater quantity due to mine pit dewatering, operation and refilling1,2,3,4
Water License· Part B, Item 4
Changes in water level and flow of Lac de Gras due to mine pit refilling3,4
Water Supply
FISHProject Activity (Location) Potential Change (Location)
Angling (Lac de Gras)
Use of Explosives(Lac de Gras)
Dike and North Inlet Closure and
Dewatering(Lac de Gras)
Water Withdrawal(Lac de Gras)
fish mortality due to fish harvest2
fish mortality due to hooking injuries2
free-swimming fish mortality due to instantaneous pressure change1,2
egg mortality due to changes in peak particle velocity1,2
fish mortality due to entrainment1,2
Dikes(Lac de Gras)
loss and gain of habitat due to dikes1,2,3,4
Infrastructure (east island)
changes in habitat quality due to changes in lake circulation1,2,3,4
loss of small lake habitats through lake alteration or destruction1,2,3,4
loss of stream habitats due to drainage basin changes1,2,3,4
Discharges, Dikes and Infrastructure(Lac de Gras, east
island)
Changes in fish tissue quality due to changes in water quality1,2,3
F-1
F-2
fish mortality due to stress and injuries during salvage1
F-3
F-4
F-5
F-6
F-7
1=could occur during construction 2=could occur during operation3=could occur during closure 4=could occur during post-closure
Environmental AssessmentPermitting
Fisheries Authorization· S35(2) Section 13
Fisheries Authorization· S32 Section 8
Fisheries Authorization· S35(2) Section 6.15
Fisheries Authorization· S30 Section 5
Fisheries Authorization· S35(2) Section 6.3, 8, 11
Fisheries Authorization· S35(2) Section 6.3, 8, 11
Fisheries Authorization· S35(2) Section 6.3, 8, 11
Fish
Effluent Detectable
Effluent Mixing Zone
Sediment and Invertebrates
Water Quality
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
Alum
inum
Amm
onia
Arsen
ic
Cadm
ium
Chrom
ium
CopperLea
d
Nicke
l
Phosphoru
sTSS
Zinc
Per
cen
t o
f E
ffec
t T
hre
sho
ldat
Mix
ing
Zo
ne
Bo
un
dar
y
Effect ThresholdDischargeBackground
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
Pe
rc
en
t o
f E
ffe
ct
Th
re
sh
old
at
LD
G 4
1
Effect ThresholdDischargeBackground
Project Related Effects - Results
Water quality effects monitoring results are within levels predicted in the EA.
Water use amounts are within levels predicted in the EA and have not caused impacts on water supply in Lac de Gras.
Monitoring of effects on fish have not identified any significant impacts and results are generally within EA predictions.
Dust deposition rates are currently higher than predicted in EA – ongoing construction.
Effluent Monitoring
Dike Monitoring
Snow Quality Monitoring
Runoff Monitoring
AEMP
AEMP Scope
TK and Community
2001 AEMP
• The scope of the AEMP was the subject of review at the February 27, 2001 DTC meeting #7.
• Final program design prepared and approved (July 2001) with DTC support.
• Some Water License items were explicitly not included.
2001 AEMP
• Approach was to set trigger values that if exceeded would raise a flag.
• Trigger values set conservatively low relative to EA effects levels.
• Trigger values not statistically-based.
• Trigger values set based on baseline data.
2006 AEMP Redesign
• INAC baseline review
• Diavik Technical Committee review
• EMAB review
• MVLWB review
• WLWB directive March 22, 2006
• 2006 AEMP to be viewed as effluent monitoring chapter of comprehensive AEMP
Why is 2006 AEMP improved?
• Follows national standards for mine effluent monitoring • MMEEM based on many years of research
• Objective clearly defined.
• Comparisons made between exposure and reference – minimal reliance on baseline data.
• Additional reference sites – added fish.
• VEC and measurement endpoints defined by program and linked to the EA thresholds.
• Two Parts:• 4 times per year water quality – every year
• 1 per year biological – every 3 years if no effects
• Formal statistical analysis.
Overview of 2006 AEMP DesignEffluent Monitoring Component
• Water Quality and Trophic Status• 13 exposure sampling points within 1% effluent plume
• 10 reference sampling points as far from effluent influence as practical
• 1 site at mouth of Coppermine River
• Consistent sampling methods at all sites
• Biological Sampling• Includes fish, benthic invertebrates and sediment sampling
• 10 exposure sampling points within 1% effluent plume
• 10 reference sampling points as far from effluent influence as practical
• Focus on area where changes most likely (exposure area)
• Results compared with results from reference areas
Effluent Monitoring Design Approaches
Distance
Con
cent
ratio
n
35
5
33
13
11 1 1 1 1 1 1 1
2 2 3
Exposure-Reference
Gradient
Hybrid
Effl
uent
5
5
11
1 1 1 1 1 1 11
32 2 3
• Support intervener recommendations that:• Scope be as per Part K of expiring License.• Update to reflect work completed and exemptions that
have been granted.• Enable integration of other monitoring program results
to meet “project-related” requirement.• Annual AEMP for approval.• Other terms and conditions as noted in DDMI Response
October 30, 2006.
AEMP - Terms and Conditions
Proposed Way Forward - AEMP
• Comprehensive AEMP with• Effluent, snow quality, runoff, dikes and TK/community
• Immediate work to focus on effluent effects monitoring.
• DDMI proceed immediately to prepare comprehensive AEMP with Board direction on scope.
• Technical workshops on effluent monitoring in December and January – EC EEM Specialists requested to facilitate.
• Draft of consolidated AEMP – January 31,2007.
• Review from interested parties – February 15, 2007.
• WLWB approval – March 31, 2007.
• Begin implementation April 2007 (water quality) – full implementation (WQ plus biological) Summer 2007.
• DDMI committed to development of new AEMP through facilitated process.
• Ask Board to request all parties to make constructive proposals towards development of new AEMP.
AEMP Presentation Summary
• Provided overview of aquatic effects monitoring.
• Reviewed all the potential effects pathways from the Project to Lac de Gras.
• Summarized effects results
• Described the 2006 AEMP (effluent monitoring)
• Terms and Conditions
• Proposed Way Forward• Technical workshops to provide input• Implementation April 2007
• Substantial progress has been made.
Outline
• Overview of the Status of the Mine
• The Application
• Status of Ammonia Management
• Status of Aquatic Effects Monitoring Plan
• Status of Closure and Reclamation Plan• Ongoing Research• Terms and Conditions• Proposed Way Forward
• Term of Water License
• Other Issues
• Final Summary
Full and Safe Closure Diavik Site - 2025
Full and Safe Closure Diavik Site - 2025
The Long Term Goal
Re-vegetation Research Study
North Inlet Water Treatment Plant Waste Sludge
Sewage Treatment Plant
Sludge
Lake Bottom Till
Soil Amendments
Fall Seeding
Continues Monitoring
Shrub Cuttings
Planting and Monitoring
Re-vegetation Research StudyYear 2 Plant Growth
Waste Rock Test Piles2003 (1st year of operations)
The Planning Began
2004 (2nd year of operations)Start Construction of the Tipping Platform
2005 (3rd year of operations) Construction of the Collection Drains
2006 (4th year of operations)Complete Construction of the Test Piles
1
4 3
2
World Class Research Team
Principle Researchers:
•Dr. David Blowes – University of Waterloo
•Dr. Leslie Smith – University of British Columbia
•Dr. Dave Sego – University of Alberta
Internal Reviewers:
•Dr. Paul Brown – Rio Tinto
•Dr. Ward Wilson – University of British Columbia
Supporters:
•DDMI
•National Research Council of Canada (NSERC)
•INAP, CFI & MEND
C&R Plan – Terms and Conditions
• Wording of Section L substantially carried forward
• Other terms and conditions as noted in DDMI Response October 30, 2006.
Proposed Way Forward – C&R Plan
• Recommend that the WLWB establish a process of review and finalization that:• Provides opportunity to review the draft,• Has realistic timelines,• Make submissions respecting revisions,• Allows participation in workshops or meetings, and• Works constructively towards approval of the Plan.
Outline
• Overview of the Status of the Mine
• The Application
• Status of Ammonia Management
• Status of Aquatic Effects Monitoring Plan
• Status of Closure and Reclamation Plan
• Term of Water License
• Other Issues
• Final Summary
Term of License
• Primary reasons given for shorter License is ability to comment and request changes.
• DDMI suggests that this process does exist.
• Requests Term of License as 15 years
Outline
• Overview of the Status of the Mine
• The Application
• Status of Ammonia Management
• Status of Aquatic Effects Monitoring Plan
• Status of Closure and Reclamation Plan
• Term of Water License
• Other Issues• Discharge limit for nitrate
• Final Summary
Other Issues - Nitrate
• Interveners recommend nitrate be added as a regulated parameter.
• DDMI accepts addition of nitrate as regulated parameter• Limit should be based on level that is protective of the
environment.• DDMI provided detailed calculations and rationale.• DDMI clarified comment regarding BHPB Toxicity Data.
Outline
• Overview of the Status of the Mine
• The Application
• Status of Ammonia Management
• Status of Aquatic Effects Monitoring Plan
• Status of Closure and Reclamation Plan
• Term of Water License
• Final Summary
Final Summary
• Reviewed the development, operation and future mine plans
• Reviewed the Renewal Application
• Reviewed Ammonia Management• Recommend discharge limit of 20 mg/L• Approve AMP• Recommend research on round whitefish
• Reviewed AEMP Scope/Purpose• Recommended scope for comprehensive AEMP• Proposed Way Forward - AEMP
• Closure and Reclamation• Proposed Way Forward – C&R Plan
Mahsi Cho