mine rehabilitation cqminingforum_michael-rodgerson
TRANSCRIPT
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M in e R e h a b ili t a t io n A Q u e e n s l a n d P e r s p e ct i v e
Presented by Michael Rodgerson
Environmental Protection Agency Emerald
Combination of two presentations by:
Dr Ian WilsonEnvironmental Protection Agency (Qld)
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R e la t iv e Va lu e o f M in in g t oQ u e e n s l a n d e r s
0500
100015002000
2500300035004000
45005000
1 8 6 0
1 8 7 0
1 8 8 0
1 8 9 0
1 9 0 0
1 9 1 0
1 9 2 0
1 9 3 0
1 9 4 0
1 9 5 0
1 9 6 0
1 9 7 0
1 9 8 0
1 9 9 0
2 0 0 0
CoalBauxiteTinCopperZinc
LeadMinSandsSilver
Gold
V a
l u e
( i n
2 0 0 0 $
p e r p e r s o n
)
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Qu e e n s la n d Co a l Pr o d u ct io n
020
40
6080
100
120140
160
180
Coal (Mt/a)
1960 2.69 Mt 3 Open-cut mines
65 Underground mines40,000 t/mine Export 0.03 Mt / $0.36M
2005 172 Mt 36 Open-cut mines 11 Underground mines
3.66 Mt/mine Export 144Mt / $15,600M 1860 20001900 1950
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M in in g 18 6 0 s t o 19 0 0
John Oxley Library
0
800
m
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Fr o m t h e 19 0 0 s t o 19 70 s
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A b a n d o n e d
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M in in g 19 6 0 o n
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M in in g To d a y
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M o d e ls o f E S D
Triple BottomLine
Regulation Self-regulation Custodianship
Externalities Offsets? CommunityInequity Tradeoffs ?
soc env
econ env soc
env
soc
econ
+ + +
Market based NestedHierarchy of Constraints
e
awareness
Accountability
Brundtland 1987 J Elkington 1994 R Sanders 2000
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T h e Qu e e n s la n d A ct s1850 1900 1950 2000
1857Gold
Fields(NSW)
Mineral Lands
1872/1882
1874GoldFields
1898 Mining
1968Mining
1989 MineralResources
1994EnvironmentalProtection
2001Amendment
1925 Coal Mining1886Mineral Lands(Coal Mining)
Special Agreements
1909-1971Mining on Private Land
Clean Air 1963
Clean Waters 1971
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H is t o r y o f M in e R e h a b Gold Fields Act 1857 (NSW) No rehab provisions
(1870 Regulation shafts near roads, fence & cover if not in use) Mineral Lands Act 1882 (fence, fill or log abandoned shafts) The Mining Act 1898
No rehab provisions. Regulations could be made about tailingsstorage, pollution & nuisance (surrender at any time if complying)
Special Agreement Acts 1957-1989 Varied (restore contours-competent advice on reveg / grazing / nil)
Mining Act 1968 Minister may specify rehab (progressive and final) Generally required restoring surface & watercourses
Mineral Resources Act 1989 Integrated rehab into mine planning and surrender processes Environmental Protection Act 1994 (since 2001)
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R e h a b ili t a t io n S t a t i s t i cs
0
10000
20000
30000
40000
50000
60000
70000
80000
1990 1994 1998 2002 2006
COAL MINING
Rehabilitated
Disturbed
METALLIFEROUSRehabilitated
Disturbed
ha
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Co m m u n it y Co n ce r n s
Size of mines Chemicals used Increasing amounts of waste (eg from
deeper open cuts)
Increasing gap between areas of disturbance and rehabilitation Discounted financial assurance
Administrative conflicts (promote/regulate) Less wealth to local communities
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R e h a b i li t a t io n Pr in cip le s
Incentives to speed up rehabilitation
Incentives for getting near a zero footprint Land suitability, stable and non-polluting Transparent decision on future landuse Objectives set in application, but can amend Assessment of residual risk
Adequate provisions to manage after rehab Quicker signoff
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Po licy Fr a m ew o r k
Applicant/miner responsibilities
Application Monitoring &research duringmining
ProgressiveRehabilitation
Report
FinalRehabReport
ObjectivesIndicators
Criteriaproposed in
EM Plan
ImprovedObjectivesIndicators
Criteria
Provide Monitoring DataHave Criteria been met ?
Residual Risk AssessmentCalculate Residual Risk Payment
GovtApprovesSurrender
CertifiesProgressive
Rehabilitation
Govt proposes rehabilitation hierarchy and goals
GovtGrants
Env Authority
GovtApproves
Amendment
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GOALS
Safe
StableNon -polluting
Useful
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REHABILITATION HIERARCHY
1. Avoid disturbance that will require rehabilitation toprevent or minimise future environmental harm
2. Reinstate the original natural ecosystem3. Develop an alternative outcome with a higher economicvalue than the previous land use
4. Reinstate previous land use (eg. grazing or crops)5. Develop lower value land use (if this is acceptable torelevant stakeholders.)
6. Leave the site in an unusable condition or with apotential to generate future pollution or adversely affectenvironmental values (unacceptable).
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Gu id e lin e 18 Goals of rehabilitation - a State perspective Rehabilitation objectives for each mine domain
Rehabilitation indicators Completion criteria & how they are set Method for determining residual risk Outline of certification process Appendices
Examples of Goals, Objectives, Indicators, Criteria Information requirements at application, progressive
certification and surrender stages
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O b j e c t i v e s
Future land-uses specified for domains Consistent with Goals & Hierarchy Matters to consider
Environmental values in vicinity
Adjoining land use Owner/community/local government views Long-term economic value
Minimise the risks Minimise the cost
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Red Dome -Domains
Pit
Tailings
Airstrip
Rehabilitatedspoil
Infrastructure
Heapleach
RecontouredSpoil
1 2 3
45
6Dam
Spoil
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I n d i c a t o r s
Must measure variability of an objective Scientifically related to an important aspect Easily and inexpensively measured Precise enough to detect meaningful change Repeatable / auditable
Assists decision making
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Co m p le t io n Cr i t e r ia
Must be relevant to objective & have finality
Is a value of one or integrates several indicators Selection facilitated by years of trial data
May compare with reference sites or proposedendpoint unique to the rehabilitated area Need to have several years at completion level to
understand effects of fire and drought Aiming for statistical validity
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Pr o g r e s s iv e R e h a b i li t a t io n Definitions
Rehabilitation completed before mining ceases Certification (cf. surrender) and residual risk payment
Legislative provisions in EP Act Processes to set objectives and completion criteria
Residual risk requirement Guidelines explaining technical requirements Possible objectives, indicators and completion criteria
Method for determining residual risk Contribute to residual risk to clear future liability
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Pr o g r e s s iv e R e h a b ili t a t io n
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B e n e f i t s o f Pr o g r e s s iv e
R e h a b i l i t a t i o n Less environmental harm from smaller disturbance
Pollutants treated or stabilised sooner Water management in place Evidence of effects of extreme weather Monitoring & improvement over a longer period Increased understanding of long term risks
Certification gives companies financial confidence Less risk to Govt accumulated at end of mine life
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H o p es fo r t h e Fu t u r e Better mine planning Clear rehabilitation requirements
Including community involvement Progressive rehabilitation the norm
Best practice environmental management Maximum water reuse zero discharge Fewer open voids and waste piles
Backfilling becoming more common
Appropriate financial assurance
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Further Information
From the Environmental Protection Agency Website
Guideline 18 Rehabilitation requirements for mining projects
Guideline 16 Final rehabilitation report and audit statementfor non-standard mining lease projects
Guideline 15 Final rehabilitation report and audit statementfor non-standard exploration and
mineral development projects
Fact sheet 11: Surrendering an environmental authority(mining activities)