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Remediation schemes to mitigate the impacts of abandoned mines Brian Bone Environment Agency for England and Wales.

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Presentation on theme: "Remediation schemes to mitigate the impacts of abandoned mines Brian Bone Environment Agency for England and Wales."— Presentation transcript:

1 Remediation schemes to mitigate the impacts of abandoned mines Brian Bone Environment Agency for England and Wales

2 Presentation aims & content “To illustrate the approach to remediation in England & Wales through 3 case studies” Remediation drivers Remedial strategy case studies: –active treatment of minewater –passive treatment of minewater –stabilisation of tailings Conclusions

3 Key drivers for remediation of abandoned mines EU Dangerous Substances Directive - requires consented discharges for all sites abandoned after 1981 where the minewater contains listed substances EU Groundwater Directive - requires consented discharges from mine waste where leachate contains listed substances UK Contaminated Land Regulations - requires remedial action where a significant pollutant linkage is identified

4 Future drivers EU Water Framework Directive - consolidates a number of directives, including the dangerous Substances and Groundwater Directives. Environmental objectives will need to be set for ALL water bodies in terms of chemical and ecological quality. Future EU Mining Wastes Directive - will require exchange of technical information on best available techniques with a view to developing methods to identify and remedy “closed waste facilities”

5 Remedial strategies Single or combination of options to prevent pollution and/or treat, selected from: –active treatment –passive treatment –prevention & control of discharge Each approach is highlighted by a case study

6 Active treatment Advantages –Track record & available expertise –Process control –Consistent effluent quality Disadvantages –Cost (op & cap) –Sludge disposal –Energy consumption

7 Wheal Jane Incident Tin/zinc mine in Cornwall closed early 1990s after 100s-1000s years mining in 1 year minewater rapidly recovered following closure temporary pump and treat scheme set up in Nov 1991 Jan 1992 sudden release of 50,000m 3 of water and sediment containing large quantities of Fe, As, Cu, Cd and Zn into the Fal estuary

8 Wheal Jane

9 Drivers & objectives for remediation EU Dangerous Substances Directive - applies to mines abandoned after 1981 Minimise the polluting effects of minewater discharges from Wheal Jane Monitor changes in water quality and the effects on the aquatic environment Determine the most cost-effective long-term remediation strategy for Wheal Jane

10 Impact of Treatment - Wheal Jane

11 Active treatment system Designed to treat 350 l/s (average 200 l/s) Lime-dosing with sludge recirculation Pre-settlement sludge density design of 20% w/w solids Metals removal to satisfy discharge consent to local stream Three key stages

12 Stage 1 Stage 2

13 Active treatment system - summary State-of-the-art active treatment plant commissioned in 2000, cost £20M to build and operate for 10 years High density sludge system is very successful, solid content of 50% w/w achieved in tailings dam Tertiary filters & presses not needed - saving £1.7M 1st 22 months of operation >12 Mcu.m of water treated and >3200te of metals removed (overall removal efficiency 99.2%)

14 Passive treatment Advantages –Low maintenance –Aesthetically pleasing –Sustainable? Disadvantages –Large land take –Lack of process control –Relatively new (track record) –Cost (capital)?

15 Objectives of Wheal Jane pilot passive treatment Examine the feasibility of passive treatment as a long-term solution for Wheal Jane minewater –develop an understanding of the key geochemical and microbiological processes –model the system to aid design of a permanent system for Wheal Jane and elsewhere

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17 Wheal Jane: passive treatment site

18 Aerobic cells

19 Wheal Jane passive treatment plant: anaerobic cell Anaerobic cell

20 Rock filters

21 Passive system - conclusions The conclusion that Wheal Jane drainage could not be treated with passive technology was tested. Further multidisciplinary studies have been carried out to understand the processes involved in passive treatment systems The studies indicate that a passive system could be redesigned to treat Wheal Jane drainage Proposal to establish an international research centre at Wheal Jane passive site

22 Prevention and control of discharges Encapsulation of mining waste Advantages –Track record of civil engineering approaches –Low maintenance Disadvantages –Surface area limits –Durability

23 Greenside Mine, Cumbria

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26 Remediation Scheme (1) Objective - to prevent mobilisation of contaminated tailings from a collapsed dam Control infiltration –run-off into dam –groundwater flow into dam –infiltration through surface Reduce gradient –regrade slope –retaining walls

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32 Remediation Scheme (2) Stabilise retaining structures –walls –underpin revetments Stabilise soil –geosynthetic pre-seeded matting

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35 August 2003

36 Summary Case studies from two sites were presented, included active and passive treatment of acid minewater and a civil engineering approach to deal with tailings Minewater treatment cases highlight the need for good planning, including treatability studies to understand key chemical and biological processes Current and future legislation pose significant challenges to cost-effective remediation in meeting chemical and ecological objectives and disposal of treatment wastes


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