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  • TAILINGS AND MINE WASTE 2014

    APPLYING SOIL MECHANICS PRINCIPLES TO TAILINGS DEWATERING,

    DENSIFICATION AND STRENGTHENING

    David Williams

  • TAILINGS AND MINE WASTE 2014

    Conference Sponsors

    AMEC Earth & Environmental Knight Pisold and Co.

    Ausenco MWH

    BASF Chemical MineBridge Software, Inc.

    CETCO Paterson & Cooke

    ConeTec Robertson GeoConsultants, Inc.

    DOWL HKM SRK Consulting, Inc.

    Engineering Analytics, Inc. Tetra Tech, Inc.

    Gannett Fleming URS

    Golder Associates, Inc. Community Sponsor

    CDM Smith

  • Overview Water recovery from tailings is most efficiently

    achieved in-plant, but this must be balanced against efficient management of tailings disposal and cost

    Densification and strengthening of tailings is best achieved by depositing them in thin layers and allowing time for consolidation and desiccation

    This can be assisted by amphirolling to drain surface water down tailings beach and increase surface area exposed to desiccation, and by subsequent dozing to compact tailings

    TAILINGS AND MINE WASTE 2014 3

  • Constraints under which TSFs Must Operate

    Climatic and topographic setting of TSF Processing plant tailings production rates Manage supernatant tailings water Meet discharge water quality Maximise tailings settled dry density Rehabilitate TSF on closure to ensure stability,

    minimise environmental impacts, and achieve some post-closure land use / function

    TAILINGS AND MINE WASTE 2014 4

  • Good Tailings Management

    Spigotting in thin lifts

    Maintaining a small decant pond

    TAILINGS AND MINE WASTE 2014 5

  • Good Tailings Management

    To achieve optimal water recovery and tailings dry density

    Which will minimise required TSF wall raises Possibly allow upstream wall raising on

    tailings, potentially using tailings to construct raise

    Will facilitate closure

    TAILINGS AND MINE WASTE 2014 6

  • Operational Tailings Water Balance

    Rainfall Evaporation fromponded water and

    wet tailings Tailings input

    Seepagerecovery

    Original groundwater tableGroundwater mounding

    Wall seepageFoundation seepage

    DecantStored wet tailingsPhreatic surface

    TAILINGS AND MINE WASTE 2014 7

  • Operational Tailings Water Balance

    TW + RR + WW = RW + EW + SE + SF + SW TW = tailings input water RR = TSF catchment rainfall and runoff WW = net waste water RW = water recycled to plant EW = entrained water SE = surface evaporation SF = seepage into foundation SW = seepage through wall

    TAILINGS AND MINE WASTE 2014 8

  • Operational Tailings Water Balance

    Best-known water volumes are initial % Solids, rainfall, and evaporation from ponded water

    Water volumes that can be determined include entrained water, runoff, input and storage of waste water, and evaporation from wet, desiccating and dry tailings

    Water volumes that are least well-known are seepage into TSF foundation and through wall

    TAILINGS AND MINE WASTE 2014 9

  • Operational Tailings Water Balance An Australian Example

    Average annual rainfall = 845 mm (range 308 to 1,542 mm, since 1994)

    Highest daily rainfall recorded = 272 mm (and 776 mm over 3 days)

    Water discharged into TSF ~5 times rainfall Pumping capacity ~20 mm/day, of which

    return water accounts for ~15 mm/day Leaving ~5 mm/day in reserve for rainfall

    TAILINGS AND MINE WASTE 2014 10

  • Tailings Continuum (Davies, 2004)

    Complex water managementInefficient water recovery

    Containment requiredSeepage likely

    Rehabilitation difficult

    Likely low OpEx and CapEx,but high rehabilitation cost

    Simple water managementEfficient water recovery

    Process chamical recoveryMinimal containment required

    Negligible seepage lossesProgressive rehab. possible

    Stable tailings mass

    High OpEx and CapEx,but low rehabilitation cost

    Tailings slurry(typically segregating)

    Thickened tailings(dewatered, ideally non-segregating)

    Paste tailings(Dewatered, ideally non-bleeding)

    "Wet" filter cake(near-saturated)

    "Dry" filter cake(85 to 70% saturated)

    Pumpable

    Non-pumpable

    CONTINUUM

    Slurry-like: No particle/particle

    interaction Saturated

    No effective stress

    Soil-like: Particle/particle

    interaction Effective stresses

    and suction Shear strength

    TAILINGS AND MINE WASTE 2014 11

  • Consistency of Tailings

    High density slurry

    Filtered (dry cake) Centrifuged (wet cake)

    Low slump paste High slump paste

    TAILINGS AND MINE WASTE 2014 12

  • Transporting Filtered Tailings

    CRICOS Provider No 00025B

    By truck

    By conveyor and stacking

    13 TAILINGS AND MINE WASTE 2014 13

  • In-Plant Recovery of Tailings Water THICKENING NOTES

    Conventional and high rate

    ~25% Solids for coal tailings and red mud 40-50% Solids for metalliferous tailings Transportable by centrifugal pumping Beaching at ~1%

    High compression thickening

    Higher % Solids Just pumpable by centrifugal pumps Beaching at up to 5%

    Paste thickening

    Raises % Solids to between 45% (red mud) and 75% Solids (metalliferous)

    Requiring transport by expensive diaphragm or positive displacement pumps

    Consistency of toothpaste Requiring considerable management

    Centrifuging and filtration

    Solid-like Potentially transportable by conveyor or truck

    TAILINGS AND MINE WASTE 2014 14

  • Water Recovery from TSF

    Generally limited to recovery of supernatant water, plus seepage through wall

    Other tailings water is lost to: Entrainment within tailings Evaporation from decant pond and wet tailings Seepage into foundation

    In order to maximise recovery of supernatant water: Direct supernatant water to decant pond Minimise size of decant pond and rapid recovery Maintain decant pumps and water return pipelines

    TAILINGS AND MINE WASTE 2014 15

  • Post-Closure Tailings Water Balance and Quality

    TAILINGS AND MINE WASTE 2014 16

  • Post-Closure Tailings Water Balance and Quality

    RR = SO + EW + SE + SF + SW RR = TSF catchment rainfall and runoff SO = spillway overflows EW = entrained water SE = surface evaporation SF = seepage into foundation SW = seepage through wall

    TAILINGS AND MINE WASTE 2014 17

  • Downstream vs. Upstream TSF Wall Raising

    Typically, TSF walls initially constructed as starter dams using borrow material

    Wall raising can be: Downstream using borrow material Upstream partially on desiccated tailings using

    borrow material and/or tailings, if suitable

    2 m downstream wall raise

    2 m high upstream raise

    TAILINGS AND MINE WASTE 2014 18

  • Upstream Wall Raising using Tailings

    Harvesting tailings

    Completed raise Compacting tailings

    Moisture-conditioning

    TAILINGS AND MINE WASTE 2014 19

  • Excessive Wall Settlement due to Borrow Pit being Infilled with Slimes

    Failure

    Resulting kink

    TAILINGS AND MINE WASTE 2014 20

  • Amphibious Excavator, Amphirol and D6 Swamp Dozer

    Parked Amphirol

    D6 Swamp Dozer

    Amphibious Excavator

    TAILINGS AND MINE WASTE 2014 21

  • Principles of Farming Tailings by Amphirol

    In good weather in a dry climate, farming can be achieved in a month-long cycle

    Amphirols exert 3 to 5 kPa bearing pressure (c.f. ~35 kPa for a D6 Swamp Dozer)

    Some surface drying and strengthening is required to allow safe and efficient amphirol operation

    Too heavy a bearing pressure and/or too soft a tailings surface leads to bogging

    TAILINGS AND MINE WASTE 2014 22

  • Principles of Farming Tailings by Amphirol

    An amphirol should: Essentially float on lightly desiccated surface Create trenches down beach to facilitate surface

    drainage Maximise surface area exposed to evaporation

    and strengthening Expose un-desiccated tailings on further farming

    An amphirol should not over-shear tailings by repeated farming, ~4 passes is optimal

    TAILINGS AND MINE WASTE 2014 23

  • Amphirols Dont Float!

    TAILINGS AND MINE WASTE 2014 24

  • Subsequent Farming by D6 Swamp Dozer

    A D6 Swamp Dozer (bearing pressure of ~35 kPa) can be used once tailings have gained sufficient shear strength and bearing capacity to safely support it

    A dozer may be used after amphirolling or simply after tailings has desiccated naturally on exposure

    Dozing improves already desiccated tailings by compaction, leading to a further increase in dry density and shear strength TAILINGS AND MINE WASTE 2014 25

  • Schematic Slurried Tailings Shear Strength Profiles with Depth

    Self-weight + Amphirol +2 m Fill + Desiccation

    Desiccation and fill are most effective for consolidation and strengthening

    TAILINGS AND MINE WASTE 2014 26

  • Safe Fill Height Placed with a D6 Swamp Dozer

    Conventional bearing capacity analysis gives:

    H = Nc.sv /F.fill - He ~ 0.143 sv - 1 H = safe fill height (m) Nc = bearing capacity factor (~5.14 for a strip) sv = appropriate (vane) shear strength (kPa) F = appropriate factor safety (perhaps ~2) fill = unit weight of fill (~18 kN/m3) He = equivalent height represented by D6 Swamp Dozer (~1 m)

    TAILINGS AND MINE WASTE 2014 27

  • Strength Gain due to Fill Placement

    Peak shear strength of loaded tailings will increase as it drains, according to:

    = .tan , up to 18 H.tan 30o or 10 H = Increase in peak shear strength = Increase in effective stress due to fill loading, up to fill height H x Unit weight of fill (~18 kN/m3) = Drained friction angle of tailings ~30o

    TAILINGS AND MINE WASTE 2014 28

  • Capping Wet and Dry Tailings

    Hydraulic capping of soft, wet tailings

    Thin lifts and desiccation to facilitate capping

    TAILINGS AND MINE WASTE 2014 29

  • Capping Tailings

    Bow-wave failure

    Pushing shallow fill on a broad front Surcharging edge

    Bearing capacity failure

    TAILINGS AND MINE WASTE 2014 30

  • Covers over Reactive Tailings

    Rainfall runoffEvapotranspiration

    from vegetated surface

    Rainfall

    Nominal 0.5 m compacted seal, if required

    Minor net percolation Construction platform/capillary break, if required

    Limited oxygendiffusion and

    net percolation PAF or saline tailings

    Seepagealong ~1% slope Infiltration and storage

    Nominal 1 m of growth medium

    Evaporationfrom ponded water

    Evapotranspirationfrom vegetated surface

    Rainfall

    Infiltration and storage

    Nominal 0.5 m compacted seal, if required

    Minor net percolation Construction platform/capillary break, if required

    Limited oxygendiffusion and

    net percolation PAF or saline tailings

    Seepagealong ~1% slope

    Nominal 1 to 2 m ofloose, rocky soil mulch

    Rainfall-shedding Wet climates Store and release Dry climates

    TAILINGS AND MINE WASTE 2014 31

  • Conclusions

    Good tailings deposition and tailings water management can achieve optimal water recovery and maximise tailings dry density, which will: Minimise tailings storage volume required and minimise

    wall raises Possibly allow upstream wall raising on tailings, potentially

    using tailings to construct raise Facilitate closure

    Soil mechanics principles underlie dewatering, densification and strengthening of tailings

    TAILINGS AND MINE WASTE 2014 32

    Slide Number 1Slide Number 2OverviewConstraints under which TSFs Must OperateGood Tailings ManagementGood Tailings ManagementOperational Tailings Water BalanceOperational Tailings Water BalanceOperational Tailings Water BalanceOperational Tailings Water Balance An Australian ExampleTailings Continuum(Davies, 2004)Consistency of TailingsTransporting Filtered TailingsIn-Plant Recovery of Tailings WaterWater Recovery from TSFPost-Closure Tailings Water Balance and QualityPost-Closure Tailings Water Balance and QualityDownstream vs. Upstream TSF Wall RaisingUpstream Wall Raising using TailingsExcessive Wall Settlement due to Borrow Pit being Infilled with SlimesAmphibious Excavator, Amphirol and D6 Swamp DozerPrinciples of Farming Tailings by AmphirolPrinciples of Farming Tailings by AmphirolAmphirols Dont Float!Subsequent Farming by D6 Swamp DozerSchematic Slurried Tailings Shear Strength Profiles with DepthSafe Fill Height Placed with a D6 Swamp DozerStrength Gain due to Fill PlacementCapping Wet and Dry TailingsCapping TailingsCovers over Reactive TailingsConclusions