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24-MMP-A5 Surface Mining Methods and Design · May 2013

Question 12 of 13: Mine Closure, Reclamation and Bond Financing

Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)

Notes on this paper

EGBC National Exam — Mining and Mineral Processing Engineering, 09-Mmp-A5 Surface Mining Methods and Design, 2013-May. 3 hours duration; one handwritten 8.5×11 in reference sheet permitted (not an open-book exam); only approved Sharp or Casio calculators allowed. Question 1 is compulsory (40 marks, parts 1.1–1.7); candidates then select FOUR of the six optional Questions 2–7 (15 marks each) to complete the paper.

Reference texts: Hartman & Mutmansky, SME Mining Engineering Handbook, 3rd ed. (dewatering, slope stability classification, dragline stripping geometry, truck dispatch, mine closure); Hustrulid, Kuchta & Martin, Open Pit Mine Planning and Design (moving-cone and Lerchs–Grossmann pit optimization, capital-cost estimating, truck-shovel match factor); Lerchs, H. & Grossmann, I.F. (1965) “Optimum Design of Open-Pit Mines,” CIM Bulletin (the graph-theoretic 2-D worked example this question is drawn from); O’Hara, T.A. (1980) “Quick Guides to the Evaluation of Orebodies,” CIM Bulletin, Feb. 1980, and Mular, A.L. & Poulin, R. (1998) CANCOST, CIM Special Volume 47 (capital-cost formulae); Bieniawski, Z.T. (1989) Engineering Rock Mass Classifications (RMR system).

Question 6: Mine Closure, Reclamation and Bond Financing (15 marks)

Question text not reproduced: the examination questions are © Engineers and Geoscientists BC. Open the official past paper (linked at the top of this page) to read the question, then follow the worked solution below.

Given.

QuantityValue
Reclamation cost, today’s dollars$1,000,000
Mine plan life10 years
Inflation rate (reclamation cost escalation)6% / year
Sinking-fund (government-secured bond) rate2% / year
Actual closureYear 4 (bankruptcy), disturbance as per full 10-year plan

6.1 – Elements of a mine closure plan (3 marks, essay). A comprehensive closure plan integrates physical, chemical/water-quality, biological and socio-economic elements, developed and costed from the earliest feasibility stage rather than only at end of life:

Re-vegetation/re-foresting of contoured waste dumps. Dump slopes are first re-graded to a stable, erosion-resistant angle (well below the material’s angle of repose, with benching/terracing on tall dumps), covered with a growth-medium layer (topsoil, or an engineered soil substitute where topsoil was not salvaged), and seeded/planted with a native species mix selected for the local climate and for early soil-stabilizing root structure, progressing toward the target end land use (forestry, range, wildlife habitat).

Acid-drainage remediation. Where waste or tailings contain sulphide minerals, closure must prevent or treat Acid Rock Drainage (ARD): source control (blending/encapsulating reactive material, engineered low-permeability or water covers to exclude oxygen), collection and treatment of any drainage that does form (active lime treatment or passive systems such as constructed wetlands/bioreactors), and long-term water-quality monitoring, since ARD can persist and require management for decades after mining ends.

Tailings-dam re-vegetation and species selection. The dam’s outer (downstream) slopes are reclaimed similarly to a waste dump, but species selection must additionally tolerate the tailings’ often poor structure, low nutrient content and any residual process chemistry (metals, pH); a nurse-crop of fast-establishing, tolerant species is typically used first to build organic matter before a longer-term native cover is introduced.

Reclamation of the tailings-pond “slimes” area. The fine, saturated, low-strength slimes at the centre of a tailings impoundment cannot support conventional re-grading or planting until they consolidate and dewater (often requiring engineered surface drainage, wick drains, or a dry cover system placed once a trafficable crust has formed), and are frequently the last portion of a tailings facility to be finally closed.

Restoring agricultural capability. Where the approved post-mining land use is agriculture, closure must salvage and stockpile topsoil separately from subsoil during operations, replace soil horizons in the correct order and to sufficient depth on re-graded land, and de-compact and amend the re-placed soil (organic matter, fertility) to restore workable, productive capability rather than simply a vegetated surface.

Abandoned pit as a fish-bearing lake, and alternatives. Where hydrogeology and water quality allow, a permanently flooded pit can be developed into a stable lake with graded, vegetated littoral (shallow-water) margins, appropriate depth and thermal stratification, and stocked or naturally colonized with fish once water quality is confirmed suitable – this requires managing final pit-wall stability below the waterline and confirming the water balance will maintain lake level. Where water quality (e.g. ARD-affected) or hydrogeology make this unsuitable, alternatives include partial backfill to reduce final pit depth and highwall exposure, engineered permanent covers/exclusion fencing to manage a non-fish-bearing water body safely, or, less commonly, complete backfill to a safe landform with no permanent water body at all.

Approach. Work the reclamation-bond financing chain sequentially: inflate today’s reclamation estimate to the target year (time value of money, future value); size the annual sinking-fund payment needed to accumulate that inflated lump sum; then re-run both the liability and the fund balance at the actual (premature) closure year to find the taxpayer shortfall.

  1. 6.2.1 – reclamation cost inflated to year 10. $$FV_{10} = P(1+i_{infl})^{n} = 1{,}000{,}000\times(1.06)^{10} = \boxed{\$1{,}790{,}848}$$
  2. 6.2.2 – annual sinking-fund deposit for that lump sum at year 10. Using the sinking-fund factor at the government bond rate $i=2\%$: $$A = FV_{10}\left[\frac{i}{(1+i)^n-1}\right] = 1{,}790{,}848\left[\frac{0.02}{(1.02)^{10}-1}\right] = \boxed{\$163{,}552/\text{year}}$$
  3. 6.2.3 – reclamation liability in year-4 dollars. The disturbance at year 4 equals the full 10-year-plan disturbance (per the question), so the liability is today’s $1M estimate inflated only 4 years (not pro-rated by disturbance extent): $$FV_4 = 1{,}000{,}000\times(1.06)^4 = \boxed{\$1{,}262{,}477}$$
  4. 6.2.4 – sinking-fund balance actually accumulated by year 4. Four annual deposits of the 6.2.2 amount, compounded at the 2% government rate: $$FV_{fund,4} = A\left[\frac{(1+i)^4-1}{i}\right] = 163{,}552\left[\frac{(1.02)^4-1}{0.02}\right] = \boxed{\$674{,}097}$$
  5. 6.2.5 – taxpayer shortfall at year 4. $$\text{Shortfall} = FV_4 - FV_{fund,4} = 1{,}262{,}477 - 674{,}097 = \boxed{\$588{,}380}$$ The fund, sized to mature gradually over the full planned 10-year life, has only reached 53% of the year-4 liability when the mine fails prematurely – the taxpayer (through the regulator’s reclamation security program) is left to cover the remaining $588,380.
ItemResult
6.2.1 Reclamation cost, year-10 dollars$1,790,848
6.2.2 Annual sinking-fund deposit$163,552/yr
6.2.3 Reclamation liability, year-4 dollars$1,262,477
6.2.4 Fund balance at year 4$674,097
6.2.5 Taxpayer shortfall at year 4$588,380

6.3 – A financial plan avoiding taxpayer liability (2 marks, essay). The structural flaw exposed above is that a gradually accruing sinking fund is, by construction, under-funded relative to the full closure liability for the entire early life of the mine – any closure before year 10 leaves a gap. Two changes together close it: (1) full up-front security – require the operator to post 100% of the current-dollar reclamation estimate (or a schedule reaching 100% within the first 2–3 years, not 10) as a bond, letter of credit or cash deposit before production begins, escalated annually for inflation and re-estimated periodically as the mine plan and disturbance footprint change, so the security held is never less than the current liability at any point in the mine’s life; and (2) third-party, regulator-held security (not an internal company reserve) so that it survives the company’s own bankruptcy and is immediately available to the regulator to complete reclamation, exactly the model BC and most Canadian jurisdictions now require under their mine reclamation security programs, precisely because the 1970s–80s-style gradually-accruing sinking fund modelled in 6.2 repeatedly left taxpayers with abandoned-mine liabilities like the one quantified above.

6.4 – Sustaining a mine-equipment/manufacturing industry after the mines close (3 marks, essay). A regional mine-equipment and fabrication industry that grew up serving a mining district’s specialized needs faces obsolescence once the local demand that shaped it disappears; sustaining it as a going concern requires deliberate diversification well before closure, on three fronts. Ownership of manufacturing plants (6.4.1) should shift from single-mine-captive ownership toward independent or multi-customer ownership structures (spin-off, employee ownership, or acquisition by a diversified equipment group) while the original mine can still provide transition revenue, so the plant is not simply liquidated with the mine. Training (6.4.2) must build transferable skills (precision fabrication, hydraulics, automation, welding to broad industrial codes) rather than single-customer-specific competence only, and actively place graduates and workers into other regional/export manufacturing sectors as local mine demand tapers. Remaining leading-edge (6.4.3) is the hardest challenge named in the question – without a local demanding customer pushing continuous innovation, a plant can slide from leading-edge to merely up-to-date to outdated; the answer is deliberately seeking export customers and international technology partnerships (or licensing) that keep imposing the same competitive pressure a large local mine once did, rather than assuming the existing product line remains competitive indefinitely on its own momentum. Achieved example (6.4.4): Sudbury, Ontario’s mining-supply and services cluster diversified from single-district (INCO/Falconbridge) captive fabrication into an internationally exporting mining-technology and services sector employing more people region-wide today than the original mines did at their peak, precisely by combining independent ownership, transferable-skills training and active export/technology partnerships. Failed example: numerous single-resource company towns (e.g. several coal or hard-rock mining towns across the Appalachian and prairie coalfields) that never diversified equipment/fabrication ownership or export markets saw their entire supporting manufacturing base close within the mine’s own closure, leaving sustained unemployment well above 20% and no transferable industrial base – the outcome the question specifically asks be contrasted against Sudbury’s success.

Check: Sudbury is used as the illustrative “achieved” case on the strength of its well-documented post-INCO/Falconbridge diversification into an export mining-supply cluster; a candidate’s own reference sheet may substitute any comparably documented regional example without changing the argument.