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by Brayden McNeill
Institution: | University of Waterloo |
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Year: | 2016 |
Keywords: | waste rock; sulfide oxidation; acid rock drainage; acid mine drainage; mine waste; acid rock drainage microbiology |
Posted: | 02/05/2017 |
Record ID: | 2117677 |
Full text PDF: | http://hdl.handle.net/10012/10861 |
Four of the historic waste rock stockpiles (WRS1-#4) at the Detour Lake mine site were studied to determine the potential for generation of acid rock drainage (ARD). The stockpiles were constructed during the original mine operations (1983 - 1999) and were covered with 1 - 1.5 m of local overburden in 2000 to provide a reclamation cover. Waste rock was composed primarily of plagioclase, horneblende, quartz and clinochlore, with small amounts of biotite. The principal sulfide minerals identified were pyrite and pyrrhotite, with small amounts of chalcopyrite and covellite. Measurements of sulfur content ranged from 0 - 2.2 wt. %, whereas the carbon content ranged from 0 - 2.5 wt. %. The neutralization potential ratios (NPR) of WRS#1 and WRS#2 ranged from 0 - 61.1 with an average of 1.6 and 0.7 in profile excavation samples. Over 50 % of samples from WRS#1 and WRS#2 were potential acid generating (PAG). WRS#3 and WRS#4 were slightly less sulfidic resulting in average NPR of 43 and 10, respectively. None of the samples from WRS#3 were PAG, and 45 % of WRS#4 samples were PAG. The hydrology of the piles is typical of waste rock piles, with a large unsaturated zone. The water tables at WRS#3 and WRS#4 are approximately 16 and 22 mBGS, respectively. The waste rock is usually near residual saturation (5 vol. %), but the passage of wetting fronts commonly increased moisture content to near matrix saturation (~25 vol. %). The cover material retains more moisture than the waste rock, and usually 10 - 20 vol. %. Thermal profiles indicate that both stockpiles remain > 0 ˚C throughout the year, except within the cover. Seasonal fluctuations in temperature are dampened and delayed with greater depth in the stockpile, except near the edge of WRS#4 where the cover was damaged suggesting the cover plays a role in regulating the temperature of the stockpiles. Air-permability testing of the cover material and waste rock indicates that the cover material impedes advective gas and heat flow. Waste rock at WRS#3 and WRS#4 had air-permeability coefficients of 10-9 - 10-10 m2, whereas the cover material had air-permeability coefficients of approximately 10-11 m2 indicating that air flow through the cover is primarily by diffusion. This observation is in agreement with pore-gas trends at WRS#3 which show O2 depletion and CO2 enrichment with depth. Pore gas at WRS#4 is at atmospheric concentrations throughout, since the destruction of the cover material has removed the barrier to advective gas flow. The results of pore-gas monitoring indicate that the installation of a simple, unengineered cover made from local material may be a cost-effective tool in the management of sulfide oxidation and potential ARD generation at this site. Pore-water quality at WRS#3 and WRS#4 is characterized as neutral mine drainage, and compares favourably to other neutral mine drainage sites. The pore-wate throughout WRS#3 and WRS#4 is neutral pH. Concentrations of SO42- between 200 and 1500 mg/L are caused by sulfide oxidation. Circumneutral pH and depletion…
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