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The open pit mining of coal results in the formation of new landforms constructed from<br />

waste rock. Rock drains, either constructed or formed during dumping by natural segregation,<br />

underlie some of these landforms. Constructed rock drains are often designed to convey<br />

surface water from higher in the watershed through the waste rock dumps. Rock drains also<br />

collect water moving through the waste rock and convey it to adjacent surface and ground<br />

water. Long-term monitoring of the chemistry of water conveyed by rock drains provides<br />

an opportunity to characterize the rates of flushing of these constituents through the waste<br />

rock piles. In this study, a conceptual model for the long-term release of nitrate (NO 3<br />

), selenium<br />

(Se), and sulfate (SO 4<br />

) from coal waste rock piles is developed and used to interpret<br />

monitoring data from eleven rock drains of varying ages in the Elk Valley, British Columbia.<br />

The hypothesis of the conceptual model is that the flushing of the first pore volume of water<br />

within the waste rock can be characterized by NO 3<br />

release. The NO 3<br />

is derived from blasting<br />

and is considered to be a conservative species. The first pore volume will also contain SO 4<br />

and<br />

Se generated by oxidation of waste rock during blasting and pile construction. Post-depositional<br />

oxidation and production of SO 4<br />

and Se are identified by the evolution of the effluent<br />

signature from an initial SO 4<br />

/NO 3<br />

ratio, representative of the initial pore fluid at deposition,<br />

to an increasing SO 4<br />

/NO 3<br />

ratio as the initial pore volume is released and Se and SO 4<br />

are<br />

produced by oxidation. This hypothesis is tested by interpreting the patterns of NO 3<br />

, SO 4<br />

,<br />

and Se release as described by SO 4<br />

/ NO 3<br />

and Se/SO 4<br />

ratios. In cases where upstream sources<br />

are contributing to the observed flow and concentrations within the rock drain, an attempt<br />

is made to correct the monitoring data so that it represents only the contribution from the<br />

waste rock overlying the rock drain. The concentrations of NO 3<br />

and SO 4<br />

were found to<br />

correspond to differences in the chronology of waste rock placement, while the Se/SO 4<br />

ratios<br />

were relatively constant and consistent with ratios associated with oxidation. A model of the<br />

evolution of the effluent chemistry was developed using a system dynamics model comprised<br />

of stocks (water storage) and flows (flushing) within blocks of waste rock placed at various<br />

times within a watershed. The model illustrates how stored water volumes, rates of flushing,<br />

production rates, dump chronology, and, where applicable, upstream sources control the<br />

evolution of rock drain chemistry over time. The goal of this work is to develop methods of<br />

evaluating the impact that various dump designs might have on the timing and magnitude<br />

of NO 3<br />

, Se, and SO 4<br />

releases.<br />

110 - Characterisation of physical mass transport through oil<br />

sands fluid fine tailings in an end pit lake: a multi-tracer study<br />

Kathryn Dompierre & Lee Barbour<br />

Department of Civil and Geological Engineering - University of Saskatchewan, Saskatoon,<br />

Saskatchewan, Canada<br />

The first end pit lake in the Athabasca oil sands region has been developed by Syncrude<br />

Canada Ltd. as part of their closure design for the Mildred Lake Mine site, 40 km north of<br />

Fort McMurray. The end pit lake, referred to as Base Mine Lake, was constructed within a<br />

mined-out pit, and incorporates 186 Mm 3 of fluid fine tailings (FFT) below an 8 m water<br />

cap. Fluid fine tailings are a dense fluid with dispersed, suspended solids, residual bitumen<br />

and elevated TDS (Siddique et al., 2007). Chemical constituents of concern may move<br />

IAH-CNC 2015 WATERLOO CONFERENCE<br />

119

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