Abstracts
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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