Abstracts
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Steven G. Shikaze & Benjamin L. Bolger<br />
Matrix Solutions Inc., Breslau, Ontario, Canada<br />
Mark King<br />
Groundwater Insight Inc., Halifax, Nova Scotia, Canada<br />
Hector Maya<br />
Rockwood Lithium Ltd., Santiago, Chile<br />
Catalina Orb, Jorge Garcia Tascon, & Jaime Solari<br />
SGA, Santiago, Chile<br />
The Salar de Atacama contains one of the world’s largest lithium brine deposits. The<br />
salar (dry salt lake) is located in the Andes in northern Chile, approximately 1,500 km<br />
north of Santiago, near the Chile/Argentina/Bolivia border. Lithium is mined from the<br />
salar by extracting (via pumping) the high salinity brine (over 300,000 mg/L total dissolved<br />
solids) from the geologic materials in the nucleus of the salar. Around the border<br />
of the nucleus, shallow lagoons are a nesting habitat for migratory flamingos, and therefore,<br />
pumping of the brines in the nucleus must consider the potential impact on water<br />
levels at these lagoons.<br />
To examine this impact in the nucleus, a numerical model study has been carried out.<br />
Because the lithium-rich brines in the salar have a fluid density much higher than the<br />
surrounding fresher water, the program SEAWAT was used to simulate brine pumping<br />
in the nucleus, and its effect on (1) the groundwater levels around the lagoons, and (2)<br />
the location of the brine-freshwater interface. The SEAWAT model, which was developed<br />
in parallel with a three-dimensional MODFLOW model for groundwater flow,<br />
was used to examine the sensitivity of model parameters such as hydraulic conductivity<br />
(K), recharge (which is very low over the nucleus), and evaporation (which is very high).<br />
285 - A review of key groundwater issues, eight years after<br />
the start of dewatering at the Victor Diamond Mine, James Bay<br />
Lowlands, Ontario<br />
Simon Gautrey<br />
Amec Foster Wheeler, Hamilton, Ontario, Canada<br />
The Victor Diamond Mine is an open pit mine located in the James Bay Lowlands, approximately<br />
90 km west of the community of Attawapiskat and 120 km east of the Ring of<br />
Fire. The mine is surrounded by contiguous wetlands that extend for thousands of square<br />
kilometers. The limestone bedrock at the site is prone to karst development and the mine is<br />
located within a few kilometers of two rivers, one of which, the Attawapiskat River, is more<br />
than 500 m wide. This submission will review two key issues related to impacts of dewatering<br />
to the wetlands and rivers that were raised as concerns prior to the start of mining and<br />
compare them to observed conditions after eight years of dewatering.<br />
From the beginning, it was known that mining would require large scale dewatering. Both<br />
the mine investors and the Attawapiskat First Nation, on whose traditional lands the mine<br />
is located, needed to know how much dewatering was going to be required and what<br />
IAH-CNC 2015 WATERLOO CONFERENCE<br />
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