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This report examines the history of arsenic pollution from Giant Yellowknife Gold Mine, and its environmental and public health impacts. It is based on extensive archival research in national and territorial archives, as well as oral histories (published and unpublished) and a review of public reports on the issue. Operating from 1948 to 2004, Giant Mine produced over 7 million ounces of gold mined from arsenopyrite ore formations located on the north shore of Yellowknife Bay. Gold processing entailed roasting the ore, producing as a byproduct arsenic trioxide dust, a highly toxic form of arsenic. In the early 1950s, arsenic emissions from Giant and Con mines totalled an estimated 22,000 lbs. per day. Though Con mine installed a scrubber in 1949, Giant mine (the source of most of the arsenic) did not install pollution control equipment until the end of 1951, after a Dene child died of acute arsenic poisoning at Latham Island. Local livestock also died as from arsenic poisoning. Government and mine officials met at the time to discuss how to address the problem of arsenic pollution, but never contemplated even a temporary shutdown of the mine. The capture of arsenic using a Cottrell Electrostatic Precipitator reduced but did not eliminate arsenic. Collection rates were further improved by the installation of a baghouse in 1958. Studies undertaken through the 1950s and 1960s revealed persistent high levels of arsenic on local produce and berries. Concerns remained about water pollution from both atmospheric deposition and arsenic- and cyanidelaced tailings effluent. The collection of arsenic, , also resulted in the fateful decision to store arsenic trioxide dust in underground chambers and mined-out stopes. Today, the 237,000 tonnes of arsenic trioxide underground at Giant remains the central environmental challenge for the reclamation and remediation of the site. Public health studies undertaken in the 1960s suggested a possible link between arsenic exposure and elevated cancer rates in Yellowknife, but these studies were not made public until the 1970s. A series of independent and government studies followed these revelations as public concern mounted over the health effects of long-term arsenic exposure. Further reductions in arsenic emissions from Giant were achieved, and the mine constructed a tailings effluent treatment system in 1981. While local activists raised concerns about sulphur dioxide and arsenic emissions in the early 1990s, territorial government studies concluded these emissions did not pose a public health risk. For the Yellowknives Dene First Nation in particular, memories of mine development and subsequent arsenic pollution of their traditional lands are painful. Some Dene worked at the mine, but the communities of Ndilo and Dettah saw few benefits from the mines overall. Yet these communities, due to their location in relation to Giant, were on the front line of arsenic exposure over the half-century ofits operation. The Yellowknives Dene not only suffered disproportional health impacts from arsenic pollution, but also the loss of harvesting areas due to the appropriation of land for the mining operations and urban growth in the city of Yellowknife.
|Item Type:||Report (Project Report)|
|Department(s):||Humanities and Social Sciences, Faculty of > Geography
Humanities and Social Sciences, Faculty of > History
|Date:||8 August 2012|
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