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Water quality impacts and river system recovery following the 2014 Mount Polley mine tailings dam spill, British Columbia, Canada. / Byrne, Patrick; Hudson-Edwards, Karen; Bird, Graham et al.
In: Applied Geochemistry, Vol. 91, 04.2018, p. 64-74.

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HarvardHarvard

Byrne, P, Hudson-Edwards, K, Bird, G, Macklin, M, Brewer, P, Williams, R & Jamieson, H 2018, 'Water quality impacts and river system recovery following the 2014 Mount Polley mine tailings dam spill, British Columbia, Canada', Applied Geochemistry, vol. 91, pp. 64-74. https://doi.org/10.1016/j.apgeochem.2018.01.012

APA

Byrne, P., Hudson-Edwards, K., Bird, G., Macklin, M., Brewer, P., Williams, R., & Jamieson, H. (2018). Water quality impacts and river system recovery following the 2014 Mount Polley mine tailings dam spill, British Columbia, Canada. Applied Geochemistry, 91, 64-74. https://doi.org/10.1016/j.apgeochem.2018.01.012

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MLA

VancouverVancouver

Byrne P, Hudson-Edwards K, Bird G, Macklin M, Brewer P, Williams R et al. Water quality impacts and river system recovery following the 2014 Mount Polley mine tailings dam spill, British Columbia, Canada. Applied Geochemistry. 2018 Apr;91:64-74. Epub 2018 Jan 31. doi: 10.1016/j.apgeochem.2018.01.012

Author

Byrne, Patrick ; Hudson-Edwards, Karen ; Bird, Graham et al. / Water quality impacts and river system recovery following the 2014 Mount Polley mine tailings dam spill, British Columbia, Canada. In: Applied Geochemistry. 2018 ; Vol. 91. pp. 64-74.

RIS

TY - JOUR

T1 - Water quality impacts and river system recovery following the 2014 Mount Polley mine tailings dam spill, British Columbia, Canada

AU - Byrne, Patrick

AU - Hudson-Edwards, Karen

AU - Bird, Graham

AU - Macklin, Mark

AU - Brewer, Paul

AU - Williams, Richard

AU - Jamieson, Heather

PY - 2018/4

Y1 - 2018/4

N2 - The Mount Polley mine tailings embankment breach on August 4th 2014, in British Columbia, Canada, is the second largest mine waste spill on record. The mine operator responded swiftly by removing significant quantities of tailings from the primary receiving watercourse, stabilizing the river corridor and beginning construction of a new river channel. This presented a unique opportunity to study spatial patterns of element cycling in a partially-restored and alkaline river system. Overall, water quality impacts are considered low with Cu, and to a lesser extent V, being the only elements of concern. However, the spatial pattern of stream Cu loading suggested chemical (dominant at low flow) and physical (dominant at high flow) mobilization processes operating in different parts of the watershed. Chemical mobilization was hypothesized to be due to Cu sulfide (chalcopyrite) oxidation in riparian tailings and reductive dissolution of Cu-bearing Fe oxides in tailings and streambed sediments whereas physical mobilization was due to erosion and suspension of Cu-rich stream sediments further downstream. Although elevated aqueous Cu was evident in Hazeltine Creek, this is considered a relatively minor perturbation to a watershed with naturally elevated stream Cu concentrations. The alkaline nature of the tailings and the receiving watercourse ensures most aqueous Cu is rapidly complexed with dissolved organic matter or precipitates as secondary mineral phases. Our data highlights how swift removal of spilled tailings and river corridor stabilization can limit chemical impacts in affected watersheds but also how chemical mobilization (of Cu) can still occur when the spilled tailings and the receiving environment are alkaline. We present a conceptual model of Cu cycling in the Hazeltine Creek watershed.

AB - The Mount Polley mine tailings embankment breach on August 4th 2014, in British Columbia, Canada, is the second largest mine waste spill on record. The mine operator responded swiftly by removing significant quantities of tailings from the primary receiving watercourse, stabilizing the river corridor and beginning construction of a new river channel. This presented a unique opportunity to study spatial patterns of element cycling in a partially-restored and alkaline river system. Overall, water quality impacts are considered low with Cu, and to a lesser extent V, being the only elements of concern. However, the spatial pattern of stream Cu loading suggested chemical (dominant at low flow) and physical (dominant at high flow) mobilization processes operating in different parts of the watershed. Chemical mobilization was hypothesized to be due to Cu sulfide (chalcopyrite) oxidation in riparian tailings and reductive dissolution of Cu-bearing Fe oxides in tailings and streambed sediments whereas physical mobilization was due to erosion and suspension of Cu-rich stream sediments further downstream. Although elevated aqueous Cu was evident in Hazeltine Creek, this is considered a relatively minor perturbation to a watershed with naturally elevated stream Cu concentrations. The alkaline nature of the tailings and the receiving watercourse ensures most aqueous Cu is rapidly complexed with dissolved organic matter or precipitates as secondary mineral phases. Our data highlights how swift removal of spilled tailings and river corridor stabilization can limit chemical impacts in affected watersheds but also how chemical mobilization (of Cu) can still occur when the spilled tailings and the receiving environment are alkaline. We present a conceptual model of Cu cycling in the Hazeltine Creek watershed.

UR - https://ars.els-cdn.com/content/image/1-s2.0-S0883292718300246-mmc1.docx

U2 - 10.1016/j.apgeochem.2018.01.012

DO - 10.1016/j.apgeochem.2018.01.012

M3 - Article

VL - 91

SP - 64

EP - 74

JO - Applied Geochemistry

JF - Applied Geochemistry

SN - 0883-2927

ER -