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Controls governing the spatial distribution of sediment arsenic concentrations and solid-phase speciation in a lake impacted by legacy mining pollution

Forty-seven sediment cores were collected as part of a spatial survey of Long Lake, Yellowknife, NWT, Canada to elucidate the physical and geochemical controls on the distribution of arsenic (As) in sediments impacted by the aerial deposition of arsenic trioxide (As2O3) from ore roasting at legacy g...

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Bibliographic Details
Published in:The Science of the total environment 2019-03, Vol.654, p.563-575
Main Authors: Schuh, Christopher E., Jamieson, Heather E., Palmer, Michael J., Martin, Alan J., Blais, Jules M.
Format: Article
Language:English
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Summary:Forty-seven sediment cores were collected as part of a spatial survey of Long Lake, Yellowknife, NWT, Canada to elucidate the physical and geochemical controls on the distribution of arsenic (As) in sediments impacted by the aerial deposition of arsenic trioxide (As2O3) from ore roasting at legacy gold mines. High-resolution profiles of dissolved As in bottom water and porewater were also collected to determine As remobilization and diffusion rates across the sediment-water interface. Arsenic concentrations in Long Lake sediments ranged from 2.2 to 3420 mg kg−1 (dry weight). Two distinct types of sediment As concentration profiles were identified and are interpreted to represent erosional and depositional areas. Water depth is the best predictor of As concentration in the top 5 cm of sediments due to the inferred focusing of fine-grained As2O3 into deeper water. At greater sediment depths, iron (Fe) concentration, as a likely indicator of As, Fe, and sulphur (S) co-diagenesis, was the best predictor of As concentration. The sediments are a source of dissolved As to surface waters through diffusion-controlled release to bottom water. Arsenic concentrations, solid-phase speciation, and diffusive efflux varied laterally across the lake bottom and with sediment depth due to the interplay between sediment-focusing processes and redox reactions, which has implications for human health and ecological risk assessments. [Display omitted] •Controls on the spatial distribution of As in mining-impacted lake sediments were investigated.•Sediment cores and profiles of dissolved As in porewaters and bottom waters were collected.•Sediment As concentrations, solid-phase speciation, and diffusive fluxes vary spatially.•Spatial variability results from sediment focusing and its potential influence on As diagenesis.
ISSN:0048-9697
1879-1026
DOI:10.1016/j.scitotenv.2018.11.065