2021
DOI: 10.1016/j.envpol.2021.117723
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Quantifying arsenic post-depositional mobility in lake sediments impacted by gold ore roasting in sub-arctic Canada using inverse diagenetic modelling

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Cited by 12 publications
(6 citation statements)
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“…Trapping of As in the oxic zone leads to As accumulation in the iron oxide layer (up to 0.3 μmol As g −1 ) near the SWI ( Figure 2B ). Other studies have reported similar concentrations of particulate As in the top layer of coastal sediments (Mucci et al, 2000 ; Chaillou et al, 2003 ), higher concentrations are generally found in contaminated marine (0.4–0.7 μmol As g −1 ; Chaillou et al, 2003 ) and lake sediments (up to 15 μmol As g −1 ; Barrett et al, 2019 ; Leclerc et al, 2021 ).…”
Section: Resultsmentioning
confidence: 60%
See 1 more Smart Citation
“…Trapping of As in the oxic zone leads to As accumulation in the iron oxide layer (up to 0.3 μmol As g −1 ) near the SWI ( Figure 2B ). Other studies have reported similar concentrations of particulate As in the top layer of coastal sediments (Mucci et al, 2000 ; Chaillou et al, 2003 ), higher concentrations are generally found in contaminated marine (0.4–0.7 μmol As g −1 ; Chaillou et al, 2003 ) and lake sediments (up to 15 μmol As g −1 ; Barrett et al, 2019 ; Leclerc et al, 2021 ).…”
Section: Resultsmentioning
confidence: 60%
“…However, the dAs concentrations observed here are about four times lower than previously found in North-Sea sediments, where e-SOx was the dominant process (van de Velde et al, 2017 ). They are also lower than in deltaic sediments that sustain an active iron cycle (Sullivan and Aller, 1996 ) and contaminated lake sediments (Barrett et al, 2019 ; Leclerc et al, 2021 ), where pore water dAs can reach up to 2 μM (and sometimes up to 10 μM). Just below the zone of As release, the pore water showed a zone with strong dAs consumption, which corresponded to the interface between the ferruginous and the sulphidic pore water.…”
Section: Resultsmentioning
confidence: 95%
“…Inverse diagenetic modelling was used to objectively constrain uxes of solutes across the sediment-water interface. 65,66 Porewater proles were modelled assuming the absence of signicant advective ux and at steady state (i.e., d C /dt ¼ 0). The onedimensional mass conservation equation provided by Boudreau 1997 67 at steady state was solved using the computer code PROFILE 68 using sediment porosity and the elements' diffusion coefficients as inputs, to yield uxes of La, P, and Fe across the sediment-water interface (SWI) at the three sampling sites.…”
Section: Flux Calculations Across the Sediment-water Interfacementioning
confidence: 99%
“…Inverse diagenetic modelling was used to objectively constrain fluxes of solutes across the sediment-water interface 65,66 . Porewater profiles were modelled assuming the absence of significant advective flux and at steady state (i.e., δC/δt = 0).…”
Section: Flux Calculations Across the Sediment-water Interfacementioning
confidence: 99%