Abstract

Nitrogen and sulfur emissions from oil sands operations in northern Alberta, Canada have resulted in increasing deposition of N and S to the region’s ecosystems. To assess whether a changing N and S deposition regime affects bog porewater chemistry, we sampled bog porewater at sites at different distances from the oil sands industrial center from 2009 to 2012 (10-cm intervals to a depth of 1 m) and from 2009 to 2019 (top of the bog water table only). We hypothesized that: (1) as atmospheric N and S deposition increases with increasing proximity to the oil sands industrial center, surface porewater concentrations of NH4+, NO3−, DON, and SO42− would increase and (2) with increasing N and S deposition, elevated porewater concentrations of NH4+, NO3−, DON, and SO42− would be manifested increasingly deeper into the peat profile. We found weak evidence that oil sands N and S emissions affect bog porewater NH4+-N, NO3−-N, or DON concentrations. We found mixed evidence that increasing SO42− deposition results in increasing porewater SO42− concentrations. Current SO42− deposition, especially at bogs closest to the oil sands industrial center, likely exceeds the ability of the Sphagnum moss layer to retain S through net primary production, such that atmospherically deposited SO42− infiltrates downward into the peat column. Increasing porewater SO42− availability may stimulate dissimilatory sulfate reduction and/or inhibit CH4 production, potentially affecting carbon cycling and gaseous fluxes in these bogs.

Highlights

  • Peatlands, ombrotrophic bogs and minerotrophic fens, cover 365,157 k­ m2 across northern Alberta, Saskatchewan, and Manitoba, Canada, with non-permafrost bogs covering 27,397 ­km2 of the high boreal and midboreal regions (Vitt et al, 2000)

  • We found only weak evidence that bog porewater ­NH4+-N, ­NO3−-N, or DON concentrations at the top

  • Page 15 of 19 766 of the bog water table are strongly affected by N emissions from oil sand operations at this time

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Summary

Introduction

Ombrotrophic bogs and minerotrophic fens, cover 365,157 k­ m2 across northern Alberta, Saskatchewan, and Manitoba, Canada, with non-permafrost bogs covering 27,397 ­km of the high boreal and midboreal regions (Vitt et al, 2000). Most of these peatlands have persisted over 6000–7000 years (Halsey et al, 2000) in areas of minimal human disturbance in a boreal continental climate with low atmospheric deposition of N and S (< 2 kg N or S ­ha−1 ­year−1). These emissions have led to wet and dry N and S deposition that is highest nearest to the oil sands industrial center and decreases with distance (Edgerton et al, 2020; Fenn et al, 2015; Hsu et al, 2016; Wieder et al, 2016a, b)

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