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Lower Athabasca River System

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The Lower Athabasca River (LAR), in northern Alberta, Canada, begins north of Fort McMurray and flows to the Athabasca Delta and Lake Athabasca. Throughout its course, the river cuts through natural bitumen deposits, (Conly et al. 2002) and runs adjacent to the Oil-Sands developments. Fine cohesive sediments and associated chemical constituents such as metals and polycyclic aromatic hydrocarbons (PAHs) play an important role in the LAR ecosystem (Ghosh et al. 2000, Garcia-Aragon et al. 2011). Therefore, there is a great demand to characterize the contribution of bitumen deposits to the sediments and chemicals in Athabasca River system. Experimental assessment of cohesive sediment deposition dynamics in Athabasca River and tributaries has been …show more content…

The focus of most of the previous studies has been based on limited measured data and mostly during the open-water season. Therefore, the Canada-Alberta Joint Oil-Sands Monitoring Program (2012) identified a need for a more systematic and comprehensive quantification and modeling of the sources, transport, flux, and fate of materials and chemical constituents entering the Lower Athabasca watersheds. To achieve this objective, there was a requirement to develop a reliable integrated hydrodynamic, sediment transport and water quality models of the …show more content…

The proposed numerical frame work for the study is summarized in Figure 1. A one-dimensional (1D) model is used for large-scale long-term simulation of flow hydrodynamics and sediment transport patterns in the LAR. Furthermore, a 1D ice model is used to predict the winter ice coverage and its effect on the river flow characteristics; however, other ice processes (such as ice breakup) are not taken into account. The results of the ice model are used to modify the sediment transport and hydrodynamic models to account for the effect of winter ice-cover. The sediment transport simulations serve as the basis for setting up contaminant transport models for a selection of three PAH (pyrene (PY), phenantrene (Ph), and C1- Benz[a]anthracenes/Chrysenes (BAC1)) and three metal (lead (Pb), arsenic (As) and vanadium (V)) constituents. The validated models are also applied to investigate the effect of some hypothetical pollution scenarios on the water column concentration of two selected chemicals, pyrene (PY) and lead (Pb) within the

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