2014 GSA Annual Meeting in Vancouver, British Columbia (19–22 October 2014)

Paper No. 78-3
Presentation Time: 1:35 PM

INFLUENCE OF OCEANIC FORCING ON NUTRIENT PROCESSING IN A NEARSHORE AQUIFER


ROBINSON, Clare E. and ANWAR, Nawrin, Department of Civil and Environmental Engineering, The University of Western Ontario, Spencer Engineering Building, London, ON N6A 5B9, Canada

The role of the nearshore subterranean estuary in regulating nutrient fluxes to coastal waters is well recognized. Complex interacting physical flow and biogeochemical processes determine whether a nearshore subterranean estuary will be a net source or sink of nitrogen (N) and phosphorous (P). A numerical model was applied to evaluate the influence of varying oceanic forcing (tides and waves) on the nutrient biogeochemistry in a permeable homogeneous nearshore aquifer. Simulations were performed using the variable-density groundwater flow model SEAWAT-2005 combined with the reactive multi-component transport model PHT3D v2.10. The model considered the transport and transformation of both marine- and land-derived chemical species (NH4+, NO3-, PO43-, Fe2+, DOM and O2). Reactions considered include DOM oxic mineralization, nitrification, denitrification, Fe oxidation, and P adsorption. Varying DOM concentrations and mineralization rates were also examined for the different oceanic conditions simulated.

Although steady wave forcing caused higher seawater recirculation, tides led to greater seawater-freshwater mixing in the nearshore aquifer and subsequently greater transformation of land-derived nutrients. Nutrient processing was strongly controlled by the availability and reactivity of marine DOM as its degradation consumed O2, released inorganic N and P, and altered redox conditions in the salt-freshwater mixing zones. For the simulations without marine DOM considered, NO3- discharge to the sea increased by 32% for the tidal case (A = 0.5 m) compared to only 13% and 8% for the wave (Hrms = 1 m) and no oceanic forcing cases. With labile marine DOM considered, the NO3- discharge decreased by 90% relative to the land-derived flux for the tidal case (A = 0.5 m). For all simulations PO43- removal was high due to adsorption to Fe oxide minerals that precipitated along redox boundaries in the subterranean estuary.