Bio-optics and fate of terrestrial CDOM as key issues in biogeochemical modelling of Arctic and subarctic coastal seas Le Fouest1* V., B. Zakardjian2, F. J. Saucier3, Z.-P. Mei3, D. Lefaivre4, S. Bélanger5, and M. Babin6 Faced with the challenges of global change and sustainable development, modern oceanography has seen the emergence of new observation and predictive tools. In the past two decades, remote sensing and numerical modelling have evolved considerably to infer oceanic variability with a high spatial and temporal resolution hard to achieve with field surveys alone. This is a key issue for understanding the carbon cycle, especially in productive coastal waters which are impacted by human induced eutrophication. Little has been done, however, about the impact of CDOM-dominated waters on plankton production modelling in the coastal ocean often constrained by complex bio-optical properties. |
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Figure 1 - Scatter plot showing the linear relationship between seawater salinity and the diffuse attenuation coefficient due to nonchlorophyllous material (kp) derived from in situ measurements. The linear regression gives the equation kp=0.0364 Salinity+1.1942 with a correlation coefficient r2=0.71. (From Le Fouest et al., 2006)
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Comparisons of model outputs for 1998 with coincident SeaWiFS ocean colour data and extensive nitrate and Chl-a measurements suggested CDOM-dominated waters largely contributed to SeaWiFS-derived Chl-a2, causing its overestimation in the western GSL. Nevertheless, the striking agreement between the simulated CDOM-dominated plume and SeaWiFS patterns made it possible to validate the regional estuarine circulation and associated mesoscale variability (Fig. 2), highlighting the farfield effects of the plume over the western part of the Gulf.
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Figure 2 - Comparisons of SeaWiFS-derived Chl-a (right panels) in respect with simulated surface (0-10 m depth-averaged) Chl-a (upper left panel) and diffuse attenuation coefficient due to nonchlorophyllous material (lower left panel) for the 2-8 July 1998 period. Arrows overlaid on the lower left panel are the simulated mean surface (0-10 m depth-averaged) currents. Note the irregular scale for the SeaWiFS-derived and simulated Chl-a panels. (From Le Fouest et al., 2006) |
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Figure 3 - Annual mean of the euphotic depth (0.1% of surface PAR; upper panels), yearly and depth-integrated (0-50 m) primary production (middle panels), and annual mean of depth-averaged (0-50 m) nitrogen nutrients (lower panels) for the simulation set up with a constant (kp=0.04 m-1; left panels) and salinity dependent diffuse attenuation coefficient due to nonchlorophyllous material (right panels). |
Figure 3 illustrates the impact of the plume on primary production by comparing model runs with and without the parameterized bulk turbidity4. The impact came primarily from differences in the euphotic depths with a marked shallowing along the estuarine plume from the Estuary towards the southwestern GSL (Fig. 3, upper panels). This difference translated into a delayed spring bloom and lower primary production rates in river-influenced areas (Fig. 3, middle panels), with a consequent effect on nutrient dynamics over half the GSL (Fig. 3, lower panels). Comparisons with literature estimates and coincident in situ data suggested nutrients were under- and overconsumed in simulations with and without riverine CDOM shading, respectively. A further sensitivity analysis (not shown) was completed by including photoacclimation, that is, the adjustment of the photosynthetic efficiency of phytoplankton to local underwater light conditions. Including photocclimation allowed simulated nutrient concentrations and lateral fluxes to get closer to observations, emphasizing the key role of this process in the plankton dynamics and nutrient budget of the GSL. References |
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