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Space Grant Consortium - University of Wisconsin - Green Bay

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Figure 5. Model pCO2 at the surface (thick black) and at 12m (SAMI, thin grey) compared to direct measurements<br />

<strong>of</strong> pCO2 (thick grey) during 2001. Indirect estimates <strong>of</strong> pCO2 from EPA pH and alkalinity at the nearest EPA station<br />

are shown in shapes. Note that the EPA station was visited overnight.<br />

Model pCO2 agrees with the open-lake direct observations and indirect estimates <strong>of</strong> pCO2 and<br />

estimates a lake-wide efflux <strong>of</strong> only 0.03 TgC/yr. For comparison, Urban et al. [2005] estimated<br />

the lake efflux to be 3 TgC/yr from indirect estimates <strong>of</strong> pCO2 taken near the coastline along the<br />

Keweenaw Peninsula. Significant spatial variability in productivity, pCO2, and carbon fluxes<br />

exist in the model, suggesting that extrapolating spatially limited observations can be<br />

problematic. The model is able to provide an estimate <strong>of</strong> the daily air-lake flux for all <strong>of</strong> the lake<br />

to fill in observational gaps.<br />

Discussion and Conclusions<br />

The model adequately simulates lake temperature, productivity and pCO2. The open lake is<br />

supersaturated with carbon during winter and spring and under-saturated or near equilibrium<br />

during summer. Lake Superior mixes to the bottom twice yearly, and no water mass within the<br />

lake is able to store carbon dioxide away from the atmosphere for long periods. The open lake is<br />

not a significant source <strong>of</strong> carbon dioxide (0.03 TgC/yr), and the near shore waters would be<br />

unable to maintain super-saturation without continued inputs <strong>of</strong> carbon.<br />

Nearshore observations along the Keweenaw Current [Urban et al., 2005] suggest the lake is<br />

heterotrophic and a source <strong>of</strong> carbon to the atmosphere in the near shore zone. The magnitude <strong>of</strong><br />

this source is extremely uncertain, because all pCO2 estimates were indirectly calculated from<br />

electrode-measured pH, temperature, and alkalinity. Direct measurements <strong>of</strong> near-shore pCO2<br />

are needed for a true understanding <strong>of</strong> the lake’s carbon cycle. When the model can agree with<br />

both near shore and open lake pCO2 observations and estimates, the whole lake carbon budget<br />

may be understood. The model does not include terrestrial inputs <strong>of</strong> carbon. Due to its long<br />

residence time (176 years [Quinn, 1992]), 90% <strong>of</strong> the allochthonous carbon is respired within the<br />

lake. The terrestrial carbon must be respired mainly in the near shore zone; otherwise, model<br />

pCO2 in the <strong>of</strong>fshore regions would be low compared to observations. The next step is to add<br />

river and run<strong>of</strong>f inputs <strong>of</strong> terrestrial carbon to the model.<br />

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