Author/Authors :
Jonathan J. Kolak، نويسنده , , David T. Long، نويسنده , , Tina M. Beals، نويسنده , , Steven J. Eisenrich، نويسنده , , Deborah L. Swackhamer، نويسنده ,
Abstract :
Sediment cores were collected from depositional basins in lakes Michigan, Ontario and Superior to assess spatial and temporal variations in Cu accumulation rates and inventories. Sediment chronologies were determined via 210Pb dating, and 210Pb inventories were used to correct for the effects of sediment focusing. Among the lakes studied, Cu loading histories generally decrease to the present, signifying a regional reduction in the anthropogenic release of Cu to the environment. Focusing-corrected Cu accumulation rates in surficial sediments vary significantly within lakes Michigan and Ontario, suggesting that recent inputs of Cu to these 2 lakes may have been dominated by localized sources. Variations in Cu accumulation rates within Lake Superior are interpreted to be insignificant, suggesting either that Lake Superior is well-mixed with respect to copper inputs or that the lake is dominated by a single source for Cu. Recent measurements of atmospheric fluxes of Cu within the Great Lakes region generally indicate that the atmosphere accounts for less than 50% of the Cu accumulating in surficial sediments. Historical Cu accumulation rates from Lake Superior are poorly correlated with Cu production associated with local smelters, but favorably agree with national production rates. Trends in historical Cu accumulation rates within all 3 lakes may indicate that recent declines in Cu loading can be attributed to the enactment of stricter environmental regulations as well as changes in the use of Cu. Focusing-corrected Cu inventories in lakes Michigan, Ontario, and Superior are generally invariant within a given lake, indicating that, historically, these lakes have been dominated either by a single source or were well-mixed with respect to Cu inputs. The disparity between the results from recent accumulation rates and historical inventories may reflect differences in how the Great Lakes respond to contaminant loading on short (e.g. years) versus long (e.g. decades) timescales.