Although sediment is a natural constituent of rivers, excess loading to rivers and streams is a leading cause of impairment and biodiversity loss. Remedial actions require identification of the sources and mechanisms of sediment supply. This task is complicated by the scale and complexity of large watersheds as well as changes in climate and land use that alter the drivers of sediment supply. Previous studies in Lake Pepin, a natural lake on the Mississippi River, indicate that sediment supply to the lake has increased 10-fold over the past 150 years. Herein we combine geochemical fingerprinting and a suite of geomorphic change detection techniques with a sediment mass balance for a tributary watershed to demonstrate that, although the sediment loading remains very large, the dominant source of sediment has shifted from agricultural soil erosion to accelerated erosion of stream banks and bluffs, driven by increased river discharge. Such hydrologic amplification of natural erosion processes calls for a new approach to watershed sediment modeling that explicitly accounts for channel and floodplain dynamics that amplify or dampen landscape processes. Further, this finding illustrates a new challenge in remediating nonpoint sediment pollution and indicates that management efforts must expand from soil erosion to factors contributing to increased water runoff.
This study determined the importance of air−water
exchange of toxaphene in the Great Lakes by comparing
this flux to other inputs and outputs in a mass balance model.
Our overall goal was to test the hypothesis that the
current water concentrations of toxaphene in Lake Superior
are due to physical limnological differences between it
and the lower Great Lakes and secondarily to evaluate
whether nonatmospheric inputs of toxaphene have had an
impact on current toxaphene burdens in lakes Superior
and Michigan. A series of water samples from the Great
Lakes were analyzed for toxaphene. A static mass budget
is presented for lakes Superior, Michigan, and Ontario.
A dynamic model of toxaphene behavior in lakes Superior
and Michigan from 1950 to 1995 is then presented. The
results of this model support our hypothesis that the colder
temperatures and lower sedimentation rates in Lake
Superior are responsible for its high water concentrations
of toxaphene and that there is no evidence of nonatmospheric
sources of toxaphene to Lake Superior. However, the model
supports the conclusion that there were nonatmospheric
sources of toxaphene to Lake Michigan.
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