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Water-Resources Investigations Report 97-4138 |
Changes in Bottom-Surface Elevations in Three Reservoirs on the
Lower Susquehanna River, Pennsylvania and Maryland, Following the
January 1996 FloodImplications for Nutrient and Sediment Loads
to Chesapeake Bay
by Michael
J. Langland and Robert A. Hainly
The Susquehanna
River drains about 27,510 square miles in New York, Pennsylvania,
and Maryland, contributes nearly 50 percent of the freshwater discharge
to the Chesapeake Bay, and contributes nearly 66 percent of the
annual nitrogen load, 40 percent of the phosphorus load, and 25
percent of the suspended-sediment load from non-tidal parts of the
Bay during a year of average streamflow. A reservoir system formed
by three hydroelectric dams on the lower Susquehanna River is currently
trapping a major part of the phosphorus and suspended-sediment loads
from the basin and, to a lesser extent, the nitrogen loads.
In the summer of 1996, the U. S. Geological
Survey collected bathymetric data along 64 cross sections and 40
bottom-sediment samples along 14 selected cross sections in the
lower Susquehanna River reservoir system to determine the remaining
sediment-storage capacity, refine the current estimate of when the
system may reach sediment-storage capacity, document changes in
the reservoir system after the January 1996 flood, and determine
the remaining nutrient mass in Conowingo Reservoir. Results from
the 1996 survey indicate an estimated total of 14,800,000 tons of
sediment were scoured from the reservoir system from 1993 (date
of previous bathymetric survey) through 1996. This includes the
net sediment change of 4,700,000 tons based on volume change in
the reservoir system computed from the 1993 and 1996 surveys, the
6,900,000 tons of sediment deposited from 1993 through 1996, and
the 3,200,000 tons of sediment transported into the reservoir system
during the January 1996 flood. The January 1996 flood, which exceeded
a 100-year recurrence interval, scoured about the same amount of
sediment that normally would be deposited in the reservoir system
during a 4- to 6-year period.
Concentrations of total nitrogen in bottom
sediments in the Conowingo Reservoir ranged from 1,500 to 6,900
mg/kg (milligrams per kilogram); 75 percent of the concentrations
were between 3,000 and 5,000 mg/kg. About 96 percent of the concentrations
of total nitrogen consisted of organic nitrogen. Concentrations
of total phosphorus in bottom sediments ranged from 286 to 1,390
mg/kg. About 84 percent of the concentrations of total phosphorus
were comprised of inorganic phosphorus. The ratio of concentrations
of plant-available phosphorus to concentrations of total phosphorus
ranged from 0.6 to 3.5 percent; ratios generally decreased in a
downstream direction.
About 29,000 acre-feet, or 42,000,000 tons,
of sediment can be deposited before Conowingo Reservoir reaches
sediment-storage capacity. Assuming the average annual sediment-deposition
rate remains unchanged and no scour occurs due to floods, the reservoir
system could reach sediment-storage capacity in about 17 years.
The reservoir system currently is trapping about 2 percent of the
nitrogen, 45 percent of the phosphorus, and 70 percent of the suspended
sediment transported by the river to the upper Chesapeake Bay. Once
the reservoir reaches sediment-storage capacity, an estimated 250-percent
increase in the current annual loads of suspended sediment, a 2-percent
increase in the current annual loads of total nitrogen, and a 70-percent
increase in the current annual loads of total phosphorus from the
Susquehanna River to Chesapeake Bay can be expected. If the goal
of a 40-percent reduction in controllable phosphorus load from the
Susquehanna River Basin is met before the reservoirs reach sediment-storage
capacity, the 40-percent reduction goal will probably be exceeded
when the reservoir system reaches sediment-storage capacity.
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