
CASE STUDY: SEFID-RUD RESERVOIR, IRAN 23.17
discharge. A final sediment concentration peak occurred when full drawdown was
achieved. A high rate of sediment discharge and continuously elevated suspended
sediment concentrations occurred throughout this entire flushing period while the
main channel was being formed.
The situation was quite different only 3 years later during the 1985-1986
flushing season when the main channel had become more stabilized (Fig. 23.15b). In that
year, the reservoir level was dropped from 220 to 196 m over only a few days
creating a very high rate of sediment release. Suspended-solids concentration
exceeded 150 g/L for about 1 week and reached a maximum value of 329 g/L.
However, the solids content of the water released from the dam declined steadily,
despite increasing discharge over the flushing period. Similar behavior was
observed during subsequent years, except in 1989-1990, when the concentration of
the flushing flow increased in February because of erosion of the Shahrud diversion
channel. It is characteristic of flushing that, even though sediment discharge can
equal sediment inflow on an annual basis, the seasonality of sediment release differs
from the seasonality of sediment inflow. At Sefid-Rud most sediment is delivered to the
reservoir by wet season floods, but most sediment is released as a highly
concentrated flow during the dry season.
23.4.6 Downstream Impacts
Barrages and intakes are installed on the Sefid-Rud River downstream of the dam
to divert reservoir releases to irrigators. These intakes and canals cannot tolerate heavy
sediment loads, since this would create serious sedimentation problems within the
irrigation system. To prevent serious downstream sedimentation problems, the
sediment concentration of water released from Sefid-Rud Dam during the
irrigation season (April - September inclusive) should not exceed 5 g/L. The sluices
on irrigation barrages remain fully open during the October through February
flushing season, passing sediment-laden river flow with minimum interruption.
Since flows during the flushing period are typically less than 150 m
3
/s, there is
insignificant backwater at these downstream structures. Irrigation intakes remain shut to
exclude the muddy water from delivery canals. Tolouie (1993) reported that this
procedure avoided operational problems below the dam caused by sediment
flushing. No information is available on changes in channel morphology or other
impacts downstream of the dam.
23.4.7 Long-Term Storage Recovery
The bed of the main channel created by flushing enlarged until a stable width was
achieved. However, the resulting channel was narrow compared to the total deposit
width, and sediment continued to be deposited on the submerged floodplain during
impounding periods. Thus, for flushing alone the reservoir capacity at first
increased rapidly, then increased more slowly, and in the future the capacity will
start to decrease once again (Fig. 23.11). Therefore two additional methods were
investigated to remove floodplain deposits on either side of the main channel: (1)
lateral erosion by piping and (2) longitudinal erosion or diversion channels. These
two techniques are discussed in the following sections.
23.5 LATERAL EROSION BY PIPING
Sediments in the upper reaches of the reservoir had been deposited in thick alternating
layers of cohesive and noncohesive material as shown in the boring data (Fig.
23.6). Cohesive deposits were 2 to 4 m thick, and desiccation and compaction during