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Hydrology in Mountainous Répons, n Artificial R eservoirs; Water an d Slopes
Proceedings of two Lausanne Symposia, August 1990). IAHS Publ. no. 194,1990.
Removal of sediment deposits in reservoirs by means of
lushing
H. SCHEUEKLEIN
Obernach Hydraulics Laboratory, Oskar von Miller-Institut,
Technical University Munich, F. R. Germany
ABSTRACT Removal of sediment deposits from reservoirs by
means of flushing is a widely used method to regain
storage volume. However, its efficiency is very often
overestimated. The importance of supporting auxilliary
measures as water level drawdown is not always recognized
to sufficient extent. Estimation of flushing efficiency by
means of theoretical approach is problematic. The
mechanism is complex and verification of the parameters
involved is difficult. In the paper a straightforward
approach starting from extreme simplifications is
presented. The method allows for a rough estimate on the
prospect of flushing including information on the
necessary drawdown to produce a desired effect. By means
of two graphs the limits and the effictivity of flushing
activities can be judged quickly. The procedure is
demonstrated by means of examples.
INTRODUCTION
Sedimentation of man-made reservoirs is one of the major problems
hydraulic engineers will have to face in future. In spite of the
various methods which can be taken to minimize sediment yield from the
watershed, the intrusion and the deposition of sediment in reservoirs
can never be avoided completely. Sediment enters the reservoir either
as bedload or as suspended load. Usually the amount of sediment
carried in suspension exceeds the bed load transport by a factor of
5 to 10. The sediment deposits in a reservoir are composed accor
dingly. First the coarse material transported close to the bed settles
down forming a delta at the reservoir entrance. Material in suspension
is carried further and deposited more or less uniformly all over the
reservoir.
REMOVAL OF SEDIMENT FROM RESERVOIRS BY MEANS OF FLUSHING
In principle, the mechanism described above takes place similarly in
any reservoir. However, the magnitude of the depositions, the pace of
the deposition process, and the importance of the depositions for the
operation of the reservoir may vary considerably.
In mountain reservoirs, usually the uniformly distributed fine
deposits are of minor importance. It is the gravel and sand settling
at the entrance of the reservoir that causes problems, such as
99
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H. Scheuerlein
100
- occupation of the most active (upper) part of the reservoir,
- raise of water level in the river upstream of the reservoir
(backwater effect),
- degradation of the river bed downstream of the dam due to trapping
of coarse material in the reservoir.
With respect
to the
reasons listed above,
it is
desirable
to
remove
particularly the deposits of coarse material at the reservoir entrance,
preferably by passing it downstream where it is needed to avoid
degradation.
An elegant method
to
solve
the
problem
is to
take advantage
of the
transport capacity of the flow itself without using external energy.
This technique which commonly is called flushing is used throughout
the world, however, not always with the desired success. The
efficiency
of
flushing depends significantly
on the
water level
in the
reservoir during the measure (ACKERS et al, SCHEUERLEIN, 1987, WHITE
et al) . Flushing can be carried out very effectively when the water
level
in the
reservoir
can be
kept
low for
some time while
the
flow
rate
is
high.
As this, on the
other hand, means
a
substantial loss
of
water, effective flushing must be oriented towards minimization of
water level drawdown and flushing time.
Theoretical treatment of reservoir sedimentation and flushing is
difficult for various reasons. The mechanism is complex and the
verification of the parameters involved is problematic due to the
stochastic character of the water and sediment afflux. For any
analysis extensive simplifications are unavoidable.
SIMPLIFIED METHOD TO ESTIMATE FLUSHING EFFICIENCY
With respect to the limited possibilities to describe and to verify
reservoir sedimentation and flushing activities analytically,
sophisticated theoretical treatment seems hardly justified. A
simplified approach has been tried by SCHEUERLEIN, 1989, however, the
procedure presented there proved to be still somewhat troublesome and
unhandy
by
incorporating
the
energy gradient
of the
flow through
the
reservoir. On the other hand, the lateral mixing of the incoming flow
on
the way
through
the
reservoir
was
left
out of
consideration.
In the following another simple method to estimate the possibility
and
the
limit
of
eventual flushing activities will
be
presented. Using
the notations of Fig. 1, and the assumptions
-
simplified prismatic shape
of the
reservoir,
-
inflow equal outflow during flushing,
-
onedimensional analysis,
the continuity equation close to the dam site at a hypothetical
drawdown water level DWL can be written as
B
D
+ B
A . (1)
= V
D 2
h
D
For geometrical reasons,
h
D
H
o
B
D
B
A
B
o ~
B
A
(2)
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101
Removal of sediment in
reservoirs
by flushing
Q A V
original river
drawdown
Longitudinal Sect ion
OWL
operationa
water level
FIG. 1 Flow through a reservoir - definition sketch.
D
A H o
o
V
(3)
substituted in (1) ,
h.
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H. Scheuerlein
102
velocity close to the dam can also be interpreted as the governing
factor for the efficiency of any flushing activity. Considering
V
D
= V
Dc
( 5 )
with
v„ = f(d) (f.i. after HJULSTROM) (6)
Dc
and
Q_ = Q (per definition) (7)
equation (4) changes to
h B - B
^ A
=
V
D c
B
A
+
ÎT ~ V ^
>
h
D
( 8
>
o
z
which after some transformation and with the substitution
«A - B :
9 )
Q
\
finally reads
- ̂ (,„,
H B
o o
Fig. 2 shows the graphic verification of equation ( 10 ) . For easier
handling the HJUSSTROM function (6) has been incorporated in the
auxilliary graphs given in Fig. 3.
With Fig. 2 and 3 a direct and straightforward determination of the
drawdown water level corresponding with a desired flushing effect,
f. i. sluicing of a certain defined grain size is possible. Further
more it is possible to check the limits of flushing at extraordinary
conditions.
The presented primitive method to estimate the margins within
which flushing activities will necessarily have to stay might help to
develop a more realistic feeling of what might be possible and what
even under favourable conditions must be impossible. It is neither
meant nor capable to describe the flushing process realistically. It
rather serves the purpose to bring unjustified expectations towards
the effictivity of flushing (particularly at partly filled reservoirs)
back to the ground.
EXAMPLES
Example : Small reservoir at a run-of-river power plant in the Alps
8/18/2019 iahs_194_0099
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8/18/2019 iahs_194_0099
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105
Removal of sediment in
reservoirs
by flushing
Given:
Q
A
= Q
D
= 400 m
3
/s
B. = B = 60 m
A o
H = 7 m
o
Question:
Necessary drawdown to guarantee flushing of coarse gravel
(d = 30 mm)?
Procedure:
^A 400 , ,, f
3
/ /
q
A
=
B 7
=
~6ÏÏ
= 6
'
6 7
L
m3/s/l
A
^A =
6
>
6 7
= n qs
H 7
u
'
o
q
A
From Fig. 3 for — =0 ,9 5 and d = 30 mm
H
O
q
A
A
= 0 4 4
v
n
H
De o
q. B
From Fig. 2 for 5- = 0,44 and
~ =
1,0
De o A
£ • o «
o
h
D
= 0,44 • 7 = 3,10 jmj
Flushing of coarse gravel would require a drawdown of
AH = H - h„ = 7 - 3,10 = 3,90 [ml
O
D » L J
Example 2: Large reservoir in the Middle East
Given:
Q
A
= Q
D
= 1000 m
3
/s
B
A
= 140 m
A
B = 420 m
o
H 90 m (operational water level)
o
Question:
Up to which grain size will flushing be effictive when the
drawdown shall not drop more than 60 m below operational water
level?
8/18/2019 iahs_194_0099
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H. Scheuerlein
106
Procedure:
h
= H - 60 = 90 - 60 = 30 [ m j
D o
^ = 30 = 0 33H 90 '
J
G
h D ,„„
From. Fig.
2 for ^- = 0,33 and
-g-
= y^j = 3
o
A
q
A
0,42
De o
q
A „ ,„
J
q
A 1000 _
n n s
From Fig. 3 for ^- = 0,42 and — -
1 4 0
.
9 0
~ °
5
°»
De o o
d
= 0,3 mm
Even with
a
water level drawdown
of 60 m
flushing efficiency would
be
very poor.
Additional question:
Necessary drawdown when flushing of coarse sand (d = 2 mm) shall
be guaranteed?
Procedure:
q
A
From Fig.
3 for ^ = 0,08 and d = 2 mm
r i
q
A
= 0,21
De o
q. B
From Fig.
2 for ~ = 0,21 and ~ = 3
De o A
^ = 0,18 ->• h
D
= 0,18 • 90 = 16,2 [mj
h
D
o
Necessary drawdown H - h = 90 - 16,2 = 7 3,8m
REFERENCES
ACKERS, P., THOMPSON, G. (1987) Reservoir sedimentation and influence
of flushing. In: Sediment Transport in Gravel-bed Rivers.
J. Wiley & Sons, London, 845-868.
ASCE (1977) Sedimentation Engineering. ASCE Manuals
and
Reports
on
Engineering Practice No. 54 , New York.
SCHEUERLEIN, H. (1987) Sedimentation of reservoirs - methods of
prevention, techniques
of
rehabilitation.
In:
First Iranian
Symposium on Dam Engineering. Tehran.
SCHEUERLEIN,
H.
(1989) Sediment sluicing
in
mountain reservoirs.
In:
International Workshop on Fluvial Hydraulics of Mountain Regions.
Trent, B 77 - B 88 .
WHITE, W.,
BETTESS,
R.
(1984)
The
feasibility
of
flushing sediments
through reservoirs. In: Challenges in African Hydrology and Water
Resources (Proceedings of the Harare Symposium). IAHR Publ.
No. 144, 577-587.