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ENVIRONMENTAL CONSIDERATIONS IN THE
DESIGN OF SPILLWAYS: ANALYSIS OF HYDRODYNAMIC BEHAVIOR
Bacchiega
jorge D., Fattor Claudio A., Barrionuevo Héctor D.
Programa Hidráulica de Obras,
Laboratorio de Hidráulica y del Ambiente,
Instituto Nacional del Agua y del
Ambiente (INA)
Casilla Correo 21 , (1802)
Aeropuerto Ezeiza, Argentina
Tel.: (54-1) 480-0457 ,
Fax:(54-1) 480-0459 , e-mail: jdelio@ina.gov.ar
ABSTRACT
The modification of spillways
can finally result in important differences from the point of view of the
hydrodynamic behavior of this hydraulic structure. Those differences could be
appreciated in the flow pattern, the energy dissipation, local scour downstream
of the plunge pool, etc. One of the reasons to modify a spillway or a plunge
pool can be based on environmental considerations like the life preservation of
fishes habitat.
This paper present an
analysis of a conventional spillway and a modified spillway for environmental
reasons, including the problem of supersaturation of total disolved gases downstream
of the stilling basin. The analysis that is presented includes flow pattern,
fluctuating pressures analysis and local scour, and establishes some
comparisons form the hydrodynamic point of view between both hydraulic
structures.
Keywords: Spillways, stilling
basin, total disolved gases, physical modeling
INTRODUCTION
The design of spillways and
stilling basins involves considerations to get a proper functioning of these
hydraulic structures with the maximum safety conditions. The design of a dam
and other structures is adapted after considering hydrologic, hydraulic,
topographic and geologic conditions, economic aspects, etc.
In the case of the spillways
is advisable to do a study through physical modeling to optimize the spillway
profile and finally to guarantee the design discharge with the corresponding
hydraulic head. The study of the stilling basin is very important, because this
structure must assure kinetic energy downstream of the plunge pool compatible
with the river morphology. The development of local scour with certain risks
for some structure as well as riverbanks stabilities must be certainly
considered. On other hand, if the hydrodynamic conditions are really dangerous
from the point of view of cavitation, the implementation of an aireation device
could be necessary to reduce these risks.
Beyond the general
considerations, there are boundary conditions to take into account. For
instance, environmental conditions can demand modifications. One of this
situation can be present when during the spillway operation the supersaturation
of total dissolved gases (TDG) is increased until reaching dangerous rates. If
besides that, the river has shallow waters and there is a rich variety and
amount of fishes, the life of them could be put in danger. These kind of phenomenon have happened on
Snake and Columbia rivers (U.S.A.) and downstream of Principal spillway of
Yacyretá dam (Argentina-Paraguay).
Remediation works to reduce TDG until reaching compatible values with
fishes habitat usually include the construction of a deflector on the spillway
profile to reduce the submergence of the jet into the plunge pool. In this way,
it is intented to decrease the air entrainment near the bottom of the stilling
basin, where the gases disolution is greater because of the increasing of the
hydraulic pressure. These kind of deflectors have been successfully installed
in Bonneville and John Day dams on Columbia River (U.S.A.), Ice Harbor and
Lower Monumental dams on Snake River (U.S.A.) and Aña-Cuá spillway of Yacyretá
dam on Paraná River (Argentina).
It is important to consider that the construction of deflectors in
existing hydraulic structures could involve a change in the hydrodynamic
behavior of the spillway-stilling basin, maybe including an increasing of fluctuating
pressures and a decreasing in the performance in the dissipation energy.
EXPERIMENTAL METHODOLOGY
The analysis of the hydrodynamic behavior of a conventional spillway and
a modified spillway including a deflector projected to diminish supersaturation
of TDG downstream of the plunge pool, was done taking into account the flow
pattern, pressure measurements (static and fluctuating terms), and velocity
records.
In relation with the pressure fluctuations, the record of this parameter
allows to characterize the intensity of turbulence in different areas of the
stilling basin through the parameter C'p. This is named adimensional
coefficient of fluctuating pressures and can be defined as:
C´p=RMS/(r.U2/2.g)
, being RMS the root mean square of fluctuating pressures.In order to
study the tendency to cavitation because of the fluctuating pressures, the
following parameter could be defined:
C0.1=(p/g+p'/g0.1%)/(r.U2/2.g)
,being p/g the static pressure
and p'/g0.1% the semiamplitude of fluctuating pressures
with an occurrence probability of 0,1%. The sum of these terms is the total
pressure with 0,1% occurrence probability, and it is related with the tendency
to cavitation.
In this way, it is possible to evaluate C´p y C0.1 as a
function of a series of adimensional parameters. Then,
C´p=f1(x/Ls, H/Hd, Fr,
S) , C0.1=f2(x/Ls,
H/Hd, Fr, S)
, being x the location in the stilling basin, Ls the stilling basin
lenght, H the hydraulic head, Hd the design hydraulic head, Fr the Froude number, and S
the submergence.
Consequently, considering the results obtained of the studies of both
hydraulic structures, it is possible to carry out a comparison of the
hydrodynamic behavior .
EXPERIMENTAL FACILITIES
A bidimensional physical model of a spillway and its stilling basin has
been constructed at scale 1:50. The stilling basin bottom has 3% slope towards
downstream; an air entrainment device is located on the spillway profile and
downstream of each pile an extension to avoid cavitation problems in the
dowmstream side of the pile has been built.
The experimental device is supplied for a 400 l/seg pumping system. The
device includes an aproximation channel to the spillway, the spillway and the
stilling basin and the tailwater area. In the channel (0,76 m wide), a middle
span and two half-spans was represented, being possible to study only uniform
hydraulic conditions.
To study the two spillways, the first one according to the project and
the second one including a horizontal deflector, is necessary to measure some
parameters like water levels, velocities, pressures. The velocity measurement
was carried out in several sections in the stilling basin, and the pressures
measurement were done in points located in the most important locations.
The fluctuating pressures records were carried out through
instrumentation including pressure transductors, amplifiers, analogic filters,
sample and hold circuits and analogic-digital converters. The sample time was
10x10-3 seg., in order to include macroturbulent phenomenon that are
characterized for the low peak frequency. The duration of the sampling is
almost three minutes in order to guarantee ergodicity and stationary, because
these conditions are necessary to allow a right statistic analysis.
ANALYSIS OF RESULTS
FLOW PATTERN
The functioning of the spillway with its original profile allows to show
a hydraulic jump in the stilling basin with different submergences depending of
the discharge for the spillway and the tailwater level of the river. Figure 1
allows to see that the water jet flowing on the air entrainment device produces
a cavity with pressures lower than atmospheric pressure, and this difference of
pressures allows the air entrainment that reaches the bottom of the plunge
pool. On other hand, the interaction between the water jet and the front of the
jump produces a superficial air entrainment in the jump, but this does not
reach the bottom of the stilling basin.
The uniform operation of the spillway allows to notice great size eddies
of horizontal axis and the recirculation currents. The flow pattern allows to
guarantee the self-cleaning of the stilling basin, that is very important in
these structures. On other hand, for the maximum discharge, the kinetic energy
downstream of the stilling basin is compatible with dam safety conditions and
riverbanks stability.
Respect to the modified profile, the studies to optimize the geometry
and location of a deflector to reduce supersaturation of TDG downstream of the
plunge pool have permitted the choosing of one device. The characteristic
dimensions of the deflector are its lenght l=0,216.Hd and the
elevation related to the spillway crest, t=0,351.Hd.
One of the most important facts is that the deflector generates the
displacement of the hydraulic jump towards downstream, and a recirculation zone
at the beginning of the stilling basin that is present for each operation
condition.
To H/Hd=1 and Q/Qmax<0,35, the presence of a
recirculation zone with inversion of velocities profile is observed, depending
the lenght and intensity of this circulation of Q/Qmax and S.
Respect of this topic, Figure 2 shows a comparison of two velocity profiles
measured in x/Ls=0,54, for H/Hd=1, and Q/Qmax=0,12 and Q/Qmax=1.
Flow pattern to a typical case to H/Hd=1 and Q/Qmax<0,35,
can be seen in Figure 3.
To H/Hd=1 and Q/Qmax>0,35 the recirculation
zone at the beginning of the plunge pool is present too; downstream of this
little sector the flow pattern is characterized for a hydraulic jump. A general
scheme can be observed in Figure 4 to Q/Qmax=1.
The mentioned recirculation is really important from the point of view
of the capacity of self-cleaning of the stilling basin. The difference with a
characteristic flow pattern related to the original profile, is that if any
material is held at the toe of the plunge pool, this will be always
recirculating while the spillways is functioning.
On other hand, because of the displacement of the hydraulic jump, the
kinetic energy downstream of the stilling basin increases in relation with the
original scheme. Then, local scour at the toe of the stilling basin is greater,
and eventually material entrainment from the river bed to the stilling basin
has been observed.

Figure 1 - 4
FLUCTUATING PRESSURES ANALYSIS
C'p and C0.1 are important parameters to study the action of
fluctuating pressures.
C'p vs. x/Ls analysis for conditions fixed for H/Hd=1 and Q/Qmax=0,35,
and H/Hd=1 and Q/Qmax=1, allows to see a different behavior in some
sectors in the plunge pool.
For Q/Qmax=0,35 and H/Hd=1, the records in the points located
on the spillway profile show higher values of C'p for the modified profile
(Figure 5). For 0<x/Ls<0,11, C'p values are lower with the modified
spillway, and this can be directly related with the existence of a
recirculation zone because the pressure fluctuations are not so high there
compared with the original spillway. For 0,11<x/Ls<0,85 , C'p is higher
when the original profile is tested, but this situation is different to
x/Ls>0,85.
The analysis of C0.1 allows to see important differences
(Figure 6). Taking into account the pressure measurements on the spillway
profile is possible to see that the total pressure related at a probability of
occurrence of 0,1% shows higher values on the original profile, getting a
maximum in x/Ls=0. This fact is determined for the influence of the hydraulic
jump, while with the modified spillway the same area is affected for a
recirculation current where macroturbulence is not prevailing.
The fluctuating pressure records on the stilling basin bottom allow to
see that for 0<x/Ls<0,12, C0.1 values are greater in this
situation because of the macroturbulent influence that is present when the
original profile spillway is tested. For 0,12<x/Ls<0,87, the records show
greater magnitudes to the modified spillway.
It is important to emphasize that the described condition is
representative of the hydrodynamic behavior observed to conditions fixed for
H/Hd=1 and Q/Qmax<0,35.
For Q/Qmax=1, the variation of C'p vs. x/Ls presents
differences between the two spillways (Figure 7). Even though the last zone of
the spillway profile is subjected to similar hydrodynamic pressures, in the
area located between 0<x/Ls<0,20 C'p these are strongly higher for the
modified spillway. Downstream of this sector, unless for the peak in x/Ls=0,47,
the highest values of C'p are related to the original spillway.
The analysis of extreme pressures through the parameter C0.1
(Figure 8) shows higher stresses for the original spillway in the last section
of the spillway and inside the stilling basin for 0<x/Ls<0,17. Downstream
of this section, and unless for a little area around x/Ls=0,47, the magnitudes
of C0.1 are higher to the alternative of spillway with deflector
(modified) in almost all the lenght of the stilling basin.

Figure 5 - 8
SCOUR DOWNSTREAM OF THE STILLING BASIN
This topic is related with the performance of the stilling basin. In
this sense, the results of the tests show a greater local scour when the
modified spillway was tested.
On other hand, the location of the deflector on the spillway profile and
its influence in the flow pattern and in the hydrodynamic behavior of the
stilling basin generate to certain kind of conditions of operation the
entrainment of river bed material in the stilling basin. This situation is
never present during the tests of the original spillway.
CONCLUSIONS
-Environmental considerations can be so important to analyze or generate
structural modifications in a spillway or its stilling basin, and consequently
to change the hydrodynamic behavior of the structure.
-The construction of a horizontal deflector on a Creager profile
spillway, thought to decrease the supersaturation of TDG during the operation
of the spillway, generates an important change in the flow pattern, being
underlined the displacement of the hydraulic jump towards downstream
(especially for Q/Qmax>0,35) and the existence of a recirculation
sector at the beginning of the stilling basin.
-The pressures field is influenced for the change of the geometry of the
spillway and consequently for the different hydrodynamic conditions expressed
by C'p and C0.1 .
-Greater local scour was observed when the modified spillway was tested,
and also it was possible to see the entrainment of river bed material inside
the plunge pool.
-It is really important to pay attention to the possible consequences
for a modification of a spillway or stilling basin, especially in relation with
pressure fluctuations on the stilling basin and the performance in energy
dissipation.
REFERENCES
-Gulliver, J.; Hibbs, D.; McDonald J; ¨Measurement of Effective
Saturation Concentration for Gas Transfer¨, Journal of Hydraulic Engineering,
ASCE, February 1998, Vol.113, Nro.2.
-Geldert D.; Gulliver, J.; Wilhelms S.; ¨Modeling Dissolved Gas
Supersaturation Below Spillway Plunge Pools¨, Journal of Hydraulic Engineering,
ASCE, May 1998, Vol.124, Nro.5.
-Angelaccio C.; Bacchiega J.; Fattor C.; Barrionuevo H.; Effects of the
Spillways Operation on the Fishes Habitat: Study of Solutions¨, XXVII IAHR
Congress, August 1997, San Francisco, U.S.A.