H. Bergmann, H. Breinhälter and O. Hable
Graz University of Technology,
Institute for Hydraulics and Hydrology
A-8010 Graz, Mandellstraße 9, Austria
Tel: ++43-316-873-6260, Fax:
++43-316-873-6264
E-mail: hable@hydro.tu-graz.ac.at
Abstract: flood and
wind-induced high water behind a dam are two of the possible geophysical events
causing its overtopping. in this paper a procedure is laid out for the
evaluation of the overtopping probability due to flood and wind events.
currently in austria spillway flood capacity is designed to accommodate some
fixed flood, such as the once in 5000 year event for dams. The design flood
itself is defined as the peak runoff. No other variables, such as the reservoir
storage volume or wave heights are considered. Additionally other parameters of
the design event (e.g. Time to peak, total flood volume) are assumed to be
suitable. Dissatisfaction with this approach has prompted an investigation of a
probabilistic approach taking account of all the other important variables, such
as initial reservoir storage, wind induced wave height, outlet valve and gate
openings. A research project has the aim to develop a new probabilistic design
concept for spillways of dams with consideration of the reservoir management.
The proposed design concept is able to optimise both safety and economy. A
practicable design software has been developed to estimate hydraulic-hydrologic
failure situations by means of the monte carlo method of risk analysis. The
development and the practical application of the proposed method is carried out
in the context of a case study concerning a reservoir of a hydro power plant in
austria.
Keywords: overtopping
probability, probabilistic design concept, dams, bivariate flood model, risk
analysis, monte carlo method
Failure of a dam
occurs when one or more of the failure events occurs, such as overtopping,
seepage, piping, instability, etc. Numerous studies of dam failures have
indicated that overtopping is a major failure mode of earth and rockfill dams
(Cheng, S., et al., 1993). The average dam failure probabilities for (all kind
of) dams was found to be approximately 10-3 per year per dam (Cheng,
S. 1993). In thirty percent of all cases overtopping is the cause of earth dam
failure (Vrijling, J. 1993). Overtopping occurs when the water level of the
reservoir behind the dam rises above the dam crest. It may result from failure
to make timely and adequate releases of floods through the spillway and flood
release outlets, wave action induced by wind, landslides, earthquakes, and other
geophysical forces, and the combination of these effects. In the context of this
paper only flood and wind events are considered for the evaluation of the
overtopping probability of the dam. Hydrological phenomena like precipitation or
runoff always appear as multivariate events. For many problems in water
management it is not satisfying to know only the frequency of single
characteristics. It will be more important to know the probability of the whole
event. Therefore they should be characterized by numerous parameters. Dam
failure is not a determinable event and hence quantitative evaluation of dam
safety requires probability theory. The proposed probabilistic design concept
for spillways of dams includes a multivariate statistical model for the
simulation of incoming flood events, which is able to describe the hydrological
process entirely.
The actual
hydraulic design practice in Austria is to select a definite load case (or
several cases, if necessary) for which the calculation is made. This design
concept deals with only one random variable, named the "peak
discharge" of the flood (e.g. HQ5000 for dams). The design flood
itself is defined as the peak runoff (an univariate value), which can be discharged by
the spillway outlets under special (mostly fixed) conditions, without
endangering the dam or important parts of the construction. Other parameters of
the design event (e.g. time to peak, total flood volume, etc.) are more or less,
as suitable assumed. Currently operating states due to reservoir management, do
not find any consideration in the official water law procedure (e.g. the initial
water level in the reservoir at the beginning of a flood event or the condition
of the crest and spillway gates and the bottom outlet or the wind depending
freeboard height) and are specified as fixed values. The uncertainty in the
estimation of design floods induced the water authorities to set up safety
principles for the dimensioning of flood spillways, which seem to be relatively
highly compared to other endangering
potentials. Mostly it has not been considered, that there exists a
spectrum of hydrographs (different combinations of peak and volume,
Fig. 8) for each probability, from which the decisive event and the resulting
peak flow has to be found out, while considering the retention.
These are
reasons to develop a probabilistic design concept for spillways, which is taking
account of the demands of safety (against uncontrolled overtopping of dams) as
well as of economy due to reservoir management. Nevertheless it has to be
considered, that the safety of hydraulic structures does not only depend on the
chosen computing method and the choice of the design probability, but also on
the quality of the available hydrological data. Especially the choice of the
design probability varies in the countries of the world. The return period of
the design events for large storage reservoirs vary from a 100 years up to
10.000 years and is limited in most countries by the probable maximum flood (DVWK,
1999).
The proposed
method, originally developed by Pohl, R. (1997) at the Dresden University of
Technology, is standing out by the fact, that the computed water level in the
reservoir is consequently the only design value for evaluating the overtopping
safety of the dam. This design value is resulting of three main load values
(Fig. 1), namely the
l
random initial
reservoir water level at the beginning of a flood event...h0
l
additional
elevation height due to a random flood event (inflow)...hr
l
required
freeboard height due to a random wind event...hf.
According to
this, the design value (=water level) itself is also a random variable, which
can be estimated by means of the method of statistical trials (Monte Carlo
Method). An exact solution is difficult or impossible, due to flood routing and
freeboard calculations. Within this design concept (Fig. 1), the
"failure" is defined as a non-desired hydraulic state, independently
of damages to property or personal injuries.

h0 + hr + hf > HC = Crest level hydraulic-hydrological “failure”
Fig. 1 Definition sketch, approach of the overtopping probability
At the beginning
of a flood event an initial reservoir water level h0 (Fig. 1) is to
be found, which is mathematically considered to be random. The separate entry of
the initial reservoir water level guarantees the economy of the design concept
and is representative for previous floods or droughts, the reservoir operation
and the flood management, the availability of crest and spillway gates and the
availability of the bottom outlet and the penstocks.
Of large
influence for the safety against overtopping of the dam is the incoming flood
event. The retention of the flood hydrograph in the uncontrolled storage
normally rises the level in the reservoir. For this reason the flood event
itself has a special meaning within this design concept. A bivariate flood model
has been developed at the Institute for Hydraulics and Hydrology at the Graz
University of Technology (Sackl & Bergmann,1986) and should become a part of
the design concept.
Characteristics of flood events
The peak QD
and volume VD of direct runoff are the best describing
characteristics of a flood event (Fig. 2, Table 1). With a sufficiently large
sample size it is possible to evaluate design events (VD and QD)
of a certain return period Tn using a bivariate statistical analysis.
In this paper no detailed description of the used bivariate statistical model is
given but further information are available by Sackl, B. (1987).
The method is
divided into the following steps (Sackl & Bergmann,1986):
Bivariate sample (VD
and Q D)
The part of
direct runoff of a flood event is estimated by the separation of the base flow,
which is done by an increasing straight line. For this quantitative method the
actual course is of no interest, it is still important to objectify the
separation. For instance this can be done by a constant separation criterion (VD/VB,1
= const.).

Fig. 2 Schematic representation of a flood event

Fig. 3 Bi-normal
density function
Table 1 Flood
characteristics
|
Area: |
|
|
|
Basin
area |
AE |
[km2] |
|
Volume: |
|
|
|
Total
flood volume |
V |
[m3] |
|
Height
of total runoff V/AE |
H |
[mm] |
|
Volume
of direct runoff |
VD |
[m3] |
|
Height
of direct runoff Vd/AE |
HD |
[mm] |
|
Initial
baseflow volume |
VB,0 |
[m3] |
|
Separated
baseflow volume |
VB,1 |
[m3] |
|
Discharge: |
|
|
|
Peak
of total runoff |
QS |
[m3/s] |
|
Peak
rate of total runoff Q/AE |
q |
[m3/s.
km2] |
|
Peak
of direct runoff |
QD |
[m3/s] |
|
Peak
rate of direct runoff QD/AE |
qD |
[m3/s.
km2] |
|
Initial
baseflow |
QB,0 |
[m3/s] |
|
Initial
baseflow rate DB,0/AE |
qB,0 |
[m3/s.
km2] |
|
Baseflow
at the end |
QB,E |
[m3/s] |
|
Baseflow
rate at the end QB,E/AE |
qB,E |
[m3/s.
km2] |
|
Time: |
|
|
|
Time
to begin |
T0 |
date,
time |
|
Time
to peak |
TS |
date,
time |
|
Time
to end |
TE |
date,
time |
|
Duration: |
|
|
|
Total
duration |
T |
[h] |
|
Time
to peak |
ta |
[h] |
|
Parameters(standard
values): |
|
|
|
Peak
runoff time VD/QD |
tm |
[h] |
|
Standard
volume VD/QD.ta |
VS |
[-] |
|
Volume
of standard hydrograph up to peak |
VS |
[-] |
|
Standard
time t/ta |
τ |
[-] |
|
Standard
duration T/ta |
τmax |
[-] |
|
Separation
criterion |
VD/VB,1 |
[-] |
Bivariate distribution function
To prevent an
escalation of variety in methods, the bivariate normal distribution function
(Fig. 3) is used exclusively. An excellent fit can be achieved by a
transformation of single samples into normal distributed samples. The easiest
way to get an approximate “normalization” is to transform the single
samples in a way that the coefficients of skewness become zero.
Lines of equal probability density function (PDF)
First of all it
is possible to compute the ISO-PDF-lines (lines of equal bivariate PDF), which
are limiting certain random areas. They are horizontal cuts through the
bi-normal PDF, which are ellipsis in the normalized VD, QD – system. With the help of
these lines is possible to make a semi-graphical test of fit.
“Design curves” – lines of equal return
period
The probability
of an event occurring in a certain VD, QD – area is equivalent to the volume above
this area up to the bivariate PDF. There are theoretically
infinite possibilities to delimit such an area for integration. The only
efficient definition of a bivariate flood probability is the so called “upper
right probability” pur which is the probability of the occurrence
of a pair of values VD, QD in the upper right quadrant
(Fig. 4). An ISO-pur-line
is a horizontal cut through the bivariate distribution function relating to the
“upper right quadrant”. It is also possible to
define an ISO-pur-line as a line of equal return period (Fig. 6) or
as a “flood design-curve” (Sackl & Bergmann, 1987). For different return
periods a spectrum of design-curves is obtained. The intersection points of an ISO-pur-line
with the VD– and QD-axes corresponding to a certain
return period Tn are the respective values Vn and Qn.
The course within these points respectively within the event-range has nearly
the shape of a quarter-ellipse (regarding only bivariate flood analysis). So
design-curves can be approximated as quarter ellipses (Fig. 5) after the
collection of flood-peaks for certain return periods QD [m³/s],
volumes of direct runoff for certain return periods VD [m³], a
typical local standard hydrograph or standard hydrograph-range, typical local
range of the time index tm = VD/QD [hours], and
mean base flow or initial base flow QB,0 [m³/s] corresponding with
the increase of base flow VD/VB,1 [-].

Fig. 4 ISO-PDF-LINES

Fig. 5 Ellipse as an approximation for an ISO-pur-line
(“design-curve”), event range from tm,min to tm,ma

Fig. 6 Curves of flood events of equal return period
Fig. 7 Standard hydrograph
Standard hydrograph – event range
![文本框: Q [m3/s]](images/A%20MULT18.gif)
Fig. 8 Spectrum of design flood hydrographs
A direct
runoff hydrograph standardized to the peak u
= 1 and the time to peak t = 1 is called standard
hydrograph. It is necessary for the model, to reduce the multivariate “flood”
process to two dimensions. The chosen analytical 2-parametric function makes it possible to
choose the type of standard hydrograph (Fig. 7) in a wide range according to the
basins properties. To obtain the standard parameters (a, m), direct runoff is
separated from measured flood events and then standardized, by the determination of the
standard volumes VS and the standard times tmax= T/ta (Table 1). There
are no floods with an extreme peak runoff and a volume equal to zero. For this
reason, there always must be a certain “event range”, which is possible to
delimit approximately with straight lines through the origin. This straight
lines are defined by the time index tm. The time to peak ta
of an event point lying on a design curve results directly from the value of the
time index tm and the assumed standard hydrograph. Therefore the
boundaries tm,min and tm,max (Fig. 6) can be estimated by
the probable minimal and maximal values for ta for a certain
watershed. The course of the “design-curves” is similar to a quarter ellipse
only within the range of tm,min and tm,max (Fig. 5).
Design flood
hydrographs
After
construction of the design curves for different return periods (Fig. 5), the
events along a “Tn-years” line are converted into a “spectrum
of design flood hydrographs” (Fig. 8) with the constant return period Tn.
The calculation
of the freeboard height as shown in the 3rd column of Fig. 9 widely
corresponds to the guideline 246/1997 of the German Association of Water
Resources Management and Land Improvement (DVWK, 1997). Both wind set-up in the
reservoir and wave run-up on the slope of the dam are considered. They are
functions of the wind direction, fetch, water depth, and wind velocity.
The flow chart
of the calculation procedure is schematically shown in Fig. 9. In this procedure
the flood event with the maximum discharge peak of n arbitrary years is
simulated n-times using random numbers, whereby the overtopping probability is
distinguished, concerning the direct probability of overtopping p2
(only due to flood meeting the initial water level) and the indirect probability
of overtopping p3 (due to flood and wind effect). A practicable
design software has been developed to estimate hydraulic-hydrologic failure
situations by means of the method of statistical testing and includes the
multivariate flood model described before.
Salza dam
impounding the river Salza is an annual storage in Austria has been chosen to
explain the results of the proposed design method. The 53 [m] high
constant-angle arch dam was built between 1947 and 1949 and covers a catchment
area of AE = 150 [km²]. Salza dam was the first arch dam of medium
size in Austria. This is the reason why an excellent flood data base
(observation period 1954 – 1999) is available for any kind of investigations.
For more details concerning technical data of the Salza dam see Table 4. The
calculation of the exceedence probability was carried out under the conditions
shown in Table 2. The results of this case
study are collected in Table 3. Both heights, the normal top water level and the
overflow crest are in any case overtopped, even in an arbitrary year. The
overtopping probability of the dam crest in an arbitrary year is between 0,7 and
15 [%] due to flood event, respectively flood and (the assumed) wind event
together (85 and 87 [%] in the design case). A specific feature of the Salza dam
is its ungated spillway crest over the whole
crest length (121 [m]) which, rising towards the flanks from elevation 771,5 to
772,5 [m a.s.l.], directs overflowing water into the middle portion irrespective
of the flow rate. So the Salza dam is rather insensitively against overtopping
and this is the reason why such high overtopping probabilities are acceptable.
Actually, priming of the spillway occurs several times a year at the Salza dam.
Table
2 Calculation assumptions to the
case study
l The initial water level was uniformly distributed between normal top water level and 8 [m] below normal top water level
l The bottom outlet is closed during a flood event
l Because of missing wind data at the Salza dam site,wind velocity was assumed with 15 [m/s]
Table
3 Results of the overtopping
probability of the Salza dam in Austria
|
|
overtopping probability [-] |
|||||
|
|
|
arbitrary year |
Design case (Q ³
HQ5000) |
|||
|
Critical water level [-] |
altitude [m a.s.l.] |
p2 only flood |
p3 flood + wind |
p2 only flood |
p3 flood + wind |
|
|
Normal top water level |
771,0 |
1,0 |
1,0 |
1,0 |
1,0 |
|
|
Overflow crest |
771,5 |
1,0 |
1,0 |
1,0 |
1,0 |
|
|
dam crest |
772,5 |
0,007 |
0,15 |
0,85 |
0,87 |
|
Further results of another case study concerning a combined concrete gravity and rockfill dam with an controlled spillway using the proposed method are reported by Hable, O. et al., (2000).
By applying the
proposed method, it is possible to estimate the correlation between the
overtopping probability and a freely selectable "critical water level"
(e.g. the maximum storage level in the reservoir, the crest level or the
overflow crest of the spillway). Therefore prognoses about the different
probabilities (e.g. of keeping of the storage level, of overtopping of the dam
or of priming of the spillway) are possible. Beyond this it is possible to
dimension spillways of hydraulic structures (not only dams) by matching the
demands of safety as well as of economy. For this reason the main advantage of
this probabilistic design method including the proposed multivariate flood model
are an almost complete and realistic processing of the available information, an
excellent simulation of the incoming flood event, a risk estimation tool as a
base for taking measures if necessary and the comparability of dams with
different spillways, storages, types of constructions and purposes concerning
their security. A research project together with the association of the power
plants of Austria (VEÖ) has the aim to develop and improve the proposed method.
It should be possible to open up new paths in the field of design works, if a
reorientation in finding of design values is made possible in the official water
law procedure.
Cheng, S. 1993:
Statistics on dam failures, In: Reliability and uncertainty analysis in
hydraulic design, edited by Ben Chie Yen and Yeou-Koung Tung, 1993.
Cheng, S., Yen,
B., Tang, W. 1993: Stochastic risk modeling of dam overtopping, In: Reliability and uncertainty analysis in
hydraulic design, edited by Ben Chie Yen and Yeou-Koung Tung, 1993.
DVWK, 1997: Freibordbemessung an Stauanlagen - DVWK - Merkblatt 246/1997, Hrsg. Deutscher Verband für Wasserwirtschaft und Kulturbau (in German).
DVWK, 1999: Hochwasserabflüsse - DVWK - Schriften 124/1999, Hrsg. Deutscher Verband für Wasserwirtschaft und Kulturbau (in German).
Hable, O.,
Bergmann, H., Breinhälter, H., Krainer, R. 2000: Flood management at dams with
consideration of the reservoir operation.- In: Proceedings of the International
Symposium on Flood Defence, University of Kassel, Germany.
Pohl, R. 1997: Überflutungssicherheit von Talsperren - In: Mitteilungen des Institutes für Wasserbau und Technische Hydromechanik der TU Dresden, Heft Nr. 11, 1997 (in German).
Sackl, B.;
Bergmann, H. 1986: A Bivariate Statistical Model and its Application to Flood
Protection Projects – In: Proceedings of the International Symposium on Flood
Frequency and Risk Analysis, Louisiana State University, Baton Rouge, USA 1986.
Sackl, B. 1987: Ermittlung von Hochwasser-Bemessungsganglinien in beobachteten und unbeobachteten Einzugsgebieten, Graz University of Technology, Dissertation 1987 (in German).
Simmler, H. 1977: Large dams in Austria, Revised and amended edition of the publication of 1964, Eigenverlag des Österreichischen Wasserwirtschaftsverbandes, Wien, in Kommission bei Springer-Verlag Wien – New York, Vienna 1977.
Vrijling, J.
1993: Development in probabilistic design of flood defenses in the Netherlands,
In: Reliability and uncertainty analysis in hydraulic design, edited by Ben Chie
Yen and Yeou-Koung Tung, 1993.

Fig.
9 Flow chart of the calculation
procedure,Pohl, R. (1997), changed and completed
Table
4.1 Main technical data of Salza
dam, Simmler, H. (1977)
General: |
|
|
Name |
Salza |
|
Nearest Town |
Gröbming(Styria,Austria) |
|
Power Station |
Salza(104[m],27[GWh]) |
|
Construction Period |
1947—1949 |
|
First filling |
September 1949 |
|
Installed Capacity |
8.000,0[kW] |
|
Owner |
STEWEAG |
|
Engineering by |
STEWEAG |
|
Construction by |
J.V.Mayreder |
|
Dam: |
|
|
Type |
Constant-angle arch dam |
|
Dam Crest |
771,5 to 772,5 [m a.s.l.] |
|
Max.Height above Foundation |
53 [m] |
|
Length of crest |
121 [m] |
|
Thickness at the Crest |
3 [m] |
|
Max.Thickness at the Base |
12 [m] |
|
Central angle |
126 [˚] |
|
Slenderness |
0.23 [-] |
|
Foundation (geology) |
Rock |
|
Dam concrete |
23.103[m3] |
|
Excavation |
10.103[m3] |
|
Reservoir: |
|
|
River |
Mitterndorfer Salza |
|
Type of Reservoir |
Annual Storage |
|
Catchment Area |
150 [km2] |
|
Normal Top Water Level |
771 [m a.s.l.] |
|
Minimum Operating Level |
745 [m a.s.l.] |
|
Total Capacity of Reservoir |
11.106 [m3] |
|
Useful Capacity of Reservoir(ln) |
10,5.106[m3] |
|
Yearly lnflow (Qg) |
145.106 [m3] |
|
Storage Coefficient(ln/Qg) |
0,0724[-] |
|
Surface at Top Water Level |
0,8[km2] |
Table 4.2 Main technical data of Salza dam in Austria Simmler, H. (1977), Changed And Completed
|
Appurtenant Works: |
|
|
Spillway |
Overflow spillway over reinforced-concrete crest |
|
Discharge Capacity |
140 [m3/s] at 1,1 [m] surcharge |
|
Probability of Design Flood |
> 100 [years] |
|
HQ100(100 year flood) |
132 [m3/s] according to Graz,University of |
|
|
Technology,Lnstitute for Hydraulics and Hydrology |
|
HQ5000(5000 year flood) |
241 [m3/s] according to Graz,University of |
|
|
Technology,lnstitute for Hydraulics and Hydrology |
|
Bottom Outlet |
ln the right flank |
|
Outlet Tunnel |
2,2[m]in diameter,160[m]long |
|
Discharge Capacity |
8 [m3/s](at normal top water level) |
|
Power lntake |
ln the left flank |
|
Power Tunnel |
2,4 [m]in diameter |
|
Designed Discharge Capacity |
9 [m3/s] |