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Castaldini, Doriano
event. Furthermore, a breach location or spillage zone has to be specified, for which records on previous flooding events
is used. Temporal input for the model consists of precipitation and discharge records (5 minute or hourly intervals).
Spillage from the channel is calculated as a function of channel discharge.
Flood routing (the process of tracing water movement through determination of time and magnitude of flow in the
watershed; Chow et al., 1988) is performed treating flow of water as kinematic wave motion, where motion of water is
described principally by the equation of continuity. Water moves according to the steepest gradient from one element to
another. For each time interval (5min or Ihr) the quantity of water in each grid-cell (25 or 50 m^) is updated as a
function of input and output. Three problems arise from the use of a drainage network for routing purposes: 1) Flow
restrictions: water can only move as far as the (diagonal) length of 1 grid element. To resolve this problems the pixel-
size and used time interval can be reduced (increasing computational expense); 2) Micro-relief: the presence of
infrastructures does not become apparent in the digital elevation model (due to its vertical resolution). To resolve this
problem additional relief is added where infrastructure is present; 3) Local drain direction is fixed: Water can only
discharge to 1 specific downstream pixel during the entire simulation. Therefore the digital elevation model is
recalculated after an arbitrary time interval on the basis of the actual elevation and the quantity of water present in a grid
cell.
42 Model output
For every interval a map is
created depicting the quantity of
water in a grid-cell. In these
maps areas with urbanisation can
be identified. Water-level in time
can be reported as a hydrograph
at any location in the area.
In figure 5 two simulations are
displayed, the first with one of
three alternative routes for the
railway and a second for the
present situation.
simulated flooded area for presence of railway
" boundary of Castelfranco Emilia Municipality
^w. alternative high velocity raiheay track
5 CONCLUSIONS
From the study of meteorological
data it became clear that on the
basis of merely precipitation no
predictions can be made with
respect to the occurrence of a
flood event. Given the
difficulties in understanding and
thus modelling the mechanisms
huilt up area
flooded area September 1973
w«^ boundary of Castelfranco Emilia Municipality
= Panaro river | à
€ simulated flooded area for present situation
boundary of Castelfranco Emilia Municipality
that provoke an event, it is
thought to be more fruitful to
make predictions with respect to
consequences of what-if
scenarios, rather than predictions with respect to occurrence. Or, as Kundzewicz (1999) puts it: “it is necessary to be
aware of the possibility of floods... living with floods seems more sustainable than a hopeless striving to combat floods”.
In this light, a distributed dynamic model is constructed which allows for the calculation of flood scenarios, which can
be fed by historical or hypothetical precipitation and discharge records.
The inclusion of alternative routes for the proposed railway allows for the evaluation and comparison of the spatial
effects of a flood event. Critical points in the model are calibration and the calculation of soil saturation prior to the
event.
Figure 5. Presence of water on surface for the 1973 flood (left), and a simulation
for one of the proposed railway routes (upper right) and the same simulation for
the current situation (lower right).
ACKNOWLEDGMENTS
The financial support for the study was provided by the European project: *A European Research Network for the
Application of Geomorphology and Environmental Impact Assessment to Transportation Systems (GETS)", (contract
ERBFMRXCT970162), Local Co-ordinator of the Modena and Reggio Emilia University, Prof. M. Panizza.
International Archives of Photogrammetry and Remote Sensing. Vol. XXXIII, Part B7. Amsterdam 2000. 233