The calculations of the drop trajectories were performed with the same CFD package Fluent (versions 4.4 and 4.5). The trajectories were calculated after the wind flow calculation for a chosen geometry, reference wind speed and wind direction.
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Drop trajectory
The motion of a drop is modelled in Fluent with equation
2.10. In Fluent, the drag
coefficient as a function of the Reynolds number of
[Morsi and
Alexander 1972] was implemented (figure 2.6).
The turbulent dispersion of drop trajectories is not easily modelled
because the -
model does not provide detailed information
on small scale eddies or fluctuating velocity components. In
Fluent it is possible to obtain the fluctuating velocity components
by solving the Langevin equation, which results in filtered white
noise. This is called the ``continuous random walk'' model
[Fluent 1997]. This model requires more computational effort
(because the time steps are smaller during the integration of the
particle trajectory equations) than the other model implemented in
Fluent, the ``random walk model'', in which the fluctuating
velocity components are random values which are kept constant over an
interval of time given by the characteristic lifetime of eddies. An
advantage of the continuous random walk model is that it can
include the effects of crossing trajectories.
The Langevin equation of the continuous random walk model is the
following [Fluent 1997]:
The integral time is estimated by the assumption that it is equal
to the Langrangian integral time
, which is proportional
to
. For the
-
model, the Langrangian
integral time is approximately
[Fluent 1997].
The model in Fluent applies a correction of the integral time
to account for the effects of crossing trajectories, depending on the turbulent
kinetic energy and the difference between wind and drop speeds
[Fluent 1997]:
In our calculations we will use two schemes: (1) the calculation of drop trajectories without turbulent dispersion, i.e. straightforward calculation according to eq. 2.10, and (2) the calculation with turbulent drop dispersion according to the continuous random walk model including trajectory crossing effects. The user-definable and other constants mentioned above are kept at their default values.
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Grid
The trajectory calculation has also implications for the
computational grid: the dimensions of the grid cells in which drop
trajectory deviations are expected to occur, should be smaller than the stopping
distance of the smallest drop. This implies a maximum dimension of 0.5
m near the façade, i.e. the approximate stopping distance of 1 m for a
0.5 mm drop at 2 m s (figure 2.8).
Façade sections
For the calculation of catch ratios , the façade is divided
into smaller areas, which we call here ``façade sections''. The applied
division with a numbering scheme is shown in figure
6.2. The measurement positions for driving rain and
wind are located at B1 (position P6) and B12 (P4/5).
Calculation of catch ratios
In a wind field calculated for a given geometry, wind speed and
direction, raindrops with a chosen diameter are released from a
`release grid'. This grid forms a horizontal plane with a certain length and
width, positioned such that the whole façade is covered with
drops. The dimensions of the release grid are not determined
automatically but interactively by trial. For the trajectory
calculations with turbulent dispersion the release grid sizes were
taken larger than strictly necessary. This means that drops from the extremities of the
release grid are released at such a distance that they --with their
dispersed trajectories-- do not hit the building. The release grid is
positioned at 2-3.5 times the Main Building height. Figure
6.3d shows an example of the width of a release grid for
a simulation at a particular wind speed, wind direction and drop
diameter, in which turbulent drop dispersion is included. The other graphs
of figure 6.3 show example drop trajectories for
the same wind speed and direction, but different drop diameters and
with/without turbulent drop dispersion.
After the trajectory calculations, the catch ratio for a
particular raindrop diameter on a particular area on the façade (façade
section) is computed by (cf. eq. 2.26):
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(6.9) |
Figure 6.4 shows an example of the
calculated catch ratio as a function of
for
several raindrop diameters. The curves indicate an average of the
respective data points, which were obtained by reducing the number of
released drops by a factor of two. (More data points are available
for lower
, because dividing a set of released drops in
two sets (with half of the original
) leads to two new
data points. This division should only be repeated a few times, of
course.) By evaluating the convergence of
as a function of
, we determined the minimum number of drops to be
released for a reliable
.
The drop diameters for which drop trajectories are calculated, are
= 0.5, 1.0, 1.5, ... 6.0 mm. The calculated
functions for a
particular façade area based on the mentioned series of drop diameters
are smoothed by interpolation.
The resulting smoothed
functions are used for further driving
rain calculations. These will be presented in section
6.4.
without turb. disp. | with turb. disp. | |||
![]() |
number in | ![]() |
number in | ![]() |
[mm] | release grid | [m![]() |
release grid | [m![]() |
0.5 | 5.4![]() ![]() |
5.9 | 1.4![]() ![]() |
15.3 |
1.0 | 4.8![]() ![]() |
5.9 | 1.3![]() ![]() |
15.3 |
1.5 | 3.1![]() ![]() |
5.9 | 8.1![]() ![]() |
15.1 |
2.0 | 1.9![]() ![]() |
5.8 | 5.1![]() ![]() |
14.8 |
2.5 | 1.9![]() ![]() |
5.8 | 5.1![]() ![]() |
14.8 |
3.0 | 1.6![]() ![]() |
5.8 | 4.2![]() ![]() |
14.7 |
3.5 | 1.5![]() ![]() |
5.8 | 3.9![]() ![]() |
14.6 |
4.0 | 1.2![]() ![]() |
5.8 | 3.1![]() ![]() |
14.5 |
4.5 | 1.2![]() ![]() |
5.8 | 3.1![]() ![]() |
14.5 |
5.0 | 1.2![]() ![]() |
5.8 | 3.1![]() ![]() |
14.5 |
5.5 | 1.0![]() ![]() |
5.8 | 2.8![]() ![]() |
14.4 |
6.0 | 1.0![]() ![]() |
5.8 | 2.8![]() ![]() |
14.4 |
Table 6.1 presents the number of released
drops in a particular simulation. For the trajectory calculations
without turbulent drop dispersion, a total of 25.810
drops
were released; these calculations took 131 hours (
5.5 days) of
CPU time on a Sun Entreprise Server with two 400 MHz UltraSparc-II
processors, 1 Gbyte RAM and the Solaris 2.7 operating system (the CPU
time was
75% of the elapsed clock time). For the trajectory
calculations with turbulent drop dispersion, the numbers were
68.3
10
released drops and 414 hours of CPU time (
17
days) respectively. Of course, the number of released drops and the
time involved with the drop trajectory calculations depend on the
reference wind speed and direction.
Raindrop spectra
As we have a rather limited number of raindrop spectrum data measured with the
disdrometer, we will use the parameterisation of raindrop spectra
reported by [Wessels 1972]. He measured raindrop spectra at De
Bilt (NL) during 1968 and 1969 and obtained a range of the parameter
of the [Best 1950] spectrum formula (eq. 2.24).
Ninety percent of his 533 observations had values of
ranging from
0.88 to 1.77 (with
,
,
, and
). We
will apply these two values of
to calculate two `extreme'
raindrop spectra: one with relatively many small drops and one with
relatively large drops.
wind | Building T | drop trajectories | ||
![]() |
![]() ![]() |
included | n.t.d. | w.t.d. |
210![]() ![]() ![]() |
3.5 m s![]() |
- | - | - |
210![]() |
3.5 m s![]() |
+ | + | - |
3.5 m s![]() |
- | + | + | |
240![]() ![]() ![]() |
5.7 m s![]() |
- | + | - |
11.2 m s![]() |
- | + | - | |
240![]() |
3.5 m s![]() |
+ | - | - |
3.5 m s![]() |
- | + | + | |
270![]() |
5.7 m s![]() |
- | + | + |
11.2 m s![]() |
- | + | - |
Table 6.2 lists the simulations which were performed. Because of their long computation times, the number of drop trajectory simulations is rather small.
© 2002 Fabien J.R. van Mook