| Chapter 3 | |
| Formation of Explosive Gas Clouds | |
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When combustible gas or evaporating liquids are accidentally released
into the atmosphere, a combustible fuel-air cloud may be formed.
Figure 3.1 shows possible events in case of an accidental release.

| Figure 3.1. | An event tree showing typical consequences of accidental release of combustible gas or evaporating liquid into the atmosphere. |
If the gas cloud formed by the release is outside the flammable concentration
range (i.e. below LFL or above UFL, see section
4.1), or the ignition source is lacking, no combustion will occur.
Subsequently the gas cloud will dilute and disappear. In case of an immediate
ignition, a fire will develop. The most dangerous situation, however, will
occur if a large flammable premixed fuel-air cloud is formed and ignites.
A serious explosion may then result.
The objective of this chapter is to:
i) Describe the difference between a jet release and an evaporating
pool.
ii) Describe experimental results from jet releases in a 1:5 scale model
of an offshore module.
iii) Describe FLACS code facilities for simulation of gas dispersion.
iv) Discuss the formation of a combustible gas cloud and ignition.
3.1 Jet Releases and Evaporating Pools
The released substance can be a gas, an evaporating liquid or a gas-liquid
(two phase) flow. The source will be characterised as a jet release (i.e.
gas, two phase or evaporating liquid), or a diffuse release, i.e. evaporating
pool. A jet release and a diffuse source are shown in Figure 3.2.

| Figure 3.2. | Jet release and evaporating pool. |
The two sources have quite different characteristics. The jet release
will have a high momentum and establish a strong flow field due to additional
air entrainment. Recirculation zones may be generated where the gas concentration
can reach a combustible level. For jet releases in a building or offshore
module, the recirculation can result in build-up of large combustible clouds.
The evaporating pool will act as a diffuse release source and the wind
forces and buoyancy will control the dispersion process. The flow velocities
will be much lower than for the jet release. If the evaporating liquid
forms a dense gas, a layer of combustible gas may be formed at the ground
level, or in a lower compartment. Similarly in an open area a dense gas
cloud will have the tendency to intrude into confined spaces such as buildings.
The intrusion of combustible gas into such confined or semi-confined spaces
poses serious problems. As discussed in Chapters 5,6 and 9 to 11, confinement
will generally cause high explosion pressures.
3.2 Gas Dispersion Tests in a 1:5 Scale Offshore Module
Bjørkhaug and Bjerketvedt (1990) have performed gas dispersion
tests in a 1:5 scale offshore module.
Gaseous methane and propane were released inside a module through various
nozzles (420 mm diameter). The reservoir was a 3m3 tank
and the initial pressure was 5-20 barg. The module had forced ventilation
with a bulk flow velocity of 0 m/s to 1.0 m/s.

| Figure 3.3. | Concentration measures at two different locations. |
One of the objectives with this test was to establish the degree of
homogeneity of the cloud in the module. Figure 3.3 shows the concentration
versus time at two different locations at the same level. The upward-pointing
release starts at 20 sec. In the early phase there is a difference in concentration,
but after about 10 sec. the curves are quite similar.
Figure 3.4 shows the concentration in two similar tests at the same
place but at different heights.

| Figure 3.4. | Concentration measurements at different heights in two tests. |
In these tests there are relatively small variations in concentration.
Further the effect of forced ventilation was investigated. Figure 3.5
shows the concentration in three tests with the same source but with different
wind velocities (i.e. bulk flow) through the module.

| Figure 3.5. | Concentration as function of time for different wind velocities through the module. |
Initially the concentration rise was similar for all three cases, at
a certain concentration level however, the transportation of fuel out of
the module was equal to the leak rate and the concentration profile is
flattening out. The higher the wind speed, the lower the concentration
where the concentration profile is flattening out. As the reservoir is
emptied, the concentration gradually decreases. If the fuel concentration
was on the rich side, it would have to pass through the flammable region.
The main findings from these experiments are:
3.3 Gas Dispersion Simulations Using FLACS
Storvik (1991) has used FLACS89 to simulate high momentum jet leaks
and subsequent gas dispersion in a scaled-down model of an offshore module.
Gas dispersion simulations with high momentum jet leaks usually require
many hours of CPU usage due to short time-step and long leak duration (several
minutes).
In FLACS89 the high momentum jet is modelled analytically conserving
the mass and momentum flow, and is coupled to the resolution of the flow
field in the simulation domain. This procedure reduces the need for high
spatial resolution near the jet and is an effective approach to simulate
high momentum leaks.
Forced ventilation is simulated using a wind as boundary condition.
This is useful for simulation of gas dispersion with specified wind speed
and turbulence parameters.
In summary: FLACS89 has built-in facilities for handling realistic gas
dispersion scenarios including external wind fields, various types of leak
sources (jet or diffuse) and wall-functions to account for boundary layer
effects.

| Figure 3.6. | FLACS simulation of gas dispersion from a jet inside an offshore module. Shaded areas show flammable regions. |
Figure 3.6 shows an example of a contour plot from a jet release in
an offshore module. Shaded areas show fuel concentration within the flammability
limits. The high momentum jet and a fairly homogeneous gas cloud on the
upper deck can be identified. The plot also depicts how the gas on the
upper deck is diluted by the flow from the lower deck through the grating
in the intermediate deck.
Results from FLACS dispersion simulations can be used as input parameters
to characterise gas clouds in FLACS gas explosion simulations.
A modified version of FLACS has been used to simulate release of gas
from high pressure pipelines (Sand et al., 1996), taking non-ideal gas
effects into account. The results showed that the lower flammability limit
of gas-air mixture reaches its most remote downstream position relatively
early, before retracting somewhat due to increased entrainment of air.
To ignite a gas cloud requires an ignition source with sufficient strength.
The minimum ignition energy depends on fuel concentration and type of fuel.

| Figure 3.7. | Minimum Ignition Energy. |
As the reservoir is emptied, the release rate will gradually be reduced
and the gas concentration in the cloud will decrease. A weak ignition source
will "sit and wait" until the gas cloud has the right composition
before it ignites. In several accidental gas explosions the time from the
release was initiated until the explosion occurred was 10 to 20 min. In
such cases it is probable that the gas concentration is decreasing at the
time of ignition. It should be stated, however, that this is speculative.

| Figure 3.8. | A weak ignition source may ignite the cloud as the release reservoir is emptied. |
When the ignition source is strong the gas cloud will be ignited when
the edge of the cloud reaches the ignition source. If the ignition source
is weak, however, the source may fail to ignite the cloud in the early
phase of the dispersion process or ignite only a small part of the cloud.
Subsequently, a homogeneous large gas cloud may be formed. This cloud enters
into the flammable concentration as the reservoir is emptied and a weak
ignition source may ignite the cloud. This discussion shows some of the
complexities involved in assessing ignition probability and formation of
explosive gas clouds.
3.5 Ventilation in Compartments
Kletz (1987) claims that "the best building has no walls".
This is true with respect to gas explosion safety. In an open building
the natural ventilation will enhance the gas dispersion and if an explosion
occurs, the open areas will relieve the pressure. If the release rates
are small there is no doubt that mechanical ventilation systems can counteract
the formation of explosive gas clouds. However, for a massive release,
the forced ventilation rate will in general be too low.
A ventilation system may also transport gas from one area to another.
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