THE SELF-IGNITION TEMPERATURE OF COAL DUST IN OXY

THE SELF-IGNITION TEMPERATURE OF
COAL DUST IN OXY-FUEL ATMOSPHERES
D. Wu1, F. Norman2, F. Verplaetsen2, J. Berghmans1, E. Van den Bulck1
Katholieke Universiteit Leuven, Department of Mechanical Engineering, Celestijnenlaan 300A, B3001
Leuven, Belgium
2
Adinex NV, Brouwerijstraat 5/3, B 2200 Noorderwijk, Belgium
Introduction
Oxy-fuel combustion, as one of the most promising technology for CO2 emissions, has been advancing in recent years. In the oxy-fuel combustion system, however, dust may be processed or deposited in
oxygen-enriched environments where little or nothing
is known about the spontaneous ignition risk. Understanding minimum temperature at which dust layer
and deposits ignite is critically important in industries
where smouldering fires can occur, causing consequent dust explosion.
An experimental investigation into the isothermal
slef-ignition of coal dust bulk has been undertaken in
oxy-fuel combustion atmospheres, with the oxygen
mole fractions in the range of 21-50% (21%, 30%,
40% and 50%). South African (SA) coal was determined for self-ignition temperature (SIT or TSI ) using
a device known as a hot oven with temperature controlled by an automated control system (EN 15188)
[1]. The typical temperature evolution curve with
time is shown in Figure 1.
200
T1 (Ignition)
TemperatureC
160
T1 (No ignition)
TO =119C
120
TO =117C
80
40
T1
Ignition
TO=119C
T1
0
40
80
120
160
Time, min
Figure 1: Thermal behaviour of the 50ml South African coal in the isothermal oven at 50% O2 in CO2.
is the radius or characteristic length of
the dust sample,
3
(~600 kg  m ),

is the bulk density of the sample
Q
is the gross calorific value
(27369 kJ  kg ), and 
1
1
is the heat conductivity
1
(0.12 W  m  K ), A is the pre-exponential factor
( s 1 ), Ea is the apparent activation energy ( J  mol1 )
and
is
the
universal
gas
constant
R
(8.314 J  K 1  mol1 ). Equation (1) also gives a linear
correlation between the terms ln( crTSI2 / ro2 ) and
1/ TSI with Ea / R as the slope, which offers the possibility to determine the apparent activation energy and
pre-exponential factor [1].
The influence of oxygen concentration and inert gas
(N2 or CO2) on the self-ignition temperature for the SA
coal sample tested in the hot oven is illustrated in Figure 2. All of them show that the oxygen concentration
has a pronounced influence on the self-ignition temperature. With increasing oxygen concentration the SIT
of the SA coal decreases. This observation is in line
with the findings of Bowes, et al [2] and Schmidt, et al
[3].
Corresponding author: [email protected]
120
110
20
25
30
35
40
45
50
O2 concentration, Vol. %
In order to evaluate the results of the experimental
determination of self-ignition temperatures, the F-K
(Frank-Kamenetskii) theory is employed.
 T2
E
Q Ea
ln( cr 2 SI )  ln(
A)  a
ro
 R
RTSI
400ml
100ml
50ml
25ml
130
100
18 Air
Self-ignition mathematical model
1
ro
ratio of 1),
140
No ignition
TO=117C
0
where  cr depends on the geometry of the dust sample
(e.g.  cr =2.76 for a cylinder with a height to diameter
Self-ignition temperature, C
1
(1)
Figure 2: The SIT of the SA coal samples in the hot
oven test.
Figure 3 shows the correlation between the characteristic lengths of the coal samples and the self-ignition
temperature using the F-K method at various oxygen
concentrations. According to equation (1), the kinetic
parameters can be calculated and are shown in Table 1.
It suggests that the slight deviation in slope for the
lines at different oxygen concentration is not regarded
as significant, which is in line with the observation of
[2]. As for the pre-exponential factors, they are on the
same order of magnitude for the different oxygen concentration. Those results suggest that the reaction
mechanism of the coal dust during the self-heating period does not change with elevating of oxygen concentration.
Air
21%
30%
40%
50%
21
The authors gratefully acknowledge the financial
contribution from the European FP7 project RELCOM
(Reliable and Efficient Combustion of Oxygen/Coal/Recycled Flue Gas Mixtures).
References
[1] CEN, Determination of the Spontaneous Ignition
Behavior of Dust Accumulations. European Standard EN15188, European Committee for Standardization, Brussels, 2007.
[2] P.C. Bowes, P.H. Thomas. Ignition and extinction
phenomena accompanying oxygen-depend selfheating of porous bodies. Combustion and Flame,
10 (3) (1966): 221-230.
2
2
ln(crTSI/r ), crTSI/r in k /m
2
22
Acknowledgements
2
y=50.986-11.861x
20
y=49.352-11.441x
2
2
[3] Schmidt. M., Lohrer, C. & Krause, U. (2003).
Self-ignition of dust at reduced volume fractions
of ambient oxygen. Journal of Loss Prevention in
the Process Industries, 16: 141-147.
y=50.122-11.622x
y=50.656-11.902x
y=50.666-12.026x
19
2,4
2,5
2,6
2,7
1000/TSI, TSI in K
Figure 3: Frank-Kamenetskii plot of self-ignition temperatures
Table 1: Kinetic parameters of the SA coal at various
oxygen concentration
Mixture gas
A
Ea
( kJ  mol )
( s 1 )
50% Vol. O2 in CO2
98 ±6
8.6×109
40% Vol. O2 in CO2
96±4
3.7×109
30% Vol. O2 in CO2
99±4
6.2×109
21% Vol. O2 in CO2
100±2
6.2×109
95±3
1.7×109
Air
1
Conclusions
A series of experiments have been undertaken to
determine the ignition characteristics of the SA coal
dust and the conclusions have been derived as follows:
1. As the basket volume increases, the critical
temperature for ignition decreases significantly.
2. A remarkable increase of the spontaneous ignition risk of the coal dust with increasing the ambient
oxygen concentration.
3. The average value of the apparent activation
energy calculated from the gradients of the straight
lines in Figure 3 is around 98 kJ  mol1 . The slight
variation apparent in the values shown for the different concentrations of oxygen is not regarded as significant. This means that the reaction mechanism is more
or less the same.