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Flame-spray interaction modelling
Alexander Snegirev [email protected] Fire Modeling and Flammability Group Department of Fluid Dynamics (Thermal Physics) Saint-Petersburg Polytechnic University
Objectives
To highlight ongoing research avenues
To present resent advances
To look for an overlap and synergy of research interests
This talk is therefore not strictly adhered to its title, albeit the flame-spray interaction remains the key issue
University of Brighton, UK, 10 August 2015 1
Research avenues
• Combustion physics
• Fire safety science
• Multiphase flows (under
development)
• Water spray fire suppression
• Halons, fuels
• Microscale combustion calorimetry
• Pyrolysis modeling
• Volatile oxidation
• Fire dynamics • Coupled
simulations • Fire
suppression
Fire modeling
Material flammability
Teaching Spray
modeling
University of Brighton, UK, 10 August 2015 2
What would happen during my talk if I consider all topics…
University of Brighton, UK, 10 August 2015 3
I did my best to select topics in this order…
University of Brighton, UK, 10 August 2015 4
An overview
Introduction Fire modeling Coupled
simulations Spray fire
suppression
Governing criteria
Spray model validation
Flame-spray interaction
Flame extinction
Fire suppression
modeling
Conclusions and future
work
University of Brighton, UK, 10 August 2015 5
Research methodology
Theory and modeling
Fire dynamics and smoke movement
Coupled simulations of
turbulent flame and pyrolysis
Water spray fire
suppression
Pyrolysis modeling
Experiment
Microscale combustion calorimetry
Sample cup
University of Brighton, UK, 10 August 2015 6
Publications
Snegirev A.Yu. Perfectly stirred reactor model to evaluate extinction of diffusion flame. Combustion and Flame 2015 (doi:10.1016/j.combustflame.2015.06.019)
Tsoy A.S., Snegirev A.Yu. Large eddy simulation of fine water sprays: comparative analysis of two models and codes. Thermophysics and Aeromechanics 22 (2015), In Press
A. Snegirev, E. Kokovina, A. Tsoy. Coupled simulations of turbulent flame and pyrolysis of combustible material / Proc. European Combustion Meeting – 2015, Paper P4-16, March 30 – April 2, 2015, Budapest, Hungary
Snegirev A.Yu., Tsoy A.S. Treatment of local extinction in CFD fire modeling. Proc. Combustion Institute 35 (2015) 2519-2526
Snegirev A.Yu. Fundamentals of Combustion Theory. St.-Petersburg, SPbPU Publ., 2014, 352 p. (In Russian)
Snegirev A.Yu. Generalized approach to model pyrolysis of flammable materials. Thermochimica Acta 590 (2014) 242-250
A.Yu. Snegirev, V.A. Talalov, V.V. Stepanov, A.S. Tsoy. Oxidation kinetics of pyrolysis volatiles and its implication to critical conditions of flame extinction. Proc. of the 10th International Symposium on Hazards, Prevention, and Mitigation of Industrial Explosions ISHPMIE-X (Bergen, Norway, June 9–14, 2014), 2014, pp. 71-84
A.Yu. Snegirev. Transient temperature gradient in a single-component vaporizing droplet. Int J Heat Mass Transfer 2013 (65) 80–94
A. Snegirev, V. Talalov, V. Stepanov, J. Harris. A new model to predict pyrolysis, ignition and burning of flammable materials in fire tests. Fire Safety Journal 2013 (59) 132-150
A.Yu. Snegirev, V.V. Talalov, V.V. Stepanov, J.N. Harris. Formal kinetics of polystyrene pyrolysis in non-oxidizing atmosphere. Thermochimica Acta 2012 (548) 17-26
Snegirev A.Yu., Frolov A.S. The Large Eddy Simulation of a Turbulent Diffusion Flame. High Temperature 2011 (49) 690–703 University of Brighton, UK, 10 August 2015 7
Building fires
Design fire scenario: a fire in the university classroom (2011)
Fire origin
Fire origin
Exit Time to escape
University of Brighton, UK, 10 August 2015 8
New Pulkovo terminal
45 MW design fire modeling
(SPbSPU, 2011)
University of Brighton, UK, 10 August 2015 9
Fires in the open atmosphere
City of Grozniy, 3/4/2013 Simulation (A. Tsoy, 2013)
University of Brighton, UK, 10 August 2015 10
Coupled simulations
Tight two-way coupling of turbulent diffusion flame and pyrolysis of combustible material governs fire growth rate
Time to ignition, burning rate and flame spread are affected
Positive thermal feedback determines critical conditions of flame ignition and flame extinction
Mass flux of
volatiles
predicted by
Pyropolis
Pyrolyzing material
Mass
flow inlet
BC
Net heat flux
predicted by
Fluent
University of Brighton, UK, 10 August 2015 11
Coupled simulations with FDS (ignition)
PMAA ignition and burning 50 kW/m2
The effect of material
transparency and
volumetric
absorption
E. Kokovina, A. Snegirev ECM 2015
University of Brighton, UK, 10 August 2015 12
Coupled simulations with FDS (steady burning)
Steady burning rate subject to the external heat flux (10x10 cm plate)
Predicted burning rates are considerably different for two versions of FDS code because of strong sensitivity to the flame
The code may not be capable of predicting self-sustained burning and surface flame spread
,0
flame rrnet extfuel
g g g
extfuel
gSteady self sustained
burning rate
q qq qm
h h h
qm
h
University of Brighton, UK, 10 August 2015 13
Sprinkler fire protection in a factory
Two types of fire load (liquid and solid combustible)
Ethanol
Solid fuel
Sprinklers
Prescribed flame spread velocity
Sprinkler location and flow rate in accordance with national fire codes СП5.13130.2009
Fuel mass loss rate is reduced due to wetting
University of Brighton, UK, 10 August 2015 14
Sprinkler fire protection in a factory
No fire suppression: rapid blockage of evacuation pathways
When oxygen in fire room is exhausted, the flame ejects through the openings
Fire suppression: 5 sprinklers activated
Fire is extinguished in 2-3 min
No fire protection system Fire protection system activates
University of Brighton, UK, 10 August 2015 15
Fire suppression in the auxiliary power unit
FirEx project objectives funded by Airbus (2007-2010):
APU
Ultimate • To assist in design and certification of the fire
suppression system
Specific
• To develop efficient computational methodology and software tools to predict discharge, spraying and spread of the extinguishing agent throughout the APU compartment
University of Brighton, UK, 10 August 2015 16
Modeling methodology
University of Brighton, UK, 10 August 2015 17
Fire suppression in the auxiliary power unit
APU
Halon 1301 discharge (experiment: VNIIPO, 2009)
Halon discharge in protected compartment
(modeling: SPbSPU+ChemInform,
2009-2010)
University of Brighton, UK, 10 August 2015 18
Unresolved issues
Validation “backlog”
– Lack of well documented experimental cases
– Model complexity: close interaction of all the submodels. Errors introduced by each submodel obscure overall model performance. A comprehensive validation is required
– The effect of spray refinement needs to be quantified by means of governing criteria
Objectives
– To undertake validation studies
– To assess sensitivity to model parameters
– To identify systematic irregularities and model drawbacks
– To evaluate the effects of spray fineness
– To apply in practical cases
University of Brighton, UK, 10 August 2015 19
Validation matrix
High-pressure fine water spray
Turbulent flame
Bounded fire source
Low-pressure sprinkler
Gaseous flame suppression
Spreading fire
Reduction of pyrolysis rate due to wetting
Spray fineness
University of Brighton, UK, 10 August 2015 20
Initial droplet characterization
“Immediate” atomization model: initial droplet size distribution functions. Initial mean diameter and its variance must be pre-assigned
Initial droplet size PDF is assumed at a spherical surface centered at the nozzle outlet
0
0
2
l
PV
220
0 0 00 4w
DQ V K P D P
1/32
01/350 0
1/3 1/3
0 0 0
1We
lv
l
V DdC C
D P D
2/3 2
0 050 1/3 2/3
0
v
w
D Dd
P Q
Nozzle
diameter K-factor Liquid flow rate
Pressure drop Initial droplet
velocity
Initial median
droplet diameter
Depends on the
nozzle geometry
University of Brighton, UK, 10 August 2015 21
Modeling liquid injection
Combined log-normal and Rosin-Rammler
Hollow or full cone
Computational particles contain a number of real droplets
50
50
50
50
ln11 erf ,
2 2
1 exp ln 2 ,
v
v
v
v
d dd d
R dd
d dd
2
2 ln 2
dv50 = 0.102 mm
University of Brighton, UK, 10 August 2015 22
The effect of spray refinement: an example
Instantaneous droplet locations colored by droplet temperature
Instantaneous vapor mole fraction
LES predictions of vaporizing water spray (full-cone, cone angle 120°, initial droplet velocity 30 m/s, ambient air temperature 20°C, initial droplet temperature 20°C, flowrate 10 l/min)
50 1=50 , S 1vd 1
50 1=200 , S 10vd 2
50 1=500 , S 10vd
1
stopping distance
spray size
S dL
H
University of Brighton, UK, 10 August 2015 23
The effect of spray refinement: an example
Instantaneous droplet locations colored by droplet temperature
Scatter plots of the instantaneous droplet velocity (relative to the gas flow) versus droplet temperature colored by droplet residence time (increased from blue to red). Scatter size scales with droplet diameter
50 1=50 , S 1vd 1
50 1=200 , S 10vd 2
50 1=500 , S 10vd
LES predictions of vaporizing water spray (full-cone, cone angle 120°, initial droplet velocity 30 m/s, ambient air temperature 20°C, initial droplet temperature 20°C, flowrate 10 l/min)
University of Brighton, UK, 10 August 2015 24
Spray structure
1 2S 1, S 1
Vu
orin
en e
t a
l.,
FT
C 2
011 (
86
) 5
33
-561
1S 1
1S 1
Stopping distance, Ld
Cone
section
Neck
Turbulent
crown
2
18
lvelo
g
d
2 1velo i
g
gS
u
Spray structure depends on the stopping distance
Fine droplets are deflected by the gas flow if , where
Spray fineness criteria:
University of Brighton, UK, 10 August 2015 25
Integrated evaporation rate in a starting jet
Coarse spray => low vapor concentration => evaporation rate increases with droplet surface area
Fine spray => high vapor concentration => no increase of evaporation rate with spray refinement
Optimum droplet dispersion exists
About 0.2 mm for fire suppression by fine water sprays
University of Brighton, UK, 10 August 2015 26
Experiment by Ditch and Yu (2008)
Ditch B., Yu H.Z. Fire Safety Science 9, 2008, 541-552
– Nozzle diameter 0.7 mm
– Cone angle 76°
– Pressure 20.68 bar
– Measurements of liquid flow rates and mean droplet diameters (dv50, d32) at the distances of 0.4 and 0.62 m downstream the nozzle
42 cm
60 cm
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The effect of numerical schemes
FDS5
FDS6
Gas velocity
Vapor
concentration
University of Brighton, UK, 10 August 2015 28
The effect of numerical schemes
z = 0.4 m z = 0.62 m
Axial distributions of total liquid/vapor flow rates
Radial distributions of liquid flow rates
FDS5
FDS6
Tsoy A., Snegirev A.
Thermophysics and
aeromechanics 2015
Vol. 22 (accepted)
University of Brighton, UK, 10 August 2015 29
Experiment by Santangelo (2010)
P.E. Santangelo, Exp Thermal Fluid Sci 34 (2010) 1353–1366
Nozzle diameter 0.5 mm
Pressure 60, 70, 80 bar, initial droplet diameter dv50 ~ 90 μ
Measured liquid flow rates and mean droplet diameters (dv50, d32) at the distance of 1 m downstream the nozzle
FDS5 FDS6
Vapor mole fraction
University of Brighton, UK, 10 August 2015 30
Simulation results
FDS5: Large-scale turbulence is under-resolved, too narrow spray is predicted, axial velocity is heavily over-estimated
FDS6: Better resolution of large-scale eddies, reasonable agreement with the experimental radial distributions
Tsoy A., Snegirev A. Thermophysics and
aeromechanics 2015 Vol. 22 (accepted)
60 bar 70 bar 80 bar
University of Brighton, UK, 10 August 2015 31
Unconfined buoyant turbulent diffusion flames
Small-scale and large-scale flames are considered
Experimental data
Q , kW D , m *
1/2 5/2
P
c T g D
* *2/5D Q D ,
m x , m
*D x
Schwille and Lueptow, 2006
15 0.18 1.0 0.18 0.018 9
Sandia, 2007 2500 2.00 0.4 1.38 0.075 18
University of Brighton, UK, 10 August 2015 32
15 kW burner fire
Schwille & Lueptow experiment (2006)
15 kW, 18 cm diameter burner, methane
dv50 = 0.6-0.8 mm
3–11.7 l/min
120º cone angle, 1.6 m height
Spray cone is much wider than the flame base
Investigated numerically by means of URANS (Snegirev, Lipjainen, 2008) and LES (Snegirev et al., 2010)
University of Brighton, UK, 10 August 2015 33
Experiment: flame height depends on water flow rate
15 kW burner fire
Undisturbed flame
(Schwille & Lueptow,
2006)
7.57 l/min
9.65 l/min 11.17 l/min
Nozzle
7.57 l/min
1.2 mm
(simulation)
University of Brighton, UK, 10 August 2015 34
15 kW burner fire: FDS simulation results
Water flow rate 7.57 l/min. The effect of spray fineness:
Time after nozzle activation 4 s 8 s 30 s
dv50 = 1.2 mm
dv50 = 0.9 mm
dv50 = 0.6 mm
University of Brighton, UK, 10 August 2015 35
Transient dynamics of flame-spray interaction
260 kW, 1 m diam., wood volatiles CH2O, mesh 88×88×128, water flow rate 10 l/min
Coarse spray, dv50 =
0.50 mm
Medium spray, dv50 =
0.20 mm
Fine spray, dv50 = 0.08 mm
Time step 0.05 s
University of Brighton, UK, 10 August 2015 36
Regimes of flame-spray interaction
Spray fineness number distinguish qualitatively different regimes of spray interaction with the flame
Coarse spray: S1 = O(1) => Spray drag number, SD
Fine spray: S1 << 1 => Spray momentum number, SM
Extinguishing a 260-kW flame above a 1-m diameter burner (0.2 s after nozzle activation): a) — coarse spray, dv50 = 0.5 mm; b) — medium spray dv50 = 0.2 mm; c) — fine spray 0.08 mm.
Wide-angle nozzle (120° cone), nozzle height 3.0 m above the floor, water flow rate 10 l/min. LES, mesh 88×88×128. Light colour surface — vapour mole fraction 0.01.
Coarse spray: Drops penetrate inside the flame
and evaporate there =>
Fine spray: Vaporized jet suppresses the flame provided jet momentum is high enough
S1 = 0.6 S1 = 0.15 S1 = 0.035
a) b) c)
DS spray droplet drag
plume momentumMS
spray momentum
plume momentum
University of Brighton, UK, 10 August 2015 37
Fire Laboratory for Accreditation of Models and Experiments (FLAME) – Sandia Labs, NM, USA (2007)
2.5 MW pool fire, 2 m diameter (JP8 – C11H21)
Nozzle: 30º cone angle, 5 m height
Spray directed to the pool center (90° and 45°)
Pressure drop affects water flow rate, initial droplet velocity and initial droplet diameter (nozzle diam. D0 = 8.74 mm)
Critical pressure (critical flow rate) separates regimes with and without flame extinguishment
Large-scale flame suppression
Nozzle
Fuel pool
University of Brighton, UK, 10 August 2015 38
FDS simulation results (Tsoy et al., Proc. ISFEH7, 2013)
Large-scale flame suppression
Low pressure
spray
High pressure
spray
University of Brighton, UK, 10 August 2015 39
Need to improve local extinction model
Time to extinction decreases as the pressure increases
Agreement with the experiment improves with grid refinement and increased number of computational droplets
Flame extinction is not resembled
Determined by reduction
of flame height Local extinction
model
Nozzle activates
Flame is down
University of Brighton, UK, 10 August 2015 40
Modeling of extinction in diffusion flames
Activation energy asymptotics for the strained laminar diffusion flamelet (Lecoustre et al, 2010; Narayanan et al, 2011; Vilfayeau et al, 2015)
Adiabatic PSR extinction model: Magnussen et al, 80s; Hewson et al, 2003; Snegirev & Tsoy, Proc. Combust. Inst. 35 (2015)
– Extinction due to excessive strain rate (high-strain limit only)
New non-adiabatic PSR extinction model (Snegirev, 2015):
– Extinction due to excessive strain rate (high-strain limit = blow-off)
– Extinction due to radiative losses from flame (low-strain limit = quenching)
Snegirev, Tsoy, PCI 35
(2015) 2519-2526
Snegirev, Combustion
and flame, 2015
University of Brighton, UK, 10 August 2015 41
The PSR extinction model
Only cell-averaged quantities are available
Reaction zone is not resolved; it occupies a small part of the cell volume
The reaction zone is treated as a PSR fed by the fuel and oxidizer streams
Temperature and composition in the feeding streams is expressed via the cell-averages
Residence time in the PSR is governed by the local (subgrid) strain
Single-step global oxidation reaction, finite rate kinetics
Critical subgrid strain exists causing extinction in the PSR
Such a critical strain depends on cooling and dilution, thereby incorporating all the extinction mechanisms
University of Brighton, UK, 10 August 2015 42
PSR theory to model local extinction
Fuel and energy balance at steady state
Reaction rate
Max flame temperature
Mixture specific heat
Flame temperature at steady state
,0fuel fuel fuel resY Y r 0 loss resh h q
exp
fuel oxn n
fuel fuel oxfuel
fuel ox
M Y Y Er A
M M T
R
,0 ,0
max 0
min ,
ˆ
fuel ox ox lossC res
P
Y Y hT T
q
c
, ,ˆ ˆ ˆ1P P no dil dil P dil dilc c Y c Y
0
ˆ
exp
fuel ox
fuel ox
n n
fuel P res
res n nfuel ox C fuel
l
o
s
x
osM c T T
AM M h Y T Y T E T
q R
The residence time is
coupled with the local
strain
University of Brighton, UK, 10 August 2015 43
PSR theory to model local extinction
Flame temperature at steady state
Critical condition
Extinction occurs, if the subgrid mixing time is less than the critical residence time
Flame temperature at extinction is not constant, being dependent on the amount of a diluent (EGR in engines and furnaces, fire suppressant)
1
0
*
max exp
n
res n
T T TA
T T E T
R
2
max 0
1 1
ext ext ext ext
E n n
T T T T T T
R Extinction temperature
is not constant!
*res A
0extT T
d dT
Classical S-curve
University of Brighton, UK, 10 August 2015 44
Model calibration
Three model parameters: n, A, E
Counter-flow flame measurements of extinction strain and temperature can be used to derive n and A for the given E
Methane-air: Sext = 430 s-1, Text = 1760 K
E = 121 kJ/mol (Coffee et al., 1983,
laminar flame speed modeling)
PSR model: n = 1.69
Heptane-air: Sext = 460 s-1, Text = 1620 K
E = 110 kJ/mol (Seiser et al., 1998,
counter-flow diffusion flame)
PSR model: n = 2.01
University of Brighton, UK, 10 August 2015 45
Implementing local extinction in CFD
Critical flame temperature (CFT) model
Perfectly stirred reactor (PSR) model
2 2O ,0 ,O
max 0ˆ
C
P
Y hT T
c
max 0, , ,extT T T E n
*
1ext extT
A
ext SGSC 1
SGS extS C
Estimating maximum
flame temperature
Solving equation for
the extinction temperature
Evaluating residence
time at extinction
Extinction?
2 2O ,0 ,O
max 0ˆ
C
P
Y hT T
c
CFTT max CFTT T
Estimating maximum
flame temperature
Assume constant
critical flame temperature
Residence time is not considered
Extinction?
University of Brighton, UK, 10 August 2015 46
Flammability diagram: comparison to the CFT model
Conventional model
New model
2
2
0,
O , 0,
,O
P CFT ext
ext ext
C
c T TY T
h
Polystyrene volatiles
(oxidation kinetics is
derived from MCC data)
2
2
max, 0,
O , 0,
,O
,P ext ext
ext ext
C
c T S TY T S
h
Local strain
University of Brighton, UK, 10 August 2015 47
Implementing in CFD
Schwille & Lueptow experiment (2006)
FDS 6
7.57 l/min, dv50 = 1.2 mm
(simulation)
Nozzle
15 kW, 0.18 m
Methane burner
University of Brighton, UK, 10 August 2015 48
The non-adiabatic PSR extinction model
,0fuel fuel fuel resY Y r
0 loss resh h q
04 4
0
ˆ14
P
loss
loss
c T Tq T T
2 2 2 20 CO CO CO CO H O H O soot vP X T X T X T C f T
exp
fuel oxn n
fuel fuel oxfuel
fuel ox
M Y Y Er A
M M T
R
2 2,0 O ,0 O
max 0
min ,
ˆ
loss refuel
P
scY Y s h qT T
c
,0 ,0 maxDa , ,fuel fuel ox resr Y Y T
University of Brighton, UK, 10 August 2015 49
Fundamental flammability limit (CH4 and C7H16)
University of Brighton, UK, 10 August 2015 50
Fundamental flammability limit (pyrolysis volatiles)
Two-distinct flammability limits (high- and low-strain) merge at the fundamental limit (MEC point)
The fundamental limit is obtained from the first principles (competition of the finite rate kinetics and radiative losses from the reaction zone)
Existing techniques typically measure either high- or low-strain limit. Lack of the experimental data for the fundamental limit, particularly for the pyrolysis volatiles
PMMA
University of Brighton, UK, 10 August 2015 51
Fire suppression modeling
Thermal activation of a sprinkler:
Reduction of pyrolysis rate due to surface wetting
2
RTI RTI RTI
gg mg
Heat exchange with Heat losses Cooling byfire plume to the mount water droplets
uT T T TdTu С С
dt
actT T
,0
,
expfuel fuel w w
Mass ofBurning ratewaterno wetting
m t m t e m t dt
University of Brighton, UK, 10 August 2015 52
Suppression of radially spreading fire
Sprinkler activation
– Conventional (thermal)
– Gefest Ltd., St-Petersburg: group enforced activation (thermal activation of the first sprinkler followed by group assignment and enforced activation of the group after 10 s delay)
Modeling
– FDS 5.5
– Large compartment, ceiling clearance 5 and 10 m
– Fire load: 300 kW/m2, max surface area 6x6 m2
– Flame spread velocity 0.01 m/s (α = 0.094 kW/m2, “fast” NFPA204M)
– Flow rate per sprinkler 29 l/min
– Reduction of pyrolysis rate by water ew = 0.3 (m2/kg)/s
– RTI = 140 m1/2s1/2, Tact = 68°C
Heating element
Ignition in
the centre
University of Brighton, UK, 10 August 2015 53
Conventional sprinkler activation
Conventional (thermal) sprinkler activation cannot prevent fire spread, the heat release rate increases to a high value. 10 m ceiling clearance
University of Brighton, UK, 10 August 2015 54
Group enforced sprinkler activation
Group enforced activation suppresses material gasification and stops burning, fire is localized and quenched. 10 m ceiling clearance
University of Brighton, UK, 10 August 2015 55
Radially spreading fire suppression: the effect of spray refinement
dv50 = 500 μ dv50 = 100 μ
Thermal activation, 5 m ceiling clearance
When the fire growth rate is too high, finer spray cannot suppress fire, being less efficient than the coarse spray
Spray momentum is
high enough to deflect
the spray
University of Brighton, UK, 10 August 2015 56
Radially spreading fire suppression: the effect of cross-wind
Due to water spraying beyond the fire origin, suppression efficiency is reduced
Advantage offered by the group activation is also reduced
University of Brighton, UK, 10 August 2015 57
Group activation Thermal activation
No cross-wind
Cross-wind 1.2 m/s
Radially spreading fire suppression: the effect of cross-wind
Скорость бокового ветра: слева – 0 м/с, справа – 1.2 м/с
University of Brighton, UK, 10 August 2015 58
Group activation Thermal activation
Heat release
rate
Number of
activated
sprinklers
Sprays in selected engineering applications
Fire suppression IC Engine Pressurized liquid
discharge
Liquid Water Liquid fuels LPG, LNG,
Halocarbons etc.
Initial mean droplet size
~0.05 – 1.0 mm ~0.004-0.02 mm 0.01-0.04 mm
Nozzle diameter ~1-10 mm ~0.2 mm Unknown in
accidental releases, ~20 mm in FSS
Atomization mechanism
Mechanical Mechanical Flashing
Thermal state of the liquid
Sub-boiling Sub-boiling Superheat, possibly
supercritical
Ambient atmosphere
Atmospheric air, hot combustion
products
Hot combustion products
Atmospheric air, hot combustion
products
Jet flow Sub-sonic,
~10-100 m/s Trans-sonic,
~100-500 m/s Super-sonic, choked,
~50 m/s
University of Brighton, UK, 10 August 2015 59
The diesel spray
Injector make Bosch (1 hole)
Hole diameter 0,2 mm
Fuel volume 30 mm3
Fuel density 808 kg/m3
Gas temperature 540 K
Injection pressure 160 MPa
Wall temperature 360 K
Chamber diameter 50 mm
Chamber length 80 mm
0.3 0.4 0.5 0.6 0.7 ms
2 MPa 6 MPa
2 MPa, RR-LN, dv50 = 8μ, γ = 2.25
Crua et al., Univ of
Brighton, UK, 2008
University of Brighton, UK, 10 August 2015 60
Conclusions
Use of either commercial or open-source software to simulate turbulent evaporating sprays often entails considerable errors in gas/droplet flow rates and velocity distributions
In LES, it is crucially important to ensure capability of the numerical scheme to replicate the large scale turbulent fluctuations
Failure to do so causes underestimated radial jet spread, overestimated jet velocity at the axis. In case of co-axial spray and flame-induced flows, capability of the spray to suppress fire is overestimated
Beyond the droplet movement and evaporation, spray-flame interaction modeling encounters the need to consider:
– Flame extinction at a subgrid level – the new model is proposed
– Reduction of solid fuel gasification due to wetting – spray-material coupling
University of Brighton, UK, 10 August 2015 61
Conclusions
Despite of dramatic difference of quantitative characteristics of sprays in different engineering applications, a similarity exists in their structure and dynamics
Such a similarity can be interpreted in terms of two dimensionless criteria which can also be considered as the spray fineness criteria
– S1 is the ratio of a stopping length for the characteristic droplet to the external length scale (e.g. the distance to the obstacle)
– S2 is the ratio of the droplet sedimentation velocity to that of the external gas flow
Two distinct criteria govern the spray-flame interaction
– In the course spray regime (S1 is of order of 1) the governing criteria is the ratio of the spray droplet drag to the plume momentum
– In the fine spray regime (S1 << 1) the governing criteria is the ratio of the spray momentum to the plume momentum
Optimum initial droplet diameter corresponds to the value below which further spray refinement does not result in a considerable increase of the evaporation rate
University of Brighton, UK, 10 August 2015 62
Future work
Non-combustible sprays
Flame-spray coupling
Flame-material coupling
Spray-material coupling
Combustible sprays
Ignition and extinction
Turbulent flame
modeling
University of Brighton, UK, 10 August 2015 63