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Investigation of Flow Patterns, Combustion And The Particles
Transportation In The Calciner “Flash Furnace" Of Cement
Industry
By
Eng. Hisham Mohammed Sameh Abo Elsaud
A Thesis Submitted to the Faculty of
Engineering at Cairo University in partial
Fulfillment of the Requirements for the
Degree of MASTER OF SCIENCE
In
MECHANICAL POWER ENGINEERING
Under Supervision of
Prof. Dr. Essam E. Khalil
Professor
Mechanical Power Engineering
Faculty of Engineering, Cairo University
Prof. Dr. Mahmoud Fouad DR. Hatem Omar Haredi
Professor Assistant Professor
Mechanical Power Engineering Mechanical Power Engineering
Faculty of Engineering, Cairo University Faculty of Engineering, Cairo University
FACULTY OF ENGINEERING, CAIRO UNIVERSITY
GIZA, EGYPT
2014
2
Abstract
In the process of studying, the working is on a calciner at one kiln line in a cement production
plant in Egypt(CEMEX), the problem at the clinker production rate limited in the kiln line
with the normal operating conditions. The CEMEX company had pursued to use alternative
fuels like biomass and coal at the Calciner but that led to more reduction of the kiln clinker
production rates. The company did a lot of calibrations and measurments on the system to
stand on the main reason. By this time I had finished my master primary studies and began to
look for an interesting thesis research point. I did a research on the academic web sites about
interesting points that focuse on the cement industry and I found that the research on calciner
studies is taking more attention. I spoke with my supervisor Prof. Essam Khalil and
presented a report on previous research studies regarding the calciner, and another report on
the alciner problem and all the calibrations done by CEMEX where I work. He welcomed the
idea and gave me a lot of advices and support on how we can work and study the problem.
He also gave me good support about the ANSYS program and the problem analysis of the
results. I would like to present all thanks for my supervisor prof. Essam Khalil.
A numerical Computational Fluid Dynamics model was developed using the ANSYS 14
software. Due to the complicated physco-chemical processes inside the Calciner, the study
was conducted into three main phases. The first phase was to investigate the effect of the
present Calciner design on the flow and mixing characteristics inside the Calciner without
combustion. The second phase was to investigate the effect of Heavy Fuel Oil (HFO)
viscosity and swirl number on the combustion characteristics inside the Calciner. The HFO
used throughout this study is Bunker C6. The third phase was to study the particulate
transport phenomena and the effect flow behavior on the particles concentration inside the
Calciner. The numerical model is based on the solution of Navier-stockes equation for the gas
flow, and on dynamics model with the influence of turbulence simulated by a two-equation
(k-ε) model. The results of the simulations conducted can be summarized in the following
points. First, the velocity of fresh air entering the Calciner from the Tertiary duct is critically
affecting the flow structure inside the Calciner. Second, The HFO viscosity must be
considered as a function of temperature during the analysis because it significantly affects the
combustion characteristics. Third, a swirl number of 0.6 could be considered optimal from
combustion improvement point of view. Fourth, Design improvements are required to
enhance the fluidization process inside the Calciner.
3
Introduction
Cement is a finely ground, inorganic powder, which when mixed with water forms a paste
that sets and hardens. The Portland cement, the most widely used cement in concrete
construction, was patented in 1824. The cement industry contains many sub-processes chain
starting from quarry, crashing, grinding and preparing of raw materials. The cement
manufacturing sub-processes are included in four main processes routes, the wet processes,
the semi wet processes, the semi dry and the dry processes.The main components of clinker
are lime (CaO), silica sio2), alumina (AL2O3) and iron oxide (fe2O3). Varying amount of these
oxides are found in different mineral compounds such as (limestone, marl and clay) and this
is the specification of the quarry.
Crushing is a size reduction for the main components of the clinker, for the limestone and
clay and iron oxides, reduction sizes of the rocks to be in ranges not exceeding 50 to 100 mm.
Grinding for the raw-mix “the mixture of calcareous and argillaceous material “added with
these corrective materials in suitable proportions and grounded produce raw meal or raw-mix,
and grind for reduction size in ranges by microns.
Raw material preparations, where the corrective additives components and the homogeneous
and blending of the raw-mix for the quality control before the kiln feed.
Clinker burning, the prepared raw material is fed to the kiln system where it is subjected to a
thermal treatment process consisting of the consecutive steps of drying /preheating,
calcination (release of CO2 from limestone), and sintering or “clinkerisation of clinker
minerals at temperature up to1450 ºC and then the clinker is cooled to 100 ºC or 200 ºC and
transported to storage.
The most fuel used in cement industry is the coal followed by heavy oil “Buncker C”, and
natural gas. In Egypt the heavy oil is the most wieldy used.
To produce 1 ton of clinker the typical average consumption of raw materials is 1.57 tons.
The cement industry has a significant effect on the environment. It is responsible for 5% of
the world’s anthropogenic CO2 emissions, and therefore it is an important sector for CO2
mitigation strategies. Around 50% of the CO2 emissions are produced during the cement
manufacturing process comes from the thermal decomposition of limestone; also known as
the calcination process. Additionally 40% comes from the combustion process [1].
The activation energy for the calcination is provided by the combustion heat of the fuel. Dry
heating of raw-mix in vertical suspension preheaters, see Figure 1.1 is mostly used, where
calcination also takes place. The innovation in the entire pyro process in modern cement
4
plants is the use of an additional calcining vessel, in which the raw-mix undergoes calcination
to a level of 90 to 95%. In this way, the calcined raw-mix enters the rotary kiln at a higher
temperature, thus reducing the energy demand and the thermal load on the kiln. After being
heated to the appropriate temperature, it enter the Calciner together with the fuel and the hot
gaseous from the tertiary and the kiln chamber.
The combustion heat released by the fuel causes calcination of the raw-mix according to the
chemical reaction:
CaCO3 --------- CaO + CO2 + 178 kj/mol (1.1)
The high fineness of the raw-mix and the good turbulent mixing cause uniform and fast fuel
combustion and calcination reactions. The products of the Calciner are fed to the last cyclone
that feeds the rotary kiln.
Figure 1.1: General pyro-processing unit of a cement production plant.
From the above, it becomes apparent that control of calcination is important because it affects
the fuel consumption, pollutant emissions and the final cement quality. Therefore,
understanding the mechanisms of flow and transport phenomena in the Calciner may
contribute to more efficient production better quality of cement and improve the calcination
mechanism.
5
Literature Review
Calciners have been studied with different geometries and operational conditions in 2D and
3D CFD simulations. Huanpeng et al [2] studied the influence of various physical parameters
on the dynamics of gas-solid two phase flow in a preCalciner using kinetic theory of granular
flow to present the transport properties of the solid phase in a 2D model. Hu et al. [3] used a
3D model for a dual combustor and preCalciner using a eulerian fram for the gas phase and
lagrangean one for the solid phase in order to predict the burn-out and the decomposition
ratio during the simultaneous injection of two types of coal and raw material into the device.
Iliuta et al. [4] investigated the influence of operating conditions on the level of calcination,
burn-out and NOx emissions of an in-line low NOx Calciner, and made a sensitivity analysis
of their model with respect to aerodynamic and combustion/calcination parameters.
Fidaros et al. [5] presented a numerical model and a parametric study of flow and transport
phenomena that take place in an industrial Calciner. This work show good prediction
capabilities for velocity, temperature and distribution of particles. Bluhm-Drenhaus et al. [6]
studied the heat and mass transfer related to the chemical conversion of limestone to lime in a
shaft kiln, CFD was used to model the transport of mass, momentum and energy in the
continuous phase, while the discrete element method (DEM) was used to model the
mechanical movement and the conversion reactions of the solid materials.
In addition to studies investigating the chemical and physical processes in cement production,
several studies investigated the potential of CO2 emission reduction. In general, CO2
emissions due to fossil fuel combustion in cement production systems can be reduced by
using more efficient technologies in the existing production process [7, 8]. Fidaros et al. [1]
showed a parametric analysis of solar Calciner, using CFD as a research tool, the study also
showed how CO2 emissions can be decreased because the required heat comes from solar
energy. Therefore, fossil fuels are not needed for the calcination processes. Kääntee et al.[9]
investigated the use of alternative fuels in the cement manufacturing process. This research
provided useful data for optimizing the manufacturing process by using different alternative
fuels with lower calorific value than those used in classical configurations. Sheinbaum and
ozawa [10] reported the energy use and the CO2 emissions in the Mexican cement industry,
concluding that the focus of the energy and CO2 emissions reduction should be on the use of
alternative fuels. Hrvoje Mikulcic and Fidaros [11] present a good application of CFD
modeling to support the reduction of CO2 emissions in cement industry for the same design
Calciner geometry reported in the literature [5].
6
HFO combustion in Calciner is non-premixed Liquid spray combustion where a nozzle is
used to atomize liquid fuel into fine droplets injected in hot gaseous environment in which it
is mixed with the oxidizer. For Calciner combustion applications, the simple swirl nozzle is
one of the most common pressure atomizing nozzles. Transport, dispersion, evaporation and
combustion of liquid fuel droplets and sprays are investigated in [12-14]. A few papers
conducted numerical and experimental studies of heavy fuel oil spray combustion in
cylindrical furnaces [15-17]. Barreiros et al. [15] investigated the effect of the burner
geometry and inlet velocities on the final products temperatures, velocities and concentration
inside the furnace. Byrnes et al. [16] carried out an experimental study on the same furnace to
predict the gas temperatures, CO2, CO, O2 and NO concentrations as well as particulate
emissions for five flames with different air excess ratios, swirl numbers, primary air excess
ratios and atomizer cup speeds. Wu et al. [17] investigated the contribution of the number,
location, type and firing mode of fuel oil atomizers on NO emissions reduction in an
industrial burner with heavy fuel oil combustion and highly preheated air. Furuhata et al. [18]
modeled heavy fuel oil spray flame stabilized by a baffle plate. They obtained good results
for flow field under isothermal conditions.
In computational fluid dynamics (CFD) studies, Physical model performance depends
critically on the accuracy of fuel property values, and the effectiveness of CFD modelling
depends on the precision of fuel thermophysical properties. Kyriakides et al. [19] developed a
model to investigate the effect of HFO thermo physical properties and compared the results
of their model against experimental data of Chryssakis et al. [20]. Recent computational
studies utilizing a simple representation of HFO composition have considered a two-
component approach, with the two components representing a residual (heavy) and a cutter
(light) part, both characterized by vapor pressures which are increasing with temperature, and
constant or temperature-dependent values for dynamic viscosity, density, latent heat, specific
heat capacity and surface tension [21], [22]. Kontoulis et al. [23] presented a good study with
a new detailed model for calculating IFO thermophysical properties that had been developed
in the model for different IFO qualities, the model builds on the assumption that marine HFO
is a heavy petroleum fraction of undefined composition. The effect of injection fuel
temperature on the penetration tip investigated by considering a five temperature values,
while the penetration tip is decreasing with fuel initial temperature, higher penetration with
the cold spray due to its minimal breakup, and illustrating a minimal breakup and evaporation
of the cold spray affected on the spray distribution including Sauter Mean Diameter (SMD)
values.
7
Present Numerical Model
In our present study for the Calciner furnace using the computational fluid dynamics CFD
ANSYS 14, to investigate all parameters and physics phenomenon affecting on the Calciner
performance, flow gaseous, heat and mass transfer, combustion reaction for heavy fuel oil,
and the solid particles transportation are presented with the influence of turbulence simulated
by a two-equation (k–ε) model.
First we will explain the system process and operating condotions as figures 2.1 and 2.2. All
data for setting the numerical models about the gaseous mass flow rate, velocities,
temperatures, air O2 & CO2 concentration, fuel consumption kg/s and solid particles CaCO3
kg/s are measured and calibrated by CEMEX project office.
Figure 2.1: show the flow gases stream entering to the Calciner
Coming from the kiln and the tertiary Duct
- The kiln line divides to two string Calciner with Calciner riser duct about 80 m height.
- The flow exhaust gaseous from the kiln enter the kiln chamber and divided to string #1 &
string #2 and by pass flow which is useless gases carried by alkali.
- The gases enter the Calciner come from kiln & tertiary duct.
- The gases from tertiary come from kiln hood, that the clinker outlet from the kiln cooling by
atmospheric air to cooling clinker temperature from 1400 K to 150 k
8
- The gaseous enter the Calciner from the kiln chamber (Temperature = 1300 K , O2 = 0.05 ,
CO2=0.12 , N2 = 0.83 )
- The gaseous enter the Calciner from the tertiary duct ( Temperature = 1123 K, O2= 0.23,
N2=0.73)
Figure 2.2: current study Calciner and kiln line section 5 m & kiln chamber explain the flow-
stream gaseous pass from the kiln enter Calciner.
From figure 2.2:
- Show the two string Calciner for one kiln line, and the Calciner geometry structure we going
to study.
- Show the powder tube feeding raw meal to the Calciner to start the calcination mechanism,
the raw meal is completely drying from the past three stage cyclone and enter the Calciner by
gravity approximately 1.5 m/s, mass flow rate 40 kg/s and temperature 800 k for one string.
- Show the powder tube feeding raw meal to the kiln coming from the final stage cyclone
connecting the Calciner after the calcination done.
- The gases flow stream coming from the kiln resulting the combustion from the main burner
fuel and the completely calcination for the raw meal entering the kiln.
- The bypass flow gases contain an alkali compounds, and it useless.
- Show the position for Burner #1 and Burner #2 for fuel atomization inside the Calciner.
9
Objectives:
 To Investigate the effect of Calciner Design on the flow stream distribution and on
the mixing rate.
 To Study The Granular Transport Phenomena of Solid Particles (CaCo3) inside the
Calciner “the Fluidization process“
 To Investigate effect of HFO viscosity on the injection velocity and the resulting
combustion characteristics :-
 Case #1 ( constant viscosity = 1.7E-5 kg/m.s)
 Case #2 ( Viscosity Function of Temperature )
 To Investigate the effect of swirl number variation of the resulting mixing
inside the Calciner and the resulting improvement on the combustion rate
Case studies:
In our numerical study for Calciner we will divide the case study to three sub cases:
 Investigate the current design of the Calciner for flow gaseous behaviour enter from
the tertiary duct and the kiln chamber ports.
 Investigate the granular transport phenomena inside the Calciner, the solid particles
CaCO3 concentration and distribution. Multi-phase case investigate the influence of the flow
gaseous enter calciner on the turbulence mixing between the gaseous and the particles.
 Investigate the effect of swirl and fuel viscosity on the Combustion characteristics
of Heavy Fuel Oils inside the Calciner.
Numerical Model
The Calciner furnace, Fig.2.2, was investigated numerically in the present study. The height
of the Calciner is 25m and volume is 150m3
. Exhaust gases from kiln chamber and
atmospheric air from tertiary duct enter the Calciner, Tube diameter 600 mm feed the solid
particles CaCO3 inside Calciner, with two burner nozzles 6 mm diameter, Figs. 2.6 and 2.7,
for the burner nozzle and fuel distributer are placed in the first 8 m height from the Calciner
bottom to spray the HFO inside Calciner. Burner #1 injects the HFO in the opposite (Z) axis
direction while burner #2 injects the HFO in the opposite (X) axis direction. The injection
characteristics are reported in Table 6. 3D model for the Calciner and the mesh was generated
using (ANSYS 14.0 Package), grid approximately 6,500,000 cells.
10
2.1 Calciner Geometry for flow stream gaseous investigation
Fig. 2.3 for the Calciner geometry with complete tertiary duct, to investigate the effect of the tertiary
duct design flow stream distribution and on the mixing rate. The boundary conditions for the
flow velocity enter from the tertiary duct for three cases study from table 1.
Figure 2.3: Calciner geometry with the complete tertiary duct Dimensions
Table 1: Boundary conditions of flow velocity simulation
Inlet Boundary Conditions kiln inlet Tertiary inlet powder tube
Axial velocity (m/s ) “ case # 4.1.1 “ 21 27 1.5
/s3
Flow Rate m 40.7 69.5 0.282
Axial velocity (m/s ) “ case # 4.1.2 “ 21 32 1.5
/s3
Flow Rate m 40.7 76.5 0.282
Axial velocity (m/s ) “ case # 4.1.3 “ 21 28 1.5
/s3
Flow Rate m 40.7 66.5 0.282
11
2.2 Calciner Geometry for Granular Transportation Model Investigation
Fig. 2.4 for the Calciner geometry after cut tertiary duct curve, To Study The Granular
Transport Phenomena of Solid Particles (CaCo3) inside the Calciner “The Fluidization
process“. The boundary conditions and case setting for gas phase and solid phase as tables 2,
3 and 4.
Figure 2.4: The Calciner geometry and mesh for the Multi-Phase model granular transportation solid
particles after cut the tertiary duct curve for computational time save
Table 2: Setting case
Setting B.C and Operating Condition CASE
Solver setting Transient, Unsteady Particle Track
Model Multi-Phase Eulerian- DDPM
Turbulent K-ε “ Mixture “
Tracking Scheme Implicit
Primary Phase Gas “ Air “
Secondary Phase Solid “ Granular “ Discrete Phase
Inlet B.C Gas Phase
Kiln Inlet “ Velocity m/s “ 21 m/s
Tertiary Inlet “ Velocity m/s “ 29 m/s
Powder Tube Inlet “ Velocity m/s” 1.5 m/s
Solid Particles Properties “ Density “ 3
1600 kg/m
12
The discrete phase injection type release by face “powder tube" with injector particles
diameter and mass flow rate as below table 4.2. and the secondary phase setting as table 4.3.
Table 3: Injection characteristics secondary phase “solid”
Discrete Phase
Injection
Type
Diameter
Distribution
Particle
Diameter
Flow Rate
Injection #1
Face Tube
Powder
Rosin-Rammler 70-200 Micron 30kg/s
Total Flow Rate 30 kg/s
Table 4: The Secondary Phase “Solid Particles “
Define Discrete Phase Model & Secondary Phase
Setting
Phase Property
Drag Law Wen-Yu
Granular Viscosity “ kg/m-s” Gidaspow
Granular Bulk Viscosity “ kg/m-s” Lun-et-al
Frictional Viscosity “ kg/m-s “ -----------
Granular Temperature “ m2/s2” algebric
Solid Pressure Pascal Lun-et-al
Packing Limit 0.8
13
2.3 Calciner Geometry for Heavy Fuel Oil Combustion Investigation
Fig. 2.5 show the Calciner geometry and the burner #1 & burner #2 position at Calciner. And
fig. 2.6 and 2.7 show the burners fuel distributer and the nozzel 6 mm diameter spray HFO
inside the Calciner.
Figure 2.5: Calciner geometry after removal of the tertiary duct for computational time saving
Figure 2.6: Side elevation of fuel Figure 2.7: Front view for the burner
distributer tangential slots nozzle (6 mm)
2.3.1 Defining the dynamic viscosity and vapour pressure
In the present work for the CFD model HFO combustion we depend on the data output from
Kontoulis et al. [23]. For setting the dynamic viscosity and vapor pressure as function with
the temperature. From the Fig.2.8 and 2.9, we use an accuracy setting for the CFD model
HFO combustion for the main thermophysical fuel properties, and use constant values for the
enthalpy, latent heat at vaporization temperature 400 K. The numerical model for combustion
of heavy fuel oil is verified against data collected from the practical consumption in the
Calciner for 24 hours clinker production at one kiln line for cement production. Boundary
14
conditions for the fuel and the oxidizer stream as well as the kiln line operating conditions are
reported in Table 5 and 6.
Figure 2.7: Computed kinematic viscosity versus of HFO qualities versus temperature
Figure 2.8: Computed vapor pressure of HFO qualities versus temperature. A corresponding curve
for C14H30 is also included.
Figure 2.9: Computed dynamic viscosity of HFO qualities versus temperature. A corres-ponding
curve for C14H30 is also included.
15
Table 5: Fuel Content by species in mass fraction.
Injection fuel oil characteristics as table 6, for the two burner #1 and #2. And the variation for
the swirl number 0.1, 0.3 and 0.6.
Tabel 6: Injection characteristics:
Composition
(mass fraction)
Heavy fuel oil
composition
Oxidizer
[Tertiary Duct]
Secandary Oxidizer
[kiln Chamber]
Carbon % 86.71
Hydrogen % 10.78
Nitrogen % 0. 21
Oxygen % 0. 21
Sulfure % 2.622
2CO - - 0.12
2O - 0.733 0.05
2N - 0.233 0.83
Heavy fuel oil properties
Lower heating value, MJ-kg-1 4.231
Specific heat J/kg 2100
Molecular weight 430
Boundary Condition
Inlet Temperature, K 400 1123 1300
Inlet Velocity, m/s 29 22
Mass flow rate, kg/s 1.5 69 42.46
2
Area, m 1.93 2.378
Inlet Boundary Conditions
Burner #1
“ cone injection “
Burner #2
“ cone injection"
X- position, mm -100 794.09
Y-position, mm 4000 7200
Z-position, mm 609.09 -237
Axial velocity, m/s 40 & 80 40 & 80
Z-axis -1 --------
X-axis -------- -1
Cone angle 30 30
Swirl Number 0.1, 0.3, 0.6 0.1, 0.3, 0.6
Radius “cone”, mm 3 3
Fuel flow rate, kg/s 0.75 0.75
Prticle Diameter, µm 500 500
16
Governing equations
3.1 Gaseous Phase
The general form of the time-averaged transport equation for momentum, heat and mass of
the gases is
 




















































S
rrr
r
rrxx
r
W
r
rV
rr
U
xt





1111
1
)(
1
)()(
(3.1)
Where U, V, W are the time-averaged velocities in the axial, radial and circumferential
direction, respectively, the transport coefficient, and  any time-averaged transported
fluid property.
3.2 Particle Dynamics
The particle trajectories are calculated from their corresponding motion equation:
i
p
p
D fgiUpUF
dt
dUp





)( (3.2)
Where the subscript “p” denotes particle. For spherical particles, FD in the drag force term is:
2
4
Re3
Dp
C
F
p
D
D


 (3.3)
Where the drag coefficient is calculated from:
2
32
1
ReRe
aa
aCD  (3.4)
And 1, 2 and 3 are constant proposed by Morsi and Alexander
The additional force term fi in Eq. (3.2) may be due to pressure gradient, thermophoretic,
Brownian or Saffman lift forces.
3.2.1 Particle Size Distribution
The solid “Raw-Mix “particle sizes follow a Rosin-Rammler distribution:
])/[( 0
n
DD
D eM 
 (3.5)
Where n is calculated from:
)/ln(
)ln(ln
DD
M
n D
 (3.6)
Each size interval is represented by an average diameter for which the trajectory calculation
is performed.
17
3.3 The Multi-Phase Model “Dense Discrete Phase Gas Solid flow”
The Lagrangian discrete phase model follows the Euler- Lagrange approach. The fluid phase
is treated as a continuum by solving the Navier-Stokes equations, while the dispersed phase is
solved by tracking a large number of particles. The dispersed phase can exchange
momentum, mass, and energy with the fluid phase. ANSYS FLUENT predicts the trajectory
of a discrete phase particle by integrating the force balance on the particle, which is written in
a Lagrangian reference frame. This force balance equates the particle inertia with the forces
acting on the particle as equation 3.2
3.3.1 Mathematical model of gas flow
A. Conservation laws
(1) Continuity equations
(a) Fluid phase
0).()( 


ggggg v
t

(3.7)
(b) Particulate phase
0).()( 


sssss v
t

(3.8)
(2) Momentum equations
(a) Fluid phase
gsgggggggggggg vvgsgPvvv
t
 .)().()( 


(3.9)
(b) Particulate phase
)(.).()( sgssssssssssss vvgsgPvvv
t




(3.10)
(3) Equation of conservation of solids fluctuating energy









gsssssssssssss DkvIPvv
t
 ).(:)().()(
3
2
(3.11)
B. Constitutive equations
(a) Fluid phase stress
Ivvv gg
T
gggg ).(
3
2
])([   (3.12)
(b) Gas shear viscosity (SGS)
2/1
2
)(
):()1.0(1.
y
ggggg

 
(3.13)
18
(c) Solid phase stress:
]).(
3
1
])([[).( IvvvIvP s
T
sssssss  
(3.14)
(d) Dissipation fluctuating energy








 ssss v
d
ge .
4
)1(3 0
22


 (3.15)
(e) Radial distribution function at contact
13/1
max,
0 1


















s
s
g


(3.16)
(f) Solid pressure
)]1(21[ 0 egP ssss   (3.17)
(g) Shear viscosity of solids
2
0
0
0
2
)1(
5
4
1
)1(96
10
)1(
5
4






 eg
ge
d
edg s
s
s
sss 





(3.18)
(h) Bulk solids viscosity


 )1(
3
4
0
2
edgsss 
(3.19)
(i) Rate Of Energy Dissipation Per Unit Volume
(3.20)
(j) Exchange of fluctuation energy between gas and particles
(3.21)
(k) Fluid-particulate interphase drag coefficients
(3.22)
(3.23)
(I) Ideal gas equation
19
3.4 Modeling fuel oil spray combustion
In non-premixed combustion, fuel and oxidizer enter the reaction zone in distinct streams.
The present modeling of mixture fraction [24,25] with the method of probability density
function (mixture fraction/PDF) requires the solution of transport equations for one or two
conservative scalar properties. The effect of turbulence is also considered. The method of
mixture fraction with PDF has been developed specifically for turbulent chemically reacting
flow simulations. The chemical reaction is determined by turbulent mixing, which controls
the limits of the kinetic rates. The method is economic, because it does not require the
solution of a large number of transport equations for each chemical species. Moreover, it
allows precise determination of auxiliary variables such as density, and it does not use
average values, in contrast to the method of finite reaction rate. The mixture fraction is as:
0
0
kkF
kk
zz
zz
f


 (3.24)
The value of ƒ is calculated from the solution of a time averaged transport equation
m
ii
i
i
i
i
S
x
f
x
f
x
f
t




















 )()( (3.25)
The source term Sm is present only when particle mass transport to the gaseous phase takes
place. Simultaneously with the solution of Eq. (2), a conservative equation for the variance of
mixture fraction, 2
f describing the interaction between chemistry and turbulence, is solved:
2
2
2
22
)()(
f
k
C
x
f
C
x
f
x
f
x
f
t
d
i
ig
it
i
i
i
i


































(3.26)
The turbulence flow of the gas phase in the furnace is governed by the equations for the
conservation of mass, momentum and energy, The renormalization group (RNG) k-ε model
include the swirling effects were applied. Radiative heat transfer in the furnace is solved
using P1 radiation model. P1 gives resonable accuracy with less effort and account for
radiation exchange between gas and particulates. Fuel droplets evaporate relatively quickly
and influence radiative heat transfer only in the near-burner region. The weighted sum-of-
gray-gases (WSGGM) model is used to determine the absorption coefficient of the gas phase.
20
3.4.1 Heavy fuel oil droplets
droplet size distributions were assumed uniform droplet size 500 µm, injected from the cone
atomizer with angle 30º
and nozzel diameter 6 mm figur 5, The particle trajectories are
calculated from their corresponding motion equation:
i
p
p
D fgiUpUF
dt
dUp





)( (3.27)
Where the subscript “p” denotes particle, ρp , up is the droplet density and velocity
respectively, For spherical particles, u and ρ is the gas phase velocity and density
respectively. The right hand side are the drag force per unit of droplet mass and force of
gravity on the droplet, respectively.
3.4.2 Particle Heat transfer
Convection / Diffusion controlled model
To predict the vaporization from a discrete phase droplet, when the temperature of the droplet
reaches the vaporization temperature Tvap, and continues until the droplet reaches the boiling
point Tbp, or until the droplet volatile fraction is completely consumed
0,0, )1( pvp
bppvap
mfm
TTT


(3.28)
The effect of the convection flow of the evaporating from the droplet surface to the bulk gas
phase (Stefan flow), and the vapor flux from the equation below becomes a source of species
I in the gas phase species transport equation.
)( ,,  isici CCkN (3.29)
Where Ni is the molar flux of vapor into the gas phase (kmol/m2
-s), Kc is convective mass
transfer coefficient (m/s), Ci,s and Ci,∞stand for the vapor concentration at the deroplet
surface (kmol/m3
) and in the bulk gas (kmol/m3
). The boiling point Tpb and the latent heat hfg
are defined as constant property inputs for the droplet particle materials. In the evaporation
process, as the particle change its temperature, the latent heat will vary according to:
 
bp
p
bp
p
T
T
pp
T
T
bpfggpfg dTchdTch ... (3.30)
Include the droplet temperature effects on the latent heat by selecting the “temperature
dependent latent heat “option in the discrete phase model. The droplet temperature is updated
according to a heat balance that relates the sensible heat change in the droplet to the
convective and latent heat transfer between the droplet and the continuous phase:
21
)()(
44
pRppfg
p
pp
p
pp TAh
dt
dm
TThA
dt
dT
cm    (3.31)
Where CP is the droplet heat capacity (j/kg-k), Tp is the droplet temperature (k), h is the
convective heat transfer coefficient (W/m2
-k), T∞ the temperature of continuous phase, dmp/dt
is rate of evaporation (kg/s), hfg is latent heat ( j/kg), εp is particle emissivity (dimensionless),
σ is stefan-boltzmann constant (5.67×10-8
W/m2
-k4
), θR is radiation temperature. Radiation
heat transfer to the particle is included by enable the P-1, using the “particle radiation
interaction“ When the vaporization rate is computed by the convection/diffusion controlled
model, the convection heat transfer coefficient “h” is calculated with a modified Nu number
as follows
)PrRe6.02(
)1ln( 3/12/1
d
p
B
B
k
hd
Nu 





(3.32)
Where dp is the particle diameter, K∞ is the thermal conductivity of the contiuous phase
(w/m-k), Pr is prandtl number of the continuous phase (CPu/K∞), BT is the spalding heat
transfer and is equal to the spalding mass transfer number Bm. To predict the convective
boiling of a discrete phase droplet when the temperature of the droplet has reached the
boiling temperature Tbp, and while the mass of the droplet exceed the nonvolatile fraction,
( 1-ƒv,0 ):
Tp ≥ Tbp and mp > ( 1-ƒv,0 ) mp,0 (3.33)
When the droplet temperature reaches the boiling point, a boiling rate equation is applied, the
mass transfer from the droplet to the gas phase is computed from the following equation
)()(
44
pRppppfg
p
TATThAh
dt
dm
   (3.34)
vaporization and the boiling point temperature are 400 K and 589 K, respectively.
22
Computational Results
4.1 Flow distribution inside the Calciner and the effect of entrance ducts
4.1.1 Case #1 Flow Simulation with Complete Tertiary Duct
Figures 4.1a and b, are the pathline of flow gases and centreline velocity contours inside the
Calciner from the tertiary duct and the kiln chamber. It is clear from the figure that the flow
velocity inside the tertiary ducts increases from 27m/s entering the circular diameter 1812
mm2
, accelerate through the rectangular tertiary duct area to 33m/s at the entering from the
tertiary duct to Calciner. Such high velocity is accompanied with high momentum directed
downwards in the direction of the inlet gases from the kiln chamber. The interaction between
the two flow streams is very difficult and the tertiary gases directs the kiln gases towards the
side wall of the Calciner, opposite wall of the tertiary entrance to the Calciner, as observed
from Fig. 4.2. This flow behaviour is not favourable as it affects the velocity homogeneity
and mixing inside the Calciner and hence the combustion efficiency and CaCO3 particulates
distribution.
a) Pathline of flow gases b) Center line velocity contours
Figure 4.1: the pathline and centerline velcity contours of flow gases for the tertiary duct and the kiln
chamber entering Calciner
23
Figure 4.2: the pathline flow gases velocity from kiln inlet
4.1.2 Case # 2 Flow Simulation with Tertiary Duct Curve Cut (Inlet Velocity 32m/s)
In order to save the computational time, the part of the tertiary duct is removed and the inlet
velocity from the tertiary to the Calciner is assumed uniform and entered as a constant
velocity of 32m/s as mass flow rate 76 m3
/s. Fig. 4.3 a and b are the pathline of tertiary and
kiln flow gases entering the Calciner. The tertiary flow gases velocity is 32m/s while the kiln
flow gases velocity is 21 m/s. It is clear from the figure that removing the tertiary duct did not
affected the flow characteristics and validate the previous analysis. The interaction between
the gas streams is shown in Fig. 4.4. The flow velocity is very high close the wall opposing
the tertiary inlet and separation regions are clear below and above the tertiary jet. The latter is
an indication of a defect in the design of the Calciner and needs improvements to enhance the
flow characteristics in this critical area.
4.1.3 Case # 3 Flow Simulation with Tertiary Duct Cut (Inlet Velocity 28m/s)
When the flow gases velocity from the tertiary duct is reduced from 32m/s to 28m/s, Fig. 4.5,
the flow momentum from the tertiary duct is reduced and a larger area is available from the
Calciner cross section to the kiln flow gases. This enhances the flow characteristics inside the
Calciner in general and reduces the possibility of kiln flow chocking. In conclusion, the flow
velocity entering the Calciner from the tertiary duct should be controlled so that it does not
exceed 30m/s inside the rectangular cross section part before the Calciner in order not to
affect the kiln flow.
24
a) Pathline of flow gases from the tertiary b) Pathline of flow gases from the kiln
Figure 4.3: Pathline of tertiary flow entering the Calciner at velocity 32m/s
Figur 4.4: Flow interaction inside the Calciner Figure 4.5: Pathline of tertiary flow entering the
close to the entaryof the tertiary duct. Calciner at velocity 28m/s.
25
Figures 4.6 a and b show the concentration of O2 and CO2 in the flow gases entering the
Calciner from the tertiary duct and the kiln chamber.
a) O2 b) CO2
Figure 4.6: O2 and CO2 concentration in the flow gases entering the Calciner as boundary
condition before combustion.
Case # 4.2 Multi-Phase Granular Transport
Eluerien-DDPM Turbulent Model for Solid Particels Position and Velocity
Investigations
Figure 4.7 is the path-line flow velocity for a kiln flow inlet velocity 21 m/s before and after
injecting the solid particles, respectively. From the figure it is clear that injecting the solid
particles inside the Calciner reduces the Kiln flow velocity and increases its radial occupation
area.
Figure 4.8, is the tertiary flow velocity entering the Calciner before and after injecting the
solid particles. The figures shows that injecting the solid particles, pushes the tertiary flow
towards the center of the Calciner. Meanwhile the circulation zones observed beside the
tertiary duct inlet almost vanished due to the reduction in the Calciner cross section area
because of the particles injection. The combined velocity contours of the tertiary and the kiln
inside the Calciner before and after injecting the solid particles, respectively, are clear in Fig.
4.9. From the figure, a reduction in the gases flow velocity is clear after injecting the solid
particles. The latter is a result of the added mass of the solid particles which is to be carried
with the flow gases up inside the Calciner and to the following stages.
26
a) Before b) After particles loaded
Figure 4.7: Kiln velocity path-lines inside the Calciner before and after injecting the solid particles
a) Before particles loaded b) After particles loaded
Figure 4.8: Tertiary velocity pathlines inside the Calciner before and after injecting the solid particles
27
a) After particles loaded b) Before
Figure 4.9: Gases velocity contours inside the Calciner before and after injecting the solid particles
Case # 4.2 Solid Particles Traces Injection:-
From Fig. 4.10 a and b. it is observable that the particles diameter distribution inside the
Calciner do not have a relation with its size. Meanwhile, due to the interaction between the
tertiary and kiln flows the particles are concentrated beside the wall facing the tertairy inlet to
the Calciner.
a) Particles track by mm b) Particles by X position
Figure 4.10: Particles track and distribution inside the Calciner .
28
4.3 HFO Combustion Numerical Investigation
HFO combustion in calciner is investigated in 3D model with two setting for dynamic
viscosity and injection velocity. Constant viscosity value 1.7×10-5
kg/m.s with injection
velocity 40 m/s and viscosity function as temperature start value 0.02 kg/m.s at the
vaporization temperature 400 K [23], with injection velocity 80 m/s and 40 m/s. Spray
combustion of HFO is modeled using cone angle 30º, particles diameter 500 µm, and the
swirl number is varied as 0.1, 0.3, 0.6.
4.3.1 The influence of viscosity grade on the HFO combustion characteristics.
Figure 4.11 compare the combustion characteristics for the two cases viscosity variation for
swirl number 0.1. Temperature distribution plane Y and Z at the center burner #1 (a, c), and
plane Y and X at the center burner #2 (b, d). It is obvious from the figure 6 (c), the delay time
of the combustion starting especially with spray fuel oil injected from burner #1 for the
viscosity function as temperature. This delay is a result of the injection of the fuel with high
viscosity at the vaporization temperature. The high viscosity value at the evaporation
temperature and its variation with temperature as Fig.2.9 [23], adds a delay time before the
start of the combustion process to change the phase of the fuel from liquid phase to vapor
phase. In the constant viscosity case figure 4.11 (a), the fuel is defined to be injected in the
vapor phase directly. Also, from the figure 4.11 (c, d) it is observable that only small portion
of the injected fuel is combusted while the rest is combusted in the area surrounding burner
#2. Also, it is observable that the maximum temperature inside the Calciner, 2200K, is higher
than the corresponding maximum temperature in the case of constant viscosity which was
2000K only. This is a result of the delay in the combustion of burner #1 and the concentration
of the combustion in the area surrounding burner #2. This in turn maximizes the heat released
in this region. Close to Burner #2, the temperature is higher than that around burner #1 and
the evaporation process takes place more rabidly.
4.2 Influence of the swirl number on combustion characteristics.
High swirl number (S) strenghtens the circulation zone and enhances mixing. By comparing
Fig.4.11 it is observiable that the circulation zone is narrow with S= 0.1 which leads to
elongated flame. Meanwhile, with S = 0.6, Fig.4.12, the circulation zone is wider than that
observed with S = 0.1 and the mixing is better. The latter leads to improved temperature
distribution inside the Calciner with S = 0.6 case. And disapperance of the flame shape when
compared with the cases of S= 0.1 and 0.3.
29
a) Burner #1, const viscosity b) Burner #2, const viscosity
c) Burner #1, viscosity Function temperature d) Burner #2, viscosity Function temperature
Fig. 4.11: Temperature distribution in the plane of burner #1 and burner #2 axis for two cases,
constant viscosity (a,b) and variation of viscosity with temperature (c,d) for S = 0.1
c) Burner #1, viscosity Function temperature d) Burner #2, viscosity Function temperature
Fig. 4.12: Temperature distribution plane of burner #1 and #2 axis, variable viscosity with
temperature for S = 0.6
30
4.3 The influence of viscosity grade on droplet trajectory penetration.
At constant viscosity, an injection velocity of 40 m/s was considered Fig. 4.13a, then 80 m/s
as in Fig. 4.13b. Injecting the HFO with high viscosity grade affected the penetration depth
inside the Calciner as is clear from Fig. 4.13 and 4.14 for burner #2 for S = 0.1 and 0.6
respectively. The change in the penetration depth affects the combustion characteristics as it
affects the interaction between the fuel and the oxidizer streams. This is confirms that the
change in the viscosity grade has a significant effect on the HFO penetration depth.
a) Burner #2, Injection Velocity 40 m/s b) Burner #2, Injection Velocity 80 m/s
Fig. 4.13: Contoure of particle injection velocity burner #2, for two cases, constant viscosity (a) and
variation viscosity with temperature (b), S = 0.1
a) Injection velocity 40 m/s b) Injection velocity 40 m/s c) Injection velocity 80 m/s
Fig. 4.14: Contoure of injection velocity burner #2, constant viscosity (a), variable viscosity with
temperature (b) & (c), for swirl number 0.6
31
4.4 CO Concentration Comparision, Center line axis of burner #1
Figures 4.15 and 4.16, are the CO concentration variation with axial position for burner #1.
The figures support the previous findings presented for the influence of the viscosity grade
variation on the heavy fuel oil spray combustion charactarestics and the influences of the
swirl numbers on enhances the fuel mixing rate with the oxidizer, Fig. 4.15 show the CO
concentration comparision for the case constant viscosity with injection velocity 40 m/s, and
the case viscosity variabe as temperature with injection velocity 80 m/s, for swirl number 0.1,
0.3, 0.6 and 2. For constant viscosity the spray combustion is defined to be injected the
domain approximatly at the vapor phase, so the CO concentration started earleir, from the
injection position burner #1 X= -609.09mm. For the case variable viscosity with temperature,
the delay for CO concentration is a result of the injection of the fuel with a high viscosity.
Fig. 4.15: CO concentration across axial center burner #1, for case viscosity constant with injection
velocity 40 m/s and case viscosity variable with temperature, for S= 0.1, 0.3, 0.6 and 2.
Figure 4.16 is the CO concentration with axial position for burner #1 at two different
injection velocities,40 and 80 m/s, and the viscosity is variable with temperature. In general,
increasing the injection velocity enhances the penetration of the injected fuel and hence the
mixing with the oxdizer. This is clear from comparing the CO concentration in the two cases
at different swirl numbers. It is observale from the figure the the CO concentration is higher
in the case of low injection velocity especially at high swirling numbers. for S= 0.6 and 2.0
the CO concentration is very high close to the burner location and then it reduces suddenly
with axial distance from the burner. This is a result of the low rate of evaporation of the HFO
and the reduction in the oxdizer quantity. For swirl number 0.1 and 0.3 the CO concentration
is reduced, compared to the two casesof 0.6 and 2.0, because of the enhanced penetration and
32
hence the availability of more oxdizer quantities. Fig. 4.17, show the plane temperature
distribution for the two axial burner #1 and #2 with injection velocity 40 m/s, viscosity
variable with temperature for S= 0.3, the figure support the previous finding presented for the
CO concentration above as Fig. 4.16.
Fig. 4.16: CO concentration across axial center burner #1, for case viscosity variable with
temperature, with injection velocity 40 m/s and 80 m/s, for S= 0.1, 0.3, 0.6 and 2.
a) Burner # 2, Injection Velocity 40 m/s b) Burner 1, Injection Velocity 40 m/s
Fig. 4.17: Temperature distribution in the plane of burner #1 and burner #2 axis for case variation
viscosity with temperature, for S = 0.3
NO emission
The heavy fuel oil in present study contains 0.21% of nitrogen, as shown in Table 5. Fig.
4.18, are the thermal NO emission rate along the centerlines of burners #1 show the thermal
NO rate for the combustion simulation for the viscosity variable temperature with two
injection velocity 40m/s and 80m/s, for considered S = 0.1, 0.3, 0.6 and 2. Accoring to the
33
Fig. 4.18 for the thermal NO around the center burner #1, it is clear the high rate NO
formation for the case injection velocity 40 m/s resulting by the high temperature at the
region front burner #1, and then increase gradually to the center of the furnace resulting the
precence of sufficient quantities of oxygen and nitrogen affected by the low penetration depth
of the injection dropet fuel and weak mixing with the oxidizer. Fig. 4.17b for temperature
plane burner #1 enhancing our analysis. For the case injection velocity 80m/s, the apsence of
the high temperature at the region front burner #1, and the good mixing rate between the
oxidizer and the fuel affected to decrease the NO thermal rate.
Fig. 4.18: Rate of thermal NO across axial center burner #1, for case viscosity variable with
temperature, with injection velocity 40 m/s and 80 m/s, for S= 0.1, 0.3, 0.6 and 2.
Figure 4.19a, b, c and d, show 3D contour X, Y and Z for the temperature distribution inside Calciner
with variation swirl number 0.1, 0.3, 0.6 and 2 for case HFO viscosity variant with temperature.
a) Swirl 0.1 b) Swirl 0.3
34
c)Swirl 0.6 d)Swirl 2
Figure 4.19: Static Temperature, angle cone 30, injection velocity 80 m/s & Partile diam. 0.5 mm for
different swirl number, viscosity function temperature.
Conclusions and Recommendations
Conclusions of the Present Study
The aim of the present study was to numerically investigate the performance of a Calciner
used in cement industry. The Calciner is a furnace placed before the rotary Kiln its main
objectives are the reduction of CO2 emissions and air pollutions while enhancing the cement
quality through separating the calcination and clinkering processes. Understanding the
physics of flow, combustion and particulates transportation inside the Calciner is of especial
importance for efficient cement production. The main physico-chemical processes taking
place inside the Calciner are, the combustion of heavy fuel oil or coal or natural gas and the
strongly endothermic calcination reaction of the raw materials. In order to conduct the present
investigations the Pyro-Clone Calciner at Assiut CEMEX Cement Company is considered
and real dimensions and operating conditions were applied.
A numerical Computational Fluid Dynamics model was developed using the ANSYS 14
software. Due to the complicated physco-chemical processes inside the Calciner, the study
was conducted into three main phases. The first phase was to investigate the effect of the
present Calciner design on the flow and mixing characteristics inside the Calciner without
combustion. The second phase was to investigate the effect of Heavy Fuel Oil (HFO)
viscosity and swirl number on the combustion characteristics inside the Calciner. The HFO
used throughout this study is Bunker C6. The third phase was to study the particulate
transport phenomena and the effect flow behavior on the particles concentration inside the
Calciner. The numerical model is based on the solution of Navier-stockes equation for the gas
flow, and on dynamics model with the influence of turbulence simulated by a two-equation
(k-ε) model.
The results of the simulations conducted can be summarized in the following points.
1. The velocity of fresh air entering the Calicner from the Tertiary is critically affecting
the flow structure inside the Calciner.
35
2. The HFO viscosity must be considered as a function of temperature during the
analysis because it significantly affects the combustion characteristics.
3. The viscosity grade affects the HFO penetration depth inside the Calciner, increasing
the HFO viscosity reduces the penetration depth for the same injection velocity. This
in turn affects the CO and NO emissions distribution along the burners axes.
4. Based on the present study results it could be concluded than A swirl number of 0.6
with cone angle of 30 degrees results in highest combustion improvements.
5. The CO and NO concentrations inside the Calciner are highly dependent on the swirl
number and HFO injection velocity.
6. Design improvements are required to enhance the fluidization process inside the
Calciner.
References
[1] Fidaros DK, Baxevanou CA, Vlachos NS. A parametric study of a solar calcinatory using
computational fluid dynamics. Energy Conversion and Management 2007;48:2784e91
[2] L. Huanpeng, L. Wentie, Z. Jianxiang, J. Ding, Z. Xiujian, L. Huilin, Numerical study of
gas–solid flow in a preCalciner using kinetic theory of granular flow, Chemical Engineering
Journal 102 (2004) 151–160.
[3] Z. Hu, J. Lu, L. Huang, S.Wang, Numerical simulation study on gas–solid two-phase flow
in pre-Calciner, Communications in Nonlinear Science & Numerical Simulation 11 (3)
(2006) 440–451.
[4] I. Iliuta, K. Dam-Johansen, A. Jensen, L.S. Jensen, Modelling of in-linelow- NOx
Calciners — a parametric study, Chemical Engineering Science 57 (2002) 789–903.
[5] Fidaros DK, Baxevanou CA, Dritselis CD, Vlachos NS. Numerical modeling of flow and
transport processes in a Calciner for cement production. Powder Technology
2007;171:81e95.
[6] Bluhm-Drenhaus T, Simsek E, Wirtz S, Scherer V. A coupled fluid dynamicdiscrete
element simulation of heat and mass transfer in a lime shaft kiln. Chemical Engineering
Science 2010;65:2821e34.
[7] Hayashi D, Krey M. Assessment of clean development mechanism potential of large-scale
energy efficiency measures in heavy industries. Energy 2007;32:1917e31.
[8] Akashi O, Hanaoka T, Matsuoka Y, Kainuma M. A projection for global CO2 emissions
from the industrial sector through 2030 based on activity level and technology changes.
Energy 2011;36:1855e67.
[9] Kääntee U, Zevenhoven R, Backam R, Hupa M. Cement manufacturing using alternative
fuels and the advantages of process modeling. Fuel Processing Technology 2004;85:293e301.
[10] Sheinbaum C, Ozawa L. Energy use and CO2 emissions for Mexico’s cement industry.
Energy 1998;23(9):725e32.
[11] Hrvoje Mikul, Milan Vujanovi, Dimitris K. Fidaros. The application of CFD modelling
to support the reduction of CO2 emissions in cement industry
[12] BACHALO, W.: Injection, dispersion and combustion of liquid fuels, 25th Int Symp on
Combustion, The Combustion Institute, 333-371, 1994
[13] CHIU, H.H.: Advances and challenges in droplet and spray combustion: Toward a
unified theory of droplet aerothermochemistry, Progress in Energy and Combustion Science
(2000) 26, 381-416.
[14] Faeth GM. Proc Combust Inst 1996; 26:1593.
[15] BARREIROS, A., CARVALHO, M.G., COSTA, M., LOCKWOOD, F.C.: Prediction of
the near burner region and measurements of NOx and particulate emissions in heavy fuel oil
spray flames, Combustion and Flame (1993) 92, 231-240.
36
[16] BYRNES, M.A., FOUMENYA, E.A., MAHMUDA, T., SHARIFAHA, A.S.A.K.,
ABBASB, T., COSTENB, P.G., LOCKWOOD, F.C.: Measurements and predictions of nitric
oxide and particulates emissions from heavy fuel oil spray flames, 26th Int Symp on
Combustion, The Combustion Institute, 2241-2250, 1996.
[17] WW, S.-R., CHANG, W.-C., CHIAO, J.: Low NOx heavy fuel oil combustion with high
temperature air, Fuel (2007) 86, 820-828.
[18] Furuhata T, Tanno S, Miura T, Ikeda Y, Nakajima T. Energy Convers Manage
1997;38:1111.
[19] Kyriakides N., Chryssakis C., Kaiktsis L., SAE 2009-01-1858 (2009).
[20] Chryssakis C., Pantazis K., Kaiktsis L., CIMAC Congress, Bergen, Norway, Jun 2010,
Paper No. 236.
[21] Goldsworthy L., International Journal of Engine Research, 7: pp. 181-199 (2006).
[22] Struckmeier D., Ph.D. Thesis, Kyushu University, Japan (2010).
[23] Panagiotis Kontoulis, Dimitris Kazangas, and Lambros Kaiktsis: A new model for
marine Heavy Fuel Oil thermophysical properties: validation in a constant volume spray
chamber; National Technical University of Athens, Greece. European Conference on Liquid
Atomization and Spray Systems , Chania, Greece, 1-4 September 2013
[24] Y.R. Shivatahnu, G.M. Faeth, Generalized state relationships for scalar properties in
non-premixed hydrocarbon/air flames, Combustion and Flame 82 (1990) 211–230.
[25] W.P. Jones, J.H. Whitelaw, Calculations methods for reacting turbulent flows: a review,
combustion and flame 48 ( 1982 ) I-26

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Investigation of Flow Patterns in Cement Industry Calciner

  • 1. 1 Investigation of Flow Patterns, Combustion And The Particles Transportation In The Calciner “Flash Furnace" Of Cement Industry By Eng. Hisham Mohammed Sameh Abo Elsaud A Thesis Submitted to the Faculty of Engineering at Cairo University in partial Fulfillment of the Requirements for the Degree of MASTER OF SCIENCE In MECHANICAL POWER ENGINEERING Under Supervision of Prof. Dr. Essam E. Khalil Professor Mechanical Power Engineering Faculty of Engineering, Cairo University Prof. Dr. Mahmoud Fouad DR. Hatem Omar Haredi Professor Assistant Professor Mechanical Power Engineering Mechanical Power Engineering Faculty of Engineering, Cairo University Faculty of Engineering, Cairo University FACULTY OF ENGINEERING, CAIRO UNIVERSITY GIZA, EGYPT 2014
  • 2. 2 Abstract In the process of studying, the working is on a calciner at one kiln line in a cement production plant in Egypt(CEMEX), the problem at the clinker production rate limited in the kiln line with the normal operating conditions. The CEMEX company had pursued to use alternative fuels like biomass and coal at the Calciner but that led to more reduction of the kiln clinker production rates. The company did a lot of calibrations and measurments on the system to stand on the main reason. By this time I had finished my master primary studies and began to look for an interesting thesis research point. I did a research on the academic web sites about interesting points that focuse on the cement industry and I found that the research on calciner studies is taking more attention. I spoke with my supervisor Prof. Essam Khalil and presented a report on previous research studies regarding the calciner, and another report on the alciner problem and all the calibrations done by CEMEX where I work. He welcomed the idea and gave me a lot of advices and support on how we can work and study the problem. He also gave me good support about the ANSYS program and the problem analysis of the results. I would like to present all thanks for my supervisor prof. Essam Khalil. A numerical Computational Fluid Dynamics model was developed using the ANSYS 14 software. Due to the complicated physco-chemical processes inside the Calciner, the study was conducted into three main phases. The first phase was to investigate the effect of the present Calciner design on the flow and mixing characteristics inside the Calciner without combustion. The second phase was to investigate the effect of Heavy Fuel Oil (HFO) viscosity and swirl number on the combustion characteristics inside the Calciner. The HFO used throughout this study is Bunker C6. The third phase was to study the particulate transport phenomena and the effect flow behavior on the particles concentration inside the Calciner. The numerical model is based on the solution of Navier-stockes equation for the gas flow, and on dynamics model with the influence of turbulence simulated by a two-equation (k-ε) model. The results of the simulations conducted can be summarized in the following points. First, the velocity of fresh air entering the Calciner from the Tertiary duct is critically affecting the flow structure inside the Calciner. Second, The HFO viscosity must be considered as a function of temperature during the analysis because it significantly affects the combustion characteristics. Third, a swirl number of 0.6 could be considered optimal from combustion improvement point of view. Fourth, Design improvements are required to enhance the fluidization process inside the Calciner.
  • 3. 3 Introduction Cement is a finely ground, inorganic powder, which when mixed with water forms a paste that sets and hardens. The Portland cement, the most widely used cement in concrete construction, was patented in 1824. The cement industry contains many sub-processes chain starting from quarry, crashing, grinding and preparing of raw materials. The cement manufacturing sub-processes are included in four main processes routes, the wet processes, the semi wet processes, the semi dry and the dry processes.The main components of clinker are lime (CaO), silica sio2), alumina (AL2O3) and iron oxide (fe2O3). Varying amount of these oxides are found in different mineral compounds such as (limestone, marl and clay) and this is the specification of the quarry. Crushing is a size reduction for the main components of the clinker, for the limestone and clay and iron oxides, reduction sizes of the rocks to be in ranges not exceeding 50 to 100 mm. Grinding for the raw-mix “the mixture of calcareous and argillaceous material “added with these corrective materials in suitable proportions and grounded produce raw meal or raw-mix, and grind for reduction size in ranges by microns. Raw material preparations, where the corrective additives components and the homogeneous and blending of the raw-mix for the quality control before the kiln feed. Clinker burning, the prepared raw material is fed to the kiln system where it is subjected to a thermal treatment process consisting of the consecutive steps of drying /preheating, calcination (release of CO2 from limestone), and sintering or “clinkerisation of clinker minerals at temperature up to1450 ºC and then the clinker is cooled to 100 ºC or 200 ºC and transported to storage. The most fuel used in cement industry is the coal followed by heavy oil “Buncker C”, and natural gas. In Egypt the heavy oil is the most wieldy used. To produce 1 ton of clinker the typical average consumption of raw materials is 1.57 tons. The cement industry has a significant effect on the environment. It is responsible for 5% of the world’s anthropogenic CO2 emissions, and therefore it is an important sector for CO2 mitigation strategies. Around 50% of the CO2 emissions are produced during the cement manufacturing process comes from the thermal decomposition of limestone; also known as the calcination process. Additionally 40% comes from the combustion process [1]. The activation energy for the calcination is provided by the combustion heat of the fuel. Dry heating of raw-mix in vertical suspension preheaters, see Figure 1.1 is mostly used, where calcination also takes place. The innovation in the entire pyro process in modern cement
  • 4. 4 plants is the use of an additional calcining vessel, in which the raw-mix undergoes calcination to a level of 90 to 95%. In this way, the calcined raw-mix enters the rotary kiln at a higher temperature, thus reducing the energy demand and the thermal load on the kiln. After being heated to the appropriate temperature, it enter the Calciner together with the fuel and the hot gaseous from the tertiary and the kiln chamber. The combustion heat released by the fuel causes calcination of the raw-mix according to the chemical reaction: CaCO3 --------- CaO + CO2 + 178 kj/mol (1.1) The high fineness of the raw-mix and the good turbulent mixing cause uniform and fast fuel combustion and calcination reactions. The products of the Calciner are fed to the last cyclone that feeds the rotary kiln. Figure 1.1: General pyro-processing unit of a cement production plant. From the above, it becomes apparent that control of calcination is important because it affects the fuel consumption, pollutant emissions and the final cement quality. Therefore, understanding the mechanisms of flow and transport phenomena in the Calciner may contribute to more efficient production better quality of cement and improve the calcination mechanism.
  • 5. 5 Literature Review Calciners have been studied with different geometries and operational conditions in 2D and 3D CFD simulations. Huanpeng et al [2] studied the influence of various physical parameters on the dynamics of gas-solid two phase flow in a preCalciner using kinetic theory of granular flow to present the transport properties of the solid phase in a 2D model. Hu et al. [3] used a 3D model for a dual combustor and preCalciner using a eulerian fram for the gas phase and lagrangean one for the solid phase in order to predict the burn-out and the decomposition ratio during the simultaneous injection of two types of coal and raw material into the device. Iliuta et al. [4] investigated the influence of operating conditions on the level of calcination, burn-out and NOx emissions of an in-line low NOx Calciner, and made a sensitivity analysis of their model with respect to aerodynamic and combustion/calcination parameters. Fidaros et al. [5] presented a numerical model and a parametric study of flow and transport phenomena that take place in an industrial Calciner. This work show good prediction capabilities for velocity, temperature and distribution of particles. Bluhm-Drenhaus et al. [6] studied the heat and mass transfer related to the chemical conversion of limestone to lime in a shaft kiln, CFD was used to model the transport of mass, momentum and energy in the continuous phase, while the discrete element method (DEM) was used to model the mechanical movement and the conversion reactions of the solid materials. In addition to studies investigating the chemical and physical processes in cement production, several studies investigated the potential of CO2 emission reduction. In general, CO2 emissions due to fossil fuel combustion in cement production systems can be reduced by using more efficient technologies in the existing production process [7, 8]. Fidaros et al. [1] showed a parametric analysis of solar Calciner, using CFD as a research tool, the study also showed how CO2 emissions can be decreased because the required heat comes from solar energy. Therefore, fossil fuels are not needed for the calcination processes. Kääntee et al.[9] investigated the use of alternative fuels in the cement manufacturing process. This research provided useful data for optimizing the manufacturing process by using different alternative fuels with lower calorific value than those used in classical configurations. Sheinbaum and ozawa [10] reported the energy use and the CO2 emissions in the Mexican cement industry, concluding that the focus of the energy and CO2 emissions reduction should be on the use of alternative fuels. Hrvoje Mikulcic and Fidaros [11] present a good application of CFD modeling to support the reduction of CO2 emissions in cement industry for the same design Calciner geometry reported in the literature [5].
  • 6. 6 HFO combustion in Calciner is non-premixed Liquid spray combustion where a nozzle is used to atomize liquid fuel into fine droplets injected in hot gaseous environment in which it is mixed with the oxidizer. For Calciner combustion applications, the simple swirl nozzle is one of the most common pressure atomizing nozzles. Transport, dispersion, evaporation and combustion of liquid fuel droplets and sprays are investigated in [12-14]. A few papers conducted numerical and experimental studies of heavy fuel oil spray combustion in cylindrical furnaces [15-17]. Barreiros et al. [15] investigated the effect of the burner geometry and inlet velocities on the final products temperatures, velocities and concentration inside the furnace. Byrnes et al. [16] carried out an experimental study on the same furnace to predict the gas temperatures, CO2, CO, O2 and NO concentrations as well as particulate emissions for five flames with different air excess ratios, swirl numbers, primary air excess ratios and atomizer cup speeds. Wu et al. [17] investigated the contribution of the number, location, type and firing mode of fuel oil atomizers on NO emissions reduction in an industrial burner with heavy fuel oil combustion and highly preheated air. Furuhata et al. [18] modeled heavy fuel oil spray flame stabilized by a baffle plate. They obtained good results for flow field under isothermal conditions. In computational fluid dynamics (CFD) studies, Physical model performance depends critically on the accuracy of fuel property values, and the effectiveness of CFD modelling depends on the precision of fuel thermophysical properties. Kyriakides et al. [19] developed a model to investigate the effect of HFO thermo physical properties and compared the results of their model against experimental data of Chryssakis et al. [20]. Recent computational studies utilizing a simple representation of HFO composition have considered a two- component approach, with the two components representing a residual (heavy) and a cutter (light) part, both characterized by vapor pressures which are increasing with temperature, and constant or temperature-dependent values for dynamic viscosity, density, latent heat, specific heat capacity and surface tension [21], [22]. Kontoulis et al. [23] presented a good study with a new detailed model for calculating IFO thermophysical properties that had been developed in the model for different IFO qualities, the model builds on the assumption that marine HFO is a heavy petroleum fraction of undefined composition. The effect of injection fuel temperature on the penetration tip investigated by considering a five temperature values, while the penetration tip is decreasing with fuel initial temperature, higher penetration with the cold spray due to its minimal breakup, and illustrating a minimal breakup and evaporation of the cold spray affected on the spray distribution including Sauter Mean Diameter (SMD) values.
  • 7. 7 Present Numerical Model In our present study for the Calciner furnace using the computational fluid dynamics CFD ANSYS 14, to investigate all parameters and physics phenomenon affecting on the Calciner performance, flow gaseous, heat and mass transfer, combustion reaction for heavy fuel oil, and the solid particles transportation are presented with the influence of turbulence simulated by a two-equation (k–ε) model. First we will explain the system process and operating condotions as figures 2.1 and 2.2. All data for setting the numerical models about the gaseous mass flow rate, velocities, temperatures, air O2 & CO2 concentration, fuel consumption kg/s and solid particles CaCO3 kg/s are measured and calibrated by CEMEX project office. Figure 2.1: show the flow gases stream entering to the Calciner Coming from the kiln and the tertiary Duct - The kiln line divides to two string Calciner with Calciner riser duct about 80 m height. - The flow exhaust gaseous from the kiln enter the kiln chamber and divided to string #1 & string #2 and by pass flow which is useless gases carried by alkali. - The gases enter the Calciner come from kiln & tertiary duct. - The gases from tertiary come from kiln hood, that the clinker outlet from the kiln cooling by atmospheric air to cooling clinker temperature from 1400 K to 150 k
  • 8. 8 - The gaseous enter the Calciner from the kiln chamber (Temperature = 1300 K , O2 = 0.05 , CO2=0.12 , N2 = 0.83 ) - The gaseous enter the Calciner from the tertiary duct ( Temperature = 1123 K, O2= 0.23, N2=0.73) Figure 2.2: current study Calciner and kiln line section 5 m & kiln chamber explain the flow- stream gaseous pass from the kiln enter Calciner. From figure 2.2: - Show the two string Calciner for one kiln line, and the Calciner geometry structure we going to study. - Show the powder tube feeding raw meal to the Calciner to start the calcination mechanism, the raw meal is completely drying from the past three stage cyclone and enter the Calciner by gravity approximately 1.5 m/s, mass flow rate 40 kg/s and temperature 800 k for one string. - Show the powder tube feeding raw meal to the kiln coming from the final stage cyclone connecting the Calciner after the calcination done. - The gases flow stream coming from the kiln resulting the combustion from the main burner fuel and the completely calcination for the raw meal entering the kiln. - The bypass flow gases contain an alkali compounds, and it useless. - Show the position for Burner #1 and Burner #2 for fuel atomization inside the Calciner.
  • 9. 9 Objectives:  To Investigate the effect of Calciner Design on the flow stream distribution and on the mixing rate.  To Study The Granular Transport Phenomena of Solid Particles (CaCo3) inside the Calciner “the Fluidization process“  To Investigate effect of HFO viscosity on the injection velocity and the resulting combustion characteristics :-  Case #1 ( constant viscosity = 1.7E-5 kg/m.s)  Case #2 ( Viscosity Function of Temperature )  To Investigate the effect of swirl number variation of the resulting mixing inside the Calciner and the resulting improvement on the combustion rate Case studies: In our numerical study for Calciner we will divide the case study to three sub cases:  Investigate the current design of the Calciner for flow gaseous behaviour enter from the tertiary duct and the kiln chamber ports.  Investigate the granular transport phenomena inside the Calciner, the solid particles CaCO3 concentration and distribution. Multi-phase case investigate the influence of the flow gaseous enter calciner on the turbulence mixing between the gaseous and the particles.  Investigate the effect of swirl and fuel viscosity on the Combustion characteristics of Heavy Fuel Oils inside the Calciner. Numerical Model The Calciner furnace, Fig.2.2, was investigated numerically in the present study. The height of the Calciner is 25m and volume is 150m3 . Exhaust gases from kiln chamber and atmospheric air from tertiary duct enter the Calciner, Tube diameter 600 mm feed the solid particles CaCO3 inside Calciner, with two burner nozzles 6 mm diameter, Figs. 2.6 and 2.7, for the burner nozzle and fuel distributer are placed in the first 8 m height from the Calciner bottom to spray the HFO inside Calciner. Burner #1 injects the HFO in the opposite (Z) axis direction while burner #2 injects the HFO in the opposite (X) axis direction. The injection characteristics are reported in Table 6. 3D model for the Calciner and the mesh was generated using (ANSYS 14.0 Package), grid approximately 6,500,000 cells.
  • 10. 10 2.1 Calciner Geometry for flow stream gaseous investigation Fig. 2.3 for the Calciner geometry with complete tertiary duct, to investigate the effect of the tertiary duct design flow stream distribution and on the mixing rate. The boundary conditions for the flow velocity enter from the tertiary duct for three cases study from table 1. Figure 2.3: Calciner geometry with the complete tertiary duct Dimensions Table 1: Boundary conditions of flow velocity simulation Inlet Boundary Conditions kiln inlet Tertiary inlet powder tube Axial velocity (m/s ) “ case # 4.1.1 “ 21 27 1.5 /s3 Flow Rate m 40.7 69.5 0.282 Axial velocity (m/s ) “ case # 4.1.2 “ 21 32 1.5 /s3 Flow Rate m 40.7 76.5 0.282 Axial velocity (m/s ) “ case # 4.1.3 “ 21 28 1.5 /s3 Flow Rate m 40.7 66.5 0.282
  • 11. 11 2.2 Calciner Geometry for Granular Transportation Model Investigation Fig. 2.4 for the Calciner geometry after cut tertiary duct curve, To Study The Granular Transport Phenomena of Solid Particles (CaCo3) inside the Calciner “The Fluidization process“. The boundary conditions and case setting for gas phase and solid phase as tables 2, 3 and 4. Figure 2.4: The Calciner geometry and mesh for the Multi-Phase model granular transportation solid particles after cut the tertiary duct curve for computational time save Table 2: Setting case Setting B.C and Operating Condition CASE Solver setting Transient, Unsteady Particle Track Model Multi-Phase Eulerian- DDPM Turbulent K-ε “ Mixture “ Tracking Scheme Implicit Primary Phase Gas “ Air “ Secondary Phase Solid “ Granular “ Discrete Phase Inlet B.C Gas Phase Kiln Inlet “ Velocity m/s “ 21 m/s Tertiary Inlet “ Velocity m/s “ 29 m/s Powder Tube Inlet “ Velocity m/s” 1.5 m/s Solid Particles Properties “ Density “ 3 1600 kg/m
  • 12. 12 The discrete phase injection type release by face “powder tube" with injector particles diameter and mass flow rate as below table 4.2. and the secondary phase setting as table 4.3. Table 3: Injection characteristics secondary phase “solid” Discrete Phase Injection Type Diameter Distribution Particle Diameter Flow Rate Injection #1 Face Tube Powder Rosin-Rammler 70-200 Micron 30kg/s Total Flow Rate 30 kg/s Table 4: The Secondary Phase “Solid Particles “ Define Discrete Phase Model & Secondary Phase Setting Phase Property Drag Law Wen-Yu Granular Viscosity “ kg/m-s” Gidaspow Granular Bulk Viscosity “ kg/m-s” Lun-et-al Frictional Viscosity “ kg/m-s “ ----------- Granular Temperature “ m2/s2” algebric Solid Pressure Pascal Lun-et-al Packing Limit 0.8
  • 13. 13 2.3 Calciner Geometry for Heavy Fuel Oil Combustion Investigation Fig. 2.5 show the Calciner geometry and the burner #1 & burner #2 position at Calciner. And fig. 2.6 and 2.7 show the burners fuel distributer and the nozzel 6 mm diameter spray HFO inside the Calciner. Figure 2.5: Calciner geometry after removal of the tertiary duct for computational time saving Figure 2.6: Side elevation of fuel Figure 2.7: Front view for the burner distributer tangential slots nozzle (6 mm) 2.3.1 Defining the dynamic viscosity and vapour pressure In the present work for the CFD model HFO combustion we depend on the data output from Kontoulis et al. [23]. For setting the dynamic viscosity and vapor pressure as function with the temperature. From the Fig.2.8 and 2.9, we use an accuracy setting for the CFD model HFO combustion for the main thermophysical fuel properties, and use constant values for the enthalpy, latent heat at vaporization temperature 400 K. The numerical model for combustion of heavy fuel oil is verified against data collected from the practical consumption in the Calciner for 24 hours clinker production at one kiln line for cement production. Boundary
  • 14. 14 conditions for the fuel and the oxidizer stream as well as the kiln line operating conditions are reported in Table 5 and 6. Figure 2.7: Computed kinematic viscosity versus of HFO qualities versus temperature Figure 2.8: Computed vapor pressure of HFO qualities versus temperature. A corresponding curve for C14H30 is also included. Figure 2.9: Computed dynamic viscosity of HFO qualities versus temperature. A corres-ponding curve for C14H30 is also included.
  • 15. 15 Table 5: Fuel Content by species in mass fraction. Injection fuel oil characteristics as table 6, for the two burner #1 and #2. And the variation for the swirl number 0.1, 0.3 and 0.6. Tabel 6: Injection characteristics: Composition (mass fraction) Heavy fuel oil composition Oxidizer [Tertiary Duct] Secandary Oxidizer [kiln Chamber] Carbon % 86.71 Hydrogen % 10.78 Nitrogen % 0. 21 Oxygen % 0. 21 Sulfure % 2.622 2CO - - 0.12 2O - 0.733 0.05 2N - 0.233 0.83 Heavy fuel oil properties Lower heating value, MJ-kg-1 4.231 Specific heat J/kg 2100 Molecular weight 430 Boundary Condition Inlet Temperature, K 400 1123 1300 Inlet Velocity, m/s 29 22 Mass flow rate, kg/s 1.5 69 42.46 2 Area, m 1.93 2.378 Inlet Boundary Conditions Burner #1 “ cone injection “ Burner #2 “ cone injection" X- position, mm -100 794.09 Y-position, mm 4000 7200 Z-position, mm 609.09 -237 Axial velocity, m/s 40 & 80 40 & 80 Z-axis -1 -------- X-axis -------- -1 Cone angle 30 30 Swirl Number 0.1, 0.3, 0.6 0.1, 0.3, 0.6 Radius “cone”, mm 3 3 Fuel flow rate, kg/s 0.75 0.75 Prticle Diameter, µm 500 500
  • 16. 16 Governing equations 3.1 Gaseous Phase The general form of the time-averaged transport equation for momentum, heat and mass of the gases is                                                       S rrr r rrxx r W r rV rr U xt      1111 1 )( 1 )()( (3.1) Where U, V, W are the time-averaged velocities in the axial, radial and circumferential direction, respectively, the transport coefficient, and  any time-averaged transported fluid property. 3.2 Particle Dynamics The particle trajectories are calculated from their corresponding motion equation: i p p D fgiUpUF dt dUp      )( (3.2) Where the subscript “p” denotes particle. For spherical particles, FD in the drag force term is: 2 4 Re3 Dp C F p D D    (3.3) Where the drag coefficient is calculated from: 2 32 1 ReRe aa aCD  (3.4) And 1, 2 and 3 are constant proposed by Morsi and Alexander The additional force term fi in Eq. (3.2) may be due to pressure gradient, thermophoretic, Brownian or Saffman lift forces. 3.2.1 Particle Size Distribution The solid “Raw-Mix “particle sizes follow a Rosin-Rammler distribution: ])/[( 0 n DD D eM   (3.5) Where n is calculated from: )/ln( )ln(ln DD M n D  (3.6) Each size interval is represented by an average diameter for which the trajectory calculation is performed.
  • 17. 17 3.3 The Multi-Phase Model “Dense Discrete Phase Gas Solid flow” The Lagrangian discrete phase model follows the Euler- Lagrange approach. The fluid phase is treated as a continuum by solving the Navier-Stokes equations, while the dispersed phase is solved by tracking a large number of particles. The dispersed phase can exchange momentum, mass, and energy with the fluid phase. ANSYS FLUENT predicts the trajectory of a discrete phase particle by integrating the force balance on the particle, which is written in a Lagrangian reference frame. This force balance equates the particle inertia with the forces acting on the particle as equation 3.2 3.3.1 Mathematical model of gas flow A. Conservation laws (1) Continuity equations (a) Fluid phase 0).()(    ggggg v t  (3.7) (b) Particulate phase 0).()(    sssss v t  (3.8) (2) Momentum equations (a) Fluid phase gsgggggggggggg vvgsgPvvv t  .)().()(    (3.9) (b) Particulate phase )(.).()( sgssssssssssss vvgsgPvvv t     (3.10) (3) Equation of conservation of solids fluctuating energy          gsssssssssssss DkvIPvv t  ).(:)().()( 3 2 (3.11) B. Constitutive equations (a) Fluid phase stress Ivvv gg T gggg ).( 3 2 ])([   (3.12) (b) Gas shear viscosity (SGS) 2/1 2 )( ):()1.0(1. y ggggg    (3.13)
  • 18. 18 (c) Solid phase stress: ]).( 3 1 ])([[).( IvvvIvP s T sssssss   (3.14) (d) Dissipation fluctuating energy          ssss v d ge . 4 )1(3 0 22    (3.15) (e) Radial distribution function at contact 13/1 max, 0 1                   s s g   (3.16) (f) Solid pressure )]1(21[ 0 egP ssss   (3.17) (g) Shear viscosity of solids 2 0 0 0 2 )1( 5 4 1 )1(96 10 )1( 5 4        eg ge d edg s s s sss       (3.18) (h) Bulk solids viscosity    )1( 3 4 0 2 edgsss  (3.19) (i) Rate Of Energy Dissipation Per Unit Volume (3.20) (j) Exchange of fluctuation energy between gas and particles (3.21) (k) Fluid-particulate interphase drag coefficients (3.22) (3.23) (I) Ideal gas equation
  • 19. 19 3.4 Modeling fuel oil spray combustion In non-premixed combustion, fuel and oxidizer enter the reaction zone in distinct streams. The present modeling of mixture fraction [24,25] with the method of probability density function (mixture fraction/PDF) requires the solution of transport equations for one or two conservative scalar properties. The effect of turbulence is also considered. The method of mixture fraction with PDF has been developed specifically for turbulent chemically reacting flow simulations. The chemical reaction is determined by turbulent mixing, which controls the limits of the kinetic rates. The method is economic, because it does not require the solution of a large number of transport equations for each chemical species. Moreover, it allows precise determination of auxiliary variables such as density, and it does not use average values, in contrast to the method of finite reaction rate. The mixture fraction is as: 0 0 kkF kk zz zz f    (3.24) The value of ƒ is calculated from the solution of a time averaged transport equation m ii i i i i S x f x f x f t                      )()( (3.25) The source term Sm is present only when particle mass transport to the gaseous phase takes place. Simultaneously with the solution of Eq. (2), a conservative equation for the variance of mixture fraction, 2 f describing the interaction between chemistry and turbulence, is solved: 2 2 2 22 )()( f k C x f C x f x f x f t d i ig it i i i i                                   (3.26) The turbulence flow of the gas phase in the furnace is governed by the equations for the conservation of mass, momentum and energy, The renormalization group (RNG) k-ε model include the swirling effects were applied. Radiative heat transfer in the furnace is solved using P1 radiation model. P1 gives resonable accuracy with less effort and account for radiation exchange between gas and particulates. Fuel droplets evaporate relatively quickly and influence radiative heat transfer only in the near-burner region. The weighted sum-of- gray-gases (WSGGM) model is used to determine the absorption coefficient of the gas phase.
  • 20. 20 3.4.1 Heavy fuel oil droplets droplet size distributions were assumed uniform droplet size 500 µm, injected from the cone atomizer with angle 30º and nozzel diameter 6 mm figur 5, The particle trajectories are calculated from their corresponding motion equation: i p p D fgiUpUF dt dUp      )( (3.27) Where the subscript “p” denotes particle, ρp , up is the droplet density and velocity respectively, For spherical particles, u and ρ is the gas phase velocity and density respectively. The right hand side are the drag force per unit of droplet mass and force of gravity on the droplet, respectively. 3.4.2 Particle Heat transfer Convection / Diffusion controlled model To predict the vaporization from a discrete phase droplet, when the temperature of the droplet reaches the vaporization temperature Tvap, and continues until the droplet reaches the boiling point Tbp, or until the droplet volatile fraction is completely consumed 0,0, )1( pvp bppvap mfm TTT   (3.28) The effect of the convection flow of the evaporating from the droplet surface to the bulk gas phase (Stefan flow), and the vapor flux from the equation below becomes a source of species I in the gas phase species transport equation. )( ,,  isici CCkN (3.29) Where Ni is the molar flux of vapor into the gas phase (kmol/m2 -s), Kc is convective mass transfer coefficient (m/s), Ci,s and Ci,∞stand for the vapor concentration at the deroplet surface (kmol/m3 ) and in the bulk gas (kmol/m3 ). The boiling point Tpb and the latent heat hfg are defined as constant property inputs for the droplet particle materials. In the evaporation process, as the particle change its temperature, the latent heat will vary according to:   bp p bp p T T pp T T bpfggpfg dTchdTch ... (3.30) Include the droplet temperature effects on the latent heat by selecting the “temperature dependent latent heat “option in the discrete phase model. The droplet temperature is updated according to a heat balance that relates the sensible heat change in the droplet to the convective and latent heat transfer between the droplet and the continuous phase:
  • 21. 21 )()( 44 pRppfg p pp p pp TAh dt dm TThA dt dT cm    (3.31) Where CP is the droplet heat capacity (j/kg-k), Tp is the droplet temperature (k), h is the convective heat transfer coefficient (W/m2 -k), T∞ the temperature of continuous phase, dmp/dt is rate of evaporation (kg/s), hfg is latent heat ( j/kg), εp is particle emissivity (dimensionless), σ is stefan-boltzmann constant (5.67×10-8 W/m2 -k4 ), θR is radiation temperature. Radiation heat transfer to the particle is included by enable the P-1, using the “particle radiation interaction“ When the vaporization rate is computed by the convection/diffusion controlled model, the convection heat transfer coefficient “h” is calculated with a modified Nu number as follows )PrRe6.02( )1ln( 3/12/1 d p B B k hd Nu       (3.32) Where dp is the particle diameter, K∞ is the thermal conductivity of the contiuous phase (w/m-k), Pr is prandtl number of the continuous phase (CPu/K∞), BT is the spalding heat transfer and is equal to the spalding mass transfer number Bm. To predict the convective boiling of a discrete phase droplet when the temperature of the droplet has reached the boiling temperature Tbp, and while the mass of the droplet exceed the nonvolatile fraction, ( 1-ƒv,0 ): Tp ≥ Tbp and mp > ( 1-ƒv,0 ) mp,0 (3.33) When the droplet temperature reaches the boiling point, a boiling rate equation is applied, the mass transfer from the droplet to the gas phase is computed from the following equation )()( 44 pRppppfg p TATThAh dt dm    (3.34) vaporization and the boiling point temperature are 400 K and 589 K, respectively.
  • 22. 22 Computational Results 4.1 Flow distribution inside the Calciner and the effect of entrance ducts 4.1.1 Case #1 Flow Simulation with Complete Tertiary Duct Figures 4.1a and b, are the pathline of flow gases and centreline velocity contours inside the Calciner from the tertiary duct and the kiln chamber. It is clear from the figure that the flow velocity inside the tertiary ducts increases from 27m/s entering the circular diameter 1812 mm2 , accelerate through the rectangular tertiary duct area to 33m/s at the entering from the tertiary duct to Calciner. Such high velocity is accompanied with high momentum directed downwards in the direction of the inlet gases from the kiln chamber. The interaction between the two flow streams is very difficult and the tertiary gases directs the kiln gases towards the side wall of the Calciner, opposite wall of the tertiary entrance to the Calciner, as observed from Fig. 4.2. This flow behaviour is not favourable as it affects the velocity homogeneity and mixing inside the Calciner and hence the combustion efficiency and CaCO3 particulates distribution. a) Pathline of flow gases b) Center line velocity contours Figure 4.1: the pathline and centerline velcity contours of flow gases for the tertiary duct and the kiln chamber entering Calciner
  • 23. 23 Figure 4.2: the pathline flow gases velocity from kiln inlet 4.1.2 Case # 2 Flow Simulation with Tertiary Duct Curve Cut (Inlet Velocity 32m/s) In order to save the computational time, the part of the tertiary duct is removed and the inlet velocity from the tertiary to the Calciner is assumed uniform and entered as a constant velocity of 32m/s as mass flow rate 76 m3 /s. Fig. 4.3 a and b are the pathline of tertiary and kiln flow gases entering the Calciner. The tertiary flow gases velocity is 32m/s while the kiln flow gases velocity is 21 m/s. It is clear from the figure that removing the tertiary duct did not affected the flow characteristics and validate the previous analysis. The interaction between the gas streams is shown in Fig. 4.4. The flow velocity is very high close the wall opposing the tertiary inlet and separation regions are clear below and above the tertiary jet. The latter is an indication of a defect in the design of the Calciner and needs improvements to enhance the flow characteristics in this critical area. 4.1.3 Case # 3 Flow Simulation with Tertiary Duct Cut (Inlet Velocity 28m/s) When the flow gases velocity from the tertiary duct is reduced from 32m/s to 28m/s, Fig. 4.5, the flow momentum from the tertiary duct is reduced and a larger area is available from the Calciner cross section to the kiln flow gases. This enhances the flow characteristics inside the Calciner in general and reduces the possibility of kiln flow chocking. In conclusion, the flow velocity entering the Calciner from the tertiary duct should be controlled so that it does not exceed 30m/s inside the rectangular cross section part before the Calciner in order not to affect the kiln flow.
  • 24. 24 a) Pathline of flow gases from the tertiary b) Pathline of flow gases from the kiln Figure 4.3: Pathline of tertiary flow entering the Calciner at velocity 32m/s Figur 4.4: Flow interaction inside the Calciner Figure 4.5: Pathline of tertiary flow entering the close to the entaryof the tertiary duct. Calciner at velocity 28m/s.
  • 25. 25 Figures 4.6 a and b show the concentration of O2 and CO2 in the flow gases entering the Calciner from the tertiary duct and the kiln chamber. a) O2 b) CO2 Figure 4.6: O2 and CO2 concentration in the flow gases entering the Calciner as boundary condition before combustion. Case # 4.2 Multi-Phase Granular Transport Eluerien-DDPM Turbulent Model for Solid Particels Position and Velocity Investigations Figure 4.7 is the path-line flow velocity for a kiln flow inlet velocity 21 m/s before and after injecting the solid particles, respectively. From the figure it is clear that injecting the solid particles inside the Calciner reduces the Kiln flow velocity and increases its radial occupation area. Figure 4.8, is the tertiary flow velocity entering the Calciner before and after injecting the solid particles. The figures shows that injecting the solid particles, pushes the tertiary flow towards the center of the Calciner. Meanwhile the circulation zones observed beside the tertiary duct inlet almost vanished due to the reduction in the Calciner cross section area because of the particles injection. The combined velocity contours of the tertiary and the kiln inside the Calciner before and after injecting the solid particles, respectively, are clear in Fig. 4.9. From the figure, a reduction in the gases flow velocity is clear after injecting the solid particles. The latter is a result of the added mass of the solid particles which is to be carried with the flow gases up inside the Calciner and to the following stages.
  • 26. 26 a) Before b) After particles loaded Figure 4.7: Kiln velocity path-lines inside the Calciner before and after injecting the solid particles a) Before particles loaded b) After particles loaded Figure 4.8: Tertiary velocity pathlines inside the Calciner before and after injecting the solid particles
  • 27. 27 a) After particles loaded b) Before Figure 4.9: Gases velocity contours inside the Calciner before and after injecting the solid particles Case # 4.2 Solid Particles Traces Injection:- From Fig. 4.10 a and b. it is observable that the particles diameter distribution inside the Calciner do not have a relation with its size. Meanwhile, due to the interaction between the tertiary and kiln flows the particles are concentrated beside the wall facing the tertairy inlet to the Calciner. a) Particles track by mm b) Particles by X position Figure 4.10: Particles track and distribution inside the Calciner .
  • 28. 28 4.3 HFO Combustion Numerical Investigation HFO combustion in calciner is investigated in 3D model with two setting for dynamic viscosity and injection velocity. Constant viscosity value 1.7×10-5 kg/m.s with injection velocity 40 m/s and viscosity function as temperature start value 0.02 kg/m.s at the vaporization temperature 400 K [23], with injection velocity 80 m/s and 40 m/s. Spray combustion of HFO is modeled using cone angle 30º, particles diameter 500 µm, and the swirl number is varied as 0.1, 0.3, 0.6. 4.3.1 The influence of viscosity grade on the HFO combustion characteristics. Figure 4.11 compare the combustion characteristics for the two cases viscosity variation for swirl number 0.1. Temperature distribution plane Y and Z at the center burner #1 (a, c), and plane Y and X at the center burner #2 (b, d). It is obvious from the figure 6 (c), the delay time of the combustion starting especially with spray fuel oil injected from burner #1 for the viscosity function as temperature. This delay is a result of the injection of the fuel with high viscosity at the vaporization temperature. The high viscosity value at the evaporation temperature and its variation with temperature as Fig.2.9 [23], adds a delay time before the start of the combustion process to change the phase of the fuel from liquid phase to vapor phase. In the constant viscosity case figure 4.11 (a), the fuel is defined to be injected in the vapor phase directly. Also, from the figure 4.11 (c, d) it is observable that only small portion of the injected fuel is combusted while the rest is combusted in the area surrounding burner #2. Also, it is observable that the maximum temperature inside the Calciner, 2200K, is higher than the corresponding maximum temperature in the case of constant viscosity which was 2000K only. This is a result of the delay in the combustion of burner #1 and the concentration of the combustion in the area surrounding burner #2. This in turn maximizes the heat released in this region. Close to Burner #2, the temperature is higher than that around burner #1 and the evaporation process takes place more rabidly. 4.2 Influence of the swirl number on combustion characteristics. High swirl number (S) strenghtens the circulation zone and enhances mixing. By comparing Fig.4.11 it is observiable that the circulation zone is narrow with S= 0.1 which leads to elongated flame. Meanwhile, with S = 0.6, Fig.4.12, the circulation zone is wider than that observed with S = 0.1 and the mixing is better. The latter leads to improved temperature distribution inside the Calciner with S = 0.6 case. And disapperance of the flame shape when compared with the cases of S= 0.1 and 0.3.
  • 29. 29 a) Burner #1, const viscosity b) Burner #2, const viscosity c) Burner #1, viscosity Function temperature d) Burner #2, viscosity Function temperature Fig. 4.11: Temperature distribution in the plane of burner #1 and burner #2 axis for two cases, constant viscosity (a,b) and variation of viscosity with temperature (c,d) for S = 0.1 c) Burner #1, viscosity Function temperature d) Burner #2, viscosity Function temperature Fig. 4.12: Temperature distribution plane of burner #1 and #2 axis, variable viscosity with temperature for S = 0.6
  • 30. 30 4.3 The influence of viscosity grade on droplet trajectory penetration. At constant viscosity, an injection velocity of 40 m/s was considered Fig. 4.13a, then 80 m/s as in Fig. 4.13b. Injecting the HFO with high viscosity grade affected the penetration depth inside the Calciner as is clear from Fig. 4.13 and 4.14 for burner #2 for S = 0.1 and 0.6 respectively. The change in the penetration depth affects the combustion characteristics as it affects the interaction between the fuel and the oxidizer streams. This is confirms that the change in the viscosity grade has a significant effect on the HFO penetration depth. a) Burner #2, Injection Velocity 40 m/s b) Burner #2, Injection Velocity 80 m/s Fig. 4.13: Contoure of particle injection velocity burner #2, for two cases, constant viscosity (a) and variation viscosity with temperature (b), S = 0.1 a) Injection velocity 40 m/s b) Injection velocity 40 m/s c) Injection velocity 80 m/s Fig. 4.14: Contoure of injection velocity burner #2, constant viscosity (a), variable viscosity with temperature (b) & (c), for swirl number 0.6
  • 31. 31 4.4 CO Concentration Comparision, Center line axis of burner #1 Figures 4.15 and 4.16, are the CO concentration variation with axial position for burner #1. The figures support the previous findings presented for the influence of the viscosity grade variation on the heavy fuel oil spray combustion charactarestics and the influences of the swirl numbers on enhances the fuel mixing rate with the oxidizer, Fig. 4.15 show the CO concentration comparision for the case constant viscosity with injection velocity 40 m/s, and the case viscosity variabe as temperature with injection velocity 80 m/s, for swirl number 0.1, 0.3, 0.6 and 2. For constant viscosity the spray combustion is defined to be injected the domain approximatly at the vapor phase, so the CO concentration started earleir, from the injection position burner #1 X= -609.09mm. For the case variable viscosity with temperature, the delay for CO concentration is a result of the injection of the fuel with a high viscosity. Fig. 4.15: CO concentration across axial center burner #1, for case viscosity constant with injection velocity 40 m/s and case viscosity variable with temperature, for S= 0.1, 0.3, 0.6 and 2. Figure 4.16 is the CO concentration with axial position for burner #1 at two different injection velocities,40 and 80 m/s, and the viscosity is variable with temperature. In general, increasing the injection velocity enhances the penetration of the injected fuel and hence the mixing with the oxdizer. This is clear from comparing the CO concentration in the two cases at different swirl numbers. It is observale from the figure the the CO concentration is higher in the case of low injection velocity especially at high swirling numbers. for S= 0.6 and 2.0 the CO concentration is very high close to the burner location and then it reduces suddenly with axial distance from the burner. This is a result of the low rate of evaporation of the HFO and the reduction in the oxdizer quantity. For swirl number 0.1 and 0.3 the CO concentration is reduced, compared to the two casesof 0.6 and 2.0, because of the enhanced penetration and
  • 32. 32 hence the availability of more oxdizer quantities. Fig. 4.17, show the plane temperature distribution for the two axial burner #1 and #2 with injection velocity 40 m/s, viscosity variable with temperature for S= 0.3, the figure support the previous finding presented for the CO concentration above as Fig. 4.16. Fig. 4.16: CO concentration across axial center burner #1, for case viscosity variable with temperature, with injection velocity 40 m/s and 80 m/s, for S= 0.1, 0.3, 0.6 and 2. a) Burner # 2, Injection Velocity 40 m/s b) Burner 1, Injection Velocity 40 m/s Fig. 4.17: Temperature distribution in the plane of burner #1 and burner #2 axis for case variation viscosity with temperature, for S = 0.3 NO emission The heavy fuel oil in present study contains 0.21% of nitrogen, as shown in Table 5. Fig. 4.18, are the thermal NO emission rate along the centerlines of burners #1 show the thermal NO rate for the combustion simulation for the viscosity variable temperature with two injection velocity 40m/s and 80m/s, for considered S = 0.1, 0.3, 0.6 and 2. Accoring to the
  • 33. 33 Fig. 4.18 for the thermal NO around the center burner #1, it is clear the high rate NO formation for the case injection velocity 40 m/s resulting by the high temperature at the region front burner #1, and then increase gradually to the center of the furnace resulting the precence of sufficient quantities of oxygen and nitrogen affected by the low penetration depth of the injection dropet fuel and weak mixing with the oxidizer. Fig. 4.17b for temperature plane burner #1 enhancing our analysis. For the case injection velocity 80m/s, the apsence of the high temperature at the region front burner #1, and the good mixing rate between the oxidizer and the fuel affected to decrease the NO thermal rate. Fig. 4.18: Rate of thermal NO across axial center burner #1, for case viscosity variable with temperature, with injection velocity 40 m/s and 80 m/s, for S= 0.1, 0.3, 0.6 and 2. Figure 4.19a, b, c and d, show 3D contour X, Y and Z for the temperature distribution inside Calciner with variation swirl number 0.1, 0.3, 0.6 and 2 for case HFO viscosity variant with temperature. a) Swirl 0.1 b) Swirl 0.3
  • 34. 34 c)Swirl 0.6 d)Swirl 2 Figure 4.19: Static Temperature, angle cone 30, injection velocity 80 m/s & Partile diam. 0.5 mm for different swirl number, viscosity function temperature. Conclusions and Recommendations Conclusions of the Present Study The aim of the present study was to numerically investigate the performance of a Calciner used in cement industry. The Calciner is a furnace placed before the rotary Kiln its main objectives are the reduction of CO2 emissions and air pollutions while enhancing the cement quality through separating the calcination and clinkering processes. Understanding the physics of flow, combustion and particulates transportation inside the Calciner is of especial importance for efficient cement production. The main physico-chemical processes taking place inside the Calciner are, the combustion of heavy fuel oil or coal or natural gas and the strongly endothermic calcination reaction of the raw materials. In order to conduct the present investigations the Pyro-Clone Calciner at Assiut CEMEX Cement Company is considered and real dimensions and operating conditions were applied. A numerical Computational Fluid Dynamics model was developed using the ANSYS 14 software. Due to the complicated physco-chemical processes inside the Calciner, the study was conducted into three main phases. The first phase was to investigate the effect of the present Calciner design on the flow and mixing characteristics inside the Calciner without combustion. The second phase was to investigate the effect of Heavy Fuel Oil (HFO) viscosity and swirl number on the combustion characteristics inside the Calciner. The HFO used throughout this study is Bunker C6. The third phase was to study the particulate transport phenomena and the effect flow behavior on the particles concentration inside the Calciner. The numerical model is based on the solution of Navier-stockes equation for the gas flow, and on dynamics model with the influence of turbulence simulated by a two-equation (k-ε) model. The results of the simulations conducted can be summarized in the following points. 1. The velocity of fresh air entering the Calicner from the Tertiary is critically affecting the flow structure inside the Calciner.
  • 35. 35 2. The HFO viscosity must be considered as a function of temperature during the analysis because it significantly affects the combustion characteristics. 3. The viscosity grade affects the HFO penetration depth inside the Calciner, increasing the HFO viscosity reduces the penetration depth for the same injection velocity. This in turn affects the CO and NO emissions distribution along the burners axes. 4. Based on the present study results it could be concluded than A swirl number of 0.6 with cone angle of 30 degrees results in highest combustion improvements. 5. The CO and NO concentrations inside the Calciner are highly dependent on the swirl number and HFO injection velocity. 6. Design improvements are required to enhance the fluidization process inside the Calciner. References [1] Fidaros DK, Baxevanou CA, Vlachos NS. A parametric study of a solar calcinatory using computational fluid dynamics. Energy Conversion and Management 2007;48:2784e91 [2] L. Huanpeng, L. Wentie, Z. Jianxiang, J. Ding, Z. Xiujian, L. Huilin, Numerical study of gas–solid flow in a preCalciner using kinetic theory of granular flow, Chemical Engineering Journal 102 (2004) 151–160. [3] Z. Hu, J. Lu, L. Huang, S.Wang, Numerical simulation study on gas–solid two-phase flow in pre-Calciner, Communications in Nonlinear Science & Numerical Simulation 11 (3) (2006) 440–451. [4] I. Iliuta, K. Dam-Johansen, A. Jensen, L.S. Jensen, Modelling of in-linelow- NOx Calciners — a parametric study, Chemical Engineering Science 57 (2002) 789–903. [5] Fidaros DK, Baxevanou CA, Dritselis CD, Vlachos NS. Numerical modeling of flow and transport processes in a Calciner for cement production. Powder Technology 2007;171:81e95. [6] Bluhm-Drenhaus T, Simsek E, Wirtz S, Scherer V. A coupled fluid dynamicdiscrete element simulation of heat and mass transfer in a lime shaft kiln. Chemical Engineering Science 2010;65:2821e34. [7] Hayashi D, Krey M. Assessment of clean development mechanism potential of large-scale energy efficiency measures in heavy industries. Energy 2007;32:1917e31. [8] Akashi O, Hanaoka T, Matsuoka Y, Kainuma M. A projection for global CO2 emissions from the industrial sector through 2030 based on activity level and technology changes. Energy 2011;36:1855e67. [9] Kääntee U, Zevenhoven R, Backam R, Hupa M. Cement manufacturing using alternative fuels and the advantages of process modeling. Fuel Processing Technology 2004;85:293e301. [10] Sheinbaum C, Ozawa L. Energy use and CO2 emissions for Mexico’s cement industry. Energy 1998;23(9):725e32. [11] Hrvoje Mikul, Milan Vujanovi, Dimitris K. Fidaros. The application of CFD modelling to support the reduction of CO2 emissions in cement industry [12] BACHALO, W.: Injection, dispersion and combustion of liquid fuels, 25th Int Symp on Combustion, The Combustion Institute, 333-371, 1994 [13] CHIU, H.H.: Advances and challenges in droplet and spray combustion: Toward a unified theory of droplet aerothermochemistry, Progress in Energy and Combustion Science (2000) 26, 381-416. [14] Faeth GM. Proc Combust Inst 1996; 26:1593. [15] BARREIROS, A., CARVALHO, M.G., COSTA, M., LOCKWOOD, F.C.: Prediction of the near burner region and measurements of NOx and particulate emissions in heavy fuel oil spray flames, Combustion and Flame (1993) 92, 231-240.
  • 36. 36 [16] BYRNES, M.A., FOUMENYA, E.A., MAHMUDA, T., SHARIFAHA, A.S.A.K., ABBASB, T., COSTENB, P.G., LOCKWOOD, F.C.: Measurements and predictions of nitric oxide and particulates emissions from heavy fuel oil spray flames, 26th Int Symp on Combustion, The Combustion Institute, 2241-2250, 1996. [17] WW, S.-R., CHANG, W.-C., CHIAO, J.: Low NOx heavy fuel oil combustion with high temperature air, Fuel (2007) 86, 820-828. [18] Furuhata T, Tanno S, Miura T, Ikeda Y, Nakajima T. Energy Convers Manage 1997;38:1111. [19] Kyriakides N., Chryssakis C., Kaiktsis L., SAE 2009-01-1858 (2009). [20] Chryssakis C., Pantazis K., Kaiktsis L., CIMAC Congress, Bergen, Norway, Jun 2010, Paper No. 236. [21] Goldsworthy L., International Journal of Engine Research, 7: pp. 181-199 (2006). [22] Struckmeier D., Ph.D. Thesis, Kyushu University, Japan (2010). [23] Panagiotis Kontoulis, Dimitris Kazangas, and Lambros Kaiktsis: A new model for marine Heavy Fuel Oil thermophysical properties: validation in a constant volume spray chamber; National Technical University of Athens, Greece. European Conference on Liquid Atomization and Spray Systems , Chania, Greece, 1-4 September 2013 [24] Y.R. Shivatahnu, G.M. Faeth, Generalized state relationships for scalar properties in non-premixed hydrocarbon/air flames, Combustion and Flame 82 (1990) 211–230. [25] W.P. Jones, J.H. Whitelaw, Calculations methods for reacting turbulent flows: a review, combustion and flame 48 ( 1982 ) I-26