insights in active pulsing air separation technology for
TRANSCRIPT
J. Cent. South Univ. (2013) 20: 3660−3666 DOI: 10.1007/s1177101318930
Insights in active pulsing air separation technology for coarse coal slime by DEMCFD approach
DONG Liang(董良), ZHAO Yuemin(赵跃民), XIE Weining(谢卫宁), DUAN Chenlong(段晨龙), LI Hao(李浩), HUA Chengpeng(华成鹏)
School of Chemical Engineering and Technology, China University of Mining and Technology, Xuzhou 221116, China
© Central South University Press and SpringerVerlag Berlin Heidelberg 2013
Abstract: To research a novel technology for dry coarse coal slime beneficiation and extend its application, active pulsing air separation technology was investigated by DEMCFD coupling simulation approach. The results show that the ash content of feed is reduced by 10%−15% and the organic efficiency is up to 91.78% by using the active pulsing air separation technology. The gas−solid flow in the active pulsing air classifier was simulated. Meanwhile, the characteristics of particle motion and the separation process of different particles were analyzed, and the mechanical structure of the classifier was also modified to achieve high separation efficiency. Therefore, a novel highefficiency dry beneficiation technique was advanced for coarse coal slime.
Key words: pulsing air; coarse coal slime; DEMCFD; separation
1 Introduction
At present, the highly efficient separation technology study is focused on the coarse coal slime in coal preparation field. With increasing content of coarse coal slime in raw coal, it has great environmental issues and economic value to approach a highly effective separation technology. In the field of traditional wet coal preparation, many separation machines have been researched such as reflux classifier [1], teetered bed separator (TBS) [2−5], spiral separator [6] and heavy medium cyclone for coarse coal slime [7]. But the separation technology can not work effectively in the arid regions and for coals that tend to slime under wet separation processes. So far, there is few report about dry separating technology for coarse coal slime. Scholars of China University of Mining and Technology (CUMT) have engaged in the research of dry coal preparation using air dense medium fluidized beds (ADMFB) [8−12] for more than 20 years. A gas−solid fluidized bed separator has been made for 6−50 mm coal preparation. Currently, <6 mm coals including coarse coal slime are not separated effectively by the ADMFB. In order to promote the application of ADMFB and popularize high by efficient dry coal preparation technology, separation characteristics for coarse coal slime using an active pulsing air classifier [13−14] (APAC) have been
investigated by DEMCFD coupling simulation approach [15−17].
In this work, EDEM (a commercial discrete element software for the simulation and analysis of particle handling and manufacturing operations) and FLUENT (a computational fluid dynamics software) were employed. The separation process of different particles, interaction between gas and particles and particle dynamics were studied intensively. Then, the mechanical structure of the classifier was modified to achieve high separation efficiency.
2 Experimental
2.1 Experiment system The experimental apparatus used is illustrated in Fig.
1. By the roots blower and a buffer tank, airflow was sent into the separation system. Rotation of a special butterfly valve was driven by an electric motor under the control of an inverter. So, an active pulsing air was generated, the velocity of which varied periodically. In the APAC, the superficial airflow velocity varied regularly. Coarse coal slime was sent into the APAC by a screw feeder, oscillated and loosed, and then stratified by density in the synergistic effect of gravity and pulsing air. A cyclone separator was used to separate cleaned coal from gas overflowed from top of the APAC and tailings sank into the collection tank at the bottom.
Foundation item: Projects(51221462, 51134022, 51074156) supported by the National Natural Science Foundation of China; Project(2012CB214904) supported by the National Basic Research Program of China; Project(20120095130001) supported by Specialized Research Fund for the Doctoral Program of Higher Education, China
Received date: 2012−07−27; Accepted date: 2012−11−29 Corresponding author: ZHAO Yuemin, Professor, PhD; Tel: +86−516−83590092; Email: [email protected]
J. Cent. South Univ. (2013) 20: 3660−3666 3661
Fig. 1 Schematic diagram of experimental apparatus: 1—Root blower; 2—Buffer tank; 3—Flowmeter; 4—Butterfly; 5—Electric motor; 6—Inverter; 7—Active pulsing air classifier; 8—Cyclone; 9—Screw feeder; 10—Electric motor; A—Feedings inlet; B— Floats outlet; C—Gas outlet; D—Tailings outlet
2.2 Separation theory of APAC The superficial airflow velocity in the APAC can be
described by
A 0 0 | cos(2π ) | v v f t = (1)
where vA is the instantaneous velocity of air, v0 is the maximum velocity of air, f0 is the pulsation frequency and t is time.
Generally, as a particle moves through an upward air current, forces such as gravity, air buoyancy and drag act on it. Because the fluid flow pattern in this work was the active pulsing airflow, not only the particle was affected by drag, but also energy transmission would replace the mass of the fluid, which might resist the particle moving through the flow. Equations (2) and (3) give the acceleration of particles [18] in the flow:
2 4 p g A p
p p A p
p g
d 3 ( ) 1 3.6 10 9 [ ]
1 d 4 ( ) 2 2
v v v g
t d d v v
ρ ρ
ρ ρ
− − × = × − + + +
− + ⋅
g A , 0 5 2
v Re
t
ρ ∂ × < ≤
∂ (2)
2 4 p g p
p p p A p
p g
d 3 ( ) 1 3.6 10 [
1 d 4 ( ) 2
A v v v g
t d d v v
ρ ρ
ρ ρ
− − × = × − + +
− + ⋅
g A
A p 5
6 0.4] ,
2 ( ) 1
1.5 10
v t d v v
ρ
−
∂ + + ×
∂ − +
× 5 0 2 10 Re < ≤ × (3)
where vp is the particle velocity, ρp is the particle density, dp is the particle diameter, g is the acceleration of gravity, ρg is the gas density and Re is Reynolds number.
It is clear that the acceleration of particles in the pulsing airflow is affected by gravity acceleration,
pulsing air velocity, particle density and diameters, etc. Under the same conditions, the higher the particle density is, the lower the particle acceleration is, and thus particles tend to sink. Conversely, the lowdensity particles tend to rise. After several pulsation periods, phenomenon of stratification and separation can be observed obviously in particles with different densities. Therefore, the APAC can be used to separate particles with different densities theoretically. Experiments of active pulsing air separation technology for coarse coal slime were conducted in this work.
2.3 Results and discussion The 1−3 mm fine coal with an ash content of
30.48% was used. The washability curves of feed shown in Fig. 2 were obtained by floatsink analysis, where β is the cumulative float, θ is the cumulative sink, λ is the characteristic ash, δ is the relative density and ε is the near density.
The results show that the contents of <1.3 g/cm 3 and
Fig. 2Washability curves of feed
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>2.0 g/cm 3 particles in feed are 31.43% and 26.57%, respectively. The separation efficiency of APAC is affected by the instantaneous velocity of air, the pulsation frequency, the feed speed and so on. The combustible material recovery and organic efficiency are employed to evaluate the separation efficiency. The results of singlefactor research are presented in Table 1. In the case of v0=8.65 m/s and f0=1.86 Hz, the feed speed Q is 6.94 g/s, the combustible recovery is 85.90% and the organic efficiency is 89.32%. Based on the singlefactor research, more experiments were designed. The results listed in Table 2 show that in the condition that v0=9.04 m/s, f0=1.86 Hz and Q=5.56 g/s, the organic efficiency is up to 91.78%. With the APAC, the ash content of feed is reduced by 10%−15%, calculated by the ash content of feed of 30.48% and the ash content of clean coal in Table 2 under different conditions. Because
of the significant misplaced phenomenon during the separation experiments, the ash content of clean coals is slightly higher and the recovery of clean coal is very low.
In order to investigate the separation process of different particles and modify the operating parameters and mechanical structure, DEMCFD coupling method was used to simulate the gas−solid two phases flow in the APAC. And the dynamic characteristics of particles were analysed.
3 Numerical simulations
3.1 DEMCFD coupling circuit In the DEMCFD coupling circuit, parameters of
fluid come from FLUENT, and parameters of particles are from EDEM. As shown in Fig. 3, the flow field of fluid is calculated by FLUENT using values of particles
Table 1 Results of singlefactor research
f0=2.33 Hz, Q=6.94 g/s vA=8.65 m/s,Q=6.94 g/s f0=1.86 Hz, vA=8.65 m/s
vA/(m∙s −1 ) Combustible material
recovery/%
Organic efficiency/%
f0/Hz Combustible material
recovery/%
Organic efficiency/%
Q/(g∙s −1 ) Combustible material
recovery/%
Organic efficiency/%
5.90 45.83 50.90 0.47 76.45 78.74 4.17 65.10 64.93
6.29 49.65 76.48 0.93 77.17 87.60 5.56 80.09 88.25
6.68 47.77 72.09 1.17 79.94 84.61 6.94 85.90 89.32
7.47 53.67 80.78 1.40 79.65 82.24 8.33 79.53 97.64
7.86 57.75 85.92 1.63 81.99 86.82 9.72 73.03 82.35
8.26 60.62 89.84 1.86 85.90 89.32 11.11 72.13 87.96
8.65 63.85 86.59 2.10 84.89 86.17 12.50 46.66 51.11
9.04 61.49 90.72 2.33 82.05 78.74 13.89 42.94 65.36
Table 2 Results of separation experiments vA/(m∙s −1 ) f0/Hz Q/(g∙s −1 ) Recovery of clean coal, γ/% Ash content of clean coal, Ad/% Organic efficiency/%
8.26 1.86 8.33 56.33 14.60 75.31
8.65 2.10 5.56 52.19 15.41 67.87
8.26 1.63 6.94 64.82 16.88 83.05
8.26 1.86 5.56 66.53 16.24 85.46
8.65 2.10 8.33 67.45 18.06 84.26
8.26 2.10 6.94 71.10 18.27 88.52
9.04 2.10 6.94 61.05 16.19 78.62
9.04 1.86 5.56 75.31 19.00 91.78
8.65 1.63 5.56 72.81 18.32 90.42
8.65 1.63 8.33 66.79 17.28 84.69
8.65 1.86 6.94 64.51 16.50 82.78
9.04 1.86 8.33 71.18 19.31 86.55
9.04 1.63 6.94 74.42 19.97 88.63
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velocity and location given by EDEM. The drag force acting on particles can be computed. And then, the status of particles is updated by EDEM. The governing equations [19] in the DEMCFD model are displayed. Figure 4 gives the HertzMindlin model [20−21] to describe the particles interaction in the EDEM software.
Fig. 3 Circuit of DEMCFD coupling simulation
1) Governing equations for gas phase flow (1) Continuity equation
g g ( ) ( ) 0 t
αρ αρ ∂
+ ∇ ⋅ = ∂
u (4)
(2) Conservation equations of momentum
g g g g ( ) ( ) ( ) p g t
αρ αρ ατ αρ ∂
+ ∇ ⋅ = −∇ − + ∇ ⋅ + ∂
u uu F (5)
(3) Conservation equation of energy
g p,g g p,g g sg ( ) ( ) ( ) c T c T k T Q t
αρ αρ α ∂
+ ∇ ⋅ = ∇ ⋅ ∇ + ∂
u (6)
(4) Conservation equations of species
t g g g
t
( ) ( ) ( ( ) ) j j j j j Y Y D Y S t Sc
µ αρ αρ α ρ
∂ + ∇ ⋅ = ∇ ⋅ + ∇ +
∂ u (7)
(5) Realizable k−ε turbulent model
t g g g ( ) ( ) ( ( ) ) k
k
k k k G t
µ αρ αρ α µ α αρ ε
σ
∂ + ∇ ⋅ = ∇ ⋅ + ∇ + −
∂ u
(8)
g g ( ) ( ) ( ( ) ) t
t ε
µ αρ ε αρ ε α µ ε
σ
∂ + ∇ ⋅ = ∇ ⋅ + ∇ +
∂ u
2
g 1 2 ( ) C S C k
ε ε
αρ ε
− + ν
(9)
where α is gas volume fraction, p is pressure, τg is stress tensor, F is the interaction term between gas and particles; cp, g is heat capacity (subscripts p is for particle phase, g is for gas phase), T is temperature, k is turbulent kinetic energy, Qsg is heat source in a unit volume, Yj is mass fraction of component j, Gk is generation of turbulence kinetic energy due to the mean velocity gradients, Sj is mass source of species j, SCt is turbulent
Schmidt number, μt is turbulent viscosity, σk and σε are turbulent Prandtl numbers for k and ε, μ is gas viscosity, ε is turbulent dissipation rate, C1 and C2 are constants in Realizable k−εmodel, ν is kinematic viscosity.
2) Governing equations for particle motion (1) Continuity equations
, , , 1
, , 1
d ( )
d
( )
i
i
n i
i D i i n ij t ij j
n i
i t ij r ij j
m F m t
d I dt
=
=
= + + +
= +
∑
∑
V g F F
ω T T
(10)
, , , , , n ij n n n n ij t ij i ij t ij k L η = − − = × F δ V T n F (11)
(2) Coulomb friction law
,
, , ,
,
, , ,
, if
/ ,
if (reset / )
t ij
t t t t ij t ij s n ij
s n ij t t
t ij s n ij t s n ij t t t
k f
f
f f k
η
=
− − ≤ −
> =
F
δ V F F
F δ δ
F F δ F δ δ
(12)
,
, ,
,
, , ,
, if
/ ,
if (reset / )
r ij
r r ij r ij r n ij
r n ij
r ij r n ij r n ij r
T
k f
f
f f k
η
=
− − ≤ −
> =
α ω T F
F α α
T F α F α α
(13)
(3) Interaction between gas and particles, F
D, 1
cell
n i i
V =
− =
∑ F F and ( 1)
D D0 β α − + = F F (14)
2 p 2
D0 f Ds
2 p
π 1 ( )
2 4
3.7 0.65exp[ (1.5 lg ) / 2]
d C
Re
ρ α
β
= − −
= − − −
F u v u v (15)
p p Ds 0.5 2
p p
24 / 1
(0.63 4.8 ) 1
Re Re C
Re Re −
≤ =
+ >
(16)
f p p
f
d Re
αρ
µ
− =
u v (17)
where mi is the mass of the ith catalyst particle, FD is drag force between gas and particles, Fij is the contact force between the ith and jth particles, Ii is inertia of moment, ωi is angular velocity, Tij is the torque due to contact force between the ith and jth particles, nij is the normal unit vector between two contacted particles, Vij is the relative particle velocity between particle i and j, Li is the arm of force, k is spring constant, d is damping constant, g is aueleration of gravity, f is friction coefficient, δ is displacement vector, η is damping coefficient, CDs is standard drag coefficient, Vcell is the volume of computational cell, subscripts “n” is the normal direction, “r” denotes the rolling, “t” designates the tangential direction and “s” corresponds to the static
J. Cent. South Univ. (2013) 20: 3664
Fig. 4Model of HertzMindlin
state. The geometric model used in simulation
experiments was designed based on the real active pulsing air classifier, as illustrated in Fig. 5. A is the inlet of feed, B is the inlet of pulsing air, C is the outlet of floats, and D is the outlet of tailings. The parameters of particles used in the experiments are listed in Table 5.
Fig. 5Model of active pulsing air classifier used in simulations (Unit: mm)
Table 5 Particle parameters in simulations
Particle index
Particle type Average
diameter/mm Density/ (g∙cm −3 )
Feeding speed/
(piece∙s −1 )
1A Lowdensity particle
1 1.40 2 000
1B Highdensity particle
1 1.80 2 000
3.2 Analysis of solid phase The curve of average zvelocity of particles versus
time obtained from simulations is described in Fig. 6. Obviously, it is seen that the difference in densities determinates the different velocities between lowdensity particles and highdensity particles. The velocities along the z direction of lowdensity particles which change periodically are positive for most of the time. Therefore, the light particles tend to move to position A. The zvelocities of highdensity particles increase at the beginning and then reduce with time. Consequently, highdensity particles tend to move to position D because of the negative zvelocity. The kinetic properties of highdensity particles are caused by the gravity and drag force. At the beginning, the dominant force is gravity and highdensity particles are accelerated to a high velocity at −z axis. With the increase of highdensity particle velocity, the fluid drag force becomes larger and larger, thus the direction of the acceleration changes so that the highdensity particle velocity becomes lower.
Fig. 6 Particle zvelocity with time in simulations
Figure 7 shows the location of particles in the APAC. Figure 8 gives the change of particles versus time at zheight. Different particles can be separated in one or two pulsation periods after entering into the APAC from position A. Lowdensity particles (1A particle 1, 1A particle 2 and 1A particle 4 in Fig. 8) in floats exist in the APAC for about four pulsation periods. Highdensity particles (1B particle 1, 1B particle 2 and 1B particle 4 in Fig. 8) in tailings exist in the APAC for about six pulsation periods. It is significant to reduce the retention time of particles in the APAC to increase the capacity and separation efficiency. The mechanical structure of the separator is modified and the design parameters are listed in Table 6. After modification, different particles in the APAC have the similar retention time, and the capacity and separation efficiency can be improved.
In Fig. 8, the 1A particle 3 is a lowdensity particle which moves to the tailings and the 1B particle 3 is a highdensity particle which moves to the floats.
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Fig. 7 Separation process of different particles in EDEM
Fig. 8 Curves of particle zheight in EDEM (a) and gas velocity in FLUENT (b) with time
Table 6 Comparison of design parameters Particle D/mm d/mm L1/mm L2/mm L3/mm L4/mm Before
modification 160 60 300 700 350 150
After modification
160 60 200 400 350 150
According to the statistics, the retention time of misplaced particles in the APAC ranges from 8 to 12 pulsation periods. During these pulsation periods, misplaced particles collide with each other, and the interaction of different particles can be strengthened. Therefore, loose and stratification process of particles could be affected seriously and the separation efficiency could be reduced. In addition, the phenomenon that misplaced particles in tailings move to the bottom along the wall of the APAC could be observed in simulations.
The total mass of different particles in feed, floats and tailings were given by EDEM, as listed in Table 7. The total misplaced material [22] can be employed to
evaluate the separation characteristics as m0=mh+ml (18)
where m0 is the total misplaced material, mh is the content of heavy material in floats and ml is the content of light material in tailings.
The total misplaced material is 18.21%. Therefore, the active pulsing air classifier has the potentiality to achieve high separation efficiency. The 76.96% recovery of light particles is close to the separation performance of TBS [23], which indicates that it is possible to separate coarse coal slime with the active pulsing air classifier.
Table 7Mass and recovery of particles in simulations
Mass/g Particles type Feed Floats Tailings
Recovery/ %
ml/% mh/%
Light particle
100.93 77.67 23.26 76.96
Heavy particle
129.87 18.77 105.72 81.40
8.13 10.08
3.3 Analysis of gas phase Because the periodical change of superficial air
velocity is the main factor for the separation of coarse coal slime, the analysis of air velocity in the APAC is significant. Figure 9 gives the air velocity−time contours within 1 s. It is clear that the velocity near wall of the APAC is lower than that near the axis when the air
Fig. 9Air velocity contours in FLUENT
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velocity fluctuates near the maximum value. Due to the velocity distribution, the drag force acting on lowdensity particles near wall of the column is not high enough, which causes lowdensity particles to sink to the bottom. In order to modify the velocity distribution and decrease the total misplaced material, a new gas distributor is employed in gas inlet. So, the recovery of clean coal can be increased during the separation process.
4 Conclusions
1) The coarse coal slime is separated at high efficiency by the active pulsing air separation technology. The ash content is reduced by 10%−15%. The organic efficiency is up to 91.78% under the conditions that v0=9.04 m/s, f=1.86 Hz and Q=5.56 g/s.
2) Different particles are separated in one or two pulsation periods. The misplaced particles retention time in the separation column is much longer than others. A modified separator is also designed, which reduces the particles retention time and increases the capacity. A new gas distributor is employed to modify the gas velocity distribution.
3) A novel highefficiency dry beneficiation technique is advanced for coarse coal slime. The separation efficiency of APAC is close to TBS. Cooperating with the airdense medium fluidized bed separator, coals with a wide range of sizes is separated efficiently.
4) Separation theory of the APAC should be researched further in the future. Firstly, the force acting on particles should be focused on in DEMCFD coupling simulations. Secondly, a highspeed dynamic camera should be used to investigate particle dynamics in the modified separator.
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(Edited by FANG Jinghua)