Coal cleaning in an air fluidized bed · 2020. 7. 29. · Two major benefits can be derived from...
Transcript of Coal cleaning in an air fluidized bed · 2020. 7. 29. · Two major benefits can be derived from...
Lehigh UniversityLehigh Preserve
Theses and Dissertations
1987
Coal cleaning in an air fluidized bed /Yih-Tun TsengLehigh University
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Recommended CitationTseng, Yih-Tun, "Coal cleaning in an air fluidized bed /" (1987). Theses and Dissertations. 4788.https://preserve.lehigh.edu/etd/4788
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COAL CLEANING IN AN AIR FLUIDIZED BED
by
Yih-Tun Tseng
A Thesis
Presented to the Graduate Committee
of Lehigh University
in Candidacy for the Degree of
Master of Science
• in
Mechanical Engineering
Lehigh University
1986
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This -thesis is accepted and approved in partial
fulfilment of the requirements for the degree of Master of
Science.
(date)
Professor Charge
Chairman of Department
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CONTENT
Abstract • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • 1·
Introduction . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . 2
Equipment and instrumentation • • • • • • • • • • • • • • • • • • • • • 8
Experimental procedure • • • • • • • • • • • • • • • • • • • • • • • • • • • • 20
Results • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • 22
Conclusions • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • • 62
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ACKNOWLEDGEMENT
The author is grateful to Bulent Kozanoglu. for his
help in carrying out these experiments and analyzing the
data. • • • • • • . It is a pleasure for the author to record his gratitude
to Dr. Edward K. Levy for his valuable guidance and
encouragement during this study.
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ABSTRACT
The purpose of this study is to develop an efficient "
method of separating coal refuse from coal in an air
flu~dized system of coal and magnetite. Special emphasis is
on processing coal particles with a top size of 20 mesh and
with fines smaller than 100 mesh. -~
By fluidizing crushed raw coal and magnetite near the
minimum fluidization velocity, good segregation can be
obtained. The ferromagnetic magnetite particles can be
separated from coal through use of magnetic separation
techniques after segregation between the coal and its refuse
is achieved.
In this work, experiments involving mixtures of coal
and magnetite were carried out. The effects of particle size
and density, bed depth, fluidizing velocity and multiple
stages of cleaning on sulfur reduction were investigated.
Finally, a rectangular inclined fluidized bed design was
developed for continuous processing of the coal.
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INTRODUCTION
Background
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Two major benefits can be derived from coal cleaning.
One is to increase the heating value of the coal and the
other is to reduce air pollution from sulfur. In addition,
coal cleaning reduces fuel transportation costs and results
in .lower capital costs for new power plants. The latter
benefit occurs because boilers can be built and maintained
more inexpensively if they are required to burn coal with
less sulfur and ash and a more consistant quality. About 35
percent of the coal in the United States • receives some
cleaning before it is burned [l].
The irnpuri ties in raw coal of concern in this study are
the noncombustible portion -- the ash and the pyritic sulfur.
Sulfur exists in coal in several forms. Some sulfur is part
of the minerals that make up the ash, while other forms of
sulfur are chemically associated with carbon. The sulfur has
three major classifications:
. Organic sulfur -- Physical coal cleaning methods are
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not able to separate I organic
sulfur from coal.
Pyritic Sulfur -- This is
sulfur.
an inorganic form of
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Sulfate Sulfur -- While hard to remove, this is
usually present in negligible
amounts.
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Physical coal cleaning can separate free pyrite from
coal, but it· cannot separate pyrite that is finely dispersed
in the coal. \ .
Liberation is the process of breaking the ·raw coal
particles in order to release some of the free ash (which ,,,
includes pyrite) fragments when the coal particles are
fractured. During the coal crushing process, many other
particles, containing solely inherent ash or free ash are
reduced in size. Breaking these types of particles changes
the raw coal's size distribution, but it does not increase
the amount of liberated impurities in the coal [2].
When wet coal cleaning methods are used, the fine coal
particles are the most difficult to clean, because they tend
to stay suspended with pyrite in the cleaning process.
Consequently the coal fines are discarded at many coal
cleaning facilities. Because the fines contain up to 25
percent of the heating value of the raw coal, there is
growing interest in recovering the combustible portion of
these small particles [l].
As an alternative to wet cleaning, dry cleaning ha:s ' .
several advantage:
• Higher thermal efficiency .
• No wastwater treatment problem .
• Reduced handling problems due to coal freezing
and plugging of and bins.
Some types of dry .systems which can be used in coal cleaning
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include pneumatic jigs, pneumatic tables and air·fluidzed
beds. The first two are in commercial use. Air tables are
effective cleaning devices down to 28 mesh (3], but they are
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inadequate when fine fractions of coal are dealt with.
In a fluidized bed where particles of different
densities and sizes exist, there is a tendency at near
minimum fluidzation conditions for the solids to stratify in
the vertical direction according to the density, and to a
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lesser extent, size. Two fechanisms control the manner in
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which particles segregate (l] .
. As a bubble rises through the bed, particles are
carried along with the wake of the bubble. This
tends to counteract solid segregation by causing
remixing of settled material. This, however, is also
the mechanism by which the less dense particles find
their way to the top of the bed .
. As bubbles move vertically upward through the bed,
they cause the dense particles to descend. The
dense particles tend to fall through the free space '
of the bubbles and drift downward through the
emulsion phase in the region disturbed by the bubble
as the bubble passes by .
Bubbles play a very strong role in mixing and
stratification, and the degree of segregation which occurs
depends very much on the excess velocity. This is ~llustrated
in Fig.l where Curve A is the case of a strongly segregated
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Top
+> .c: tJl
•ri (l)
=x: re, Q) ~
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(A) (B) (C)
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Uo = Umf. completely stratified Uo > Umf. partially mixed Uo >> Umf. well mixed
, A I
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Bottom
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Concentration of dense component
Figure 1. Effect of fluidizing vel·ocity on ·solids stratification. (Ref. 4 )
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bed very near minimum fluidization, curve Bis the concentration profile for the case of soliids at. an intermediate fluidization velocity and Curve C is the case of a perfectly mixed bed operated at high fluidizing velocities.
Previous Research
Particle segregation has been studied by many researchers in the last twenty years.
One of the first studies was carried out by Rowe and Sutherland. They concluded that no bubbles appear and
therefore no particle mixing occurs at gas velocities up to about 1.2 Umf in binary mixtures [5]. Later, Rowe, et al., studied the mixing effect of a single bubble passage through a two dimensional fluidized bed [6]. Rowe, Nienow and Agbim found that the effects of density ratio and excess velocity are considerable while those of size difference and shape are slight in segregation of binary mixtures (7].
Chen and Keairns [8] performed segregation experiments with dolomite and char and observed sharp segregation near the flow rate of the jetsam particle's minimum fluidization velocity (The component which tends to segregate and settle to the bottom is called jetsam, while the one which tends to float is called flotsam in the technical literature). They found that segregation is much more sensitive to particle density difference than to particle diameter. All of their results supported the conclusions of the earlier study by Rowe, et al .
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Nienow, Rowe and Cheung [9] studied the segregation and
mixing behavior of binary mixtures of powders differing in
density and developed a mixing index. Their mixing index
agress with the experiments with a standard deviation of+/-
9 percent for mixtures with up to 50 percent jetsam by
volume.
One of the coal cleaning related segregation Btudies
was perf armed by Nienow, Rowe and Chiba [ 1 O]. They carried
out experiments for ternary systems of char, sand and shale
and observed that large particles of low density such as coal '
tend to remain on the surface and can be separated from
denser ones, such as shale in a fluidized bed of intermediate
density such as sand, Fig. 2. Their experiments also showed
that the flotsam particles are drawn deeper into the bed with
increasing gas velocity. But the degree of segregation in
their experiments was far from perfect.
Weintraub, Deurbrouck and Thomas (11] studied
segregation in ternary systems. They found that minerals of
different density, such as coal and coal refuse, can be
separated in a fluidized bed of fine size and high density
material. They successfully separated various fractions of
coal and ash impurities ranging from 9.5mm top size down to
"'._ 3 O mesh bottom size in times ranging from sixty seconds for
the coarse material up to five minutes for the finest
particles in a fluidized bed of small magnetic particles.
Fig. 3 shows the distribution of coal and refuse with
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location in the bed and with time in one of their
experiments.· They observed that the coal becomes uniformly '
dispersed within the magnetite while the.refuse material '
sinks to the bottom of the bed. They also found that the
degree of segregation is affected by the size distribution of
magnetite.
Objective of Investigation
The objective of this study is to develop an efficient
method of separating coal refuse from coal in an air
fluidized system of coal, coal refuse and magnetite.
Special emphasis is on processing coal particles with a
top size of 20 mesh and with fines smaller than 100 mesh.
Fina1·1y a continuous inclined bed was designed, built
and tested for this application.
EQUIPMENT AND INSTRUMENTATION
Fluidized Beds
Three fluidized beds were used for this investigation.
The first, borrowed from Dr. J. Chen of the Chemical
Engineering Department, was a 10.16cm (4 inch) cylindrical
bed (see Fig. 4). A series of fluidization experiments was
carried out with magnetite, glass and plastic particles.
These were intended to determine the effects of particle
density and size on minimum fluidization velocity ~nd to
develop qualitative guidelines on the fluidization and
stratification behavior of mixtures of particles.
The second bed was a 15.24cm (6 inch) diameter
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n • 1·49 t1/cmJ r1a1& ~
Sand JctlGID : 90°/o Sand
3·5°4 Shale
Flotsaa: 6·5°/o Char
d,• O·BBmm
d,• 3·03~
dp • 5 ·18 "'"'
-p . • 2·S0g/cmJ
p • 0·97 vi Chl3
Shale rich
.• rich , H ··'-- , .. .. ·-~- ,. . .';
Bed hc.ght.
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(Ill 4'
(u-u.,l • 13 cm/s
Sand
. --=-~~- ... . . . . . . . . .•' . :
8
6 . (u-u., l • 28 cm/s
4 Sand
0 o 0-2 0·4' 0-6 0·8 1·0 0·2 0·4 0·6 O·B 1·0
Weight fraction.xJ, (1-x,l
Figure 2. Segregation pattern--char and shale in sand. (Ref. 5 )
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-Figure 3.
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RELATIVE CONCENTRATION
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% component in increment average% component in bed
' ' ' ' ' ' ' " ' ' ' ' '
-·-
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' ' '
fu ~. t~i .... fi-fl r 1, .;,, r~, ~ _;1 ...
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~' ~ C:1 (1
·I ,~1 (~ r] gj ~ lf"' .,.
•:·.\ ,- . . ... _,,__ ...... . . . .
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f16
l,s I r' .. ~13
l,2
r'o ~~
ls I -r1 r6 rs r4
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Distribution of coal and refuse with location in bed and with time. (Ref. 5)
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cylindrical bed fabricated from plexiglass for easy
obser~ation. of the solids. The grid was of .porous plate
design. The bed was designed to permit easy removal of
layers of the bed ma.terial through use of a vacuum .sampler.
In the batch experiments, solid concentration was measured by
suddenly shutting off the fluidizing air, defluidizing the
bed and measuring t-he composition of each layer (see Fig. 5) .
Based on the results from the above two beds, the 132cm
··(52 inch) long, 10.16cm (4 inch) wide rectangular bed
illustrated in Fig. 6 was designed. With this inclined
rectangular bed, material is fed to the bed at one end and
flows out from the other end while a vacuum sampler is used
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to remove the material in the top layer.
Air Flow Rate Arrangement
Air flow rate was measured using four Schutte &
Koerting rotameters. The tubes and floats used for this
study, listed in Table 1, were selected to give a range of
air flow rates up to 0.694 m3; min (24.5 ft 3;' min) at
room temperature and pressure.
illustrated in Fig. 7.
Vacu11m Sampler
The flow circuit is
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The vacuum sampler is illustrated in Fig. 8. This
device consisted of a jet pump (model GL from Penberthy
Oudaille Co.), a gas flow control valve and a catch container -
for collecting the solids. The thicknesses of the bed layers
were measured with a millimeter scale.
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Pressure tap • Air from rotameter •
Figure 4. The first fluidized bed •
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Figure 5.
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Detachable part for easy access to material in the bed
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Distributor
••,---- Air from rotameter
The second fluidized-bed. I
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Distributor
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Air from rotameter
Figure 6. The inclined fluidized bed.
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Tube Float Max. flow (m3 I min)· Model Model at 21 ° c, 101.4 kpa
2-B R-22 0.022 ..
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3-HCF 34-J 0.154
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4-HCF 44-J 0.321
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5-HCF 54-J. 0.694 .
.. . TABLE 1. Rotameter tubes and floats.
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4 Air outlets
5-HCF 4-HCF 3-HCF ... .
2-B
Flow control valve Flow control 0 valve
Pressure regulating valve
Figure 7. The flow Circuit.
Inlet
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Con trol valve '
·"'-Air inlet
Discharge
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Suction Catch con tainer .
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Measuring gadget •
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Figure a. Vacuum sampler.
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Solid Separation
Where.a sufficiently large size difference existed,
between the different materials used in a fluidization
experiment, the materials were separated after fluidization
by dry sieving.
For the experiments involving magnetite and coa.l, a
magnetic separator, purchased from Eriez Magnetics Company,
was used to separate the coal from the magnetite. This
device, Shown in Fig. 9, consists of a vibratory feeder for
transporting material uniformly to the belt and a belt and
pulley set. One pulley was made of a permanent magnet and
the other was made of steel. The speeds of the feeder and
belt are adjusted manually by the controller. By
appropriately adjusting the speeds of the feeder and the
belt, coal can be efficiently separated from magnetite for
different combinations of coal and magnetite.
A demagnetizing coil, also purchased from the Eriez
Magnetics Company, was used to restore the magnetite to it's '- _>
original unmagnetized state. This was necessary to prevent
agglomeration of the magnetite after passage through the
magnetic separator. This demagnetizing coil was held
vertically and the magnetized magnetite particles were poured
, .. through the coil. In preliminary tests, the magnetized
magnetite were found to be fully demagnetized after passing
through the coil twice.
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Controller
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·-- Vibratory feeder
Belt & pulley set ::
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Figure 9. Magnetic separator •
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Float and Sink Apparatus
The purpose of these tests is ·to determine the effect
of the size distribution of the crushed coal on its ability
to liberate and release pyrite.
The Float-Sink apparatus is made of Pyrex glass. The
two flasks are joined together and filled with solvent to
just above the top part of the joint. A weighed coal sample
and additional solvent are added to bring the liquid level to .
three quarters full. The· solvent and sample mixture is
stirred very well. This keeps the sample from balling and
insures uniform wetting of the sample. This is needed for
achieving proper segregation. Solvent is again added to
1.27cm (1/2 inch) of the top. The sample is again stirred
well in both the top and bottom flasks but gently to avoid
combining the contents of the two flasks. Then the stopper
is carefully inserted, the flasks are separated, the samples
are filtered and dried, and the corresponding sink and float
solid residues are weighed.
Material Preparation
Each kind of material, illustrated .in TABLE 2, was '. I
divided into narrow size ranges by use of dry sieving.
In addition, TABLE 2 also includes density, theoretical
minimum fluidization velocity and experimental _minimum
fluidization velocity for each size range of the materials.
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Material ;_.,
Plastic
Glass
Magnetite
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.Particle Particl-e (Umf) Diam. Range exp.
µ.m Mesh No. (Mesh No.) (cm/s)
850 20 d) 20 14.20
600 JO 20) d) JO 12.80
425 40 · JO) d > 40 8.70
.. • JOO 50 d) 50 4.60
212 70 50) d ) 70 4.11
1.50 100 70)d)l00 2.28
125 120 100)d)120 1.49
JOO 50 40) d > 50 13. 47 .
250 60 50) d > 60 7.37
212 70 60) d > 70 5.97 180 80 7q) d > 80 3.99 150 100 80) d >100 3.53 125 120 100)d>l20 1.86
106 140 120) d )140 1.37
90 170 140) d) 170 1.16
75 200 170)d>200 0.70
63 230 200) d )230 O. 67
45 325 2JO)d ;>325 0.52
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·r·ABLE 2 : · List of Bed i1aterials
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(U ) mfthe.
p (g/cmJJ
(cm/s) 20.47 1.00 "
13.39 8.J8
6.613 2.25
4.139 2.444
1.414
14.37 5.00
10.15
7.37
5.35 3.73 •
2.59 1. 87
1.35 0.94
. o.66
0.34
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Particle Particle (Urnfix • (U ) p Material Diam. Range mfthe. (g/cmJ)
(cm/s) µm Mesh No. (Mesh No.) (cm/s)
Coal #1 850 20 d) 20 J0.20 28.50 1 • .50
600 JO 20) d) 30 22.50 20.10
425 40 JO) d > 40 12.50 10.60
300 50 40) d) · .50 7.00 6.80
250 60 50 > d) 60 2.70 2.50
212 70 60) d > 70 2,JO 2.20
180 80 70) d) 80 1.70 1. 80 · .
. 150 100 \ 80) d )100 a.Bo 0.70
. .
Coal l/2 850 20 d> 20
600 JO 20 > d) JO
425 40 JO) d )_ 40
·300 50 40) d ) 50 250 60 50) d) 60 .. II
212 70 60) d) 70
180 Bo 70 > d > 80
150 100 80) d ) 100
Coal #J 850 20 d) 20 . . . .. .
600 JO 20) d) JO 425 40 JO) d) 40
JOO 50 40)d > 50 250 60 50 > d) 60 " II
212 70 60) d) 70
180 80 . 70) d ) 80 . '
150 100 80) d )100 .
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. Coal #1 - An· anthracite coal. 'Mineral contents is unknown.
Coal #2 - Raw coal from PP&L Rushton mine. ·, Coal #J - Ravi coal from Minesota Power.
II . . .
- ·rhe same as J.n coal dl. • • • t •
. ·rABLE 2 (continued)
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Chemical Analysis (
In order to know the sulfur concertration in each layer •
of coal after steady state fluidization was achieved,
samples of coal from each of the tests and from each bed layer
were sent to the Warner Laboratory in Cresson, PA, for sulfur
analysis.
EXPERIMENTAL PROCEDURE
The experiments were divided into three phases. In the
first phase, the 10.16cm (4 inch) diameter bed was used to
obtain the minimum fluidization velocities of each size of
all the materials mentioned above. This was accomplished by
measuring the bed flow rate -- pressure drop profiles. The
pressure drop between the top and bottom of the bed was
obtained by subtracting the pressure drop across the grid
from the gage pressure measured at the plenum.
In the second phase, the detachable 15.24cm (6 inch)
diameter bed was used. Experiments for each particle
combination were preceded by explorary runs to determine the
time required to reach steady state. These runs consisted of
repeated measurements of the composition at the top of the
bed to observe its change with time.
Each experiment was run with the bed initially well
· mixed. The different particles were added simultaneously to
the bed and fluidized at velocities, much higher than the
minimum bubbling velocity, for 5 minutes to insure that all
the particles were well mixed. Then, the air was shut off
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suddenly and increased gradually to the desired velocity.
Most experiments were then run at the minimum bubbling
velocity. After the bed was fluidized for 30 minutes, the
air was shut off abruptly. The materials was removed layer
by layer by use of the vacuum sampler. The number of layer
depended on the bed depth, with each layer typically being 1
to 2 cm thick.
Flotsam concentration p·rofiles were obtained by
separating the flotsam from the magnetite in the magnetic
separator.
In the final phase, the 132 cm (52 inch) long 10.16 cm
(4 inch) wide inclined bed was used. Fluidizing experiments
were performed at minimum bubbling velocity with the bed
inclined at different angles. During these tests,material was
fed in at one end and removed at the other. Tests to measure
residence time of particles in the bed as a function of feed
rate of bed material and angle of inclination were carried
out.
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RESULTS
Fluidization Behavior of Mixtures
In the first phase of the experiments, each of the
samples listed in TABLE 2 was loaded separately into the
fluidized bed and bed pressure drop was measured as a
function of fluidizing velocity. Shown in Figure 10, 11 and
12 are typical pressure drop -- flow rate curves for three
materials. The point of minimum fluidization is indicated in
each case and is also tabulated in TABLE 2.Figure 13 contains
a summary of minimum fluidization velocity as a function of
particle size for each material. Even though the three coal
types differ from one another, no significant difference
exists in their minimum fluidization curves. Therefore, the
Umf versus particle size characteristics are represented by
the curve marked" Coal" in Figure 13.
Because of its low density, plastic with particle
density of the order 1 g/c.c should be closest in behavior to
the carbonaceous portion of the coal. It was, therefore,
expected that when the experiments were run with mixtures of
coal and magnetite, the behavior would be at least
quantitively similar to that of plastic and magnetite. Both
plastic and glass possess the property of being easily
observed in mixtures with magnetite.
The minimum fluidization velocities of binary mixtures
of magnetite with plastic and glass were measured and some
comments on the results are shown in TABLE 3.
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AP [cm Wate~]
20
15
10
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1 Umf I I I
0.5
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Material: Glass (50 Mesh)
• - . •
1.0 1.5 2.0
• 3 [m x 10 kg/sec]
Figure 10. Typical fluidization curve for glass. •
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AP , I
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(cm Water]
20
15 •
10
5
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' • I I I I I Umf I I
0.5
,.
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Material: Magnetite (140 mesh)
1.0 1.5
Figure 11. Typical fluidization curve for magnetite .
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2.0 • 3
[m x 10 kg/sec]
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6P [cm Water]
20
15
10
5
r·
,
0.5
l • I I I I I
• • I
. •
I
Umf
1.0
.
Material: Plastic (30 Mesh)
• •
1.5 2.0 • 3
[m x 10 kg/sec]
Figure 12. Typical fluidization curve for plastic .
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Umf [cm/sec]
20
15
10
5
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100
Figure
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13.
• •
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Magnetite
600 . .. 500 . 200 300 400
Variation of minimum fluidization velocity with particle size .
• •
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Coe.l
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Plastic
700 800
d [µ.m]
.. •
·•
Minimum fluidization velocity of mixtures of 50 mesh
magnetite w·i th plastic is plotted as a function of mixture
concentration in Figure 14.
Figure 14 indicates that the minimum fluidization
velocity of the mixture typically lies between the two
individual minimum fluidization velocities but it is a little "
higher than either in the range between 65 and 75 volume
percent of magnetite.
Each of the mixtures listed in TABLE 3 was fluidized at
its minimum fluidization velocity for ten minutes. It was
observed that when particles individually having identical
minimum fluidization velocities were mixed together, they
fluidized uniformly with bubbling occuring over the entire
height of bed and with relatively little segregation of
materials. One example of this situation is a mixture of 50
mesh magnetite with 20 mesh plastic.
In cases where the minimum fluidization velocities of
the individual materials are not close to each other, then
the material with the larger minimum fluidization velocity
tends to segregate and settle to the bottom of the bed with
the other material floating to the top. Two examples of this
situation are mixtures of 50 mesh magnetite with 40 mesh
~ -. plastic and 6 o mesh magnetite with 7 o mesh glass.
Finally, if Urnf 1 >> Umf2 and Umf 1 > Ugas > Umf2,
component 1 settles to the bottom of the bed and forms a
packedlayer while component 2 forms a fluidized layer on I )
27
I
.·
N a,
.
,
-
•
TABLE 3. Minimum fluidization velocities -of different mixed material.
Plastic (Mesh Size) Glass (Mesh Size) . Material
30 40 20 50 \
Umf [cm/sec] 12.80 8.70 14.20 4.60 .
Volume ~ .
50 r 30 10 50 30 10 30 10 0
Magnetite 50 14. 57 + 12.83•
50Mesh - " 15. 64 + 14. 39 + 70 15.64 +. •
Umf: - -. ' . =13.47 cm/s 14.75+ 12.95 ' 90 ' .• +
Magnetite· 50 , f?.O·Mesh •
70 Umf =7.37 cm/s 90 10.79+ 11.13 + 9. 36 +
+ Well mixed with no segregation.
* Good segregation. Bed free surface has almost 100% glass.
** Bottom one third of the ved is packed. The rest of the
bed has a larger flotsam concentration in comparison to
the bottom.
70 100 :
4.11 2.28 !
50 -~, 50 J
-
7.89•~ 4. 72'!- j I
r i l I
·-
I I
' ;
i
I i .
' i ' I ' I -
20
Umf
[cm/sec]
15
10
5
•
30 Mesh Plastic with 50 Mesh Magnetite
40 Mesh Plastic with 50 Mesh Magnetite
25 50 75 100
--(volume% of magnetite)
· Figure 14. Minimum fluidization velocities of binary
• mixtures.
29
.....
• _________ _....,_ .. _A. ... ----.-..-.. -----·-·--~ ............. . ----~ .... • -· ··-· Ao•... ·#-~ ·- -·~ . ·• ....... -.. ~ ......... #----· ·--·· -~··· -~-..... -·---- ........... ·- .... . ....
top. This occured,for example,with a mixture of 60 mesh .
magnetite and lOOmesh glass.
Effects of Gas Velocity and Bed Depth
In the second phase, experiments were carried out in
the 15.24 cm (6 inch) diameter bed to determine the effect of
bed depth on the time required for the bed to achieve steady
state conditions. In these experiments, a mixture of 10
weight percent coal and 90 weight percent magnetite was added
to the bed, fluidized at an air velocity much larger than the
minimum bubbling velocity for 5 minutes to mix the mixture
well and then fluidized at near minimum bubbling velocity
for different periods of time. (The minimum bubbling velocity
is defined as the velocity at which small bubbles begin to
form at the distributor. From experiments, Umb / Umf usually
lies between 1.6 and 1.8,and Umb can be determined by
observation when bubbling begins to occur.) The air supply
was then shut off, the bed material was sucked out and
analyzed layer by layer. The fluidization time was increased
and the experiment was repeated. This procedure was continued
until the concentration distribution remained unchanged with
duration of the experiment.
The results are summarized • in Figure 15 where the
'transient response time of the bed is plotted as a function of
bed depth. It was found that the time to reach steady state
increases sharply with bed depth. Beds of just a few
centimeters in depth reach steady state in 2 to 3 minutes
30
..
..
..
.,
• •
' . .
•
. ··- ..
-... ·,
. .
. . . . .
•
..
...
30
25
\ " 20 ~ .,... a '-"'
cu ~
-rt +l
Q) 15 Ul ~ 0 p. Ul (1)
P::
10
5
•
l 2 3 4 5 6 7
Bed depth (cm)
8
•
. •
9
Figure 15 • The effect of bed depth on the time to reach stea1y state conditions.
31 ':" .
•
•
.• •--
'
I • • • I
10
• ~ ...
•·
•
. .
••
while beds of 10 cm in depth need 25 to 30 minutes to reach
steady state conditions.
In the segregation experiments which follow, each
mixture was fluidized for 30 minutes to insure that steady
state conditions were reached, then the bed material was
removed layer by layer through use of the vacuum sampler to
obtain the concentration profile as a function of distance
from the top of the bed.
The mixtures of 50 mesh magnetite with 30 mesh plastic
and of 100 mesh magnetite with 60 mesh coal were
fluidized individually at different air flow rates to
determine the effect of air flow rate on segregation
conditions. The results for the mixture of 50 mesh magnetite
with 30 mesh plastic, shown in Figure 16, demonstrate that an
air flow rate close to minimum bubbling velocity has the best
effect on segregation. The results for a mixture of 100 mesh
magnetite with 60 mesh coal are shown in Figure 17. No
segregation was achieved at either flow rate because these
materials have almost
velocities.
identical • • minimum fluidization
The effect of bed depth on the shape of the steady
state concentration profile was determined from the
._ experiments with mixtures of 170 mesh magnetite and 100 mesh
coal. The results are shown in Figure 18 as weight fraction
of coal versus the dimensionless distance below the free
surface of the bed.
32
... • •
. . ..
..
,.__ # '-"
u •rt .µ Ul
... ro r-i ~
~ 0
C • 0
•rt .µ u Al ~ ~
(l) J:; ~ r-i 0 >
\
...
•
60
50
40
30
20
10
' 0 I
' ' ' ~\
Uo
• -.... )(· ....
[cm/s] · Uo/Umb
10.7 0.75
14.2 1.00
18.0 1.27
Mesh Volume%
·,. mag 50 80
1
,· .. \ ..
plas 30 20
\ '--J. \ .
• \ .
•
\ : \ ·. \ .
• \ •• >(
X • \ .. • •
• • ~ •• '- .
'o )( '-...... . 0
0 ...... • --- ....__Q . ' . '
''M.. 'o\ '•)( \
• • • • . ')(
• • r
2. 3 4 5 6 7 8
Bed Depth (cm]
0 \ \ \ • . ~ ·. ', 'i( ....
9 10
Figure 16. The effect·of air flow rate on segregation .
... .
33
. .
•
.. I• • I•
•
..
..
•
' - - ---'
' ·' .
•
• •
-
. .. ..
.. . • ..
...
•
50
,.....
"" '"" r-4
40 ,0 0 u
q..,. 0
t: 0
~r-4 Jc .µ 30 , ___ ,,,, ~ u «s Jc ' ~ µ..
Q)
a :;:,
,...,t
0 20 :>
10
. ..
o •. I • •
1 ·2 3
Uo [cm/s]
- -----x--
•
)( ·..-.
3.2
3.9
·mag
plas
)(-- --.. ... ,..._,- t'
'
. -:
Uo/Umb.
0.82
1.00
Mesh Volume%
100 80
60 20
" It ~, "lt' ••
• ·-• • • • •
•
4 5 6 7 8 9 10
· Bed Depth [cm] •
. Figure 17. The effect of air flow rate on segregation.
34
•
•
•
•
...
. .. •·
• •
.. .
. .
The mixing index is a method to judge the efficiency or
quality of segregation. Different • • mixing indexes provide
different ways to evaluate the degree of segregation. For
objectivity, four different mixing indexes are shown in
TABLE 4 to compare the segregation conditions in mixtures.
It was found that the differences between the profiles of
shallow and deep beds are relatively small, thus indicating
that the depth of the bed has very little effect on
efficiency of segregation.
Sink and Float Tests
In the sink and float tests, 50 gram samples of coal
N0.2 .and.coal NO. 3 (coal N0.2 -- raw coal from PP & L,
coal N0.3 -- raw coal from Minnesta Power) were tested with a
liquid solvent of 2.0 specific density. The purpose of these
tests was to determine the effect of the size distribution of
the crushed coal on its ability to liberate and release
pyrite. The coal was separ~ted into narrow fractions. The
number of grams of feed coal which sank in the heavy medium
was then determined as a function of the size of the feed
coal. These results are shown for the two coals in TABLE 5
and Figure 19. In both cases a relatively large increase in
the amount of material which sank occured in the size range
~ between 80 to 100 mesh. This most likely indicates a critical
size below which more extensive liberation of the pyrite
begins to occur. Interestingly, in the case of the Minnesota j Power coal, almost none of the coal sank until the grid size
35
.. '
. . .
•
1·
.
• • f I original·coal weight concentration 7 0
\ - .3.81
' \ \
. .. . .
\ \ o 'I I I
6 ~ \ .. ' . \.\ • • 7 cm ••
• ', \ • -0-0--0 4 cm
' s:: 5 ~ \ --*---*- 3 cm 0
-r4 ' 2 +> .~\
cm - •
«s • M \\ ~+l ~ Q) ~' ... r-4 u
«s ~ 4 ' '- ··o, 0 0
,_ -- ' I (J u -.)( '
' ' ~"- ' '\o ' - ' 4, \ ' ••A .. 3 \ 4 ..
\
' \ • f
X 0
- \ ~---~ ·2
1
o. 2 5 0.5 0. 7 5 1.0 .. .
Z / L.( z: distance from the free surface)
Figu~e 1s. The effect of bed depth on segregation. _.., .
• -....
36 ...
..
... -- - ... .a .... --- .. -·--····-········· .
·- •• ·~- . ·' - • -J- • • f •
r' I I
,_ . . . - ..
e I I""'
. ... . . .. . ' .
• 1 "• r ,. l"-r, '' ' I • ~ !' ... > f •; I
• I:• , .. '
'··,, ~. _: .. _.:, .. _ ... ..: ......... · .. ,
. ~ - .......... --- . - . .. .. ..
• • • I
....
TABLE 4. The mixing index calculations. --· -
•' ·- - -- - . .
Xj 0.90 (average jetsam volume percentage) --H=2cm H=3cm H=4cm H=7cm
% X % % X % % X % % X %
(cm] w V [cm] w V (cm] w V :cm] w V
o.5 0.5 17 0.5 7. 0 1 7
1.0 4~0 10 1.0 4.0 11
1.5 3.4 9 1.5 4.0 11
2.0 2.0 6 2.0 3.8 10
2.5 3.5 9
3.0 3.5 7
Il 0.922 0.966 •
I2 0.0733 0.0677
I3 0.922 0.922
I4 0.865 0.870
Xhdh
Il =
h=H
h
!2 =
X = X H H
n 2 L (V - V ) i=l j i j
~
0.5 6.0 15 1.0 7.2 lS
1.0 4.2 11 2.0 3.5
2.0 3.7 10 3.0 3.3
3.0 2.6 7 4.0 3.3
4.0 2.3 6 5.0 3.1
6.0 3.0
7.0 3.0
0.966 0.911
0.0566 0.0877
0.944 0.911
0.885 0.884 .
X (H- h)
I
H X = X
(1 - -V ) j
H H
-* V , • J
9
9
9
8
8
a
.
Perfect Perfect I •
segre . mixing
0 l·
1 0
0 1
0 1
, (Tho-Ching Ho, Kirkpatrick, Wang, Hopper)
(Daw)
I3 = X / X , (Rowe, Nienow, Agbim)
I4 =
tpp layer bed
the .... % refuse in • 1n the produ~t recovery of the
•
the product at a 50 % mixture.
37
, (Weintraub, Deurbrouck ,Thomas)
. ---·-·------· --~- .. - -·· .
. ··- ··~•· -~ .~.,., .. .,.. ~ ·-- ....... _._... ... . ---.----------------... --····--- .. . '
..
TABLE 5
Effect of size of particles on mass of coal sinking during sink/float test. Based on 50 gram samples.
Size ----# 30
# 40
# 50
# 60
# 70
# 80
#100
#140
Minnesota Power Coal
(g) ----1.0
1.3
1.2
1.5
3.0
3.0
9.0
11.0
38
PP&L
(g) ----
4.1
4.5
3.5
5.3
5.5
4.5
6.0
8.5
....
•
..
'
-
,_, •• _ ........ - ...... • ••-• I '
•
From sink and float test: ....
PP&L coal. ·
---------- Minnesota Power c.oal.
25%
20%
15%
10%
5%
• •
• I I
• I ~ / )c
/ /
-- --~-r /)( )C
X • I I
I )( /
I I
X / I.
I
I I
I
I I I
40 50 60 70 80 100 140 <140
Mesh size
Figure 19. Sink/ float test.
39
. .
.. ,
•
-----------...,....-~---=sc-.,-,. --,"·,
was reduced to below 60 mesh, whereas in the PP & L coal, at
least s percent sank even in the larger fractions. This may •
indicate that the PP & L coal is amenable to physical
cleaning in larger size fractions than is the case for the
Minnesota Power coal.
Fluidized Bed Segregation with Coal and Magnetite
Experiments with mixtures of magnetite and coal were
carried out to measure the coal concentration and sulfur
concentration in the coal as a function of the dimensionless
distance from the top of the bed.
These experiments consist of two stages. A batch of
PP & L coal was separated into narrow size fractions, each
of which was weighed as shown in TABLE 6.
In the first stage of segregation, each of the coal
fractions (200 gram) was fluidized with the suitable size
fraction of magnetite (1800 gram). The minimum fluidization
velocity of the magnetite was chosen to be slightly higher
than that of the coal to achieve good segregation conditions.
Initially the mixture was fluidized at an air flow rate much
higher than minimum bubbling velocity for 5 minutes to mix
the mixture well. It was then fluidized at minimum bubbling
velocity for 30 minutes to achieve steady state conditions.
Bed depths were in the range of 5 to 8 cm. Divided into four
layers, the material in the bed was sucked out layer by layer
through use of the vacuum sampler. Each layer of material was
put into the magnetite separator and the magnetite was
40
•.
.-TABLE 6. Size distribution for PP&L coal
Particle Diam _____ ... ______ _ m Mesh No.
425
300
250
212
180
150
106
40
50
60
70
80
100
140
<140
I
Particle Range (Mesh No.)
30 > d > 40
40 > d > 50
50 > d > 60
60 > d > 70
70 > d > 80
80 > d > 100
100 > d > 140
140 > d
41 •
Weight (g)
1494
1500
1167
451
782
1160
468
1023
'
Weight%
19
19
15
6
10
14
6
13
'
·,
separated magnetically from the coal. Pyrite is not
ferromagne~ic, so the liberated pyrite goes with the coal
fraction. By weighing the coal in each layer, the coal
concentration profiles were obtained and by chemical analysis
of the coal samples from each layer, the sulfur concentration
in the coal was obtained.
In the second stage (top), the top coal layer from the
first cleaning stage was added to clean magnetite to form 10
percent coal mixtures. In the second stage (bottom), the
bottom layers of the beds from the first cleaning stage
was also added to clean magnetite to form 10 percent coal
mixtures. Segregation experiments were then repeated as in
the first stage. This process is illustrated in Figure 20.
The purpose of this second set of experiments was to
determine the effect of multistage operation on coal cleaning
ability. Samples of coal from each of the tests and from
each bed layer were sent to a testing laboratory (Warner
lab.) for sulfur analysis.
The coal concentration profiles in the first stage,
second stage (top) and second stage (bottom) are shown in
Figures 21 to 25. These show that the coal concentration
profiles in the first stage, the second stage (top), and
second stage (bottom) have almost identical profiles for each
combination of coal and magnetite. A summary of the results
is shown in Figures 26, 27 and 28.
From the results of the chemical analyses for the
42
•
•
•
'
'
..
-
-
coal and magnetite ( narrow size fraction)
If'
"
'
--
:,
Magnetite
-
----..
.,_ ___ ... -.....
-- .
---.....
TWO identical mixtures in the 1st stage
... ,
.... •
....._ ,
'
....... ,
I ...... ,.
.... ,
Magnetite
The· second stage (top) The second stage (bottom)
Figure 20. Multistag.e process • • ••
43
I
• f
.. . • f
..
•
•
•
•
•
..
..
•
• •
. .. . .
-••
· ....
201 o
15%
101
51
Original coal weight% -- 101
40 mesh coal & 50 mesh magnetite
4
..
+ -The 1st trial in the 1st stage. 6 -The 2nd trial in the 1st stage. • -The 2nd stage (top). 0 -THe 2nd stage ·c bottom).
+
•
0.25 0.5 o. 7 5 1.0
Z / L
( Z: distance. from the free surface) •
, • I I I
..
Figure 21. Coal concentration profiles (40 mesh coal).
••
44
.. . . ~-
. .
I
•
•
•
. .
.. • I
• .. ' .
..
.. •
•
•
-
. .. . ..
--
i:: 0
-ri +J •, «s .:. . ~
~ .µ s:: Q)
,-t u «s s:: 0 0 uo
251
20%
15\
101
51
• •
• •
..
Original coal weight I -- 10%
60 mesh coal & 70 mesh magnetite
+ -The 1st trial • the 1st stage. in 6 -The 2nd trial in the 1st stage. e -The 2nd stage ( top ) . O -The 2nd stage ( bottom ) .
• •
• 0 +
•
•
I
0.25 0.5 o. 7 5 1.0 z / L
( z: distance from the free surf~~~) .
Figure 22. Coal concentration profiles (60 mesh coal) . ..
45
,,.
.. . . .. .
•·
• •
.. .
I
'
. , I
• • •
' I
\
..
• •
.. .
-.
-
..
J
• 251
.•· 0
20% +
151
101
51
J
Original coal weight% -- 10% 80 mesh coal & 100 mesh magnetite
+ -The 1st 6 -The 2nd e -The 2nd 0-The 2nd
•
0.25 I
trial trial stage stage
•
•
• the 1st stage . in in the 1st stage. ( top). (bottom).
A ........ -----oo- . +
~
•
o.s 0.75 1.0 Z / L
..
( Z: distance from the free surface)
Figure 23. Coal concentration profiles (80 mesh coal) .
46
..
•
•
'
•
.. ,.
• •
-
- .
...
'
..
•
. .
•
'
. . ..
~ 0 ..... .µ &U
• M ~.µ
i:: Cl)
ri u cd h 0 0 uo
...
251
201
., 15%
101
51
,.
I I • I f
, ••
original coal. weight I -- 101 .. . . .
'•
100 mesh coal & 140 mesh magnetite
+ -The 1st trial in the 1st stage • ~ -The 2nd trial in the 1st stage. • -The 2nd stage (top). o -The 2nd stage (bottom).
•
• 0 9 \ -f
. ' 0
A A
A
0. 2 5 0.5 o. 7 5 . 1.0
Z / L
( z: distance from the free surface)
Figure 24. Coal concentration profiles (100 mesh coal) .
47
•
..
•
•
•
• •
-
. .
.. . ~. -
~ ..
. . •,•
...
.. .
. .
. .
r
...
. ,•
~ 0
-ri .µ ftS
• H ~~
i:: cu
.-t u ,a s:: 00 uu
251
20\
15%
10\
5%
'•
Original coal weight I -- 10 I
140 mesh coal & 140 mesh magnetite
+ ·-The 1st trial • the 1st stage. in A -The 2nd trial in the 1st stage. e -The 2nd stage ( top ) . o -The 2nd stage ( bottom ) ·. •
•
• ..
o. 2 5 0.5 0.75 1.0
Z / L
( Z: distance from·the free surface)
Figure 25. Coal concentration profiles (140 mesh coal).
48
•
·... .
•
•
•
...
, .
..
• •
•
original coal weight I -- 101
... <D 40 mesh coal & 50 mesh magnetite • - 60 mesh •
coal & 70 mesh magnetite 80 mesh coal & 100 mesh magnetite
mesh coal & 140 mesh magnetite •
25% - @ l~O mesh coal & 140 mesh magnetite . . . •
i:: 0
•
-r4 .µ
20% ., • M
~+J C Q)
~u ftS i:: 00 00
15%
. -.· ..
,
10\ .•
..
5\
...
.. .
... 0.25 0.5 0.75 1.0
... Z / L
( z: distance from the free surfa~e)
•
" Figure 26. Coal concentration profiles in the 1st stage. Summary fer all size fractions.
I •
. . . ' • 49
. ..
•
. ..
• • -
.. ;
•
.
..
. .
...
- ~
..
..
•
original coal weight% -- ld%
25\ ·mesh magnetite (1) 40 mesh coal & 50
$ 60 mesh coal & 70 mesh magnetite·· 80 mesh coal & 100 mesh magnetite
.. s:: @ 100 mesh coal & 140 mesh magnetite O· @ 140 mesh coal & 140 mesh magnetite •r-1 .µ 20% RS
• H ~.µ
i:: Cl)
r-40 cd i:: 0 0 uo
151
10%
5%
o. 2 5 0.5 0.75 1.0 Z / L
( z: distance from the free surface) .,
Figure 27. Coa~ concentration profiles in the 2nd stage (top). Summary for all size fractions.
50
•
.
• •
.. .
.. .
. ..
•
•
..
- ..
...
• •
• !- I· I •
.- . . . '·
••
•• •
Original coal weight% -- 10%
40 mesh coal & 50 mesh magnetite 60 mesh coal & 70 mesh magnetite··
251 80 mesh coal & 100 mesh magnetite 100 mesh coa·l & 140 mesh magnetite
• 140 mesh coal & 140 mesh magnetite . .
\ ..
,::: 0 .. ..... 20% +l ,u . ~
~.µ ~ Cl)
r-4 0 ctl. ~ 0 0 uo 151
10%
5%
• •
. -.. ., . . o. 25 0.5 0.75 1.0 z I L
.... ( z: distance from the free surface")
Figure 28. Coal concentration profiles in the 2nd stage (bottom). Summary for all size fractions.
51
I
•
•
I
. .
.
'-..
parent coal, the sulfur concentration is plotted as a
function of size fraction of coal in Figure 29. Compared to
Figure 19 in the sink and float test, the sulfur
concentration curve in Figure 29 and the sink portion . ,
concentration curve have the same basic shape.
The sulfur concentration profiles in the first stage,
second stage (top) and second stage (bottom) are shown in
different ways from Figures 30 to 37. In all stages of
cleaning, the sulfur concentration in the coal in the top
layer is always less than that in the other layers. This
occurs because pyrite has almost the same density as
magnetite and tends to be distributed uniformly within the
magnetite. Coal, in the other hand, floats to the top of the
bed resulting in a layer of coal which is deficient in
sulfur. In all cases, the second stage of cleaning resulted
in additional reductions in sulfur concentration for the coal
at the top of the bed.
Inclined Fluidized Bed
In the final phase, the inclined bed was fabricated,
installed in the laboratory, debugged and tests were carried
out with it. Fluidization experiments were performed at
minimum bubbling velocity with the bed inclined at different
angles. During these tests, material was fed in at one end
and removed from the other. The results showed that the bed
was fluidized uniformly over the entire length. Tests to
measure residence time of particles in the bed as a function
52
., .
..
-
:~ .
s:: 0 ~
~ ~ ::s ctS ~ ~ M .µ ::s s:: tJl (1)
0 s:: 0 0
•
4
3
' 2
1'
1
40
'
..
-
50
{
Instrumental sulfur
- - - - - Pyritic Sulfur
•
"""" , / ,,,,
60
Mesh
• I /v
)( /
• / 'C /
~ /
' ' -- ,,
,<
70 80 100 140 >140
• size
Figure 29. Sulfur concentration in
raw coal from PP & L
53
..
•
I
•
...
•
•
'
•
'
• . •
'
. . .
. .. ..
.. .
.. .
..
..
. .
4\
3%
2%
1% .'•
.... .
(
••
Original coal weight I -- 10% •
40 mesh coal & 50 mesh m·agnetite ••
+ -The 1st trial in the 1st stage • A -The 2nd trial in the 1st stage. • -The 2nd stage ( top ) .• o -THe 2nd stage (bottom) .
A --
Z:
I
l .. I I •
I I I • I
o. 2 5
' ) , '
distance
• •
0.5 o. 7 5
z I L .._
from the free surface
I • I ' f
1 • 1 I I
.. ...
1.0
..
)
Figure 30. Sulfur concentration profiles (40 mesh coal).
\_/ 5 4
..
•
•
,
I I
-
• • •
•
I U It
orig~nal coal weight% -- 101
60 mesh coal & 70.mesh magnet~te
+ -The 1st trial in the 1st stage. ~ -The 2nd trial in the 1st stage. e -The 2nd stage (top). o -The 2nd stage (bottom). • •
• . .
.. . _ ..
i: I 0
I - ..... -· -~ 4\ ~ «J
M ..µ 0 .. ~ i::
:l Q) ~o .-i ,::: ::1 0 (I) 0 3%
' I I ..:
I
. . . 2%
I
I • . . w.
I I
,., •
1% I -I I .. I
0.25 0.5 0.75 1.0 - .. .. . . . :, ·' Z / L
( z: distanc& from the free surface) .... )
Figure 31. Sulfur concentration profiles (60 mesh coal).
55
.... .. • •
' I
. . ...
. .. ..
•
.. .
•
..
•
•
-
-..
. .
..
•
... .
~ 0
•rt 4% • .µ ~ RS
H .µ
J.-4 i:: :::i QJ ~o r-i i::: :::i 0 Ul 0 3%
1%
·:- .
Original coal weight t -- 10% ' ' • ' I
· 80 mesh coal & 100 mesh magnetite
+ -The 1st trial in the 1st stage. A -The 2nd trial in the 1st stage. • -The 2nd stage (top) . o -The 2nd stage ( bottom ) •
I l I I I •
I I
I
+ •
• +
I
I
I I I I I
.. ,
~ . . ..
0.25 0.5 0.75 1.0 z / L
( Z: distance from the free surface:
Figure 32. Sulfur concentration profiles (80 mesh coal).
56
..
•
'.,
•
. .
••
-
..
. . .,
• •
-
•
. '
-. .. ..
..
•
....
'j
'"., ···!'-,
•
· ...
4%
3\
2%
1%
.
'
original coal weight% -- 10% 100 mesh coal, 140 mesh magnetite
+ -The A -The • -The o -The
I I
I
I I
I I
I
I
let trial 2nd trial 2nd stage 2nd stage
'·-
-t·
0. 2 5
I the 1st stage. in in the 1st stage. ( top). ( bottom ) .
A
+ +·
•
0.5 0.75
z I L
•
I
I 1.0
.... '
( z: distance from the free surface )
Figure 33. Sulfur concentration profiles (100 mesh coal) •
57
•
·.-.. ..
•
..
•
-:-"'""'
. .. .
I
•
-
, ...
. •
I ·•• ••
•
.. .. .
..
..
..
-
·' .
. .
.... .
.... .
4%
3\
2%
1%
•
Original coal weight% -- 10%
·140 mesh coal & 140 mesh magnetite·
+ -The A -The e -The O -The
I I I I I
I I
1st 2nd 2nd 2nd
I I I I I I I
0.25
trial trial stage stage
A
in the 1st stage. in the 1st stage. ( top). ( bottom ) •
...
0 .. :t
-to
A
·O. 5 o. 7 5
z I L
1.0
( Z: distance from the free surface)
Figure 34. Sulfur concentration profiles (140 mesh coal).
. . ..
. . 58
•
•
•
.
. •
.
'
...
..
-
-
.. .
•
..
original coal weight% -- 10 I · •
(I) 40 mesh coal & 50 mesh magnetite 60 mesh coal & 70 mesh magnetite
mesh coal 100 mesh magnetite 80 &
.... ~ 100 mesh coal & 140 mesh magnetite 140 mesh coal & 140 mesh magnetite
® • ..
.'•
i:: . 0 4\
•rl • .6,J ~ «J
M .µ
M S:: :::J Q) G). 'H 0 r-i J:'.:: :::1 0 3% Ul 0
0.25 0.5 0.75 1.0
Z / L
( Z: distance from the free surface)
Figure 35. Sulfur concentration profiles in the 1st stage. Summary for all size fractions .
•
59
. •
. ..
-
-• ' I '
• •
. . ..
.
•
. .. ..
•
-
-..
•
• •
.
•
Original coal weight% -- 10%
(D 40 mesh coal & 50 mesh magnetite ... •. ® 60 mesh coal & 70 mesh magnetite
® 80 mesh coal & 100 mesh magnetite 100 mesh coal & 140 mesh magnetite
• 140 mesh coal & 140 mesh magnetite
,:: 0
•ri 4% • +l ~ «s
H +l
M s:: ::I Q) CH 0 .-. ,:: ::I 0 Ul 0 3%
~--~@------------2%
1%
0. 2,5 0.5 0. 7 5 1.0
Z / L
( z: distance from the free surface)
Figure 36. Sulfur concentration profiles in the 2nd stage (top). Summary for all size fractions.
. . . ..
•.
60
•
• •
'
-/ ...... ~,
...
-
•· . • •
. '. . .
..
. .
.. .
.. -
...
•
..
. .
•
.. . . ..
....
i:: 4\ 0 -ri
• .µ ~ ro
~ .µ
M i::: ::, (1) ~u ,... i:: 3% :l 0 Ul 0
2%
lt
original coal ~eight% -- lOt
(I) 40 mesh coal & 50 mesh magnetite 60 mesh coal & 70 mesh magnetite 80 mesh coal & 100 mesh magnetite
100 mesh coal & 140 mesh magnetite 140 mesh coal & 140 mesh magnetite
o. 25 0.5 o. 75 .
Z / L
•
I 1.0
( Z: distance from the free surf ace, )
Figure 37. Sulfur concentration profiles in the 2nd stage (bottom). Summary for all size fractions .
61
.'• •
•
•
1. •
..
•
of feed rate of bed material and angle of inclination were
carried out and these results are shown in TABLE 7.
Visual observation of the bed shows that when a
suitable mixture of magnetite and coal is fed to the bed, the
. exit stream is highly segregated, with the top layer rich in
coal. The results are shown in TABLE a.
CONCLUSIONS
A study of the fluidization experiments of coal and
magnetite in a air fluidized system has resulted in the
following conclusions :
. When particles which individually have identical
minimum fluidization velocities are mixed together, they
fluidize uniformly with bubbling occuring over the entire
height of the bed and with relatively little segregation of
materials. • • minimum fluidization velocities of the
• When the
individual materials are not equal, the material with
the larger minimum fluidization velocity tends to segregate
and settle to the bottom of the bed with the other material
floating to the top .
. If Umfl >> Umf2 and Umfl > Ugas > Umf2, component 1
settles to the bottom of the bed and forms a packed layer
while component 2 forms a fluidized layer on top. Therefore,
some amount of component 2 which is trapped in component l
has no chance to rise upward .
• The time to achieve steady state conditions increases
62
·---... . . .. -·------... , ...•. -... _ .......... ------ff .. -.... ~ •• ....... __ ............. ·-••• • '•· ..... .._...;. .. .._ ........ • '• I t ...... I"••-••"·- - ...... , .... , I
"
,.
TABLE· 7. Test results with inclined bed.
....
-
•
Q 8
(c.c/sec) {degree)
0 .14
42 0.28 0.55
. 1. 1
0.14 0.28
25 0.55 1. 1
a .14
10 0.28
-- 0. 55 · · . l . 1
Q - material feeding rate
8 - angle of inclination
.h1 - bed depth at inlet
h2 -_bed depth at exit (
bl
(cm)
9 9 8 6
.
9 .
8 7 6
8 .. 8 7 f,
63
h2 Resident Time
(cm) (min:sec) .
3 2:50 3 2:45
2.5 2: 15· 2.5 1:55
2.5 6:30 2.5 6:25 2.5 5:45 2.5 5:30 ....
2.5 10:30 --· . -- - - .
2.5 10:30 .,
2.5 9;50 .2.4 9:30
....
-·
•
TABLE 8
TEST RESULTS WITH INCLINED BED
. Resident
Q e hl h2 Time Mixture (C.C/sec) (degree) (cm) (cm) {min:sec)
1 10 0.14 8 2.5 10:30 ' •
~
2 10 0.14 8 2.5 10:30
1 -- mixture of 10% Weight mesh 60 PP&L coal
with 90% Weight mesh 70 magnetite.
2 -- mixture of 10% Weight mesh 80 PP&L coal ¢
with 90% Weight mesh 100 magnetite.
64
..
Coal W. Concentration • Top Layer lil
21%
23%
sharply with bed depth. ..
.Air flow rates close to minimum bubbling velocity
(Umb / Umf = 1.6 to 1.8) has the best effect on segregation.
; The depth of the bed has little effect on efficiency
of segregation .
. With both the Minnesota Power and PP&L coals, finer
particles release more pyrite and there is a critical size ..
below which more extensive liberation of the pyrite begins
to occur .
. The coal concentration profiles are qualitatively
similar in shape for all cases studied .
. The sulfur concentration in the coal in the top layer
is always less than that in the coal in other layers of the
bed because pyrite has almost the same density as magnetite
and tends to be distributed uniformly within the magnetite .
. Multistaging is more effective than single stage
cleaning on sulfur segregation in coal from the bottom of the
bed to the top .
. For certain size fractions of coal, sulfur reduction
can always be achieved by fluidizing the coal with the
pertinent size fraction of magnetite .
• Al though a complete study of the continuous process
is beyond the scope of this experiment, the inclined bed
shows a promising way to clean the coal.
The experimental data and results developed in this
study support the final conclusion that an air fluidized bed
65
• r ,· i • ' : '!1 ~· I
is effective in segregating coal-minerals from coal when a
··bed mixture of coal and magnetite is used.
(
66
.. 0 a
l ,l•
• \ ~·:-:;,
•
REFERENCES
'
1. ''New per spec t iv e on co a 1 c 1 ea n in g '' E PR I Jou r n a 1 ,
November 1985,15.
2. "Coal cleaning test facility : 1985 plan", EPRI CS-4071,
Projects 1400-6, 1400-11 Interim Report, July 1985.
3. E.K. Levy, "Coal cleaning in a multistage air fluidized
bed", Research Proposal, January 4, 1985.
4. P. N. Rowe, A. w. Nienow and A. J. Agbim, "A preliminary
Quantitative study of particle segregation • in gas
fluidized beds -- binary systems of near spherical
particles", ~rans. Inst. Ch~m. En~s.,
P. 324.
Vol. 50, 1972,
5. P.N. Rowe and K.S. Sutherland, "Solids mixing studies i·n
gas fluidized beds part II: The behavior of deep beds
of dense materials", Trans. !!!st. Chem. ~ngrs., Vol. 4 2,
1964, T 55.
6. Rowe, Partridge, Cheney, Henwood and Lyall, "The
Mechanisms of Solids Mixing in Fluidized Beds", !ra!}s.
Instn. Chem. Eng., Vol. 43, T 271 (1965).
7. P. N. Rowe, A. w. Nienow and A. J. Agbim, "A preliminary
8.
quantitative study of particle segregation I
in gas
fluidized beds -- Binary systems of near spherical
particles", Trans. Instn. Chem. Engr., Vol. 50, 1972.
J. L. P. Chen and D. Keairns, "Particle segregation I in
a fluidized bed", Canadian J. Chemical Engineering, Vol.
53, August 1975, P. 395.
67
I
9. A. w. • Nienow, P. N. Rowd, L. Y. -L. Cheung, II A
quantitative analysis of the mixing of two segregating
powders of different density in a gas-fluidized bed",
Po~~er Tech_!!2_logy, 20, 1978, P. 89-97.
10. A. w. Nienow, P. N. Rowe and T. Chiba, "Mixing and
segregation of a small prpportion of large particles in
gas fluidized beds of considerably smaller ones", AICHE
§.y!!!Eosiu~ ~erie~ No. 176, Vol. 74, P. 45.
11. W. Weintraub, A Deurbrouck and Thomas, "Dry-cleaning
coal in a flui-dized bed medium", DOE Report RI-PMTC-4
(79) •
I
68
•
h
H
-V
j
·v • • J1
w
X bed
X top
• •
• •
• •
• •
• •
• •
• •
Nomenclature
The depth from the surface
Bed depth
Average jetsam volume percentage
Jetsam volume percentage in the i layer
Weight
Average Jetsam volume percentage
Jetsam volume percentage in the top layer
)
\.
\
•
69
----~-----.-.-··.,,..,.,,.;I~·-,·, .. '
,t
Biography
NAME: Yih-Tun Tseng
DATE OF BIRTH: Jan. 18, 1960
PLACE OF BIRTH: Hsin-Chu, Taiwan, R.O.C.
NAME OF FATHER: Chia-Sheng Tseng
NAME OF MOTHER: Hwan-Chin Sam
INSTITUTION ATTENDED: National Taiwan University
DEGREES : B.S. (Aug. 1, 1978)
'
..
...
4 I