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  • 8/12/2019 Abdullah, Husain, Pong - 2003 - Analysis of Cold Flow Fluidization Test Results for Various Biomass Fuels

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    Available online at www.sciencedirect.com

    Biomass and Bioenergy 24 (2003) 487494

    Analysis of cold ow uidization test results for variousbiomass fuels

    M.Z. Abdullah, Z. Husain, S.L. Yin Pong

    School of Mechanical Engineering, Engineering Campus, Universiti Sains Malaysia, 14300 Nibong Tebal, Penang, Malaysia

    Received 11 July 2001; received in revised form 3 October 2002; accepted 16 October 2002

    Abstract

    A systematic theoretical and experimental study was conducted to obtain hydrodynamic properties such as particle size

    diameter, bulk density, uidizing velocity, etc. for locally available biomass residue fuels in Malaysia like rice husk, sawdust,

    peanut shell, coconut shell, palm ber as well as coal and bottom ash. The tests were carried out in a cold ow uidization

    bed chamber of internal diameter 60 mm with air as uidizing medium. The height of the chamber could be raised up to

    630 mm by ve separate cylindrical rings. Bed-pressure drop was measured as a function of supercial air velocity over a

    range of bed heights for each individual type of particle. The data were used to determine minimum uidization velocity,

    which could be used to compare with theoretical values. The particle size of biomass residue fuel was classied according to

    Gildarts distribution diagram. The results show that Gildarts particle size (B) for sawdust, coal bottom ash, coconut shell

    have good uidizing properties compared to rice husk, type (D) or palm ber, type (A). The bulk density and voidage are

    found to be main factors contributing to uidizing quality of the bed.? 2003 Elsevier Science Ltd. All rights reserved.

    Keywords: Biomass residue fuel; Coal bottom ash; Fluidizing velocity

    1. Introduction

    Feasibility studies on the ecient combustion by

    existing combustors for low-grade fuels having high

    ash content, high moisture content and low heating

    value have not been encouraging and have indicated

    the need for development of suitable uidizing bed

    chamber systems [1]. Fluidization bed technology is

    a method to achieve higher combustion eciency

    of 9698% and about 6080 times higher heat

    Corresponding author. Tel.: +604-593-7788x6314; fax: +60-

    4-594-1025.

    E-mail address: zoeb [email protected] (Z. Husain).

    transfer rate in steam boiler rings than those ob-

    tained by submerging the heat exchanger in combus-

    tion gases of the fuels [2]. It gives a boiler eciency

    of 80 85% with added advantage of low combustion

    temperature (800900

    C) and thus low emission ofNOx. The uidized combustion of low grade fuels

    is now a well-recognized technology well adapted in

    power plants. The uidizing medium can be air/gas

    [3]. The combustion zone in uidized bed boilers op-

    erate under special hydrodynamic conditions essential

    for good combustion process.

    Prachir Barce [4] proposed that laboratory model

    uidized bed can be used to simulate the process

    and eventually a full-sized boiler can be constructed.

    Among the various parameters and properties of the

    0961-9534/03/$- see front matter? 2003 Elsevier Science Ltd. All rights reserved.

    P I I : S 0 9 6 1 - 9 5 3 4 ( 0 2 ) 0 0 1 5 0 - 2

    mailto:[email protected]:[email protected]
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    488 M.Z. Abdullah et al./ Biomass and Bioenergy 24 (2003) 487 494

    Nomenclature

    A cross-sectional area of the bed (m2)

    Ar Archimedes no.

    di arithmetic mean of the aperture (opening)

    of adjacent sieves (m)

    dm mean diameter of particle (m)

    D diameter of the bed

    G1, G2 weights of lled-in and empty cylinders

    (kg)

    M mean of particles (kg)

    Remf Reynolds no. at minimum uidized con-

    dition

    U supercial gas velocity (m/s)

    Umf minimum uidized velocity

    xi weight fraction of samples collectedbetween two sieves

    void fraction

    mf voidage at minimum uidization ve-

    locity

    viscosity of uidizing medium

    (N s=m2)

    b bulk density (kg=m3)

    f uidizing gas density (kg=m3)

    p particle density (kg=m3)

    s solid density (kg=m3)

    P pressure drop across bed (Pascal)

    material that are to be taken into account are particle

    size, uidizing gas/air velocity, bulk density which in-

    uences the bed behaviour [5,6]. It has been estimated

    that 23% of total power generated in this country

    can be produced by burning biomass residue as fuel.

    Biomass residues such as rice husk, palm ber, co-

    conut shell are available in plenty from various mills

    and they can be used as fuels more eciently through

    uidized bed systems.

    2. Theoretical analysis

    2.1. Bulk density

    Bulk density is the overall density of loose material

    including interparticle distance separation. It is dened

    as overall mass of material/unit volume. It is measured

    simply by pouring weighed quantity of sample of par-

    ticles through a funnel into a graduated cylinder and

    volume occupied determines the bulk density:

    Bulk density b= G1 G2=Vi;

    where G1and G2are the weights of lled in and empty

    cylinders and Vi internal volume of cylinder (Vi =

    1000 ml).

    2.2. Solid density

    Solid density is dened as density of particles in-

    cluding the voids within the individual particle. It is

    dened as the weight of the particle divided by the vol-

    ume. Solid fuels have to be converted into loose par-

    ticle form before making into pellets using a press to

    determine solid density. In some cases the material is

    poured into a 30 mm diameter female mold and man-

    ually compressed to 6 MPa by mechanical pressure.

    2.3. Voidage

    A mass of material has particles resting on each

    other due to force of gravity to form a packed bed.

    Depending on the shape of particles and packing char-

    acteristics, however, a certain volume of space in be-

    tween the particles remains unoccupied, such space is

    called voidage. It is dened as

    = voidage volume

    volume of particles + voids:

    voidage is related to solid and bulk density given

    by [7]

    = 1 b=s: (1)

    2.4. Classication of particle size

    All types of particles cannot be uidized satisfac-

    torily. The particle size is an important parameter for

    uidization. The particles can be classied according

    to [8]classication based on density and particle size.

    Category (C) whose particle size diameter is less

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    490 M.Z. Abdullah et al./ Biomass and Bioenergy 24 (2003) 487 494

    Fig. 1. Schematic diagram of uidized bed apparatus.

    The air velocity in the cylinder of internal diameter

    D= 60 mm.

    U= Q

    4 D2: (9)

    The pressure drop in pascal across the bed given by

    P= g[H2(m=f 1)] + Z2 Z1; (10)

    wherem= 1000 kg=m3 for water.

    4. Material preparation and properties

    The materials are grouped as conventional solid fu-

    els such as coal and non-conventional biomass residue

    fuels such as coconut shell, palm bre, peanut shell,

    etc. The coal bottom ash is unburnt particles of coal

    collected from pulverized coal-red boiler furnace.

    Sawdust specimen is collected from logging opera-

    tions in Malaysia. The mean diameter is obtained from

    the data collected from sieving the sawdust particles.

    The mean diameter

    dm= 1

    xi=di=

    1

    1:275= 0:786 mm:

    Peanut shell in its natural form is not used to carry

    out the tests. A grinder is used to produce peanut

    shell particles. The mean diameter is calculated as per

    Table1.

    Coconut shell is also not used in the natural formand same procedure used for peanut shell. Palm ber

    is obtained from palm oil mills after removing oil from

    the fruit. It is dried and shredded into particles size

    and a sieve shaker used to determine the mean diam-

    eter. The coal specimen is collected from the thermal

    power station at Kapar in Malaysia. It is used as pul-

    verized fuel in boilers and specimen collected from the

    ball mill. The mean diameter is obtained from sieving

    process. The mean diameter of coal bottom ash is also

    obtained from sieving process.

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    M.Z. Abdullah et al./ Biomass and Bioenergy 24 (2003) 487 494 491

    Table 1

    Determination of mean diameter of sawdust

    Diameter range (mm) Arithmetic mean of Weight collected (g) Weight fractionxi xi=di

    aperture di (mm)

    0 0.15 0.075 4.5 4:5=340:2 = 0 :0132 0.17630.15 0.30 0.225 2.4 2:4=340:2 = 0 :0071 0.0352

    0.30 0.50 0.400 3.2 3:2=340:2 = 0 :0094 0.02500.50 0.85 0.675 25.1 25:1=340:2 = 0 :0738 0.122

    0.85 1.00 0.925 180.1 180:1=340:2 = 0 :5291 0.6188

    1.00 1.50 1.250 125.1 125:1=340:2 = 0 :3674 0.2939

    W= 340:2

    xi=di= 1 :275

    Table 2

    Hydrodynamic properties of biomass residue fuels

    No. Name of specimen Mean diameter Bulk density Solid density Voidage HHV Gildartdm (m) (kg=m3) (kg=m3) () (kJ=kg) classication

    1. Sawdust 786.5 241 570.3 0.5770 12987.2 B2. Rice husk 1500 129 630.1 0.800 10298.5 D

    3. Peanut shell 613.4 250 566.8 0.5590 12004.3 B4. Coconut shell 987.4 430 547.92 0.2152 17289.3 B

    5. Palm ber 600 73 407.36 0.8200 14105.9 A

    6. Coal 518.8 945 1450 0.3483 32635.8 B7. Bottom ash 475 1188 1400 0.1514 2265.9 B

    5. Solid and bulk density of particles

    Sawdust is turned into pellets by using a hydraulic

    press under a manual pressure of 6 MPa and solid

    density determined as the mean of specimen divided

    by volume. The solid density of other biomass residue

    fuels is calculated in a similar manner. Coal and coal

    bottom ash solid densities are calculated by displace-

    ment of water using a measuring cylinder. The bulk

    densities of the materials are calculated by the method

    outlined earlier. The caloric values of the materials

    are obtained by a bomb calorimeter. The voidage ofthe materials is calculated from Eq. (1). The results

    are given in Table2.

    6. Results and discussion

    Sawdust of mean particle size 0:786 mm classied

    as Gildart B is used in this study. The plots of pres-

    sure drop P across the chamber against supercial

    velocity gas velocity U is shown in Fig. 2. The in-

    tersection of slope of xed bed of voidage mf andhorizontal constant uidized pressure drop is taken as

    a measure of minimum uidized velocity Umf. The

    value of Umf from graph is 0:22 m=s. The pressure

    drop (W=A) = 212 Pa for sawdust for a bed height of

    90 mm almost coincides with the experimental value.

    Rice husk of mean diameter particle size 1:5 mm

    classied as Gildart D is used in the study. The plot of

    pressure drop Pacross the chamber against super-

    cial gas velocity is shown in Fig. 3. The minimum

    uidized velocityUmf= 0:37 m=s. The static pressure

    drop P= W=A = 155 Pa for a bed height of 120 mmhas a value slightly lower than the experimental result.

    The result for peanut shell is shown in Fig. 4.The

    value ofUmf= 0:29 m=s. The value of pressure drop

    P= (W=A) = 295 Pa for the bed height of 120 mm,

    which is slightly higher than experimental results. It

    has been observed that no uidization occurs for palm

    ber classied as Gildart A type.

    Big voids are immediately noticeable as soon as gas

    allows to ow across the bed; the chamber bed begins

    to expand. The particles are in the form of powder,

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    492 M.Z. Abdullah et al./ Biomass and Bioenergy 24 (2003) 487 494

    0

    50

    100

    150

    200

    250

    300

    350

    0.00 0.10 0.20 0.30 0.40 0.50 0.60 0.70

    Gas Velocity (m/s)

    PressureDrop

    (Pa)

    0.22

    Fig. 2. Pressure drop vs. supercial velocity for a bed height of 900 mm for sawdust; umf = 0:22 m=s.

    0

    100

    200

    300

    400

    500

    600

    700

    800

    0.00 0.10 0.20 0.30 0.40 0.50 0.60 0.70 0.80 0.90 1.00

    Gas Velocity (m/s)

    PressureDrop

    (Pa)

    0.37

    Fig. 3. Pressure drop vs. gas velocity for a bed height of 120 mm for rice husk; umf = 0:37 m=s.

    0

    50

    100

    150

    200

    250

    300

    350

    400

    0.00 0.10 0.20 0.30 0.40 0.50 0.60 0.70

    Gas Velocity (m/s)

    PressureDrop

    (Pa)

    0.29

    Fig. 4. Pressure drop vs. supercial velocity for a bed height of 120 mm for peanut shell; umf = 0:29 m=s.

    interparticle forces are known to be high and impact

    of gravitational forces on particles is weak due to its

    light weight.

    Coal is the conventional fuel used in boilers as fuel

    in power house. The mean particle size of 0:518 mm

    classied as Gildart B type. The plot of pressure drop

    P against the supercial velocity U is shown in

    Fig.5.The value ofUmf = 0:51 m=s and static pres-

    sure P= W=A =833 Pa for the bed height of 90 mm

    which is lower than the experimental value.

    Coal bottom ash has a mean diameter particle

    size of 0:475 mm and is classied as Gildart B type.

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    M.Z. Abdullah et al./ Biomass and Bioenergy 24 (2003) 487 494 493

    0

    500

    1000

    1500

    2000

    2500

    3000

    0.00 0.20 0.40 0.60 0.80 1.00 1.20

    Gas Velocity (m/s)

    PressureDrop(P

    a)

    0.51

    Fig. 5. Pressure drop vs. supercial velocity for a bed height of 900 mm for coal; umf = 0:51 m=s.

    0

    500

    1000

    1500

    2000

    2500

    0.00 0.20 0.40 0.60 0.80 1.00 1.20

    Gas Velocity (m/s)

    PressureDrop

    (Pa)

    0.58

    Fig. 6. Pressure drop vs. gas velocity for a bed height of 900 mm for coal bottom ash; umf = 0:58 m=s.

    The plots of pressure drop P against supercial

    velocity are shown in Fig. 6. The value of Umffrom graph is 0:58 m=s and value of pressure drop

    P= (W=A) = 1047 Pa for a bed height of 90 mm

    and is the same as obtained from experiment.

    7. Conclusion

    The results show that Gildarts type B particles

    (sawdust, peanut shell, coconut shell, coal and bottom

    ash) have good uidizing behavior and good bubbling

    bed. It has been found that Gildarts type D (rice husk)

    and type A (palm ber) particles have poor uidiza-

    tion behavior.

    Bulk density and voidage are found to be two main

    factors contributing to uidizing quality of a bed. The

    larger the bulk density, the better is the uidizing qual-

    ity of bed. Voidage gives adverse eect to uidization.

    Particles in the form of powder is poor as uidizing

    material and gives rise to expanding bed chamber. The

    experimental uidized velocity does not coincide with

    theoretical values for most of biomass residue fuels

    except rice husk.

    References

    [1] Van Swaaij WPM, Afgan NH. Heat and mass transfer in xed

    and uidized bed. Washington DC: Hemisphere Publishing

    Corporation, 1986. p. 21929, 33351, 37180.

    [2] Harrison D. Fluidization. Science Progress, in Oxford

    1974;61:191217.

    [3] Delgado J, Aznar MP, Corella J. Biomass gasication with

    steam in uidized bed: eectiveness of CaO, MgO and

    CaOMgO for hot raw gas cleaning. Ind. Eng. Chem. Res.

    1997;36:153543.

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    [4] Basu P, Fraser SA. Circulating uidized bed boilers design

    and operations. Stoneham, MA: Butterworth-Heinemann,

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    [5] Mchirgui A, Tadrist L, Pantaloni J. Inuence of particle-size

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    [6] Howard JR. Fluidized bed technologyprinciples and

    applications. Bristol, New York: Adam Hilger, 1989. p. 1 69.

    [7] Cheremisino NP, Cheremisino PN. Hydrodynamics of

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    1984. p. 210, 13761.

    [8] Geldart D, Abrahemsen AR. Fluidization of ne porous

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    [9] Ergun S. Fluid ow through packed columns. Chemical

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    [10] Leva M. Fluidization. New York: McGraw-Hill, 1959.