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    IX JAPAN-BRAZIL SYMPOSIUM ON

    DUST PROCESSING - ENERGY - ENVIRONMENT

    IN METALLURGICAL INDUSTRIES

    September, 8-11, 2013

    Gorceix Fundation Auditorium, Ouro Preto, Brazil

    THE STATE-OF-THE-ART EMPLOYMENT OF WOODY

    BIOMASS AND BIOGAS IN MANUFACTURING INDUSTRIES

    CENTERING AROUND STEEL INDUSTRY

    Tateo USUI ( Osaka Univ., Japan; now at Univ. Federal de Ouro Preto, Brazil )

    Hirok azu KONISHI , Kazuh ira ICHKAWA , Hideki ONO, Hiroto sh i KAWABATA

    ( Graduate School of Engneering, Osaka Univ., Japan )

    Paulo Santos A ss is ( Univ. Federal de Ouro Preto, Brazil)

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    1. INTRODUCTION

    The purpose of this paper is to show the

    idea of an excellent employment of woody

    biomass and biogas in manufacturingindustries centering around steel industry.

    In the beginning, how come to recognize

    the present research themeis explained by

    looking back on our previous works.

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    2. BACKGROUND FOR THE PRESENT WORK

    The first author and coworkers used to be,carried out experimental studies on

    carbonization of coal and wood in Graduate

    School of Engineering, Osaka University, in order

    to use both carbonization gas and coal-char or

    charcoalin the following ironmaking processes.

    semi-coal-charor semi-charcoal

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    2.1 Pre-reductionof iron oxide pellets by

    coal carbonization gas

    ( Iron bath smelting reduction process)

    In the first step, three sorts of bituminous

    coal were carbonized under various rising

    temperature conditions (see Figs.1and 2).

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    Carbonization experiment

    Carbonization furnace

    Gas

    chromatograph

    155 I.D.100

    320

    850

    N2inlet

    Thermocouple

    81 I.D.

    Heater

    Coal particles

    280

    Alumina balls

    Ribbon heater

    Water inlet

    (273 K)

    Condenser

    Exhaust

    gas

    Tar filter

    Carbonization conditionsCarrier gas: N2 1.0 L/min (s.t.p.) Heating rate: 200 K/hTC, max: 823 K, 873 K, 973 K, 1073 K, 1273 K

    Experimental apparatusFig. 1

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    Coal Pellets

    Backgrounds (Iron bath smelting

    reduction total process Image )

    Carbonization furnace Pre-reductionfurnace

    Exhaust gas

    Carbonization gas

    Fe

    Smelting furnace

    Coal

    Char

    Fe2O3

    Utilization of V.M. of coal

    in an iron bath smelting

    reduction total process

    Iron bath smelting reduction total process

    Fe3O4, FeO, Fe

    Smelting furnace Smelting furnace

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    Reference

    T. Usui, T. Yokoyama, T. Nakahashi and Z. Morita, 1993 Ironmaking ConferenceProceedings (Iron and Steel Society), pp. 389-398.

    Application

    Fig. Mole fraction of carbonization gas before

    reduction as a function of carbonization time.

    Tc, max=1073 K

    Carbonization conditions

    Coal: Muswellbrook coalCarrier gas: N2 1.0 L/min (s.t.p.)Maximum carbonization temperature

    (TC, max): 1073 K

    Heating rate: 200 K/h

    Utilization of volatilematter (V.M.) of coal

    Pre-reduction of iron oxide inan iron bath smelting reduction

    total process

    Backgrounds(Pre-reduction of iron

    oxide with carbonization gas of coal)

    Fig. 3

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    Fig. Variations of final fractional reductionsFandFH with reduction temperature TR.

    Reduction temperature

    1173, 1273 K

    Reduction of iron oxide by

    hydrogen in hydrocarbons

    800 1000 1200

    0

    0.2

    0.4

    Reduction temperatureTR(K)

    Fra

    ctinalreduction

    F,

    FH

    ()

    Muswellbrook coal

    Fractional reduction

    (gravimetric method)

    Fractional reduction due to H

    Tar filter: room temperature

    800 1000 1200

    0

    0.2

    0.4

    Reduction temperature TR(K)

    Frac

    tinalreduction

    F,

    FH

    ()

    Newlands coal

    Fractional reduction (gravimetric method)

    Fractional reduction due to H

    Tar filter: room temperature

    Final fractional reductions Fand FH

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    2.2Carbon composite iron oxide pellets

    using semi-coal-char

    It was found in the above-mentioned carbonizationexperiments under rising temperature conditions that when the

    carbonization was interrupted halfway, the volatile matter

    release was interrupted corresponding to the interrupted

    carbonizing temperature, i.e., the maximum carbonizing

    temperature Tc,max ; and that when the carbonization was

    started again the release of the residual volatile matter began

    at the very interrupted carbonizing temperatureTc,max and the

    same total amount of carbonization gas was released as the

    one without interruption.

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    From these findings we proposed the novel

    carbon composite pellets, in which the semi-coal-char

    including the residual volatile matter was used ascarbonaceous material. When we use fully

    carbonized coal char as carbonaceous material, the

    reduction of carbon composite pellets starts at first assolid / solid reaction under rising temperature

    condition like in a blast furnace. Whereas, when we

    use the semi-coal-char as carbonaceous material,the reduction of carbon composite pellets starts from

    the beginning as gas / solid reaction just after the

    reduction temperature arrives at Tc,max .

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    Therefore, the first merit is the decrease instarting temperature of reaction and the second

    one is the rate enhancement of reduction reaction

    by the residual volatile matter (see Fig.5). The

    decrease in starting temperature of reduction

    reaction of iron ore in a blast furnace leads to thedecrease in consumption of reducing agent.

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    Heating pattern

    0 120 240 360

    400

    600

    800

    1000

    1200

    1400

    Carbonization time (min)

    Carb

    onizationtemperatu

    re(K)

    Tc,max = 1273 K

    873 K

    1073 K

    973 K

    823 K

    TC, max = 1273 K

    Carbonization time t (min)

    Carboniz

    ationtemperatureT

    C

    (K)

    In order to obtain the semi-coal-char, Newcastle blend coal wascarbonized from room temperature to TC, max= 823, 873, 973, 1073and 1273 Kat200 K/h, and kept at TC, maxuntil arrival time of 6 h.

    Fig. 2

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    0

    0.05

    0.1

    0.15

    0.2

    0.25

    0.3

    823 873 973 1073 1273

    Totalgasvolume

    [m3(s.

    t.p.)]

    Maximum carbonization temperature TC, max (K)

    H2

    CO

    CO2

    CH4

    C2H4

    C2H6

    C3H8

    Carbonization experiment (total gas volume)

    Total gas volume ( Newcastle blend coal )H2gas releases more than any other gasesat TC, max= 873, 973, 1073, 1273 K.The higher TC, maxis, the more H2gas releases.Char contained much hydrogen at TC, max = 823 K.

    Fig. 4

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    F.C. V.M. Ash S C H O N

    72.2 15.9 11.9 0.53 75.3 2.87 7.31 2.06

    TC, max823 KTable. Analysis of Char carbonized at Tc, max = 823 K

    (mass%)

    TC, max1073 K

    TC, max1273 K

    F.C. V.M. Ash S C H O N

    82.7 4.43 12.9 0.42 81.5 1.54 1.91 1.74

    Table. Analysis of Char carbonized at Tc, max = 1073 K(mass%)

    F.C. V.M. Ash S C H O N

    83.2 2.51 14.3 0.52 81.7 0.90 1.34 1.27

    Table. Analysis of Char carbonized at Tc, max = 1273 K

    (mass%)

    Analysis of the char obtained by carbonization

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    Reduction of carbon composite iron oxide pellets

    Ar gas inlet

    Alumina

    crucible

    Gas outlet

    Pellets

    Thermo-

    couple

    Preparation of carbon compositeiron oxide pelletsChar : Fe2O3 = 1 : 4BinderBentonite (1 mass added)Particle size: under 4563 mPellets size: about 15 mmKeeping at 378 K for 24 hto remove waterReduction experiment and analysisReduction conditionsAr or N2gas atmosphereHeating rate: 0 or 3K/minAnalysisGas chromatography, SEM, XRD

    Electric

    furnace

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    Relation between fractional reduction and reduction time of

    carbon composite pellets at 1073 K in N2atmosphere

    Semi-coal-char

    Reduction behavior of carbon composite pellet atTC, max= 823Kwas higher thanany other pellets by about 10 .When TC, maxwas lower, namelythe pellet had more residual

    V.M., the reduction of carboncomposite pellet was muchenhanced.

    TC, max = 823 K

    TC, max = 1073 K

    TC, max = 1273 K

    Char

    Fr

    actionalreductionF

    (-)

    Reduction time t (min)

    0 10 20 30 40 50 600

    5

    10

    15

    20

    25

    10TR= 1073 K

    ( Fig. 5 )

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    TC, max = 823 K

    TC, max = 1073 KTC, max = 1273 K

    Semi-coal-char

    Fractionalreducti

    onF(-)

    Reduction time t (min)0 20 40 60 80

    0

    20

    40

    60

    80

    100

    Fig. 5. Reduction curves for semi-coal-char

    composite pellets ( TR= 1173 K ).

    TR= 1173 K

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    0 10 20 30 40 50 600

    20

    40

    60

    80

    100

    Char (TC, max = 823 K) (V.M. 15.9 %)

    Coke (V.M. 0.6 %)Graphite (Purity 98 %)

    Reduction time t [min]

    Fractionalre

    ductionF

    [%]

    Early stageChar Coke, GraphiteLater stageChar, Coke Graphite

    Reduction rate

    Effect of V.M. and crystallization Reduction rate

    Influence of several kinds of carbon materials

    Reduction at 1273 K in

    N2gas atmosphere

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    2.3Carbon composite iron oxide

    pellets using semi-charcoal

    The above-mentioned carbonization

    experiments on coal were expanded into

    those on charcoal; semi-charcoal including

    the residual volatile matter was used as

    carbonaceous material in the novel carbon

    composite pellets.

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    The rate enhancement effect of reduction

    for semi-charcoal composite pellets isstronger than that for semi-coal-charcomposite pellets, because the gasification

    rate of semi-charcoal is higher than that of

    semi-coal-char. This is caused by the

    following reasons: amorphous nature of

    semi-charcoal is stronger than that of semi-

    coal-char (see Fig.6) and the activationenergyof semi-charcoal is lower than that of

    semi-coal-char (see Table 1).

    R d i f i id b d bi

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    A lot of steel engineers

    researched various meansto decrease coke in a blast

    furnace in order to reduce

    CO2emission.

    Carbon neutral(No CO2emission)Rich resources

    Biomass

    Reduction of iron oxide by woody biomass

    Woody biomass

    Japanese

    cedar

    Application(Carbonaceous material)

    Injection into a blast furnace

    Preparation of carbon com-

    posite iron ore agglomerateJapanese

    cypressBiomass

    waste

    http://www.dex.ne.jp/mantan/search/std2_search_preview.jhtml?start=15&lastServiceTime=1113451861319&number=13
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    Sample

    F.C. V.M. Ash T.S T.C H O N

    8.12 90.8 1.05 0.014 50.7 6.16 41.1 1.01

    Carbonaceous materialJapanese cypressTable. Analysis of Japanese cypress (mass%)

    Iron oxide: Reagent grade hematite (Fe2O3)

    (95 mass%, Wako Pure Chemical Industries Ltd.)

    Sample for carbonization experiment

    Sample for reduction experiment of iron oxide pellets

    SiO2 Al2O3 Fe2O3 CaO MgO K2O Na2O

    58.79 14.27 2.99 0.70 1.28 0.70 3.42

    Table. Chemical analysis of Bentonite (mass%)

    BinderBentonite(1 mass% added)

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    Heating pattern of carbonization of Japanese cypress

    Carbonization time t (min)

    In order to obtain the semi-charcoal, Japanese cypress was

    carbonized from room temperature to TC, max= 823, 1073 and

    1273 K at 200 K/h, and kept at TC, maxuntil arrival time of 6 h.

    Carbonizationtem

    peratureTC(K

    )

    823 K

    0 120 240 360

    800

    1000

    1200

    600

    400

    1400

    1073 K

    TC, max = 1273 K

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    Total gas volume generated by carbonization

    Totalg

    asvolume[m3(s.t.p.)]

    Maximum carbonization temperature Tc, max (K)

    H2

    CO

    CO2

    CH4

    C2H4

    C2H6

    C3H8

    Total gas volume generated by carbonizationH2 gas was released more than any other gases at TC, max = 1273 K,but was released less than CO, CO2and CH4gases at TC, max= 823 K.

    The higher TC, maxwas, the more H2gas was released.Semi-charcoal retained much V.M., namely H2gas, at Tc, max = 823 K.

    823 1073 1273

    0.01

    0.02

    0.03

    0.04

    0

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    Table Analysis of semi-charcoal obtained by carbonization of Japanese cypress.

    Tc, max =

    823 KTc, max =

    1073 K

    Volatile matter

    (V.M.)Hydrogen

    Tc, max =

    1273 K

    (mass%)

    Analysis of the semi-charcoal obtained by carbonization

    It was confirmed that the semi-charcoal of TC, max= 823 K

    retained much V.M., namely hydrogen.

    0.04 0.824.810.5692.61.167.0091.80TC,max= 1273 K

    0.03 0.555.891.3391.21.019.6489.35TC,max= 1073 K

    0.01 0.609.892.9385.80.7618.6580.60TC,max= 823 KSemi-

    charcoal

    S NOHCAshV.M.F.C.Component

    Coke 87.1 0.97 11.97 84.6 0.26 1.35 1.220. 60

    0.01 41.11.016.1650.71.0890.88.12Japanesecypress

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    Semi-charcoal has many micro pores with the size of about 10 m.

    Semi-charcoal obtained by carbonization

    Tc, max = 823 K Tc, max = 1073 KT

    c, max = 1273 K

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    Semi-charcoalTc, max = 823, 1073, 1273 KCO2 1.0 L/min (s.t.p.)TG= 1073, 1173, 1273 K

    Experimental conditions

    Reaction rate

    Weight loss measurement

    6375 mBinder 2 mass% Pellets

    CO2N2

    TG

    R.T.

    600 [K/h]

    Fig. Schematic of reduction furnace.

    Gasification of semi-charcoal

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    TG= 1173 K TG= 1273 K

    Tc, max is low Reaction rate is high

    Gasification of semi-charcoal

    Fig. Weight loss curves of semi-charcoals

    obtained by carbonization at Tc, max = 823,

    1073, 1273 K and coke at TG = 1173 K in

    CO2 gas atmosphere.

    0 20 60Reaction time [min]

    We

    ightloss[%]

    0

    -20

    -60

    40

    CokeSemi-charcoal c max= 1273 K c max= 1073 K c max= 823 K

    -40

    -80

    -100

    Fig. Weight loss curves of semi-charcoals

    obtained by carbonization at Tc, max = 823,

    1073, 1273 K and coke at TG = 1273 K in

    CO2 gas atmosphere.

    0 20 60Reaction time [min]

    We

    ightloss[%]

    0

    -20

    -60

    40

    -40

    -80

    -100

    Gasification of semi charcoal

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    Arrhenius plots of reaction rate of gasification

    Tc, max

    E[kJ/mol]

    823 K1073 K 1273 K Coke

    138 162 219139

    Gradient Activation energy

    Tc, max is low

    Activation energy is low

    Gasification of semi-charcoal

    -100.7 0.8 1.0

    1/TG [K-1]

    Reactionrate:ln

    kC,

    CO2

    [1/min]

    -6

    0.9

    -4

    -2

    [10-3]

    TG[K]

    11001200 100013001400

    -8

    Semi-charcoal

    Tc,max= 823 K Tc,max= 1073 K Tc,max= 1273 K Coke

    Fig. Reaction rate per unit mass at TG= 1073,

    1173, 1273 K in CO2atmosphere.

    This result of activation energy might

    be influenced by specific surface area

    and crystallizationof these samples.

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    Carbonaceous material

    Activation energy

    (kJ/mol)

    Graphite

    Bintyo char

    Bamboo char

    Coke

    Glassy carbon

    Activated carbon

    Semi-charcoalat Tc,max= 823 K

    Semi-charcoalat Tc,max

    = 1073 K

    Semi-charcoal at Tc,max= 1273 K

    Semi-coal-char at Tc,max= 1073 K

    Coke

    217(29)

    182(29)

    181(29)

    200(29)

    211(29)

    149(29)

    138 *

    139*

    162*

    174*

    219*

    Table 1. Comparison of activation energies for

    variouscarbonaceous materials.(27)

    * Present work

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    2(Cu-K) /degree

    Diffraction

    intensity/arb.un

    it

    (b) Semi-charcoala) Semi-coal-char

    20 30 40 50 60 7020 30 40 50 60 70

    2(Cu-K) /degree

    Diffractionintensity/arb.unit : Carbon

    TC, max = 1273 K

    1073 K

    823 K

    TC, max = 1273 K

    1073 K

    973 K

    : Carbon: Unknown

    The crystal structures of semi-coal-char and semi-charcoal

    Semi-charcoalSemi-coal-char

    Amorphous

    structure

    Crystalline

    structureFig. 6

    R d ti f i h l it i id ll t

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    Reduction of semi-charcoal composite iron oxide pellets

    Preparation of semi-charcoal composite iron oxide pelletsSemi-charcoal : Fe2O3= 1 : 4Binder Bentonite (1 mass%)Particle size: 2335, 6375, 105150 mPellets size: about 15 mmKeeping at 378 K for 24 h to remove water

    Reduction experiment and analysis

    Reduction conditionsN2gas atmosphereAnalysisGas chromatography

    Reduction behavior of iron oxide in semi-charcoal composite

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    TR= 1073 K

    Fig. Reduction curves of semi-charcoal

    composite pellets using semi-charcoal at

    Tc,max= 823, 1073, 1273 K and coke at

    TR = 1073 K in N2gas atmosphere.

    Fractional reduction

    Reduction time [min]

    FractionalreductionF

    [%]

    0 30 60

    15

    30

    Tc,max= 823 K

    Tc,max= 1073 K

    Tc,max= 1273 K

    0

    Particle size: 6375 m

    Reduction behaviorF of semi-charcoal compositepellet at TC, max= 823Kwas 19 %

    for 60 minand higher than any

    other pellets by 78 %.When TC, maxwas lower, namelythe pellet had more residual

    V.M., the reduction of semi-

    charcoal composite pellet was

    much enhanced.

    Reduction behavior of iron oxide in semi-charcoal composite

    pellets at TR= 1073 K in the N2gas atmosphere

    Coke

    823 K1073 K

    1273 K

    Tc,max

    Coke

    Reduction behavior of iron oxide in semi-charcoal composite

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    Fig. Reduction curves of semi-charcoal

    composite pellets using semi-charcoal at

    Tc,max= 823, 1073, 1273 K and coke at

    TR =1173 K in N2gas atmosphere.

    TR= 1173 K

    Reduction time [min]

    Fractionalredu

    ctionF

    [%]

    0 30 60

    25

    50

    0

    Fractional reduction

    Particle size: 6375 m

    Reduction behaviorF of semi-charcoal compositepellet at TC, max= 823Kwas 40 %

    for 60 minand higher than any

    other pellets.When TC, maxwas lower, namelythe pellet had more residual

    V.M., the reduction of semi-

    charcoal composite pellet was

    much enhanced.

    TC,max= 823 K

    TC,max= 1073 K

    TC,max= 1273 K

    Coke

    823 K1073 K

    1273 K

    T

    c,max

    Coke

    Reduction behavior of iron oxide in semi-charcoal composite

    pellet at TR= 1173 K in N2gas atmosphere

    Reduction behavior of iron oxide in semi-charcoal composite

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    TR= 1273 K

    Fig. Reduction curves of semi-charcoal

    composite pellets using semi-charcoal at

    Tc,max= 823, 1073, 1273 K and coke at

    TR = 1273 K in N2gas atmosphere.

    Reduction time [min]

    Fractionalredu

    ctionF

    [%]

    Tc,max= 823 K

    Tc,max= 1073 K

    Tc,max= 1273 K

    0 30 600

    50

    100

    Fractional reduction

    Reduction behaviorF of semi-charcoal compositepellets at TC, max= 823, 1073 and

    1273 K were over 90 % for 60 min

    and indicated the same behaviorat TR= 1273 K.These reducibility of semi-charcoalcomposite pellets were high and

    were not dependent on residual

    V.M. at TR= 1273 K.

    Particle size: 6375 m

    Coke

    823 K1073 K

    1273 K

    Tc,max

    Coke

    Reduction behavior of iron oxide in semi-charcoal composite

    pellets at TR= 1273 K in N2gas atmosphere

    The influence of crystallinity of semi-charcoal on reduction of

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    Reduction time [min]

    FractionalreductionF

    [%]

    823

    1073

    1273

    CharCharcoal

    0 10 20 30 40 50 600

    20

    40

    60

    80

    100

    Tc,max (K)

    Fig. Reduction curves of carbon composite pellets

    using semi-charcoal and semi-coal-char at

    Tc,max = 823, 1073, 1273 K with time at TR =

    1273 K in N2gas atmosphere.

    Semi-charcoal composite pellet

    Semi-coal-char composite pellet

    The influence of crystallinity of semi-charcoal on reduction of

    iron oxide in semi-charcoal composite pellet at TR= 1273 K

    Fractional reduction

    Reduction rateReduction rate of semi-charcoalcomposite pellets are higher

    than that of semi-coal-char

    composite pellets.

    Semi-charcoal Semi-coal-char

    Reducibility

    Amorphous

    structure

    Crystalline

    structure

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    Total gas volume generated by carbonization

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    Total gas volume generated by carbonization

    Totalgasvolume[m3(s.t.p.)]

    Maximum carbonization temperature TC, max (K)

    H2

    CO

    CO2

    CH4

    C2H4

    C2H6

    C3H8

    Total gas volume generated by carbonizationH2 gas was released more than any other gases at TC, max = 1273 K,but was released less than CO, CO2 and CH4gases at TC, max= 823 K.

    The higher TC, maxwas, the more H2gas was released.Semi-charcoal retained much V.M., namely H2gas, at TC, max = 823 K.

    823 1073 1273

    0.01

    0.02

    0.03

    0.04

    0

    Japanese

    cypress

    O/C H/C mole ratio (Van Krevelen diagram)

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    moleratio

    mole ratio

    demethanation

    Dehydration, decarboxylation

    Calorific power low Semi-coal-charTC, max = 823 KTC, max = 873 KTC, max = 973 KTC, max = 1073 KTC, max = 1173 KTC, max = 1273 KSemi-charcoal

    TC, max= 823 KTC, max= 1073 KTC, max= 1273 KCoke

    TC, max = 823 K

    873 K

    973 K

    1173 K

    1073 K

    1273 K

    Tc, max = 823 K

    1073 K

    1273 K

    Semi-coal-char

    Coke

    Semi-charcoal

    The higher TC, maxwas,the lower O/C and H/C

    values were.

    0 0.05 0.10

    0.2

    0.4

    0.6

    O/C, H/C mole ratio (Van Krevelen diagram)

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    3. OUTLINE OF THE PRESENT STUDY

    From the accumulated date mentioned-above on semi-charcoal, in the first step, the

    first author is going to study the optimum

    conditions for the use of both semi-charcoal

    and carbonization gas (biogas) released at

    carbonization in ironmaking such as carboncomposite agglomerates by data analyses in

    Univ. Federal de Ouro Preto with Prof. Assis;

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    we can expect that the lower the

    carbonizing temperature Tc,max is, the

    better the reactivity of semi-charcoal

    becomes but the less the amount of

    carbonization gas releases in the

    carbonizing step.

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    As the carbonizing temperature Tc,max

    decreases, the activation energy of semi-

    charcoal decreases gradually, while the

    amount of carbonization gas release in the

    carbonizing step, namely, the amount of

    biogas, decreases rather drastically. There

    will be some optimum carbonizing

    temperature Tc,max in an actual process forboth preparing reactive semi-charcoal and

    producing much biogas.

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    In the second step, the experimental

    program will be proposed to search theoptimum conditions for the use of both

    semi-charcoal and carbonization gas

    released in the carbonizing step. Of

    course, the experimental program has

    to be expanded from wood to variouskinds of biomass.

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    In addition, literatures on various

    kinds of biomass will be collected andanalyzed. Application of semi-

    charcoal to another manufacturing

    industry will also be searched.

    In the third step, the experimental

    apparatus will be designed for thenext year research period.

    CONCLUDING REMARKS

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    CONCLUDING REMARKS

    From the previous study on pre-reduction of

    iron oxide pellets by coal carbonization gas, we

    proposed a novel carbon composite pellets; semi-coal-char was used as carbonaceous material to

    enhance the rate of reduction and at the same

    time to decrease the starting temperature ofreduction reaction. We expanded these results to

    semi-charcoal.

    The first author is going to study the optimumconditions for the use of both semi-charcoal and

    carbonization gas released at carbonization in

    ironmaking by data analyses in Univ. Federal de

    Ouro Preto with Prof. Assis.

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    Muito obrigado.

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    O/C, H/C mole ratio (Van Krevelen diagram)

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    moleratio

    mole ratio

    demethanation

    Dehydration, decarboxylation

    Calorific power low Semi-coal-charTC, max = 823 KTC, max = 873 KTC, max = 973 KTC, max = 1073 KTC, max = 1173 KTC, max = 1273 KSemi-charcoal

    TC, max= 823 KTC, max= 1073 KTC, max= 1273 KCoke

    TC, max = 823 K

    873 K

    973 K

    1173 K

    1073 K

    1273 K

    Tc, max = 823 K

    1073 K

    1273 K

    Semi-coal-char

    Coke

    Semi-charcoal

    The higher TC, maxwas,the lower O/C and H/C

    values were.

    0 0.05 0.10

    0.2

    0.4

    0.6

    / , / ( g )