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j m a t e r r e s t e c h n o l . 2 0 1 3; 2(4) :323–331 Available online at www.sciencedirect.com www.jmrt.com.br Original Article Model predictions of PCDD and PCDF emissions on the iron ore sintering process based on alternative gaseous fuels Jose Adilson de Castro a,, Jorge Luiz Pereira a , Vagner Silva Guilherme a , Elisa Pinto da Rocha a , Alexandre Bôscaro Franc ¸a b a Post-Graduation Program of Metallurgical Engineering, Universidade Federal Fluminense, Volta Redonda, RJ, Brazil b Universidade Federal de São João Del-Rei, Ouro Branco, MG, Brazil a r t i c l e i n f o Article history: Received 29 March 2013 Accepted 12 June 2013 Available online 7 November 2013 Keywords: Multiphase flow Sintering PCDD/F a b s t r a c t The technology of fuel gas utilization on the iron ore sintering process has been proposed as an alternative for reducing the environmental load and improvements on the sinter qual- ity have been obtained with additional decrease on the return of fines (<5 mm). This paper deals with the numerical simulation of this innovative technology in order to evaluate the emissions of poly chlorinated di-benzene dioxin (PCDD) and Poly Chlorinated di-benzene furan (PCDF). The methodology is to partially replace solid fuel (coke breeze) by steelworks gaseous fuels; coke oven gas (COG), blast furnace gas (BFG) and mixture of these gases. A multiphase mathematical model based on transport equations of momentum, energy and chemical species coupled with chemical reaction rates and phase transformations is pro- posed to analyze the inner process parameters and the rates of PCDD and PCDF formations. A base case representing the actual industrial operation was used to validate the model and afterwards used as reference to predict four cases of fuel gas utilization: (a) 10% of the wind boxes inflow from N01 to N12 wind boxes with COG, (b) same condition with BFG, (c) same condition with 50% COG and 50% BFG and (d) mixture of 25% COG and 75% BFG. The model predictions indicated that for all cases, except only BFG, the sintering zone is enlarged and the solid fuel consumption is decreased. In order to maximize the steelworks gas utilization it is recommended the use of mixture of COG and BFG with optimum inner temperature dis- tribution. It was found out that for all cases of gas utilization the PCDD and PCDF emissions could be decreased due to enlargement of the high temperature zone on the sintering bed and hence increasing the residence time of the reacting gas within the high temperature zone. © 2013 Brazilian Metallurgical, Materials and Mining Association. Published by Elsevier Editora Ltda. 1. Introduction The iron ore sintering process in the integrated steelworks is a well established technology and has been responsible to provide high quality of agglomerate raw materials for the blast Corresponding author. E-mail: [email protected] (J.A. de Castro). furnace. However, further improvements regarding energy efficiency, flexibility of raw materials and environmental load have continuously been demanded. The process is complex and involves various physical and chemical phenomena such as heat, mass and momen- tum transfer coupled with chemical reactions [1–4]. These 2238-7854 © 2013 Brazilian Metallurgical, Materials and Mining Association. Published by Elsevier Editora Ltda. http://dx.doi.org/10.1016/j.jmrt.2013.06.002 Este é um artigo Open Access sob a licença de CC BY-NC-ND Este é um artigo Open Access sob a licença de CC BY-NC-ND
Transcript
Page 1: Model predictions of PCDD and PCDF emissions on the iron ore … · 2017. 2. 12. · (PCDF). The methodology is to partially replace solid fuel (coke breeze) by steelworks gaseous

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j m a t e r r e s t e c h n o l . 2 0 1 3;2(4):323–331

Available online at www.sciencedirect.com

www. jmrt .com.br

riginal Article

odel predictions of PCDD and PCDF emissions on the ironre sintering process based on alternative gaseous fuels

ose Adilson de Castroa,∗, Jorge Luiz Pereiraa, Vagner Silva Guilhermea,lisa Pinto da Rochaa, Alexandre Bôscaro Francab

Post-Graduation Program of Metallurgical Engineering, Universidade Federal Fluminense, Volta Redonda, RJ, BrazilUniversidade Federal de São João Del-Rei, Ouro Branco, MG, Brazil

r t i c l e i n f o

rticle history:

eceived 29 March 2013

ccepted 12 June 2013

vailable online 7 November 2013

eywords:

ultiphase flow

intering

CDD/F

a b s t r a c t

The technology of fuel gas utilization on the iron ore sintering process has been proposed as

an alternative for reducing the environmental load and improvements on the sinter qual-

ity have been obtained with additional decrease on the return of fines (<5 mm). This paper

deals with the numerical simulation of this innovative technology in order to evaluate the

emissions of poly chlorinated di-benzene dioxin (PCDD) and Poly Chlorinated di-benzene

furan (PCDF). The methodology is to partially replace solid fuel (coke breeze) by steelworks

gaseous fuels; coke oven gas (COG), blast furnace gas (BFG) and mixture of these gases. A

multiphase mathematical model based on transport equations of momentum, energy and

chemical species coupled with chemical reaction rates and phase transformations is pro-

posed to analyze the inner process parameters and the rates of PCDD and PCDF formations.

A base case representing the actual industrial operation was used to validate the model and

afterwards used as reference to predict four cases of fuel gas utilization: (a) 10% of the wind

boxes inflow from N01 to N12 wind boxes with COG, (b) same condition with BFG, (c) same

condition with 50% COG and 50% BFG and (d) mixture of 25% COG and 75% BFG. The model

predictions indicated that for all cases, except only BFG, the sintering zone is enlarged and

the solid fuel consumption is decreased. In order to maximize the steelworks gas utilization

it is recommended the use of mixture of COG and BFG with optimum inner temperature dis-

tribution. It was found out that for all cases of gas utilization the PCDD and PCDF emissions

could be decreased due to enlargement of the high temperature zone on the sintering bed

and hence increasing the residence time of the reacting gas within the high temperature

zone.Meta

have continuously been demanded.

© 2013 Brazilian

. Introduction

he iron ore sintering process in the integrated steelworkss a well established technology and has been responsible torovide high quality of agglomerate raw materials for the blast

∗ Corresponding author.E-mail: [email protected] (J.A. de Castro).

238-7854 © 2013 Brazilian Metallurgical, Materials and Mining Association. Puhttp://dx.doi.org/10.1016ste é um artigo Open Access sob a licença de CC BY-NC-ND

llurgical, Materials and Mining Association. Published by Elsevier

Editora Ltda.

furnace. However, further improvements regarding energyefficiency, flexibility of raw materials and environmental load

Este é um artigo Open Access sob a licença de CC BY-NC-ND

The process is complex and involves various physicaland chemical phenomena such as heat, mass and momen-tum transfer coupled with chemical reactions [1–4]. These

blished by Elsevier Editora Ltda.

/j.jmrt.2013.06.002

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324 j m a t e r r e s t e c h n o l . 2 0 1 3;2(4):323–331

Raw materials

Sinterreturned

Charging system

Bed layer

Ignition furnace

Gas cleaning system

Exhaust gas

–5mm

Sinter coolingsystem

+5mm

Blast furnace sinter

Iron oreblend

Additivesslagbond Mixer

micropelletizer

Fig. 1 – The sintering plant facilities for integrated steelworks.

phenomena take place simultaneously increasing consider-ably the complexity of process analysis. The raw materialsused in the iron ore sintering process are obtained from sev-eral sources, like iron ore (mining sinter feed), dust recyclingwithin the steelworks and addition of slag agents for blast fur-nace and enhance the sinter product quality, namely reactivityand mechanical strength, which plays crucial role on the blastfurnace performance and reducing agent consumption.

In the conventional operation, the combustion of the solidfuels (coke breeze or anthracite) begins at the top layers, andas it moves, a relative narrow band of ignition zone movesdownward through the bed, that can be strongly affectedby the quality of the raw materials [5–9]. Several chemicalreactions and phase transformations are affected not onlyby the heat front modifications but also due to changes inlocal gas composition and initial melting temperature of themixture of raw materials. When local temperature and com-position of the solid is reached, the phase transformations aredriven by heat supply and diffusion that takes place withinthe sinter bed where the mechanism of liquid formationplaying the major role. The materials partially melt downwhen the local temperature reaches the melting tempera-ture and as it moves, the contact with cold gas promotes there-solidification and thus, the particle agglomeration formsa continuous and porous sinter cake. The final sinter cakeproperties are strongly dependent upon the thermal cycle, ini-tial raw material composition and thermophysical properties.Fig. 1 shows a schematic view of the sintering facilities andperipheral system for gas treatment and sinter cooling andclassification.

In this paper, the sintering process is analyzed, when fuelgases such as natural gas (NG), coke oven gas (COG) and blastfurnace gas (BFG) are sucked through the sinter bed. It is

expected that the fuel gas reaching the thermal front combustearlier leading to the result of enlargement of the sinteringzone, which in turn, can increase the liquid formed (mushy)

and residence time of the materials within the sintering tem-perature improving the amount of calcium ferrite and bondingphases. Several attempts have been made aiming at predictingthe final properties of the sinter product.

One of the most important parameters is the size dis-tribution which influences strongly the sinter performancewithin the blast furnace. Previous models addressed the sin-tering phenomena [1–3,10–15]. Kasai et al. [16] investigatedthe influence of sinter structure on the macroscopic sinterproperties. A detailed explanation of the sintering mecha-nism and particle interaction was provided in order to clarifythe bonding forces responsible for the sinter structure andstrength. In the present days, the reduction of CO2 emissionshas become an urgent issue in the steel industry as counter-measure for greenhouse emissions [17,18]. It is estimated thatnearly 60% of the steel industry emissions are attributed to thepig iron production unit operations, which includes sinteringand blast furnace processes, and only the sintering processrepresents around 20% of this amount [18]. Therefore, sinter-ing and blast furnace processes offer opportunities to decreasethe CO2 emissions in the whole steelmaking since smalldecrease in coke breeze consumption and bonding agent usedin iron ore sintering process could decisively contribute todecrease the environmental load of the steelmaking industry.Therefore, alternative sources of energy with lower environ-mental impact or replacement of the coke breeze by in-housegaseous fuel are attractive technologies and could contributeto enhance the iron ore sintering process in the integratedsteelworks [11,13,14,17].

The concept of gaseous injection into the sinter bed hasbeen successfully applied and enhancement of the sinterproperties related to reducibility and strength have beenobserved [11,17], in addition to drastically decrease the

returned fines (<5 mm). In this perspective, the present workaims to apply a comprehensive multiphase multicomponentmathematical model to analyze the effect of gaseous fuels
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j m a t e r r e s t e c h n o l . 2 0 1 3;2(4):323–331 325

Gas flowa

c

b

ore

ore

46.5 micron

Before sintering(pseudo particle)

Dendrites structures of liquidsolidified interface ore liquid(SEM)

Gas flow

After sintering (liquid phases solidified)

and

stto[

2

Tpptfatiiqmmftii

fsTnctto

Fig. 2 – Intra bed phenomena

uch as natural gas, coke oven and blast furnace gases throughhe sinter bed of an industrial sintering machine and quan-ify the impact of this technology on the sintering processf iron ore with regard to the PCDD and PCDF emissions

18].

. Methods

his paper proposes a model to evaluate the coupledhenomena of PCDD and PCDF formation in the sinteringrocess of an industrial strand machine based on the mul-iphase and multicomponent concept [1–15]. The model isormulated using transport equations of mass, momentumnd energy for gas, solid and liquid phases taking into accounthe local phenomena of porous sinter formation, as schemat-cally shown in Fig. 2(a) and (b), while Fig. 2(c) shows an SEMmage of dendrites structure. This model considers the initialuasi-particle already formed and as the reactions take place,ultiphase phenomena occur. Therefore, a model based onultiphase transport phenomena is expected to be suitable

or modeling the mass, momentum and energy transfer withinhe sintering bed. The chemical species are individually takennto account by solving the transport equation of each chem-cal species of the gas and solid phases.

The solid phase includes the mixture of iron ore sintereed, fine sinter (returned fine sinter), coke breeze (or otherolid fuel), scales (fines from steel plant), fluxes and limestone.he liquid phase is composed of melted and formed compo-ents in the liquid phase [3–6,18–23]. The re-solidified phase

omprises the liquids re-solidified and phases formed duringhe re-solidification process. Eqs. (1)–(4) describe the conserva-ion equations for momentum, energy and chemical speciesf each phase considered in the model [7–15,19,20].

final sinter microstructure.

Momentum:

∂(�iεiui,j)

∂t+ ∂(�iεiui,kui,j)

∂xk= ∂

∂xk

(�i

∂ui,j

∂xk

)− ∂Pi

∂xj− Fi−l

j(1)

Continuity:

∂(�i�i)∂t

+ ∂(�i�iui,k)∂xk

=Nreacts∑

m=1

Mnrm (2)

Enthalpy balance:

∂(�iεiHi)∂t

+ ∂(�iεiui,kHi)∂xk

= ∂

∂xk

(ki

Cpi

∂Hi

∂xk

)+ Ei−l +

Nreacts∑m=1

�Hmrm (3)

The chemical species are individually considered within thegas, or components of the solid or liquid phases, as presentedin Eq. (4).

∂(�iεi�n)∂t

+ ∂(�iεiui,k�n)∂xk

= ∂

∂xk

(Deff

n∂�n

∂xk

)+

Nreacts∑m=1

Mnrm (4)

The indexes i and l represent the phases, j and k are the indexesfor coordinates, component direction n is chemical speciesand m the indicator of the reactions, M is the molecular weightof the chemical species, P is phase pressure, F is componentof momentum interactions among the phases and r is the rate

of chemical reactions. �, ε, Cp, k and H are phase density,volume fractions, heat capacity, heat conductivity and heatgenerated/consumption due to chemical reactions (endother-mic or exothermic), respectively.
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326 j m a t e r r e s t e c h n o l . 2 0 1 3;2(4):323–331

Table 1 – Phases and chemical species considered in the model of the sintering process.

Equations of the gas phaseGas Momentum u1,g, u2,g, u3,g, Pg, εg

Energy hg

Chemical species N2, O2, CO,CO2, H2O, H2, SiO, SO2, CH4, C2H6, C3H8, C4H10

Equations of the solid phaseSolid Momentum u1,s, u2,s, u3,s, Ps, εs

Energy hs

Chemicalspecies

Coke breeze C, Volatiles, H2O, Al2O3, SiO2, MnO, MgO, CaO, FeS, P2O5, K2O, Na2O, S2

Iron ore (sinterfeed) Fe2O3, Fe3O4, FeO, Fe, H2O, Al2O3, SiO2, MnO, MgO, CaO, FeS, P2O5,K2O, Na2O

Return sinter (bed) Fe2O3, Fe3O4, FeO, Fe, H2O, Al2O3, SiO2, MnO, MgO, CaO, FeS, P2O5,K2O, Na2O

Solidified materials Fe2O3, Fe3O4, FeO, Fe, H2O, Al2O3, SiO2, MnO, MgO, CaO, FeS, P2O5,K2O, Na2O, Ca2Fe3O5, Al2MgO4

Fluxingagent CaO, H2O, Al2O3, SiO2, MnO, MgO, TiO2

Sintercake Fe2O3, Fe3O4, FeO, Fe, H2O, Al2O3, SiO2, MnO, MgO, CaO, FeS, P2O5,K2O, Na2O, Ca2Fe3O5, Al2MgO4

FeK2

Liquid Chemical species Intrabed liquid

The quantity Ei−l is the heat transfer among the phases andaccounts for convective and radiation intra bed heat trans-fer, since conductive heat transfer is include in Eq. (3). Thegas–solids momentum interactions are represented by Fi−l.The model equations are completed with suitable correla-tions for the thermophysical properties of the phases, rateequations for the source terms and the initial and boundaryconditions representing the sintering process. The chemicalspecies considered in this model are presented in Table 1.

The source terms are modeled based on semi-empiricalcorrelations taking into account the intra bed phenomena. Themomentum transfer between the solid and gas are modeledbased on the modified Ergun’s equation, which takes intoaccount the local soft-melting behavior of the raw materialswith the volume fraction and effective diameters modified bythe soft-melting data, as follows [1–15,20].

Fsg =

[1.75�g + 150�g

| �Ug − �Us|

(εs

dsϕs

)] (εs

(1 − εs)3dsϕs

)

× | �Ug − �Us|(ug,j − us,j) (5)

The overall heat transfer coefficient between the gas and thepacked bed [20] is given by Eq. (6).

Eg−s = 6εs

dsϕs

kg

(dsϕs)[2 + 0.39(Reg−s)1/2(Prg)1/3](Tg − Ts) (6)

In Eq. (6), the gas–solid interface heat transfer is given bythe product of the overall effective heat transfer coefficient,the interfacial area and the average temperature differencesof the bed and gas phase. The parameters of the sinter bedεs, ds and ϕs are temperature dependent and account for theeffective volume fraction, particle diameter and shape fac-tor, respectively, which strongly affect the momentum andenergy transfer on the soft-melting zone. The solid diameters

and shape factors are given as raw materials properties fromthe harmonic average of the particle size distributions. In thepresent model these parameters are calculated by using soft-melting experimental data for the raw materials used [5,20],

2O3, Fe3O4, FeO, Fe, H2O, Al2O3, SiO2, MnO, MgO, CaO, FeS, P2O5,O, Na2O, Ca2Fe3O5, Al2MgO4

as presented in Eqs. (7)–(9).

εi = 1 − (0.403(100di)0.14)

×(

1 − MAX(

0, MIN(

1,

(Ts − Tim

�Tm

)))Sm

100

)(7)

εs =∑

εi + εl + εls (8)

ds = dinitial + (dfinal − dinitial)(

εl + εls

εs

)3(9)

In Eqs. (5)–(9), the indexes i stands for iron ore sinter feed,retuned sinter, solid fuels, fluxes and mill scales on the sinter-ing mixture charged on the sinter bed, l and ls are the liquidand solid bridges volume fractions formed during sinteringphenomena. The average size of the sintering structure aregiven by Eq. (9) with the parameters dinitial and dfinal represent-ing the average particle size of the quasi particles charged inthe bed and the particle size for complete sintering product[15,20].

In the present model these parameters are given for eachsintering mixture with their own softening-melting data,where the model uses the parameters Tim, �Tm and Sm repre-senting the initial melting temperature, meting temperatureinterval and percentage of volume shrinkage. This parame-ters are obtained from the pressure vs. temperature curveobtained from the softening-melting experiment [5,6]. Themodel formulation is completed assuming initial and bound-ary conditions for momentum, energy and chemical speciesof each phase.

The computational domain is defined by the region of thesinter strand for the industrial scale process simulation andthe equations are solved considering steady state conditions,therefore the first terms on the left of the equations are set

to zero and the initial conditions are regarded as guess val-ues for the numerical iterations. The boundary conditionsis assumed for the solid phase at the charging position ofthe strand the composition, particle diameters and volume
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o l . 2 0 1 3;2(4):323–331 327

fadsa

cidtaatAotuwvi

1400 Measured

Predicted

Measured

Predicted

Measured

Predicted

75 mm

355 mm725 mm

1200

1000

800

600

400

200

00 5 10 15 20 25 30 35 40

Distance along strand direction (m)

Tem

pera

ture

(ºC

)

45 50 55 60 65 70 75 80 85 90

This multiphase multicomponent model is composed of a set

F(

j m a t e r r e s t e c h n

raction distribution and moisture content. The outlet bound-ry condition for the solid phase is assumed to be fullyeveloped flow and no slip condition is assumed at the sintertrand. The other boundaries such as lateral and bed surfacere assumed zero velocity gradient.

For the energy balance equations convective and radiationoefficients are assumed for each of these surfaces. The gasnlet and outlet flow rates are determined by the pressurerop specified for each wind box and it is calculated itera-ively by considering simultaneously the momentum balancend pressure drop of each wind box. The gas inlet temper-ture is specified at the surface of the bed and the outletemperature is calculated by assuming fully developed flow.s for the chemical species of the gas phase, specified valuesn the surface of the sinter bed are assumed and similarly tohe solid phase, the gas velocity is calculated at the outlet bysing fully developed flow conditions at the bottom of the bed

ith the integral mass balance restriction for each wind box

olume. The solution of the differential equations represent-ng the model of this complex process is solved numerically.

0.8

(Base)

(BFG)

(NG)

(COG)

Bed

hei

ght,

mB

ed h

eigh

t, m

Bed

hei

ght,

mB

ed h

eigh

t, m

0.6

0.4

0.2

0

0.8

0.6

0.4

0.2

0

0.8

0.6

0.4

0.2

0

0.8

0.6

0.4

0.2

0

0 5 10 15 20 25 30 35 40Distan

Dista

Distan

Dista

0 5 10 15 20 25 30 35 40

0 5 10 15 20 25 30 35 40

0 5 10 15 20 25 30 35 40

Fig. 4 – Temperature patterns for the cases of alter

0.8

Bed

hei

ght,

mB

ed h

eigh

t, m

0.6

0.2

0.4

0 0 5

(BFG-COG) - Sinter mix

(BFG-COG) - Gas

10 15 20 25 30 35 40Distan

0 5 10 15 20 25 30 35 40

0.8

0.6

0.2

0.4

0

ig. 5 – The gas and solid temperature intra bed distributions fora) PCDD for the base scenario; (b) PCDD for the scenario mixing

Fig. 3 – Model validation using intra bed temperature data.

of partial differential equations that can only be solved bynumerical method due to their nonlinearities on the boundaryconditions and source terms.

1200

1200

1200

1200

1000

1000

1000

800

800

600

600

400

400

200

200

800 600 400200

1000 800 600 400200

45ce, m

nce, m

ce, m

nce, m

50 55 60 65 70 75 80 85

45 50 55 60 65 70 75 80 85

45 50 55 60 65 70 75 80 85

50 55 60 65 70 75 80 85

native gaseous fuels considered in this study.

45 50

1200

12001000 800 600 400

200

1000 800400600

200

ce, m55 60 65 70 75 80 85

45 50 55 60 65 70 75 80 85

the mixing of blast furnace and coke oven gas (BFG-COG).BFG and COG.

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328 j m a t e r r e s t e c h n o l . 2 0 1 3;2(4):323–331

0

A

B

5

10

2 m/s

15

20

Z

Ignition zone

X Y

25

Distance along the strand (m)

30

35

40

45

50

55

60

65

70

75

80

85 5

34

21

00

0.2

0.4

0.6

2.2

PCDD[Ng/Nm3]

2

1.8

1.6

1.4

1.2

1

0.8

0.6

0.4

0.2

0

5

10

15

20

2 m/s

Ignition zone

25

x Y

Z30

Distance along the strand (m)

35

40

45

50

55

60

65

70

75

80

85 54

32

100

0.2

0.4

0.6

2.2

1.6

1.4

1.2

1

0.8

0.6

0.4

0.2

PCDD[Ng/Nm3]

Fig. 6 – Comparison of PCDD emissions for the proposed operation of combining BFG and COG fuels. (a) PCDF concentrationed B

for the base scenario; (b) PCDF concentration for the combin

In this work, the set of differential equations is discretizedby using the finite volume method (FVM) and the resultingset of algebraic equations are solved by the iterative pro-cedure using the line by line method combined with the

tri-diagonal matrix solver algorithm [24]. It has been devel-oped a computational code implemented in Fortran 90/2000language with the executable compatible with all Windowsversions using single or parallel processing using MPI routines.

FG-COG scenario.

A typical run takes about 8 h in an i7 8 cores multiprocesscomputer.

In this paper, the numerical grid used to simulate theindustrial strand of the sinter machine was discretized based

on the Cartesian coordinate system with 22 × 180 × 18 controlvolumes, assumed suitable for the calculations after contin-uous grid refinement to assure solutions independent of thecontrol volume size. The numerical convergence was accepted
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j m a t e r r e s t e c h n o l . 2 0 1 3;2(4):323–331 329

0

5

10

15

20

25

X Y

Z2 m/s

Ignition zone

30

35Distance along the strand (m)

40

45

50

55

60

65

70

75

80

85 54

32

100

0.2

0.4

0.6

0.5

1

1.5

2

2.5

3.5

3

4

4.5

5

PCDF[ng/Nm3]

0

A

B

5

10

15

20

2 m/s

Ignition zone

X Y

Z

25

30

Distance along the strand (m)

40

45

50

55

60

65

70

75

80

85 54

32

10

0.2

0.4

0.6

5

PCDF[ng/Nm3]

4.5

4

3.5

2.5

1.5

3

2

1

0.5

35

the

ftms

3

It

Fig. 7 – Model predictions of PCDF concentrations for

or tolerance of the order of 10−6 for the velocity and tempera-ure fields, meanwhile, for the chemical species the overall

ass balance was accepted less than 1% for all chemicalpecies calculated.

. Results and discussions

n this section the model was applied to simulate the indus-rial operation of the sintering process currently used in the

proposed scenario compared with actual operation.

large facilities. A base case which corresponds to an actual sin-ter plant operation was used to demonstrate the model accu-racy and validate the model predictions. Afterwards, in orderto analyze the effect of the partial substitution of the solid fuelby gaseous fuel on the PCDD and PCDF emissions in the sinter-ing process, three cases were simulated to verify the feasibilityof the new technology proposed based on partial substitution

of the coke breeze by gaseous fuel available at the steelworks.The model validation was carried out by monitoring the sin-ter bed temperature into three distinct heights of the bed by
Page 8: Model predictions of PCDD and PCDF emissions on the iron ore … · 2017. 2. 12. · (PCDF). The methodology is to partially replace solid fuel (coke breeze) by steelworks gaseous

n o l

r

330 j m a t e r r e s t e c h

inserting encapsulated thermocouples and recording the tem-perature measurements along the moving bed. The data usedin these calculations were the averaged values of 1 h of unin-terrupted operation. In this interval, three measurement runswere obtained and the averaged values of the temperatureswere used to compare with the numerical predictions. Fig. 3presents the comparison of temperature predictions by themodel and measured data obtained in the industrial sinteringmachine for the actual operation conditions.

The calculated results were compared with the measureddata obtained by thermocouples inserted within the sinter bedin fixed positions of 75 mm, 355 mm and 725 mm from top ofthe bed and the temperatures were recorded at intervals of10 m along the strand. Excellent concordance of the opera-tional measurements and model predictions were observed,as shown in Fig. 3.

In the scenarios proposed in this study the gaseous fuelsavailable in a steelmaking plant were taken into account. Thescenarios analyzed consider injections from the positions ofthe wind boxes N01 until N15 of a total of 23 wind boxes. Thesepositions were selected to guarantee the gaseous fuel to beconsumed within the bed.

Four fuel injection scenarios were selected: (a) 2% fuel gasthrough the wind boxes from N01 to N15 where replaced bydry blast furnace gas (BFG); (b) same condition with naturalgas (NG); (c) same condition with coke oven gas (COG) and (d)a mixture of 50% of COG and BFG. Fig. 4 shows the comparisonfor the temperature pattern within the sinter bed for a verticalslice located at middle position of the bed width of the fourscenarios considered.

As can be observed, the sintering zone was graduallyenlarged for BFG, NG and COG injection scenarios. Thisexpected behavior can be explained due to the amount of heatreleased when the gaseous fuel was burned out. The resultsindicated that the sintering zone was gradually enlarged fromBFG to COG gaseous fuel when compared with the base caseof actual operation.

The results indicated that the coke oven gas was the mosteffective fuel to enlarge the sintering zone while the blast fur-nace gas showed lower effect. Thus, a combined scenario ofblast furnace gas and coke oven gas is proposed to utilizeboth the abundant steelmaking gases, as shown in Fig. 5. Thecombined scenario of BFG-COG shows intermediate temper-ature pattern, as expected, and indicated feasible operationpractice since the temperature distributions are compatiblewith actual operation practice. Fig. 6(a) and (b) combined withFig. 7(a) and (b) shows predicted PCDD and PCDF emissionsof the industrial sintering process compared with the actualoperation used as base scenario for analyzing the emissions.

As could be observed, the combined utilization of auxil-iary gaseous fuel replacing coke breeze decreased the totalemissions and concentrated the emissions around the windbox N18, which can be used to improve the effectiveness ofthe countermeasures to avoid the gas emissions by using hightemperature burners only in this wind box.

4. Conclusions

In this paper the innovative technology of gaseous fuel injec-tion in the iron ore sinter bed was simulated based on a

. 2 0 1 3;2(4):323–331

multiphase mathematical model able to predict the processphenomena within the sinter bed taking into account thecoupled phenomena of momentum, heat and mass transferto analyze the possible emissions of PCDD (Poly ChlorinatedDi-benzene Dioxin) and PCDF (Poly Chlorinated Di-benzeneFuran) on the gas flue. The model was validated by sinter bedtemperature measurements obtained by inserting thermocou-ples into the sinter bed of the industrial sinter machine.

The model was used to analyze cases of gaseous utilizationin the sinter bed and partially replace the solid fuel. Simu-lation results indicated that gaseous injection enlarges thesintering zone and enhance the sintering phenomena, whichconfirmed previous predictions based on model and experi-mental procedures reported in the literature [11,13,14,17]. Thecalculated results indicated that solid fuel can be decreasedfor the gaseous fuel scenarios (2.3 kg for BFG, 5.8 kg for NG,6.5 kg for COG and 5.8 kg for COG-BFG per ton of sinter prod-uct) which also confirmed similar trends previously presentedby the authors [11,14].

This study confirmed that this technology is attractive forsteel plants which have excess of process gas such as COG andBFG and can represent considerable decrease in the solid fuelused for the sintering process and can contribute to make thisprocess more environmentally cleaner. For these new oper-ational conditions, regarding to the PCDD/F emissions, thisstudy indicated that based on calculated results the gaseousinjections can contribute to reduce the PCDD and PCDF emis-sions and clarify that when the sintering zone is enlarged thedioxin (PCDD) and furans (PCDF) can be decomposed withinthe bed and the adsorption on the sinter porous structure canbe decreased.

Based on the simulations results, for the scenarios consid-ering the mixture of COG (50) and BFG (50%) the amount aboutof 20% for PCDD and 25% of PCDF decrease compared with theactual operation practice can be expected.

Conflicts of Interest

The authors declare no conflicts of interest.

Acknowledgements

This study was partially supported by Conselho Nacionalde Desenvolvimento Científico e Tecnológico (CNPq) andFundacão Carlos Chagas Filho de Amparo a Pesquisa do Estadodo Rio de Janeiro (Faperj), Brazil.

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