synthesis of inorganic polymers from vitreous slags produced …€¦ · synthesis of inorganic...

1
Synthesis of Inorganic Polymers From Vitreous Slags Produced by EAF Smelting of Bauxite Residue Hertel T 1 , Xakalashe B 2 , Friedrich B 2 , Pontikes Y 1 1 KU Leuven, Department of Materials Engineering, 3001 Leuven, Belgium 2 RWTH Aachen University, IME Institute of Process Metallurgy and Metal Recycling, 52056 Aachen, Germany ABSTRACT In this study, an integrated two-step process is presented for a zero-waste valorisation of BR. In the first step, BR is smelted with additives in an electric arc furnace (EAF) to remove metallic Fe and to produce simultaneously a vitreous slag. The slag produced is activated using an alkaline solution to produce an inorganic polymer. The mechanical properties and microstructure of the final product were then determined. INTRODUCTION METHODS AND MATERIALS RESULTS CONCLUSIONS Close-to zero-waste valorisation of BR via a two-step process iron removal was achieved through carbothermic reduction in an EAF with a satisfactory recovery of more than 80 % The combination of silica fluxing during the smelting of BR, followed by water quenching of the molten product has shown to favour the formation of a vitrified slag The results demonstrated the high reactivity of the vitreous slag and the formation of a dense IP with satisfactory strength of about 75 MPa REFERENCES 1. K. Evans, J Sustain Metall, 2 (4) 316- 331 (2016). 2. M. Gräfe, G. Power and C. Klauber, Hydrometall 108, 60–79 (2011) ACKNOWLEDGEMENTS The research leading to these results has received funding from the European Community’s Horizon 2020 Programme (H2020/2014–2019) under Grant Agreement No. 636876 (MSCA-ETN REDMUD). This publication reflects only the authors’ view, exempting the Community from any liability. Project website: http://www.etn.redmud.org. Bauxite Residue (BR) OXIDES Dried BR 71,5% lignite coke 7,1% silica sand 21,4% Smelting 1500 - 1550 °C BR slag Inorganic Polymer + alkaline activator Water quenching Pig iron 100 μm BSE a) slag plagioclase Ca 0.9 Na 0.1 Al 1.7 Si 2.3 O 8 binder iron 2 μm BSE b) slag binder Intensity (a.u.) Wavenumber (cm -1 ) 1800 1600 1400 1200 1000 800 600 400 1652 939 970 705 691 579 434 429 579 BR slag IP Compressive Strength of Inorganic Polymer: 76.6 ± 4.8 MPa Component (wt%) Fe SiO 2 Al 2 O 3 CaO TiO 2 Na 2 O Others Loss on ignition BR 30.4* 5.5 24.0 10.2 5.6 1.8 0.2 9.4 BR slag 7.0** 39.5 30.3 10.5 7.9 3.2 1.6 - *expressed as Fe, present as Fe 2 O 3 in BR ** expressed as Fe, present as FeO and Fe in BR slag Resource: But: Low industrial scale use XRD SEM XRF Compressive strength, FTIR XRF amorphous 96,0% Fe 1,0% Plagioclase 3,0% XRD of BR slag: XRF of BR and BR slag: FTIR of Inorganic Polymer: SEM-BSE of Inorganic Polymer: a) low b) high magnification Why? Low reactivity as binder, for instance 2 1 1 1 V ~

Upload: others

Post on 18-Jan-2021

4 views

Category:

Documents


0 download

TRANSCRIPT

Page 1: Synthesis of Inorganic Polymers From Vitreous Slags Produced …€¦ · Synthesis of Inorganic Polymers From Vitreous Slags Produced by EAF Smelting of Bauxite Residue Hertel T1,

Synthesis of Inorganic Polymers From Vitreous Slags Produced by EAF Smelting of Bauxite Residue Hertel T1, Xakalashe B2, Friedrich B2, Pontikes Y1

1KU Leuven, Department of Materials Engineering, 3001 Leuven, Belgium2RWTH Aachen University, IME Institute of Process Metallurgy and Metal Recycling, 52056 Aachen, Germany

ABSTRACT In this study, an integrated two-step process is presented for a zero-waste valorisation of BR. In the first step, BR is smelted with additives in an electric arc furnace (EAF) to remove metallic Fe and to produce simultaneously a vitreous slag. The slag produced is activated using an alkaline solution to produce an inorganic polymer. The mechanical properties and microstructure of the final product were then determined.

INTRODUCTION METHODS AND MATERIALS

RESULTS

CONCLUSIONSClose-to zero-waste valorisation of BR via a two-step processiron removal was achieved through carbothermic reduction in an EAF with a satisfactory recovery of more than 80 %The combination of silica fluxing during the smelting of BR, followed by water quenching of the molten product hasshown to favour the formation of a vitrified slagThe results demonstrated the high reactivity of the vitreous slag and the formation of a dense IP with satisfactorystrength of about 75 MPa

REFERENCES1. K. Evans, J SustainMetall, 2 (4) 316-331 (2016).2. M. Gräfe, G.Power and C.Klauber,Hydrometall 108,60–79 (2011)

ACKNOWLEDGEMENTSThe research leading to these results has received funding from the European Community’s Horizon 2020 Programme (H2020/2014–2019)under Grant Agreement No. 636876 (MSCA-ETN REDMUD). This publication reflects only the authors’ view, exempting the Community from anyliability. Project website: http://www.etn.redmud.org.

Bauxite Residue (BR)

OX

IDES

Dried BR71,5%

lignite coke7,1%

silica sand21,4%

Smelting 1500 - 1550 °C

BR slag

InorganicPolymer

+ alkaline activator

Water quenching

Pig iron

100 µmBSEa)

slag

plagioclaseCa0.9Na0.1Al1.7Si2.3O8

binder

iron

2 µmBSEb)

slag

binder

Intensity (a.u.)

Wavenumber (cm -1)

1800 1600 1400 1200 1000 800 600 400

2

2

BR slag

Inorganic Polymer

1652 939

970

705

691

579

434

429579

BR slag

IP

Compressive Strength of Inorganic Polymer: 76.6 ± 4.8 MPa

Component (wt%) Fe SiO2 Al2O3 CaO TiO2 Na2O Others Loss on ignition

BR 30.4* 5.5 24.0 10.2 5.6 1.8 0.2 9.4

BR slag 7.0** 39.5 30.3 10.5 7.9 3.2 1.6 -

*expressed as Fe, present as Fe2O3 in BR** expressed as Fe, present as FeO and Fe in BR slag

Resource:

But: Low industrial scale use

XRDSEMXRF

Compressive strength,FTIR

XRF

amorphous96,0%

Fe1,0%

Plagioclase3,0%

XRD of BR slag:

XRF of BR and BR slag:

FTIR of Inorganic Polymer:

SEM-BSE of Inorganic Polymer: a) low b) high

magnification

Why? Low reactivity as binder, for instance

2

1

1

1

V

~