© The Minerals, Metals & Materials Society 2018
Boyd R. Davis, Michael S. Moats, Shijie Wang, Dean Gregurek, Joël Kapusta, Thomas P. Battle, Mark E. Schlesinger, Gerardo Raul Alvear Flores, Evgueni Jak, Graeme Goodall, Michael L. Free, Edouard Asselin, Alexandre Chagnes, David Dreisinger, Matthew Jeffrey, Jaeheon Lee, Graeme Miller, Jochen Petersen, Virginia S. T. Ciminelli, Qian Xu, Ronald Molnar, Jeff Adams, Wenying Liu, Niels Verbaan, John Goode, Ian M. London, Gisele Azimi, Alex Forstner, Ronel Kappes and Tarun Bhambhani (eds.)Extraction 2018The Minerals, Metals & Materials Serieshttps://doi.org/10.1007/978-3-319-95022-8_9

Pyrometallurgical Processing of Desulphurization Slags

Christoph Pichler1, Jürgen Antrekowitsch1   and Karl Pilz2
(1)
Chair of Nonferrous Metallurgy, Montanuniversitaet Leoben, Leoben, Austria
(2)
Voestalpine Stahl GmbH, Linz, Austria
 
 
Jürgen Antrekowitsch

Abstract

A special desulphurization slag accrues during the processing of iron ore to steel , which is needed to generate high quality steel . Sulphur removing is done by different technologies, but the most common one is the generation of a high sulphur containing slag by sulphur affine elements. Currently, this desulphurization slag is partly recycled, however, huge amounts are still dumped. To utilize this desulphurization slag for future purposes, a recycling process must be established. Therefore, first characterization of this material started some years ago at the Chair of Nonferrous Metallurgy, Montanuniversität Leoben. Subsequent trials in lab scale size were performed, also some investigations for different treatment steps were evaluated, starting with a parameter study in a hot stage microscope at various gas-atmospheres. Finally, the developed recycling process concept was verified in pilot scale trials to confirm the new recycling technology. Due to the successful treatment process, also a patent was applied.

Keywords

RecyclingDesulphurization slagLandfill

Introduction

Due to the strong increasing crude steel production, the occurring by-products and residues from the iron - and steel industry are rising as well. This fact in conjunction with an environmental aspect is crucial to intensify the investigation in the field of recycling wastes and by-products from the iron - and steel industry. Some successful applications of utilizing materials from this industry sector are already in operation like the standardized cement from blast furnace slag because of its latent-hydraulic properties [1, 2]. Furthermore, the basic oxygen furnace slag can be used for road construction in different layers, due to its hardness [3]. Some other by-products cannot be used directly in a further application, because of their properties or chemical composition. One example is the desulphurization slag , which is the product at hot metal desulphurization. Such a sulphur removal is mandatory in the iron and steel industry, because sulphur is well known as steel parasite [4, 5].

Sulphur in the Iron- and Steel Industry

This short chapter describes the influence of sulphur in the steel product and the possibilities for a successful removing.

Influence of Sulphur and Its Input Material

Beside phosphor, sulphur is one of the major steel parasites. The complete dissolution of sulphur leads to the formation of iron sulphide. At fast cooling rates, the iron sulphide separates at the grain boundaries. This compound builds together with iron a eutectic with low melting temperature , which is responsible for the red shortness during hot forming. The iron sulphide itself leads to the hot shortness at about 1200 °C. The binary system of sulphur an iron is pictured in Fig. 1 [4, 5].
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Fig. 1

Binary system of sulphur and iron [6]

Manganese forms together with sulphur a compound, which leads to problems during welding processes, and lamellar fractures occur. Only at some special steel types the sulphur is needed, like free-cutting steels. In earlier times lead was used in such steel types, which was prohibited in the last years and was substituted by sulphur, since of similar properties. Typically, sulphur contents are 0.15–0.3% in free-cutting steels [4, 5, 7].

The main source for sulphur in hot metal is the used coke at the blast furnace process. About 80% of the total sulphur input is contributed by this material. The remaining part of the sulphur feed is coming from ores and additives [5, 8].

Desulphurization Technologies for Hot Metal

Different methods can be used for a successful desulphurization. Examples are the removal via the gas phase, through diffusion equalization, with sulphur affine metals or the usage of the partition equilibrium between a slag and iron . Within the hot metal or steel production different desulphurization technologies take place during different processing steps. The first removal is done in the blast furnace itself by the slag , where about 4% of the fed sulphur remains in the pig iron . The main step is done between the blast furnace and the steel plant in a pig iron ladle or torpedo ladle. To reach the defined level, the secondary metallurgy of steel is the last possibility to perform a desulphurization [5].

A summary of possible concepts for the desulphurization, divided into groups, is given in the following Table 1.
Table 1

Overview of possible desulphurization concepts an additives

Group

Process

Place of treatment

Type of desulphurization agent

casting stream mixing process

soda desulphurization

Ladle/mixer

Soda

Mechanical mixing process

Diverse mixer; Hoesch mixing process

blast furnace gutter; pig iron ladle

CaO ; CaC2; soda/lime (1:1)

Pneumatic mixing process

Injection lance; injection process

Torpedo ladle

CaC2 + CaO ; Mg and Mg + CaO

Electromagnetically mixer

Electrochemical gutter

 

Pre-melted slag

Depending on the operated desulphurization process various amounts of desulphurization additives are needed and also the required time together with a temperature loss is varying [5].

Fundamental of the Roasting for Sulphur Removing

For special types of desulphurization slags some processes are available [9, 10], but in most cases a successful concept is not available and therefore it gets dumped. This information is also mentioned in the IRC Reference Report Best Available Techniques (BAT) Reference Document for Iron and Steel Production from March 2012. One main idea is the separation of sulphur without generating of a new waste. This can be achieved through a removal of sulphur in the off-gas linked to a sulphuric acid generation.

In the field of metallurgy, the roasting process is typically used to generate metal oxides from sulphide ores. This leads to the fact that such a roasting step can be used to treat sulphur containing slags as well. Different roasting technologies are available like the multiple hearth furnace , the fluidized bed roaster, a rotary hearth furnace , a shaft furnace or a sinter belt. All these processes are working in solid state [1114].

Recycling of Desulphurization Slag from the Pig Iron Desulphurization

The considered desulphurization slag is generated in a hot metal ladle desulphurization through an injection lance. The obtained slag contains the sulphur and gets removed from the ladle. Here, a separation in three different grain size fraction can be achieved. The biggest fraction are so called “skulls” (>120 mm) which can be used as scrap in the basic oxygen furnace or an electric arc furnace . With respect to the sulphur content, in the most cases it is possible to recycle the “middle” sized-fraction (10–120 mm) in the blast furnace , but too high sulphur levels avoids such a reuse. In this case the middle fraction has to be treated together with the “fine” fraction (0–10 mm), which has the highest sulphur content. At the moment, no satisfying concepts are available to remove the sulphur from these fractions. Therefore, intensive research in the past leads to the following described process design.

Characterization and Parameter Definition in a Hot Stage Microscope (Lab Scale Trials)

For this investigation the fine fraction of the desulphurization slag was used, that typically contains 4–6% S, CaO , MgO, C, SiO2 , FeO, Fe2O3 and Femetallic. The first step was a detailed chemical analysis of the used material to obtain information about the detailed composition.

To clarify the possibility for a roasting process, a hot stage microscope was applied. Usually such a device is used to determine the softening behaviour of slags, dust, ashes or other materials. Therefore, a shadow image of a cylindrical sample gets detected at the continuous increasing temperature . Through geometrical changes of the cylinder during the heating, which can be recognized by the projected picture of the sample, it is possible to define the softening point and/or melting point from the considered sample. Such practical results are needed for pyrometallurgical process developments. In the case of desulphurization slag , the hot stage microscope is used to perform lab scale trials. This means, that the cylindrical sample (diameter: 3 mm; height: 3 mm) gets heated (10 K/min.) to defined temperatures and different gas atmospheres. The different continuously added gases, to generate a specific atmosphere in the furnace , were pure oxygen, synthetic air and pure carbon monoxide. To interpret the success of the treatment, the continuously released off-gas composition was analysed and furthermore, a scanning electron microscope analysis from the treated sample was used.

Various trials were performed in lab scale, in the end it was possible to define the temperature range together with the needed treatment conditions for a successful recycling . A representative result for a detailed explanation is shown in Fig. 2.
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Fig. 2

Main results from the lab scale trials (example for 1400 °C and pure oxygen atmosphere)

The results were applied in order to define useful process parameter for a successful treatment of the desulphurization slag . This analysis showed, that it is needed to perform such a process in liquid state. This is necessary since lower temperatures (in solid state ) lead to a not satisfying sulphur removal . Regarding the detected gases via a gas analyser attached to the hot stage microscope , it was possible to define the best conditions. A representative example is shown in Fig. 2. After a heating up to 1400 °C in an oxidizing atmosphere (provided by the usage of pure oxygen), the carbon from the liquid slag starts to combust and leaves the reaction room with the off-gas stream. After a complete removal of carbon, the sulphur starts to react and forms SO2, which is gaseous as well. The light microscope picture of the treated slag at the mentioned conditions shows a lot of pores, which indicates the gas formation. A subsequent performed chemical analysis of the remaining slags shows sulphur amounts which are lower than 0.01%.

These successful investigation and parameter definition in such a small scale leads to an up-scale of the trial size into a technical scale device, which is mentioned in the following chapter.

Recycling Process Development in Technical Scale Size

The lab-scale experiments showed, that oxygen in the furnace atmosphere is mandatory to reach a very low level of sulphur in the slag at the end of the treatment. Therefore, a furnace should be used which can supply oxygen with a well mixing effect to homogenize the slag together with the supplied oxygen. Regarding these demands, a TBRC (Top Blown Rotary Converter) is a useful furnace design. Such a TBRC, with a reaction room of about 70 l and an oxygen-methane burner is available at the Chair of Nonferrous Metallurgy, Montanuniversitaet Leoben.

Different experiments using the defined process conditions from the lab scale trials were performed in this furnace . The process control was done via a gas analyser in the off-gas stream. Depending on the temperature and CO 2 value in the off-gas, oxygen was additional added to the reaction room by a burner which is operated overstoichiometrically condition for a quick and complete sulphur removing. It is possible to control the process with the temperature and the off-gas analyser. The end of the treatment can be easily recognized by the trend of SO2 in the off-gas. This can be shown in the following Fig. 3.
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Fig. 3

Off-gas analysis from a TBRC trial at 1400 °C

A successful sulphur removal from the desulphurization slag can be easily recognized by the characteristic SO2 peak in the off-gas analysis, as it is represented in Fig. 3. After reaching the maximum of SO2, the oxygen is rising in the analysis and indicates that most of the sulphur is removed as well. A range of TBRC trials with different parameter and slag additives to obtain the appropriate viscosity of the slag for an ideal treatment were executed. It was possible to confirm the results from the lab scale trial with sulphur levels in the treated slag lower than 0.01% in the technical scale trial with 50–100 kg charged material per batch . To get an impression of the used TBRC in Fig. 4 the tapping after a successful treatment is shown.
../images/468727_1_En_9_Chapter/468727_1_En_9_Fig4_HTML.jpg
Fig. 4

Tapping of the TBRC after the treatment

Due to the very satisfying results this process design was verified by pilot scale trial, which was the next step in the development.

Pilot Scale Trial for the Treatment of Desulphurization Slag

As next step in this investigation pilot scale trials with 200–1000 kg desulphurization slag were performed in a short drum furnace , which has a similar facility design to the TBRC. To optimize the process itself and also to minimize the treatment time, an additional oxygen lance was installed additionally to the natural gas -oxygen burner. With the individual control of the oxygen flow it is possible to optimize the defined process conditions.

Different performed trials in this scale confirmed the results from the former executed investigations. It was possible to verify the feasibility of this process design and the pilot scale trial allowed to define the most useful process parameter.

Conclusion

The needed desulphurization of pig iron generates a special type of residue, the so called desulphurization slag . At the moment no useful recycling technology is in operation for this residue, and the desulphurization slag often goes to landfill . To prevent dumping different research projects are ongoing at the moment. In the case of desulphurization slag it was possible to develop an oxidizing recycling process within several years starting with fundamental theoretical considerations and lab scale trials, up to pilot scale investigations with 500 kg of treated material. It was possible to remove the sulphur of the slag via the off-gas. The remaining slag will be reused in the primary iron and steel production. A detailed flowsheet about the implementation of this new recycling process is shown in Fig. 5.
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Fig. 5

Possible process flowsheet for the treatment of desulphurization slag

It is possible to reach sulphur levels in the treated slag which are lower than 0.01% and this can be seen as very good results. This led to a patent which was applied for this process. Due to the changings in the composition and viscosity of the slag different additives were evaluated and the optimum was defined.