The quality of raw materials (iron ore, coal, and coke) has a clear impact on the carbon emissions of the hot metal production in steel making. So far, very little work has been done to measure and quantify this impact. Yet for benchmarking, technology choice and general carbon optimization are important elements. The total slag production of a blast furnace gives an accurate and relevant measure of the raw materials quality and is the main variable on which plant operators have no control. To quantify the impact of a varying amount of slag produced together with hot metal, a method is developed based on a differential approach. For a number of different blast furnaces with different operating points and burden compositions, the carbon footprint or carbon cost of slag production is determined using this method and a robust value for the carbon cost of the slag is derived. This value can also be used in the comparison of the carbon cost of different steel making routes or in life cycle assessments for steel and slag applications.
When comparing carbon efficiency of hot metal in a blast furnace, differences in quality and mix of raw materials complicate quantification of the carbon footprint. Lower quality raw materials contain more gangue in the ores and ash in the coal that the furnace must process and in the end, this translates into more blast furnace slag production. This obviously requires energy but no precise estimates could be cited when researching the carbon footprint penalty of lower quality raw material.
It is obvious that hot metal production with a higher slag burden will emit more CO2 per ton of hot metal. Slag burden is a parameter that is often not under control of the process operator but is rather dictated by local availability of raw materials or sourcing strategies aimed at optimizing cost of hot metal production. In the past, these differences in slag burden were neglected also because the production practices are often regionally similar, leading to insignificant differences in slag burdens. For benchmarks on a larger scale, however, slag burdens can vary between 150 kg/t and 650 kg slag/t hot metal. These differences effectively distort comparison in term of fuel consumption and carbon footprint.
In the literature, no previous work was found in attempting to quantify the energy or carbon impact of slag, so we set out to develop our own method. We incorporated a large set of detailed process data on the 30 blast furnaces of the ArcelorMittal group and also on many more through professional exchanges. First attempts to find correlations between carbon consumption and slag burden failed, indicating that many other parameters are significant in the overall performance of a blast furnace. Also, attempts to calculate in a theoretical way the energy need to process slag were not satisfactory. Therefore, a more refined method based on monitored data had to be developed.
Materials and Methods
Method to Determine the Carbon Cost of Slag Production
To determine the part of CO2 due to the slag production in the BF process route (carbon cost of slag), a differential reasoning can be developed. The difference in overall emissions of an increase of slag quantity while keeping the hot metal production exactly at the same level should give a reliable estimate of the CO2 impact of the slag quantity. In order to assess the CO2 due to the production of slag over the range of slag quantities regularly encountered, this differential calculation can be done for several installations with different operating points.
The idea is simple but may be a bit complicated to bring into practice because the slag quantity in the blast furnace has an impact on the overall functioning of the blast furnace process. If the carbon demand of the blast furnace changes, so will be the amount of waste gases produced. Since the carbon in this waste gas is not fully consumed, it is necessary to determine exactly what changes to the blast furnace gases will happen while the hot metal production is being kept constant. It is common practice in carbon accounting for the steel industry to substitute steel waste gases for natural gas when it leaves the shop limits because it hugely simplifies the accounting of waste gases in other activities than the ones where the gases were generated. So a credit for an equivalent quantity of natural gas corresponding to the change in blast furnace gas can be attributed to the process. In LCA terms this can be viewed as “system expansion.”
Next to the changes in the blast furnace itself there is also a need to look at some upstream emissions. To maintain a blast furnace operating well, the chemical composition of the slag needs to meet certain chemical requirements, primarily the basicity of the slag. This determines the capacity of the slag to remove unwanted elements such as sulfur out of the hot metal. It also impacts the melting point of the slag. The gangue of iron ores and the slag are in general acid (higher Si-content), so it is necessary to add limestone or dolomite to adjust this slag chemistry. These fluxes also end up in the slag and are proportional to the slag burden attributed to the raw materials. In general, the emissions related to these fluxes are found in the sinter plant upstream of the blast furnace but there are other possibilities depending on the hot metal production route as previously discussed. In any case, these fluxes will create CO2 emissions too which are part of the generation of the slag and caused by the chemistry of the gangue material.
The two aforementioned aspects are considered to be the predominant aspects of the CO2 emission due to a marginal increase in the quantity of slag. This is an assumption that was tested by the methodology described below. It is expected that other aspects contribute to the carbon footprint, such as total quantity of the gangue, sulfur or phosphorous content, and initial acidity of the gangue; however, it is expected their influence is less significant. The main question to answer is if there exists a single value or a simple relation which can take into account the total slag burden, within a sufficient broad range, and which can predict with an acceptable precision (±10 %) the carbon cost of slag in the BF route.
The operation of the blast furnace is modeled using the mathematical model of the blast furnace (MMBF).
The Mathematical Model of the Blast Furnace (MMBF)
The mathematical model of the blast furnace (MMBF) is the standard model used for the ArcelorMittal blast furnaces .
The model development started in the middle of the 50′s, thanks to the contribution of J. Michard , who proposed to divide the blast furnace in two parts which would act as two independent reactors (Fig. 1). This principle was based on vertical probing analysis performed by the former IRSIDFootnote 1 in operating blast furnaces and was confirmed by the dissection of Japanese and Russian blast furnaces after shut down for relining. After a first mathematical analysis in a graphical form done by André Rist , a computer software was released.
The basic principle of the model is the existence in the blast furnace of a thermal reserve zone in which gas and solids have the same temperature fixed by the reactivity of coke in the solution loss reaction. When the quality of iron burden is good, this thermal reserve zone includes a chemical reserve zone in which gas and solids reach a chemical equilibrium (FeO + CO = Fe + CO2).
Due to these simultaneous equilibriums, the lower part (processing zone) of the furnace sets the important operating parameters (fuel and blast rates) and the upper part recovers the available heat and reducing potential of gas to pre-process the burden.
The algorithm adopted in the model is based on the determination of a linear system, which links different types of operational data (see Annex 4).
Fundamentally, the model is a mass and energy balance that ensures the fundamental equilibria of the different chemical reactions and heat transfers in the blast furnace. Given its longevity and widespread use, the blast furnace model has proven to be a capable tool to model the most diverse operating points and successfully predicts that the different output parameters of the BF products give a set of input data. The detailed description of the model is given in Annex 4.
Data and Calculations
For the purpose of analyzing the impact of differential slag burdens, five different existing blast furnaces were considered. Data used are from the year 2012 and come from the European Blast Furnace Committee data exchange and from our internal blast furnaces data collection. Additionally, a theoretical operation was added corresponding to the reference blast furnace used in the ULCOSFootnote 2 project [5, 6] to measure the carbon efficiency of the different breakthrough technologies studied during this research program. For one blast furnace, an extreme operating condition was added with exceptionally high slag production rate (Table 1). The data had to be checked for consistency with the MMBF model and some minor adjustments were required to guarantee the thermodynamic equilibrium of the process.
In order to determine the slag effect, two operating points are considered for every blast furnace: the first one is the reference situation with normal operation using the reported slag volume and the second one is calculated one with 50 kg slag/ton Hot Metal more. Since all equations (related to slag) are linear this amount itself is not very important but it needs to be high enough to remain unaffected by the noise of calculation precision.
The increased slag weight is modeled by varying the quality of the minerals used in sinter while the iron entries in the blast furnace remain the same. Also, the consumption ratios of pellets and lump do not change. Calculations were made at a constant flame temperature.
There are three steps in the calculation:
Blast furnace balance using MMBF to calculate coke consumption. MMBF calculates coke rate at a given coal rate (or the opposite, depending on the fixed conditions).
Calculation of stove fuel consumption using a simplified stove model. By difference with the first step, this permits to calculate the CO2 BF credit due to net BF gas export.
Upstream requirements for coke production and limestone impact are considered. In this paper, adjustments to the carbon input are only via coke, since injected fuels can vary in carbon content (oil, coal, natural gas).
With these three calculations, a global balance of an iron making plant including coke making and sintering was performed to account for cross effects of BF operation on upstream processes. Figure 2 presents the model of such a plant and identifies inputs and outputs used for assessment of slag effect.
The boundary of the model considered includes operations needed for the operation of the blast furnace, i.e., coke plant to transform coal into coke, sinter plant to prepare iron ores for blast furnace, coal grinding for direct injection into the blast furnace, blowers and stoves to generate hot wind for the blast furnace and the blast furnace itself. Inputs are indicated on the left and output on the right. Outputs from the blast furnace are blast furnace gas, hot metal and gas. Coke gas is also considered to account for the quantity of coke used. Blast furnace gas is used at the stoves and also at the coke plant; coke gas is used at the coke plant and at the sinter plant. Remaining gases are exported to other shops in the plant (or to external power plant). Power consumption and generation are not indicated in the graph.
To produce a BF slag with a sufficiently low viscosity and that is efficient in purifying the liquid hot metal at an optimal temperature, the chemistry of the slag needs to be managed very strictly. Considering main iron ores used in steel industry, a CaO content of about 40 % in weight needs to be aimed for. To achieve this, limestone must be added to the sinter causing an upstream CO2 emission due to the decarbonation of 315 kg CO2/t slag; one tonne of CaO produced releases 786 kg CO2 because there is one mole of CO2 by mole of CaO (ratio of molar weight):
And 40 % of CaO is needed to get the right slag chemistry:
Replacing part of limestone by dolomite will marginally increase these CO2 emissions.
The blast furnace model predicts an additional emission of 235 kg CO2/t slag which in total gives 550 kg CO2/t slag (see Table in Annex 3).
The CO2 impact of the slag results from the difference between the reference operation and the newly calculated operation using a different slag volume. The carbon cost of slag is equal to the ratio of the CO2 balance change and the slag volume change.
Results and Discussion
The calculations were carried out for the five considered blast furnaces, the ULCOS Model and one operation with very high slag burden. The summary of the results is shown in Table 2.
The results of the calculations show a remarkable constant value for the CO2 cost of treating gangue through the Blast Furnace route independently of the quantity or nature of the slag as well as the operating practices.
Since the blast furnace model is based on a set of linear equations, we expected that for every blast furnace and every working point the impact of a charge of slag impact can be represented by a constant. What is remarkable is that this constant is very similar for all the cases considered with very different operating practices and raw materials quality.
Figure 3 (from Table 2) presents the relation between slag rate and slag rate effect. Slag rate effect seems to be quite constant with an average value of 550 kg CO2/t slag (Std dev = 18 kg CO2/t slag, i.e., ±3 %).
This confirms the hypothesis that the melting of the slag and the basicity correction are the most important energy-related aspects of the processing of slag and are significantly more important than all other aspects like sulfur or phosphorous content, initial acidity, and overall blast furnace performance, which could also have an impact on the CO2 cost of the slag treatment.
Importance of Assessment of the Carbon Cost of Slag
The identification of this constant which can take the carbon cost of slag into account with sufficient precision allows to benchmark the efficiency of blast furnaces. This constant can be applied in the formulas proposed in the draft CEN standard for greenhouse gas (GHG) emissions in energy intensive industries (part 2: iron and steel industry) .
On top on the importance for process benchmarking, there are three other areas where this assessment of the carbon cost of slag burden could be relevant:
Evaluation of Different Steelmaking Routes
When comparing different steel making routes in terms of carbon footprint (pellet—blast Furnace—basic oxygen furnace; sinter-blast furnace-basic oxygen furnace; pellet-direct reduced iron-electric arc furnace), it is essential to define the system boundaries in a precise way. The total balance of the produced products and by-products (steel, waste gases, and granulated slag) should also be compared. Many studies tend to omit upstream production steps for one or more product streams leading to erroneous answers when carbon footprint of the different routes is compared. This can easily be corrected but also the impact of the by-products needs to be made comparable. Slag produced by direct reduced iron in an electric arc furnace is not comparable to blast furnace slag because it has no latent hydraulic properties. Hence, we need to compare a production route which produces stones as by-product with a production route that produces a cement substitute. To compare carbon footprint of steel produced by both production routes, the blast furnace route should receive a credit which corresponds to the additional value of its by-product.
Moreover, the evaluation of slag valorization methodologies, where with an additional production step electric arc furnace slag is turned into an hydraulic slag, is only possible if there is a criterion to determine the additional value of treated slag such as in the Zero Waste technology for GGBFS  (Ground Granulated Blast Furnace Slag).
Evaluation Supply Chain from Extraction to Steel
An important aspect is to know how important the quality of raw materials is in the supply chain up to hot metal. In general, there is a choice between (i) concentrating ores (at the expense of additional energy), by removing as much gangue from the ores as possible (giving rise to tailing ponds which create vast waste lands), while producing concentrated ore pellets and (ii) taking the iron ores and feed them directly into sinter plants where all the fluxes to create an ideal slag chemistry can be added.
Figure 4 gives a synthetic view of these two approaches. The left side of the figure presents the route where beneficiated iron ore is produced along with tailings; this route leads to a processed iron ore pellet with low gangue. A high rate of pellets in the blast furnace generates a relatively low slag volume that is illustrated in the central graph by the zone “with” (beneficiation). The right part of the figure presents the route where iron ore is used as it is processed in a sinter plant. Sinter has a higher gangue level than pellets and leads to higher slag volume that is illustrated in central graph by the zone “without beneficiation” with higher slag volume.
Unlike the slag of other steel making processes (electric arc furnace, basic oxygen furnace), the blast furnace slag has the right chemistry to become a cement clinker substitute  when quenched and ground afterwards and is known as GGBFS. In order for society to decide on the desirability of making granulated slag, the question should be answered whether the CO2 cost of the production of granulated slag is higher or lower than the production of the cement product it can substitute . If it is lower, there should be no reason to discourage the production of slag. If however more CO2 is required than for clinker, the pressure to decrease the slag volume produced should be proportional to the additional CO2 requirement.
Slag Life Cycle Analysis
Another problem that can be dealt with using this carbon cost value is the accounting of GGBFS in Life cycle analysis (LCA). A commonly used method is the system expansion method where a by-product is attributed an equal impact as the product it replaces and which is used as a credit for the main product of the process [11, 12]. System expansion has disadvantages in that the value depends on an exogenous element and is ultimately linked to the evolution of technologies that have nothing to do with the own activities. Furthermore it allows hot metal production to be credited by non-existing CO2. The ISO 14,044 standard therefore prefers a direct allocation to sub-processes. The CO2 value for granulated slag as derived above allows dividing the hot metal production into two sub-processes, one for hot metal and one for slag.
The present analysis shows that the carbon footprint or carbon cost of slag on the Blast Furnace process can be estimated rather precisely by a single value of about 550 kg CO2/t slag. This value has proven to be rather robust within a wide range of slag burden independent of the nature of the raw materials (sinter, pellets, lump ore) used in the Blast Furnace. By crediting the Blast Furnace process for the production of slag using this value and for the Blast Furnace gas produced using a natural gas equivalent, the inherent efficiency of the hot metal production of every blast furnace operator can be measured and compared. It also allows studying the optimal burden composition—pellets, sinter, lump ore—to have the lowest possible CO2 emissions. Moreover, it enables to benchmark the blast furnace route with other steelmaking technologies that do not produce valuable by-products that replace valuable products with high CO2 footprint (cement in this case).
This value finally gives the carbon footprint impact of producing a ton of slag which if it is turned into GGBFS is much lower than the benchmark value of 766 kg CO2/t clinker for gray cement clinker . This means that the generation of more GGBFS as such is desirable as its production does not cause more emissions than the product it could substitute.
Institut de la Recherche SIDerurgique, former Name of the ArcelorMittal Global R&D organisation, Maizières-lès-Metz, France.
ULCOS stands for Ultra-Low Carbon dioxide (CO2) Steelmaking; see: http://www.ulcos.org/en/about_ulcos/home.php.
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The contributing editor for this article was Bart Blanpain.
MMBF gives fuels balance (calculation of coke or coal rate for energy requirement) with blast furnace gas (BFG) generation.
A part of BFG is used for blast heating. The rest is exported at natural gas equivalence (MJ exported gas = 0.056 kg CO2).
Upstream in CO2 equivalence is calculated for.
Coke consumption (simplified CO2 balance at coke plant).
Lime needed for slag formation.
Fuel for sintering.
See Table 3.
See Table 4.
Annex 4—Description of the Mathematical Model of Blast Furnace (MMBF)
Description of BF Operation
The blast furnace is a continuous reactor operating at steady state. It allows counter current flows of condensed phases (solids and liquids) and gases which exchange mass and energy. The analysis of these heat and oxygen transfers lead to define three zones which are schematized on Fig. 1:
An upper zone of intense heat exchange, where cold charge solids (coke and mineral burden) are quickly heated to a temperature of 950 °C. As soon as the temperature reached 450 °C, the reduction of higher iron oxides (hematite and magnetite) starts.
An intermediate isothermal zone at a temperature of 950 °C covering most of the stack and in which the reduction of iron oxides progresses to the level of wüstite (Fe0.947O) without noticeable heat transfer. Gas and solids have the same temperature in this “Thermal reserve zone” and, if burden reducibility is sufficient, a “Chemical reserve zone” can develop. This chemical reserve zone is due to a pause of oxygen exchange due to a chemical equilibrium between gases, wüstite and metallic iron nuclei.
A lower zone of intense heat exchange, where iron oxides coming from the thermal reserve zone are reduced to metal before melting. Pig iron and slag reach their final temperature (1500 °C) while alloy elements (Si, P, Mn) are reduced parallel to carburization of pig iron and slag/pig iron reactions.
The existence of the thermal reserve zone is due to the specific behavior of coke which reacts with the upcoming gas to regenerate its reduction potential through the so called “Solution loss reaction”: CO2 + C → 2CO. This reaction is highly endothermic and requires high temperature to evolve with a significant kinetics. The thermal reserve zone is at the temperature when this reaction starts. Metallurgical cokes react above 950 °C but lower temperature (750–800 °C) can be observed in charcoal blast furnaces due to higher reactivity of this material.
The existence of a zone where heat and mass transfers stop is the basis of the blast furnace model which considers a boundary in the lower part of the thermal reserve zone separating the preparation and processing zones which are described below.
The preparation zone, in the upper part of the furnace, is characterized by the absence of consumption or formation of carbon by the solution loss reaction or by carbon deposition. Forgetting the gas coming from burden decomposition, the volume of reducing gases (CO + CO2 and H2 + H2O) remain constant all over this zone and there is a simple oxidation of CO to CO2 and H2 to H2O resulting from reduction of higher iron oxides when the gas flows to the top.
The boundary between the preparation and processing zones is defined by the following boundary conditions:
Identical temperatures of gas and solids at the level of thermal reserve zone;
Gas composition with an oxidation degree corresponding to the wüstite-iron equilibrium. At 950 °C, this composition is such as
When the reducibility of the burden is sufficient, iron can leave the preparation zone as pure wüstite in equilibrium with the gas and a chemical reserve zone is included in the thermal reserve zone. Usually, the reduction of higher oxide is not fast enough to reach these ideal conditions and when the gas reaches this “equilibrium composition,” the mineral burden still contains some residual magnetite which can be estimated by means of the “Deviation from ideality (Omega)” which measures an excess oxidation of iron as compared to wüstite.
In the preparation zone also occur some reactions with the burden components:
Evaporation of moisture of coke and mineral burden;
Decomposition of iron hydrates;
Decomposition of iron and calcium carbonates.
Finally, the preparation zone can be considered as recovering heat and chemical potential of the gas delivered by the processing zone. The main heat effect is heating of the burden by transfer of sensible heat from upcoming gas. The only limit is that sensible heat exceeds the requirements to keep drying potential through sufficient top gas temperature.
The lower part of the blast furnace is also a heat and mass exchanger. It receives the prepared materials and processes the liquid products of the metallurgical operation, pig iron, and slag. In this zone, the gasification of coke and injected reducing agents in the nozzle raceway delivers a gas composed of CO, H2, and N2 at a temperature of over 2000 °C and this gas ensures the heat requirements for heating, melting, and final processing of liquids. Due to its reducing potential, it also allows oxygen transfer from solid or liquid oxides.
Looking at the solids leaving the preparation zone, the metallurgical path is as follows:
Final reduction of iron oxides and heating of solids to melting temperature accompanied by regeneration of reducing gas through the solution loss reaction;
Melting of the solids in a zone located above the level of nozzles;
Drainage of liquids to the hearth through a coke bed (the dead man) and final heating to tapping temperature;
Separation of liquid phases in the hearth and achievement of metal/slag reactions.
Parallel to these four steps, some side reactions occur:
End of decomposition of calcium carbonate;
Decomposition of phosphates of the mineral burden.
Reduction by carbon and dissolution of alloying elements (Si, Mn, P);
Desulfurization of pig iron by slag/metal reaction with formation of CaS;
Formation of slag by dissolution of gang material and formation of calcium silicates.
While the gas reduction reactions have very limited heat effect, the regeneration and carbon reduction reactions require a large amount of heat ahead of heating and melting requirements and the heat and mass balance of the processing zone set the operation conditions of the blast furnace.
The MMBF is mainly a heat and mass balance model which transcribes the assumptions of the metallurgical model. This results in an algebraic model allowing the computation of operating parameters under the following conditions:
Equilibrium of heat and mass balances of the blast furnace, processing, and preparation zones;
Achievement of boundary conditions of the processing zone, identical temperatures of gas and solids at the boundary between zones, gas composition at wüstite-iron-gas equilibrium and iron burden with an oxidation degree equal to 1.056 + Omega;
Achievement of various constraints determined by the operator ahead of those resulting from the above-mentioned ones.
All this results in a set of linear equations solved to give the characteristics of an operating point.
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Cite this article
Buttiens, K., Leroy, J., Negro, P. et al. The Carbon Cost of Slag Production in the Blast Furnace: A Scientific Approach. J. Sustain. Metall. 2, 62–72 (2016). https://doi.org/10.1007/s40831-016-0046-8
- Blast Furnace
- Hot Metal
- Slag allocation
- Carbon efficiency
- CO2 emissions
- Granulated blast furnace slag
- Life cycle analysis