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BY 4.0 license Open Access Published by De Gruyter July 29, 2020

Determination of chromium valence state in the CaO–SiO2–FeO–MgO–CrOx system by X-ray photoelectron spectroscopy

  • Deman Liu , Jiang Diao EMAIL logo , Yiyu Qiu , Guang Wang , Gang Li and Bing Xie

Abstract

The chromium valence states in the CaO–SiO2–FeO–MgO–CrOx system were investigated by X-ray photoelectron spectroscopy (XPS). The results indicated that the XPS peaks of Cr 2p3/2 and Cr 2p1/2 locate at the binding energy of ∼577 and ∼586 eV, respectively. There are three kinds of chromium ions such as bivalent Cr(ii), trivalent Cr(iii), and hexavalent Cr(vi) in the CaO–SiO2–FeO–MgO–CrOx slag. Cr(iii) is the dominant valence state, and more than 77.99% Cr is trivalent Cr(iii). The fraction of Cr(ii)/Cr is in the range of 11.24–17.22%. The fraction of Cr(vi)/Cr is below 4.80%. The fraction of Cr(ii)/Cr decreases with increasing slag basicity, Cr2O3 content, temperature, or oxygen pressure log(PO2), while the fraction of Cr(iii)/Cr increases with increasing basicity, Cr2O3 content, temperature, or oxygen pressure. The trend of change is opposite. Low log(PO2), high Cr2O3 content, and high temperature are beneficial to reduce the toxic hexavalent Cr(vi). The slag basicity has little influence on the fraction of Cr(vi)/Cr.

1 Introduction

Steel slag is a by-product of steelmaking industry. In the steelmaking process, the amount of steel slag is about 10%–15% of the crude steel output [1,2]. Since the domestic steel slag comprehensive utilization level is lower than the developed countries [3,4], although the yield of Chinese crude steel is huge, still a large amount of steel slag is untreated and only stockpiled for disposal [5]. Some steel slags such as stainless steel slag, electric arc furnace steel slag, and chromium-containing hot metal steelmaking slag contain a certain amount of chromium oxides. It is possible that part of the chromium may exist in the form of toxic hexavalent chromium Cr(vi) in steel slag. Steel slag stockpiled in the open-air slag yard would pollute air, soil, and groundwater. The chromium element may exist in the form of bivalent Cr(ii), trivalent Cr(iii), and hexavalent Cr(vi) in silicate melts or metallurgical slag [6,7]. Thus, the chromium oxides can be expressed as CrOx. Therefore, study on the valence state of chromium in the metallurgical slag and its influencing factors has a very important significance for the clarification of the existing forms of chromium-containing phases and prevention of the pollution of toxic hexavalent chromium.

Considering the testing cost and the accuracy of testing results, a simple method for rapid detection of chromium valence states in slag is still sparse. Some studies also investigated the chromium valence states through thermodynamic calculation. Xiao and Mirzayousef-Jadid et al. [8,9] calculated the chromium valence states in the CaO–SiO2–CrOx system. It was found that both divalent and trivalent chromium coexist in these slags. Low slag basicity and low oxygen potential lead to the increase in divalent chromium oxide, instead of trivalent chromium oxide. Pretorius et al. [10] calculated the chromium valence states in CrOx–SiO2, CaO–CrOx–SiO2, and CaO–SiO2–Al2O3–CrOx systems and found that the valence states of chromium were mostly affected by the oxygen partial pressure. In recent years, X-ray photoelectron spectroscopy (XPS) was applied to valence state detection in metallurgical slag [11,12,13]. XPS can carry out not only qualitative analysis of the valence states of elements in metallurgical slag but also quantitative analysis.

In this article, the research object is the CaO–SiO2–FeO–MgO–CrOx system, which is the main component of chromium-containing steel slag. The slag samples were prepared under different experimental conditions and XPS was used to determine the chromium valence states [14,15] in the slag through qualitative analysis and semi-quantitative analysis. Through the investigation of influence factors affecting chromium valence states, we expect to provide a theoretical reference for reducing the toxic hexavalent chromium.

2 Experimental

2.1 Materials

The chemical compositions of chromium-containing steel slag used in the present study are given in Table 1. Analytical reagents CaO (≥98.0%), MgO (≥98.0%), and SiO2 (≥99.0%) were provided by Chengdu Kelong Chemical Reagent Factory. FeO was synthesized using analytical reagent Fe2O3 and reduced iron powder (Fe). Fe2O3 (≥70.0% Fe) and Fe were obtained from Tianjin HengXing Chemical Reagent Co., Ltd and Macklin Reagent, respectively. Highly purified Cr2O3 (≥99.0%) from Wenzhou Dongsheng Chemical Reagent Factory was used as the starting chromium oxide.

Table 1

Slag compositions and experiment parameters

No.Slag composition/mass%Rlog(PO2)T/K
CaOSiO2Cr2O3FeOMgO
R14116625122.56−41,873
R24215625122.80−41873
R34314625123.07−41,873
R44413625123.38-41,873
Cr546.815.2225123.07−41,873
Cr644.914.63.525123.07−41,873
Cr741.113.48.525123.07−41,873
O84314625123.07−3.51,873
O94314625123.07−4.51,873
O104314625123.07−51,873
T114314625123.07−41,823
T124314625123.07−41,773

2.2 Methods

A horizontal tube MoSi2 furnace (SGL-1700; Shanghai Jvjing Precision Instrument Manufacturing Co., Ltd) with a proportional–integral–differential controller was used to prepare the slag samples. Fine powders of the raw materials were carefully weighed and well-mixed together in an agate mortar. A 40 g mixture was charged into a MgO crucible. The MgO crucibles containing the slag samples were positioned inside a square alumina holder. The alumina holder was pushed into the even-temperature zone of the tube MoSi2 furnace.

According to the equilibrium of C–O reaction and the process conditions of steelmaking end point, the calculated oxygen potential log(PO2) values are around −5.6 to −3.0. Therefore, the designed log(PO2) values in the present work are −5.0 to −3.5 and are listed in Table 1. Gas mixtures of CO–CO2 were employed to obtain the targeted oxygen potential. The gas compositions of CO–CO2 at equilibrium states were gained by equation (1) [16]. The calculated volume ratios of CO/CO2 are listed in Table 2.

(1)2CO+O2=2CO2ΔGθ=565390+175.17T.
Table 2

Volume ratios of CO/CO2

log(PO2)T/Klog KVCO/VCO2
−3.51,8736.6236:1
−41,8736.6220:1
−41,8237.0533:1
−41,7737.5157:1
−4.51,8736.6211:1
−51,8736.626:1

In view of the sensitivity of chromium to oxygen, the experiments were started by evacuating and filling the furnace chamber with purified argon before the CO–CO2 gas mixture was introduced. Figure 1 shows the temperature control curves in experiments. When the target temperature of each experiment was reached, the samples were held for 60 min in the furnace chamber. After experiments, the MgO crucibles were quickly pulled out of the reaction tube and quenched in liquid nitrogen. The slag samples were separated from the crucibles and milled to below 0.074 µm, then subjected to XPS analyses.

Figure 1 Temperature control curves in experiments.
Figure 1

Temperature control curves in experiments.

The XPS measurements on the slag sample prepared under various conditions were carried out by means of a spectrometer (Thermo Scientific Escalab 250Xi). In the testing, Al K Alpha was used as the source gun type, and the energy type size was 0.1 eV. The measurements were conducted with a spot size of 500 µm. In order to ensure the experimental results, the vacuum degree was controlled below 5 × 10−9 mbar.

3 Results and discussion

3.1 Chromium spectra

Figure 2 illustrates the typical XPS wide scan spectrum of the CaO–SiO2–FeO–MgO–CrOx slag. The auger peaks of the constituent elements in the slag were marked on the spectrum. Two minor peaks around the binding energies of 573–593 eV represent Cr 2p. A major peak at a binding energy of ∼284.6 eV [17] represents C 1s, which appeared due to the contamination of hydrocarbon.

Figure 2 XPS wide scan spectrum of slag sample R3.
Figure 2

XPS wide scan spectrum of slag sample R3.

For qualitative and quantitative analyses, the valence state of chromium element in the slag samples and the broad peak covering several peaks were analyzed. The Cr 2p spectra were divided into Cr 2p1/2 and Cr 2p3/2 by spin–obit interaction. As shown in Figure 3, the peaks of Cr 2p3/2 and Cr 2p1/2 locate at the binding energy of ∼577 and ∼586 eV, respectively. The broad peak was deconvoluted into several separate peaks to determine the individual area of each peak. Generally, it can be deconvoluted into three individual valence states, i.e., Cr(ii), Cr(iii), and Cr(vi). The proportions of above three kinds of ions in the slag samples were deduced from the area under the computer-resolved peaks. As can be seen in Figure 3, Cr(iii) is the main existing form of Cr element, Cr(ii) comes second, while only trace amount of Cr(vi) in the slag. The result is consistent with that of Mittal [18]. The reason for the existence of Cr(ii) and Cr(vi) is that the trivalent chromium can be reduced by the FeO in the slag and oxidized by the small amount of oxygen in the atmosphere.

Figure 3 The fitted Cr 2p spectrum of slag example R3.
Figure 3

The fitted Cr 2p spectrum of slag example R3.

3.2 Effect of log(PO2) on the valence state of chromium

In view of the absence of Cr(ii) and Cr(vi) in the starting materials, the redox reactions of Cr(iii) can be described as follows:

(2)Cr2++14O2=Cr3++12O2Cr3+Cr2+=k1pO21/4,
(3)Cr3++34O2=Cr6++32O2Cr6+Cr3+=k2pO23/4.

According to the stoichiometry of chromium,

(4)nCr=nCr2++nCr3++nCr6+,
(5)nO=nCr2++1.5nCr3++3nCr6+.

Therefore, x can be calculated by the following equation:

(6)x=nOnCr=1.0+1.5Cr3+Cr2++3.0Cr6+Cr2+1.0+Cr3+Cr2++Cr6+Cr2+=1.0+1.5k1pO21/4+3.0k1k2pO21.0+k1pO21/4+k1k2pO2.

The value of x can be obtained by relating Cr(iii)/Cr(ii) and Cr(vi)/Cr(ii) to the oxygen pressure using the law of mass action. As it is very difficult to detect the fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr, we applied the ion and molecule coexistence theory [19,20,21] to obtain these fractions. The calculation process is detailed in one of our previous study [22].

Figure 4 shows both the calculated x and experimental x in the present study. It can be found that the x in CrOx increases with increasing oxygen pressure log(PO2). The result is consistent with Jadid’s finding in the CaO–SiO2–CrOx slag and the CaO–SiO2–Al2O3–CrOx slag [16]. Statistics of the various valence states of chromium in the CaO–SiO2–FeO–MgO–CrOx slag are shown in Figure 5. The fraction of Cr(ii)/Cr decreases with increasing oxygen pressure log(PO2), while Cr(iii)/Cr and Cr(vi)/Cr increase. However, the increase tendency of Cr(vi)/Cr is not obvious, and the fraction of Cr(vi)/Cr is always below 4.5% under the present experimental conditions.

Figure 4 x in CrOx under different oxygen pressure.
Figure 4

x in CrOx under different oxygen pressure.

Figure 5 Fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr as a function of oxygen pressure in the CaO–SiO2–FeO–MgO–CrOx slag.
Figure 5

Fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr as a function of oxygen pressure in the CaO–SiO2–FeO–MgO–CrOx slag.

3.3 Effect of basicity on the valence state of chromium

Figure 6 illustrates the fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr as a function of slag basicity in the CaO–SiO2–FeO–MgO–CrOx slag. It is obvious that Cr(iii)/Cr increases with increasing slag basicity, while Cr(ii)/Cr decreases. It is in good agreement with the increase tendency of x in CrOx in Jadid’s study [8], and the results of comparison are shown in Figure 7. This can be interpreted as more CaCr2O4 and MgCr2O4 generated with increasing CaO content [23,24]. Meanwhile, it is also found that the fraction of Cr(vi)/Cr is almost constant with the increase in slag basicity.

Figure 6 Fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr as a function of slag basicity in the CaO–SiO2–FeO–MgO–CrOx slag.
Figure 6

Fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr as a function of slag basicity in the CaO–SiO2–FeO–MgO–CrOx slag.

Figure 7 x in CrOx under different basicity.
Figure 7

x in CrOx under different basicity.

3.4 Effect of Cr2O3 on the valence state of chromium

Compared with ordinary steel slag, the chromium-containing steel slag contains a higher Cr2O3 content. Therefore, it is necessary to make clear whether the increase in Cr2O3 content has an effect on the valence distribution of chromium. The influence of Cr2O3 content on the fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr in the slag can be seen in Figure 8. With the increase in Cr2O3 content, the fraction of Cr(iii)/Cr increases obviously, and Cr(ii)/Cr shows an opposite trend. Furthermore, the fraction of Cr(vi)/Cr shows a slight downward trend. It can be concluded that increasing the amount of Cr2O3 in the chromium-containing steel slag does not increase the risk of generating toxic hexavalent chromium substances.

Figure 8 Fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr as a function of Cr2O3 content in the CaO–SiO2–FeO–MgO–CrOx slag.
Figure 8

Fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr as a function of Cr2O3 content in the CaO–SiO2–FeO–MgO–CrOx slag.

3.5 Effect of temperature on the valence state of chromium

Figure 9 shows the effect of temperature on the fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr in the CaO–SiO2–FeO–MgO–CrOx slag. With the increase in temperature, the fractions of Cr(ii)/Cr and Cr(vi)/Cr decrease slightly, while the fraction of Cr(iii)/Cr increases slightly, but on the whole, all the changes are very small.

Figure 9 Fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr as a function of temperature in the CaO–SiO2–FeO–MgO–CrOx slag.
Figure 9

Fractions of Cr(ii)/Cr, Cr(iii)/Cr, and Cr(vi)/Cr as a function of temperature in the CaO–SiO2–FeO–MgO–CrOx slag.

4 Conclusions

  1. There are three kinds of chromium ions such as bivalent Cr(ii), trivalent Cr(iii), and hexavalent Cr(vi) in the CaO–SiO2–FeO–MgO–CrOx slag. Cr(iii) is the dominant valence state, Cr(ii) comes second, while only trace amount of Cr(vi) in the slag. More than 77.99% Cr is trivalent Cr(iii). The fraction of Cr(ii)/Cr is in the range of 11.24–17.22%. The fraction of Cr(vi)/Cr is below 4.80%.

  2. The fraction of Cr(ii)/Cr decreases with increasing slag basicity, Cr2O3 content, temperature, or oxygen pressure log(PO2), while the fraction of Cr(iii)/Cr increases with increasing basicity, Cr2O3 content, temperature, or oxygen pressure. The trend of change is just the opposite.

  3. Low log(PO2), high Cr2O3 content, and high temperature are beneficial to reduce the toxic hexavalent Cr(vi). The slag basicity has little influence on the fraction of Cr(vi)/Cr.


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Acknowledgments

This study was financially supported by the National Natural Science Foundation of China (No. 51974047 and 51604047).

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Received: 2018-03-29
Accepted: 2018-12-09
Published Online: 2020-07-29

© 2020 Deman Liu et al., published by De Gruyter

This work is licensed under the Creative Commons Attribution 4.0 International License.

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