Yang Liab,
Tiehong Pengc,
Wenkuan Manb,
Liangchen Jub,
Feng Zheng*d,
Mei Zhangb and
Min Guo*b
aThe State Key Laboratory for Refractories and Metallurgy, School of Materials and Metallurgy, Wuhan University of Science and Technology, Wuhan 430081, China
bSchool of Metallurgical and Ecological Engineering, University of Science and Technology Beijing, Beijing 100083, China. E-mail: guomin@ustb.edu.cn; Fax: +86 10 62334926
cMetallurgical Corporation of China Ltd., Beijing, China
dNano-Science and Nano-Technology Research Center, Materials Science and Engineering College, Shanghai University, Shanghai 200444, P. R. China
First published on 13th January 2016
Ti-bearing electric arc furnace slag (Ti-bearing EAF slag) is the main solid waste generated in the direct reduction iron making process. During the extraction process of Ti from Ti-bearing EAF slag, a by-product containing abundant Si and Al was seldom utilized, thus leading to waste of valuable elements and secondary pollution. In this paper, NaA zeolite (6Na2O·6Al2O3·12SiO2) and sodalite (SOD, 4Na2O·3Al2O3·6SiO2) were synthesized successfully using the by-product as a precursor. The effects of the SiO2/Al2O3 molar ratio (n(SiO2)/n(Al2O3)), H2O/Na2O molar ratio (n(H2O)/n(Na2O)), hydrothermal temperature and time on the crystal phase and microstructure of the prepared zeolites were systematically investigated. The results indicated that NaA zeolite with good crystallinity and cubic morphology was obtained at 140 °C for 3 h with n(SiO2)/n(Al2O3) and n(H2O)/n(Na2O) fixed at 2.0
:
1 and 100
:
1, respectively. Decreasing n(H2O)/n(Na2O), raising the hydrothermal temperature and prolonging the hydrothermal time were beneficial for the formation of spherical SOD zeolite. The phase transformation between NaA and SOD zeolite was discussed and a mechanism was proposed to explain the phenomenon of these zeolites coexisting in the obtained samples. In addition, the removal performances of Cu2+ in aqueous solutions using zeolites synthesized at different temperatures were studied. The maximum removal capacity of the prepared zeolite can reach 1.346 mmol g−1 for 180 min.
:
1. Their frameworks are composed of [SiO4]4− and [AlO4]5− tetrahedra which are linked at their corners to form channels and cages. Generally, zeolite molecular sieves are synthesized from chemical reagents or minerals with rich Al and Si,2–5 leading to high cost, huge discharge of waste and high energy consumption. Thus, extensive efforts have been made to search cheaper raw materials and economic methods for synthesis of zeolite molecular sieves.6–11 Qian et al.11 prepared highly crystalline NaA zeolite with high Ca2+ exchange capacity (CEC) by using coal gangue as raw materials via the in situ crystallization technique. Bukhari et al.12 compared direct hydrothermal method and indirect fusion method of converting coal fly ash to zeolite and using prepared zeolites as adsorbents for the removal of heavy metal ions from aqueous solutions. They found that the zeolites prepared by hydrothermal method showed better crystalline structure and performed better at immobilizing heavy metal ions. Therefore, the synthesis of zeolite from waste materials by hydrothermal method would have wide application prospects in solid waste reclamation utilization.
Ti-bearing electric arc furnace slag (Ti-bearing EAF slag) which contains Ti, Mg, Al and Si contents is the main solid waste generated in direct reduction ironmaking process, and at present, much more attention has been paid only on extraction of Ti by using various approaches such as acid leaching method,13,14 selective enrichment method15,16 and alkali fusion method17,18 etc. However, few efforts have been taken to recycle other valuable elements comprehensively, which result in the potential secondary waste generated during this utilization. In order to make full use of valuable elements existed in Ti-bearing EAF slag, a novel process based on alkali fusion-water leaching-acidolysis process has been proposed by our group.19–21 During the alkali fusion process, the elements existed in Ti-bearing EAF slag were converted to their corresponding sodium salts. Then the alkaline solution containing sodium aluminate and sodium silicate were obtained in the water leaching process, which was an ideal precursor to prepare NaA zeolite.22 However, until now, none of the work has been reported yet.
In this paper, NaA and sodalite (SOD) zeolites were synthesized from the leaching solution of the fused Ti-bearing EAF slag by hydrothermal method. The effects of SiO2/Al2O3 molar ratio ((n(SiO2)/n(Al2O3)), H2O/Na2O molar ratio (n(H2O)/n(Na2O)), hydrothermal time and temperature on the preparation of zeolites were systematically investigated. The transformation mechanism from NaA zeolite to SOD zeolite was also discussed. In addition, the removal capacities of the prepared zeolites with respect to Cu2+ in solution were studied. This paper may explore a novel pathway for efficient and comprehensive utilization of the Ti-bearing EAF slag.
| Composition | TiO2 | Al2O3 | MgO | SiO2 | CaO | Fe2O3 |
|---|---|---|---|---|---|---|
| Content | 50.9 | 19.4 | 12.9 | 8.0 | 5.4 | 2.9 |
According to our previous research,22 Si and Al could be converted to Na2SiO3 and NaAlO2 during the molten NaOH treatment, respectively. Then, they were separated from other elements by water leaching and dissolved in water to form the precursor, which was the raw material to prepare zeolite.
:
1.5 and then roasting at 700 °C for 1 h to obtain alkali fusion slag. After that, the alkali fusion slag was dissolved in distilled water with mass ratio at 1
:
10 and stirred by electromagnetic stirring for 0.5 h. Finally, the obtained suspension was filtered and the obtained filtrate containing mainly Na2SiO3 and NaAlO2 was used as precursor to synthesize zeolite.
:
1 to 2.6
:
1. Then the precursor was well stirred and controlled H2O/Na2O molar ratio (n(H2O)/n(Na2O)) varied from 40
:
1 to 130
:
1. After that, 80 mL precursor was transported into a 100 mL Teflon lined stainless steel autoclave for hydrothermal treatment at a desired temperature for several hours to synthesize zeolite. Finally, the prepared zeolite was filtered, washed, and dried at 90 °C for 12 h before further measurement and characterization. The whole procedure can be depicted in detail as shown in Fig. 1.
| Ct = C0At/A0 | (1) |
The concentration of the heavy metal ions in the solid phase (Qt, mmol g−1) was calculated using integral mass balance for the heavy metal ions in the vessel according to eqn (2).
| Qt = V(C0 − Ct)/m | (2) |
| 12Na2SiO3 + 12NaAlO2 + 12H2O = 6Na2O·6Al2O3·12SiO2(NaA) + 24NaOH | (3) |
| 6Na2SiO3 + 6NaAlO2 + 5H2O = 4Na2O·3Al2O3·6SiO2(SOD) + 10NaOH | (4) |
According to eqn (3) and (4), SiO2/Al2O3 molar ratio (n(SiO2)/n(Al2O3)), H2O/Na2O molar ratio (n(H2O)/n(Na2O)), hydrothermal time and temperature may play important roles in synthesis of NaA and SOD zeolites from Ti-bearing EAF slag.
:
1, but the crystallinity was poor. Moreover, an obvious diffraction peak assigned to SOD zeolite could be detected at 2θ = 14°, suggesting that a few SOD zeolite coexisted with poor crystallized NaA zeolite. When n(SiO2)/n(Al2O3) was adjusted to consist with the stoichiometry of reactions (2.0
:
1), the intensities of diffraction peaks of NaA zeolite became stronger while that of diffraction peak at 2θ = 14° assigned to SOD zeolite became weaker, indicating that the crystallinity of prepared NaA zeolite became better. Further decreasing n(SiO2)/n(Al2O3) to 1.4
:
1, SOD zeolite became the predominant phase in the obtained sample, suggesting that NaA zeolite would be converted to SOD zeolite with the amount of NaAlO2 increasing. This phenomenon may be ascribed to the formed SOD zeolite with high structure stability. According to ref. 23, it is known that cubic NaA and SOD zeolites can be built using the β-cage consisting of 24 T-atoms [T = Si4+ or Al3+] (Fig. 3a) where primary units is SiO4 and AlO4 tetrahedra. In NaA zeolite, each β-cage is connected to the six nearest neighboring β-cages through double T4-rings ([D4R]) as shown in Fig. 3b. In SOD zeolite, each β-cage is connected to the six nearest neighboring β-cages through common simple T4-rings ([S4R]) (Fig. 3c). Therefore, the mass density of SOD zeolite (2.29 g cm−3) is slightly higher than that of NaA zeolite (2.00 g m−3), resulting in SOD zeolite showed a higher framework density and structure stability compared to NaA zeolite.
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Fig. 2 XRD patterns of prepared samples with different n(SiO2)/n(Al2O3). (n(H2O)/n(Na2O) = 100 : 1, T = 140 °C, t = 3 h). | ||
Since NaAlO2 is necessary for the formation of zeolite framework, the presence of aluminum atom on neighboring T (Si, Al) atom site distorts silicon tetrahedron by shortening one of the Si–O bonds.24,25 Thus, increasing the amount of NaAlO2 in solution would result in more serious distortion of [SiO4] tetrahedral, leading to the zeolite framework unstable and easy conversion to SOD zeolite with higher stable structure.
The morphologies of obtained zeolites with different n(SiO2)/n(Al2O3) were shown in Fig. 4. From SEM images analysis, it can be seen that cubic grains and spherical particles were formed and agglomerated in all the prepared samples, which were respectively identified as NaA zeolite (cubic) and SOD zeolite (spherical). Notably, when n(SiO2)/n(Al2O3) was 1.4
:
1, spherical particles with less imperfect cubic grains appeared, suggesting that the main phase of the obtained sample was SOD zeolite as shown in Fig. 4a. With n(SiO2)/n(Al2O3) increasing from 2.0
:
1 (Fig. 4b) to 2.6
:
1 (Fig. 4c), highly crystallized cubic grains with larger size and intact crystal plane were formed. Meanwhile, the amount of spherical particles decreased obviously, indicating that higher n(SiO2)/n(Al2O3) was beneficial for crystallization of NaA zeolite.
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Fig. 4 SEM images of samples prepared with different n(SiO2)/n(Al2O3). (a) 1.4 : 1, (b) 2.0 : 1, (c) 2.6 : 1 (n(H2O)/n(Na2O) = 100 : 1, T = 140 °C, t = 3 h). | ||
Fig. 5 was the XRD patterns of samples obtained with different n(H2O)/n(Na2O). It can be seen that no obvious diffraction peaks appeared with n(H2O)/n(Na2O) at 130
:
1, indicating that few crystalline structure could be formed from the precursor. Decreasing n(H2O)/n(Na2O) to 100
:
1 and 70
:
1, diffraction peaks with strong intensities assigned to NaA zeolite appeared, suggesting that well crystallized NaA zeolite could be prepared when n(H2O)/n(Na2O) ranged from 70
:
1 to 100
:
1. However, further decreasing n(H2O)/n(Na2O) to 40
:
1, NaA zeolite was converted to SOD zeolite, indicating that strong alkalinity was benefit for the formation of SOD zeolite rather than NaA zeolite. Based on the aforementioned analysis, it is believed that low alkalinity is unfavorable for the crystallinity, and high alkalinity can promote the transformation from a metastable phase (NaA zeolite) to a new phase with high framework density (SOD zeolite). Therefore, relatively pure NaA zeolite could be obtained when n(H2O)/n(Na2O) was fixed at 100
:
1.
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Fig. 5 XRD patterns of samples prepared with different n(H2O)/n(Na2O). (n(SiO2)/n(Al2O3) = 2.0 : 1, T = 140 °C, t = 3 h). | ||
SEM images of samples prepared with different n(H2O)/n(Na2O) were illustrated in Fig. 6. It can be seen that when n(H2O)/n(Na2O) was 40
:
1, only uniform spherical particles appeared, indicating that obtained sample were mainly SOD zeolite (Fig. 6a). With n(H2O)/n(Na2O) increasing to 70
:
1, many small cubic NaA zeolite particles were clearly identified among the spherical SOD zeolites (Fig. 6b). Further increasing n(H2O)/n(Na2O) to 100
:
1, highly crystallized cubic grains with intact crystal plane and uniform size combined with some little spheres were obtained. Moreover, the size of the obtained cubic particles became larger and the surface of cubic particle appeared smoother, implying that the crystallinity of the prepared NaA zeolites became better. When n(H2O)/n(Na2O) was continuously up to 130
:
1, no crystallized product but amorphous gel was formed. This observation agreed well with the XRD results (Fig. 5).
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Fig. 6 SEM images of samples prepared with different n(H2O)/n(Na2O). (a) 40 : 1, (b) 70 : 1, (c) 100 : 1, (d) 130 : 1 (n(SiO2)/n(Al2O3) = 2.0 : 1, T = 140 °C, t = 3 h). | ||
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Fig. 7 XRD patterns of samples obtained at different hydrothermal temperatures. (n(SiO2)/n(Al2O3) = 2.0 : 1, n(H2O)/n(Na2O) = 100 : 1, t = 3 h). | ||
Fig. 8 gave the SEM images of samples obtained at different hydrothermal temperatures. The amorphous phase samples obtained at 100 °C for 3 h had predominant amorphous floccule morphologies (Fig. 8a), while cubic grains with uniform size covered by some amorphous substance were synthesized at 120 °C (Fig. 8b). With the temperature increasing to 140 °C, the amorphous floccule disappeared and majority of well crystallized cubic grains combined with some little spheres on their surface were formed (Fig. 8c). Further increasing the temperature to 160 °C, most of the cubic NaA zeolite was converted to SOD zeolite with spherical morphology (Fig. 8d), which was also evidenced by the XRD results shown in Fig. 7.
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Fig. 8 SEM images of samples obtained at different hydrothermal temperatures. (a) 100 °C, (b) 120 °C, (c) 140 °C, (d) 160 °C (n(SiO2)/n(Al2O3) = 2.0 : 1, n(H2O)/n(Na2O) = 100 : 1, t = 3 h). | ||
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Fig. 9 XRD patterns of samples synthesized at different hydrothermal time. (n(SiO2)/n(Al2O3) = 2.0 : 1, n(H2O)/n(Na2O) = 100 : 1, T = 120 °C). | ||
Fig. 10 showed the SEM images of samples synthesized at different hydrothermal time. As shown in Fig. 10a, it clearly revealed that 3 h crystallized sample were a lot of cubic particles covered by some amorphous floccule. With the hydrothermal time increasing to 6 h, the amorphous floccule disappeared and highly crystallized cubic grains combined with some little spheres on the surface could be obtained (Fig. 10b). In addition, the crystal plane of obtained cubic grains became more intact crystal plane and the sizes of the grains were uniform with about 10 μm (shown as inset in Fig. 10b). However, the aggregation degree of cubic particles became more serious, and the defined cubic structure started to collapse with time prolonging to 9 h (Fig. 10c). As shown in the inset of Fig. 10c, it can be seen that cubic particles with surface corrosion and some imperfect spherical particles were coexisted in the obtained sample. With the time up to 12 h, nearly all the cubic structure destroyed and the spherical crystal grains became the majority phase. This means that relatively long reaction time was beneficial for the conversion of metastable NaA zeolite into more thermodynamically stable SOD zeolite phase.27
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Fig. 10 SEM images of samples synthesized at different hydrothermal time. (a) 3 h, (b) 6 h, (c) 9 h, (d) 12 h (n(SiO2)/n(Al2O3) = 2.0 : 1, n(H2O)/n(Na2O) = 100 : 1, T = 120 °C). | ||
The parallel experiments were conducted at 160 °C for different time to investigate the phase transformation mechanism further. The XRD patterns and SEM images of samples obtained at 160 °C for different time were shown in Fig. S1 and S2,† respectively. According to the analysis of XRD and SEM results, the same conclusion can be drawn: the prepared zeolites could transform from cubic NaA zeolite to spherical SOD zeolite with the reaction time prolonging. Moreover, the higher temperature, the longer hydrothermal time would be beneficial for the formation of SOD zeolite.
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Fig. 11 FT-IR spectra of samples synthesized at different hydrothermal temperatures. (a) 120 °C, (b) 140 °C, (c) 160 °C (n(SiO2)/n(Al2O3) = 2.0 : 1, n(H2O)/n(Na2O) = 100 : 1, t = 3 h). | ||
Based on the above analysis, it can be found that the samples synthesized from Ti-bearing EAF slag would transform from NaA zeolite to SOD zeolite with the temperature increasing or time prolonging. Generally, it is believe that the formation of two different phases was resulted from temperature gradients or compositional variations during the course of the reaction. However, it is important to find out the transformation mechanism of the existing cubic NaA zeolite converted to SOD zeolite step by step.
Fig. 12 illustrated the formation process of cubic NaA zeolite and the phase transformation mechanism from cubic NaA zeolite to spherical SOD zeolite. At the very beginning, amorphous aluminosilicates precursor aggregated into irregular particles by the arrangement of Si and Al tetrahedral units (primary building) (step 1). These particles further aggregated into secondary building units (SBUs) such as simple 4-rings ([S4R]) and simple 6-rings ([S6R]) by the association of TO4 (T = Si, Al) tetrahedral units (step 2). Then some of β-cages were formed by further polymerization of simple 4-rings ([S4R]) and simple 6-rings ([S6R]). Surface crystallization then occurred to form many crystalline islands by connecting β-cages via double 4-rings ([D4R]) (step 3). When the crystalline islands extended and fused together, a cubic shell of NaA zeolite could be obtained (step 4 and 5). After the formation of the crystalline cubic shell, the crystallization process extended inward to the amorphous core to increase the thickness of the shell (step 6).
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| Fig. 12 Schematic diagram of NaA zeolite formation process and the phase transformation from NaA zeolite to SOD zeolite. | ||
When the core–shell cubes formed, mass transportation across the crystalline shell became difficult. As the crystalline shell extended inward to the amorphous core, the pressure in the core may increase if the core was dense, because the process of crystallization of the core of zeolite A was a process of density decrease. Based on the aforementioned analysis, it is known that nucleation of SOD zeolite, having a higher density in comparison with NaA zeolite, took place in the amorphous cores of cubic particles where the pressure was built up (step 7). Moreover, high pressure induced phase transformation from a low density zeolite to a high density one was also reported in other research.31 The SOD nucleus expanded in size to break through the NaA zeolite cubic shells to form spherical structure, which can be confirmed by the SEM image (step 8). As shown in the SEM image, the well-developed surfaces of some cubic particles were corroded by the flakes developed within their centers. The broken cubes did not show regular edges, and the cubic morphology was partially maintained in the particle (part A). In other particles such as part B, the SOD zeolite with spherical morphologies developed further to break the cubic shells of NaA zeolite and left only one surface of cubic. Finally, the consumption of NaA zeolite occurred through an Ostwald ripening process and resulted in the cubic NaA zeolite convert to SOD zeolite with spherical morphology (step 9). The results obtained by Wang et al.32 and Radulović et al.33 confirmed that the formation of more stable phase occurred following the Ostwald ripening rule. This process was characterized by a simultaneous growth and dissolution of particles separated in the same media. With time prolonging or temperature increasing, more stable phases like SOD or cancrinite will form at the expense of the metastable NaA zeolite. However, the appearance of these new phases requires the occurrence of a series of very complex processes mass (transference, nucleation and growth) by the rupture of the chemical equilibrium of the system. The stable phases reach the required equilibrium conditions to promote the formation of the final zeolite materials.
According to the above analysis, it is believed that the transformation from NaA zeolite to SOD probably caused by local high pressure rather than by nucleation and growth from residual inhomogeneities in the aluminosilicate gel. Fortunately, we found some intermediate phases (Fig. S4†) formed during the transformation from NaA zeolite to SOD following the Ostwald ripening rule. Therefore, under the present synthetic conditions, no pure NaA zeolite could be produced at any synthetic stage, although reasonably large cubic particles appeared and NaA zeolite became the major phase in the obtained samples as shown in Fig. 8c and 10b.
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| Fig. 13 Relationship between contact time and removal capacity of Cu2+ by zeolite synthesized at different temperatures. | ||
According to eqn (1) and (2), it can be calculated that the removal capacity of Cu2+ by zeolite synthesized at 120 °C for 180 min was 1.346 mmol g−1, much better than that of obtained at 140 °C or 160 °C, which were only 0.722 and 0.673 mmol g−1, respectively. The removal of Cu2+ in wastewater was attributed to different mechanisms of ion exchange as well as adsorption process. During the ion exchange process, Cu2+ can move through the pores of zeolites and channels of the lattice to take place ion exchange with Na+ in zeolite. The diffusion is faster through the pores, whereas it is retarded when the ions move through the smaller channels.9,37 Based on the aforementioned analysis, the pores and channels of SOD zeolites were much smaller than that of NaA zeolites, leading to difficult movement of Cu2+ to exchange with Na+ ions. Therefore, the removal performance of NaA zeolite for Cu2+ was better than that of SOD zeolite.
:
1 and 100
:
1, respectively. Decreasing n(H2O)/n(Na2O), raising the hydrothermal temperature and prolonging the hydrothermal time were beneficial for the formation of spherical SOD zeolite. Moreover, when n(SiO2)/n(Al2O3) and n(H2O)/n(Na2O) were controlled at 2.0
:
1 and 100
:
1, respectively, hydrothermal conditions were fixed at 120 °C for 12 h or 160 °C for 3 h, single crystal of SOD zeolite could be synthesized. However, no matter which condition was chosen, NaA zeolite was coexisted with SOD zeolite. In addition, the removal performances of Cu2+ in Cu2SO4 solutions using zeolites synthesized at different temperatures were studied. The maximum removal capacity reached 1.346 mmol g−1 by zeolite obtained at 120 °C for 3 h.
Footnote |
| † Electronic supplementary information (ESI) available. See DOI: 10.1039/c5ra26881h |
| This journal is © The Royal Society of Chemistry 2016 |