journal article·2019-08

Thermal process and mechanism of phase transition and detoxification of glass-ceramics from asbestos tailings

W.M. Zheng, H.J. Sun, T.J. Peng, L. Zeng

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Abstract

Abstract Based on the chemical and mineral composition of asbestos tailings, the asbestos tailings powder was pre-fired, formed into green body and finally heat-treated to prepare glass-ceramics through the processes of crystallization and sintering. The main crystal phases of the sample were forsterite and enstatite, and the minor crystal phases were magnesioferrite and diopside. The effects of crystallization temperature (787–867 °C) and sintering temperature (1150–1250 °C) on crystallization and phase change, micromorphology and physical-chemical properties of glass ceramics were investigated by means of thermogravimetry-differential scanning calorimetry analysis (TG-DSC), X-ray diffraction (XRD), scanning electron microscopy (SEM-EDS) and mechanical properties tests. The results showed that the toxic phase chrysotile was almost converted into forsterite when the asbestos tailings powder was pre-fired at 700 °C for 1 h. During the sintering process of the green body, with the increase in the crystallization temperature, the content of the forsterite firstly increased and then decreased, and the enstatite increased gradually. After crystallizing at 850 °C for 1 h and holding at different sintering temperatures for 1 h, the glass-ceramics samples were obtained. With the increase in sintering temperature, the content of diopside in the samples gradually decreased, the hematite gradually disappeared and magnesioferrite precipitated at the same time. The crystal morphology was transformed from aggregates of spherulites and ellipse into intertwined bodies of spherulites, ellipse and round bar-like shape. The glass-ceramics achieved optimum compactness at the sintering temperature of 1200 °C with the water absorption rate being 0.026%, the bulk density being 3.164 g/cm3, and the flexural strength being 88 MPa, which reached the standard of glass ceramics for construction. In the process of preparing glass-ceramics from asbestos tailings, the phase transition and detoxification in asbestos tailings were realized, which had certain practical value for the utilization of asbestos tailings and the preparation of high value-added materials.
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Research context

OpenAlex topics: Recycling and utilization of industrial and municipal waste in materials production · Occupational and environmental lung diseases · Glass properties and applications

SciVX discovery tags are terminology-based. OpenAlex topics are source-provided classifications.

References (24)

Show source-provided references
1. Utilization of serpentine resources in China10.4028/www.scientific.net/MSF.814.583 ↗
2. Serpentine minerals: intergrowths and new combination structures10.1126/science.206.4425.1398 ↗
3. Microwave thermal inertisation of asbestos containing waste and its recycling in traditional ceramics10.1016/j.jhazmat.2005.11.035 ↗
4. Comparative effect of chrysotile leaching in nitric, sulfuric and oxalic acids at room temperature10.1016/j.chemgeo.2013.06.004 ↗
5. Magnesium oxide production from chrysotile asbestos detoxification with oxalic acid treatment10.1016/j.jhazmat.2017.04.019 ↗
6. Treatment and recycling of asbestos-cement containing waste10.1016/j.jhazmat.2011.08.057 ↗
7. Comminution of asbestos by a mechanical grinding in asbestos-containing cement board10.2109/jcersj.113.804 ↗
8. Safe decomposition of asbestos by mechano-chemical reaction10.4028/www.scientific.net/MSF.561-565.2257 ↗
9. Hydrothermal conversion of chrysotile asbestos using near supercritical conditions10.1016/j.jhazmat.2010.03.094 ↗
10. Treatment of airborne asbestos and asbestos-like microfiber particles using atmospheric microwave air plasma10.1016/j.jhazmat.2011.08.062 ↗
11. Recycling of the product of thermal inertization of cement-asbestos for various industrial applications10.1016/j.wasman.2010.07.006 ↗
12. Recycling of the product of thermal inertization of cement-asbestos in geopolymers10.1016/j.conbuildmat.2011.12.087 ↗
13. Investigation of plasma treatment for hazardous wastes such as fly ash and asbestos10.1002/(SICI)1520-6416(199902)126:3<73::AID-EEJ8>3.0.CO;2-J ↗
14. Detoxification mechanism of asbestos materials by microwave treatment10.1016/j.jhazmat.2014.09.030 ↗
15. Influence of the type of pre-calcined asbestos containing wastes on the properties of sintered ceramics10.1016/j.conbuildmat.2015.12.110 ↗
16. Lightweight glass–ceramic tiles from the sintering of mining tailings10.1016/j.ceramint.2014.12.049 ↗
17. Effect of MgO addition on sinterability, crystallization kinetics, and flexural strength of glass–ceramics from waste materials10.1016/j.ceramint.2015.10.142 ↗
18. A low cost route for fabrication of wollastonite glass–ceramics directly using soda-lime waste glass by reactive crystallization–sintering10.1016/j.ceramint.2012.08.044 ↗
19. ChemInform abstract: thermal decomposition of Asbestos and recycling in traditional ceramics10.1016/S0955-2219(99)00290-3 ↗
20. Exploration of the role of heat activation in enhancing serpentine carbon sequestration reactions10.1021/es049473m ↗
21. The mechanism of decomposition of serpentines from peridotites on heating10.1007/s10973-013-3483-7 ↗
22. Treatments of asbestos containing wastes10.1016/j.jenvman.2017.08.038 ↗
23. Kinetic study of the dehydroxylation of chrysotile asbestos with temperature by in situ XRPD10.1007/s00269-003-0298-2 ↗
24. Kinetics of densification of powder compacts during the initial stage of sintering with constant rates of heating. A thermal analysis approach. Part III. Copper powder compacts10.1016/0040-6031(83)80304-9 ↗