Our plain-English summary of Structural and microstructural aspects of asbestos-cement waste vitrification, by J. Iwaszko, A. Zawada, I. Przerada, et al (Spectrochimica Acta. Part A, Molecular and Biomolecular Spectroscopy, 2018).
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The study
- Authors: J. Iwaszko, A. Zawada, I. Przerada, M. Lubas
- Journal: Spectrochimica Acta. Part A, Molecular and Biomolecular Spectroscopy
- Published: 2018;195:95-102
- Cited by: 13 articles, as counted by NIH iCite
- Read it: PubMed · Publisher
Abstract
The main goal of the work was to evaluate the vitrification process of asbestos-cement waste (ACW). A mixture of 50 wt% ACW and 50 wt% glass cullet was melted in an electric furnace at 1400 °C for 90 min and then cast into a steel mold. The vitrified product was subjected to annealing. Optical microscopy, scanning electron microscopy (SEM), Fourier transform infrared spectroscopy (FT-IR) and X-ray diffraction (XRD) were used to evaluate the effects of the vitrification. The chemical constitution of the material before and after the vitrification process was also analyzed. It was found that the vitrified product has an amorphous structure in which the components of asbestos-cement waste are incorporated. MIR spectroscopy showed that the absorption bands of chrysotile completely disappeared after the vitrification process. The results of the spectroscopic studies were confirmed by X-ray studies - no diffraction reflections from the chrysotile crystallographic planes were observed. As a result of the treatment, the fibrous asbestos construction, the main cause of its pathogenic properties, completely disappeared. The vitrified material was characterized by higher resistance to ion leaching in an aquatic environment than ACW and a smaller volume of nearly 72% in relation to the apparent volume of the substrates. The research has confirmed the high effectiveness of vitrification in neutralizing hazardous waste containing asbestos and the FT-IR spectroscopy was found to be useful to identify asbestos varieties and visualizing changes caused by the vitrification process. The work also presents the current situation regarding the utilization of asbestos-containing products.
Copyright © 2018 Elsevier B.V. All rights reserved.
In plain English
In this Polish laboratory study, the authors tested vitrification (melting waste into glass) as a way to dispose of asbestos-cement waste. They took a piece of asbestos-cement roofing sheet from dismantling, ground it, and mixed it 50/50 by weight with crushed window glass. They melted the mix at 1400°C for 90 minutes, cast it into a steel mold, and annealed it. Chemical and microscopic tests indicated that the asbestos in the waste was chrysotile. After melting, the result was a transparent, green glass block. Infrared tests found the chrysotile signals had completely disappeared, X-ray tests found no crystalline phases, and scanning microscopy detected no asbestos fibers. The glass block was about 72% smaller than the apparent volume of the starting mix. Boiling finely powdered samples in water left the water less alkaline for the glass (pH 10.7) than for the asbestos-cement waste (pH 12). A solid, unmilled sample gave pH 8.8. The authors read the difference as greater resistance to leaching. The authors concluded that vitrification is an effective way to neutralize asbestos-containing waste, turning it into a harmless product.
We wrote this plain-English summary from the full article with the help of AI, and a second AI model checked each sentence against the article. It is not the authors' wording; the abstract and the article are their own account.
What the study did and found
- Design: Laboratory experiment (materials science study) testing vitrification of asbestos-cement waste, assessed by optical and scanning electron microscopy, infrared spectroscopy (FT-IR), X-ray diffraction, chemical analysis and a water leaching test
- Who was studied: A fragment of an asbestos-cement roofing sheet obtained from dismantling, Poland (Czestochowa University of Technology)
- Exposure: Asbestos-cement waste (asbestos identified as chrysotile) mixed 50% by weight with glass cullet from white window glass, melted at 1400°C for 90 minutes, cast into a steel mold, then annealed at 700°C
- Main results:
- Elemental analysis of the fibers in the asbestos-cement waste (mainly magnesium, silicon and oxygen) led the authors to assume the asbestos was chrysotile, which they report X-ray and spectroscopic studies confirmed
- The infrared absorption bands characteristic of chrysotile, present in the asbestos-cement waste, completely disappeared in the vitrified material
- X-ray diffraction found calcite, larnite and chrysotile in the asbestos-cement waste, but no crystalline phases in the vitrified material, which was amorphous
- No asbestos fibers were detected by scanning electron microscopy
- The vitrified product was a homogeneous, transparent, compact glass block with a green tint
- The vitrified material measured about 14 cm3, about 72% less than the apparent volume of the starting 50/50 mixture
- Water in which powdered samples (under 63 micrometres) were boiled reached pH 12 for asbestos-cement waste, 11.6 for glass cullet and 10.7 for vitrified material. The authors interpreted the difference as higher resistance of the vitrified material to ion leaching
- A solid (unmilled) sample, tested separately, gave leachate pH 8.8
- Compared with the glass cullet, the vitrified material contained more calcium, aluminum, magnesium and iron oxides (increases of 300%, 530%, 30% and 180%). The authors attributed this to the asbestos-cement components dissolving into the glass
- The authors' conclusion: The authors concluded that vitrification is an effective method of neutralizing asbestos-containing waste, binds the waste components into the glass structure and converts asbestos-cement waste into a harmless product. They also concluded that FT-IR spectroscopy is useful for identifying asbestos varieties
Topics
Medical terms in this study, explained in our Lexicon: Asbestos-Cement, Scanning Electron Microscopy (SEM), Infrared Spectroscopy (IR), X-Ray Diffraction (XRD), Chrysotile.
Related studies
- Application of Product of Vitrification of Asbestos-Cement Waste and CRT Glass Cullet as Reinforcing Phase in Surface Composites Produced by FSP Method — J. Iwaszko, K. Kudła, et al. (2024)
- Non-combustible waste vitrification with plasma torch melter — J.K. Park, Y.P. Moon, et al. (2001)
- Structural defects play a major role in the acute lung toxicity of multiwall carbon nanotubes: physicochemical aspects — I. Fenoglio, G. Greco, et al. (2008)
- Exploring High Aspect Ratio Gold Nanotubes as Cytosolic Agents: Structural Engineering and Uptake into Mesothelioma Cells — S. Ye, A.A. Azad, et al. (2020)
- Mortality for Mesothelioma and Lung Cancer in a Cohort of Asbestos Cement Workers in BARI (Italy): Time Related Aspects of Exposure — F. Cuccaro, A.M. Nannavecchia, et al. (2019)
- Treatment and recycling of asbestos-cement containing waste — F. Colangelo, R. Cioffi, et al. (2011)
Browse more research in Spectrochimica Acta. Part A, Molecular and Biomolecular Spectroscopy, or return to medical research.
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How to cite it
Cite the study
J. Iwaszko, A. Zawada, I. Przerada, M. Lubas. Structural and microstructural aspects of asbestos-cement waste vitrification. Spectrochimica Acta. Part A, Molecular and Biomolecular Spectroscopy 2018;195:95-102. doi:10.1016/j.saa.2018.01.053. PMID: 29414587.
Cite our summary
“Structural and microstructural aspects of asbestos-cement waste vitrification.” AsbestosClaims.Law Library. https://asbestosclaims.law/library/research/structural-and-microstructural-aspects-of-asbestos-cement-waste.
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