Samples of commercial chrysotile-asbestos and asbestos cement, which were equal in number, were prepared. The content of fibers, up to 80 microm in length, was 87.4 and 85.0% in the first and second samples, respectively. Chemical analysis confirmed that there were cement components onto the surface of fibrils in the second sample. Onto the surface of native asbestos fibers, there were considerable distribution bands of active centers in the range of pH values of 5, 6.4, and 7.3; their largest number was at pH 6.4. Asbestos cement fibers had a band at pH 7.3, i.e. there was displacement towards the neutral region. Thus, their capacity for oxidative processes is likely to be lower than that in the fibers from the first sample. The mutagenic activity of the commercial chrysotile, examined in the micronucleus test, was substantially higher (p < 0.01) than that in the asbestos cement sample wherein it did not differ from that seen in the control experiment (saline solution). Mutagenicity was not found in cement and asbestos cement dust (2-3% of fibers) either. It is probable that the absence of mutagenicity in the cement-coated asbestos fibers may be attributable to a considerable reduction in their potencies for the formation of active radicals (oxygen, lipid peroxidation, and others).
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Materials (Basel)
November 2024
Institute of Sustainable Construction, Faculty of Civil Engineering, Vilnius Gediminas Technical University, 10223 Vilnius, Lithuania.
This article presents research on the effectiveness of utilizing asbestos waste, particularly chrysotile asbestos, in the production of Portland cement. The study aimed to evaluate the feasibility of transforming asbestos cement (Eternit) through thermal treatment and its enrichment with mineral additives, enabling its integration into the clinker synthesis process. Differences in the physicochemical properties of types of cement produced from conventional raw materials and those manufactured using asbestos waste were analyzed.
View Article and Find Full Text PDFAm J Ind Med
February 2025
Institute for Translational Epidemiology and Tisch Cancer Institute, Icahn School of Medicine at Mount Sinai, New York, New York, USA.
Background: Asbestos exposure and its pathological consequences, especially malignant mesothelioma (MM) still represent a major public health problem on a global scale. After the ban of asbestos in most western countries, nonoccupational exposure plays an essential role in MM pathogenesis. However, few studies have quantified asbestos lung burden after environmental exposure.
View Article and Find Full Text PDFMaterials (Basel)
November 2024
Faculty of Production Engineering and Materials Technology, Department of Materials Engineering, Czestochowa University of Technology (CUT), 19 Armii Krajowej Ave., 42-200 Czestochowa, Poland.
In this study, the vitrification of asbestos-cement waste (ACW) and glass cullet from cathode-ray tubes (CRTs) was performed. The resulting product of vitrification from the abovementioned waste was used as the reinforcing phase in a composite with the AA7075 alloy matrix. The composite was made by means of the FSP (friction stir processing) method.
View Article and Find Full Text PDFHistopathology
February 2025
Surgical Pathology and Cytopathology Unit, University Hospital of Padova, Padova, Italy.
Crit Rev Toxicol
November 2024
Chemical and Product Safety, Risk Sciences International, Ottawa, ON, Canada.
Asbestos is a group of naturally occurring fibrous minerals that were commonly used in the construction of cement pipes for drinking water distribution systems. These pipes deteriorate and can release asbestos fibers into drinking water, raising concerns about potential risk to human health. The objective of this work was to synthesize human, animal, and evidence on potential health risks due to ingested asbestos in drinking water and evaluate the weight of evidence (WoE) of human health risk.
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