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Utilization of sewage sludge in the manufacture of lightweight aggregate

This paper presents a comprehensive study on the possibility of sewage sludge management in a sintered ceramic material such as a lightweight aggregate. Made from clay and sludge lightweight aggregates were sintered at two temperatures: 1100 °C (name of sample LWA1) and 1150 °C (name of sample LWA2)...

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Autores principales: Franus, Małgorzata, Barnat-Hunek, Danuta, Wdowin, Magdalena
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Springer International Publishing 2015
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC4669375/
https://www.ncbi.nlm.nih.gov/pubmed/26635022
http://dx.doi.org/10.1007/s10661-015-5010-8
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author Franus, Małgorzata
Barnat-Hunek, Danuta
Wdowin, Magdalena
author_facet Franus, Małgorzata
Barnat-Hunek, Danuta
Wdowin, Magdalena
author_sort Franus, Małgorzata
collection PubMed
description This paper presents a comprehensive study on the possibility of sewage sludge management in a sintered ceramic material such as a lightweight aggregate. Made from clay and sludge lightweight aggregates were sintered at two temperatures: 1100 °C (name of sample LWA1) and 1150 °C (name of sample LWA2). Physical and mechanical properties indicate that the resulting expanded clay aggregate containing sludge meets the basic requirements for lightweight aggregates. The presence of sludge supports the swelling of the raw material, thereby causing an increase in the porosity of aggregates. The LWA2 has a lower value of bulk particle density (0.414 g/cm(3)), apparent particle density (0.87 g/cm(3)), and dry particle density (2.59 g/cm(3)) than it is in the case of LWA1 where these parameters were as follows: bulk particle density 0.685 g/cm(3), apparent particle density 1.05 g/cm(3), and dry particle density 2.69 g/cm(3). Water absorption and porosity of LWA1 (WA = 14.4 %, P = 60 %) are lower than the LWA2 (WA = 16.2 % and P = 66 %). This is due to the higher heating temperature of granules which make the waste gases, liberating them from the decomposition of organic sewage sludge. The compressive strength of LWA2 aggregate is 4.64 MPa and for LWA1 is 0.79 MPa. Results of leaching tests of heavy metals from examined aggregates have shown that insoluble metal compounds are placed in silicate and aluminosilicate structure of the starting materials (clays and sludges), whereas soluble substances formed crystalline skeleton of the aggregates. The thermal synthesis of lightweight aggregates from clay and sludge mixture is a waste-free method of their development.
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spelling pubmed-46693752015-12-11 Utilization of sewage sludge in the manufacture of lightweight aggregate Franus, Małgorzata Barnat-Hunek, Danuta Wdowin, Magdalena Environ Monit Assess Article This paper presents a comprehensive study on the possibility of sewage sludge management in a sintered ceramic material such as a lightweight aggregate. Made from clay and sludge lightweight aggregates were sintered at two temperatures: 1100 °C (name of sample LWA1) and 1150 °C (name of sample LWA2). Physical and mechanical properties indicate that the resulting expanded clay aggregate containing sludge meets the basic requirements for lightweight aggregates. The presence of sludge supports the swelling of the raw material, thereby causing an increase in the porosity of aggregates. The LWA2 has a lower value of bulk particle density (0.414 g/cm(3)), apparent particle density (0.87 g/cm(3)), and dry particle density (2.59 g/cm(3)) than it is in the case of LWA1 where these parameters were as follows: bulk particle density 0.685 g/cm(3), apparent particle density 1.05 g/cm(3), and dry particle density 2.69 g/cm(3). Water absorption and porosity of LWA1 (WA = 14.4 %, P = 60 %) are lower than the LWA2 (WA = 16.2 % and P = 66 %). This is due to the higher heating temperature of granules which make the waste gases, liberating them from the decomposition of organic sewage sludge. The compressive strength of LWA2 aggregate is 4.64 MPa and for LWA1 is 0.79 MPa. Results of leaching tests of heavy metals from examined aggregates have shown that insoluble metal compounds are placed in silicate and aluminosilicate structure of the starting materials (clays and sludges), whereas soluble substances formed crystalline skeleton of the aggregates. The thermal synthesis of lightweight aggregates from clay and sludge mixture is a waste-free method of their development. Springer International Publishing 2015-12-03 2016 /pmc/articles/PMC4669375/ /pubmed/26635022 http://dx.doi.org/10.1007/s10661-015-5010-8 Text en © The Author(s) 2015 Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.
spellingShingle Article
Franus, Małgorzata
Barnat-Hunek, Danuta
Wdowin, Magdalena
Utilization of sewage sludge in the manufacture of lightweight aggregate
title Utilization of sewage sludge in the manufacture of lightweight aggregate
title_full Utilization of sewage sludge in the manufacture of lightweight aggregate
title_fullStr Utilization of sewage sludge in the manufacture of lightweight aggregate
title_full_unstemmed Utilization of sewage sludge in the manufacture of lightweight aggregate
title_short Utilization of sewage sludge in the manufacture of lightweight aggregate
title_sort utilization of sewage sludge in the manufacture of lightweight aggregate
topic Article
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC4669375/
https://www.ncbi.nlm.nih.gov/pubmed/26635022
http://dx.doi.org/10.1007/s10661-015-5010-8
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