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Biodegradation of Emerging Pharmaceuticals from Domestic Wastewater by Membrane Bioreactor: The Effect of Solid Retention Time

Although conventional biological treatment plants can remove basic pollutants, they are ineffective at removing recalcitrant pollutants. Membrane bioreactors contain promising technology and have the advantages of better effluent quality and lower sludge production compared to those of conventional...

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Autores principales: ALOBAIDI, Raghad Asad Kadhim, ULUCAN-ALTUNTAS, Kubra, MHEMID, Rasha Khalid Sabri, MANAV-DEMIR, Neslihan, CINAR, Ozer
Formato: Online Artículo Texto
Lenguaje:English
Publicado: MDPI 2021
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC8036512/
https://www.ncbi.nlm.nih.gov/pubmed/33805955
http://dx.doi.org/10.3390/ijerph18073395
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author ALOBAIDI, Raghad Asad Kadhim
ULUCAN-ALTUNTAS, Kubra
MHEMID, Rasha Khalid Sabri
MANAV-DEMIR, Neslihan
CINAR, Ozer
author_facet ALOBAIDI, Raghad Asad Kadhim
ULUCAN-ALTUNTAS, Kubra
MHEMID, Rasha Khalid Sabri
MANAV-DEMIR, Neslihan
CINAR, Ozer
author_sort ALOBAIDI, Raghad Asad Kadhim
collection PubMed
description Although conventional biological treatment plants can remove basic pollutants, they are ineffective at removing recalcitrant pollutants. Membrane bioreactors contain promising technology and have the advantages of better effluent quality and lower sludge production compared to those of conventional biological treatment processes. In this study, the removal of pharmaceutical compounds by membrane bioreactors under different solid retention times (SRTs) was investigated. To study the effect of SRT on the removal of emerging pharmaceuticals, the levels of pharmaceuticals were measured over 96 days for the following retention times: 20, 30, and 40-day SRT. It was found that the 40-day SRT had the optimum performance in terms of the pharmaceuticals’ elimination. The removal efficiencies of the chemical oxygen demand (COD) for each selected SRT were higher than 96% at steady-state conditions. The highest degradation efficiency was observed for paracetamol. Paracetamol was the most removed compound followed by ranitidine, atenolol, bezafibrate, diclofenac, and carbamazepine. The microbial community at the phylum level was also analyzed to understand the biodegradability of pharmaceuticals. It was noticed that the Proteobacteria phylum increased from 46.8% to 60.0% after 96 days with the pharmaceuticals. The Actinobacteria class, which can metabolize paracetamol, carbamazepine, and atenolol, was also increased from 9.1% to 17.9% after adding pharmaceuticals. The by-products of diclofenac, bezafibrate, and carbamazepine were observed in the effluent samples.
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spelling pubmed-80365122021-04-12 Biodegradation of Emerging Pharmaceuticals from Domestic Wastewater by Membrane Bioreactor: The Effect of Solid Retention Time ALOBAIDI, Raghad Asad Kadhim ULUCAN-ALTUNTAS, Kubra MHEMID, Rasha Khalid Sabri MANAV-DEMIR, Neslihan CINAR, Ozer Int J Environ Res Public Health Article Although conventional biological treatment plants can remove basic pollutants, they are ineffective at removing recalcitrant pollutants. Membrane bioreactors contain promising technology and have the advantages of better effluent quality and lower sludge production compared to those of conventional biological treatment processes. In this study, the removal of pharmaceutical compounds by membrane bioreactors under different solid retention times (SRTs) was investigated. To study the effect of SRT on the removal of emerging pharmaceuticals, the levels of pharmaceuticals were measured over 96 days for the following retention times: 20, 30, and 40-day SRT. It was found that the 40-day SRT had the optimum performance in terms of the pharmaceuticals’ elimination. The removal efficiencies of the chemical oxygen demand (COD) for each selected SRT were higher than 96% at steady-state conditions. The highest degradation efficiency was observed for paracetamol. Paracetamol was the most removed compound followed by ranitidine, atenolol, bezafibrate, diclofenac, and carbamazepine. The microbial community at the phylum level was also analyzed to understand the biodegradability of pharmaceuticals. It was noticed that the Proteobacteria phylum increased from 46.8% to 60.0% after 96 days with the pharmaceuticals. The Actinobacteria class, which can metabolize paracetamol, carbamazepine, and atenolol, was also increased from 9.1% to 17.9% after adding pharmaceuticals. The by-products of diclofenac, bezafibrate, and carbamazepine were observed in the effluent samples. MDPI 2021-03-25 /pmc/articles/PMC8036512/ /pubmed/33805955 http://dx.doi.org/10.3390/ijerph18073395 Text en © 2021 by the authors. https://creativecommons.org/licenses/by/4.0/Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (http://creativecommons.org/licenses/by/4.0/ (https://creativecommons.org/licenses/by/4.0/) ).
spellingShingle Article
ALOBAIDI, Raghad Asad Kadhim
ULUCAN-ALTUNTAS, Kubra
MHEMID, Rasha Khalid Sabri
MANAV-DEMIR, Neslihan
CINAR, Ozer
Biodegradation of Emerging Pharmaceuticals from Domestic Wastewater by Membrane Bioreactor: The Effect of Solid Retention Time
title Biodegradation of Emerging Pharmaceuticals from Domestic Wastewater by Membrane Bioreactor: The Effect of Solid Retention Time
title_full Biodegradation of Emerging Pharmaceuticals from Domestic Wastewater by Membrane Bioreactor: The Effect of Solid Retention Time
title_fullStr Biodegradation of Emerging Pharmaceuticals from Domestic Wastewater by Membrane Bioreactor: The Effect of Solid Retention Time
title_full_unstemmed Biodegradation of Emerging Pharmaceuticals from Domestic Wastewater by Membrane Bioreactor: The Effect of Solid Retention Time
title_short Biodegradation of Emerging Pharmaceuticals from Domestic Wastewater by Membrane Bioreactor: The Effect of Solid Retention Time
title_sort biodegradation of emerging pharmaceuticals from domestic wastewater by membrane bioreactor: the effect of solid retention time
topic Article
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC8036512/
https://www.ncbi.nlm.nih.gov/pubmed/33805955
http://dx.doi.org/10.3390/ijerph18073395
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