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Treatment of Ammonium-Rich Digestate from Methane Fermentation Using Aerobic Granular Sludge
Digestate produced by cofermentation of agricultural waste and manure can be difficult to dispose of because its high ammonium content impedes its use in agriculture due to generation of odor and overfertilization. This study investigated the possibility of treating such nitrogen-rich digestate with...
Autores principales: | , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
Springer International Publishing
2018
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Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6133121/ https://www.ncbi.nlm.nih.gov/pubmed/30237635 http://dx.doi.org/10.1007/s11270-018-3887-x |
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author | Świątczak, Piotr Cydzik-Kwiatkowska, Agnieszka |
author_facet | Świątczak, Piotr Cydzik-Kwiatkowska, Agnieszka |
author_sort | Świątczak, Piotr |
collection | PubMed |
description | Digestate produced by cofermentation of agricultural waste and manure can be difficult to dispose of because its high ammonium content impedes its use in agriculture due to generation of odor and overfertilization. This study investigated the possibility of treating such nitrogen-rich digestate with aerobic granular sludge depending on the nitrogen load in the reactor. At nitrogen loading rate of 1.0 g TN/(L·day), the nitrogen removal efficiency was high (64.9 ± 9.8%), ammonium nitrogen was completely oxidized, and nitrate was the main nitrification product. At nitrogen loading rate of 3.4 g TN/(L·day), ammonium oxidization was still good (93.6 ± 2.0%), but the percentage of partial nitrification was high (over 68%) and nitrogen removal efficiency worsened to 30.2 ± 2.6%. Despite this, the overall amount of nitrogen removed was 0.86 g TN/(L·day) and was over nearly two times higher than at the lower nitrogen loading rate. At both nitrogen loading rates, in the effluent nitrogen in a form of suspended solids predominated. To diminish the overall N loading in the effluent, treatment is therefore recommended enabling removal of solids, e.g., microfiltration, should be applied, or the digestate should be separated into solid and liquid phases, and only the liquid fraction should be subjected to biological treatment. At high N load in aerobic granules, a very versatile community of N-metabolizing microorganisms was present. More than 50% of all bacteria in aerobic granules were able to metabolize nitrogen, and the predominant genera (35%) was Thauera, which indicated that stable ammonium removal was achieved mostly as a result of heterotrophic nitrification. |
format | Online Article Text |
id | pubmed-6133121 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2018 |
publisher | Springer International Publishing |
record_format | MEDLINE/PubMed |
spelling | pubmed-61331212018-09-18 Treatment of Ammonium-Rich Digestate from Methane Fermentation Using Aerobic Granular Sludge Świątczak, Piotr Cydzik-Kwiatkowska, Agnieszka Water Air Soil Pollut Article Digestate produced by cofermentation of agricultural waste and manure can be difficult to dispose of because its high ammonium content impedes its use in agriculture due to generation of odor and overfertilization. This study investigated the possibility of treating such nitrogen-rich digestate with aerobic granular sludge depending on the nitrogen load in the reactor. At nitrogen loading rate of 1.0 g TN/(L·day), the nitrogen removal efficiency was high (64.9 ± 9.8%), ammonium nitrogen was completely oxidized, and nitrate was the main nitrification product. At nitrogen loading rate of 3.4 g TN/(L·day), ammonium oxidization was still good (93.6 ± 2.0%), but the percentage of partial nitrification was high (over 68%) and nitrogen removal efficiency worsened to 30.2 ± 2.6%. Despite this, the overall amount of nitrogen removed was 0.86 g TN/(L·day) and was over nearly two times higher than at the lower nitrogen loading rate. At both nitrogen loading rates, in the effluent nitrogen in a form of suspended solids predominated. To diminish the overall N loading in the effluent, treatment is therefore recommended enabling removal of solids, e.g., microfiltration, should be applied, or the digestate should be separated into solid and liquid phases, and only the liquid fraction should be subjected to biological treatment. At high N load in aerobic granules, a very versatile community of N-metabolizing microorganisms was present. More than 50% of all bacteria in aerobic granules were able to metabolize nitrogen, and the predominant genera (35%) was Thauera, which indicated that stable ammonium removal was achieved mostly as a result of heterotrophic nitrification. Springer International Publishing 2018-07-09 2018 /pmc/articles/PMC6133121/ /pubmed/30237635 http://dx.doi.org/10.1007/s11270-018-3887-x Text en © The Author(s) 2018 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 Świątczak, Piotr Cydzik-Kwiatkowska, Agnieszka Treatment of Ammonium-Rich Digestate from Methane Fermentation Using Aerobic Granular Sludge |
title | Treatment of Ammonium-Rich Digestate from Methane Fermentation Using Aerobic Granular Sludge |
title_full | Treatment of Ammonium-Rich Digestate from Methane Fermentation Using Aerobic Granular Sludge |
title_fullStr | Treatment of Ammonium-Rich Digestate from Methane Fermentation Using Aerobic Granular Sludge |
title_full_unstemmed | Treatment of Ammonium-Rich Digestate from Methane Fermentation Using Aerobic Granular Sludge |
title_short | Treatment of Ammonium-Rich Digestate from Methane Fermentation Using Aerobic Granular Sludge |
title_sort | treatment of ammonium-rich digestate from methane fermentation using aerobic granular sludge |
topic | Article |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6133121/ https://www.ncbi.nlm.nih.gov/pubmed/30237635 http://dx.doi.org/10.1007/s11270-018-3887-x |
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