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Microbial resource management of one‐stage partial nitritation/anammox

About 30 full‐scale partial nitritation/anammox plants are established, treating mostly sewage sludge reject water, landfill leachate or food processing digestate. Although two‐stage and one‐stage processes each have their advantages, the one‐stage configuration is mostly applied, termed here as oxy...

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Autores principales: Vlaeminck, S. E., De Clippeleir, H., Verstraete, W.
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Blackwell Publishing Ltd 2012
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC3821686/
https://www.ncbi.nlm.nih.gov/pubmed/22452819
http://dx.doi.org/10.1111/j.1751-7915.2012.00341.x
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author Vlaeminck, S. E.
De Clippeleir, H.
Verstraete, W.
author_facet Vlaeminck, S. E.
De Clippeleir, H.
Verstraete, W.
author_sort Vlaeminck, S. E.
collection PubMed
description About 30 full‐scale partial nitritation/anammox plants are established, treating mostly sewage sludge reject water, landfill leachate or food processing digestate. Although two‐stage and one‐stage processes each have their advantages, the one‐stage configuration is mostly applied, termed here as oxygen‐limited autotrophic nitrification/denitrification (OLAND), and is the focus of this review. The OLAND application domain is gradually expanding, with technical‐scale plants on source‐separated domestic wastewater, pre‐treated manure and sewage, and liquors from organic waste bioenergy plants. A ‘microbial resource management’ (MRM) OLAND framework was elaborated, showing how the OLAND engineer/operator (1: input) can design/steer the microbial community (2: biocatalyst) to obtain optimal functionality (3: output). In the physicochemical toolbox (1), design guidelines are provided, as well as advantages of different reactor technologies. Particularly the desirable aeration regime, feeding regime and shear forces are not clear yet. The development of OLAND trickling filters, membrane bioreactors and systems with immobilized biomass is awaited. The biocatalyst box (2) considers ‘Who’: biodiversity and its dynamic patterns, ‘What’: physiology, and ‘Where’: architecture creating substrate gradients. Particularly community dynamics and extracellular polymeric substances (EPS) still require insights. Performant OLAND (3) comprises fast start‐up (storage possibility; fast growth of anammox bacteria), process stability (endured biomass retention; stress resilience), reasonable overall costs, high nitrogen removal efficiency and a low environmental footprint. Three important OLAND challenges are elaborated in detailed frameworks, demonstrating how to maximize nitrogen removal efficiency, minimize NO and N(2)O emissions and obtain through OLAND a plant‐wide net energy gain from sewage treatment.
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spelling pubmed-38216862014-02-12 Microbial resource management of one‐stage partial nitritation/anammox Vlaeminck, S. E. De Clippeleir, H. Verstraete, W. Microb Biotechnol Research Articles About 30 full‐scale partial nitritation/anammox plants are established, treating mostly sewage sludge reject water, landfill leachate or food processing digestate. Although two‐stage and one‐stage processes each have their advantages, the one‐stage configuration is mostly applied, termed here as oxygen‐limited autotrophic nitrification/denitrification (OLAND), and is the focus of this review. The OLAND application domain is gradually expanding, with technical‐scale plants on source‐separated domestic wastewater, pre‐treated manure and sewage, and liquors from organic waste bioenergy plants. A ‘microbial resource management’ (MRM) OLAND framework was elaborated, showing how the OLAND engineer/operator (1: input) can design/steer the microbial community (2: biocatalyst) to obtain optimal functionality (3: output). In the physicochemical toolbox (1), design guidelines are provided, as well as advantages of different reactor technologies. Particularly the desirable aeration regime, feeding regime and shear forces are not clear yet. The development of OLAND trickling filters, membrane bioreactors and systems with immobilized biomass is awaited. The biocatalyst box (2) considers ‘Who’: biodiversity and its dynamic patterns, ‘What’: physiology, and ‘Where’: architecture creating substrate gradients. Particularly community dynamics and extracellular polymeric substances (EPS) still require insights. Performant OLAND (3) comprises fast start‐up (storage possibility; fast growth of anammox bacteria), process stability (endured biomass retention; stress resilience), reasonable overall costs, high nitrogen removal efficiency and a low environmental footprint. Three important OLAND challenges are elaborated in detailed frameworks, demonstrating how to maximize nitrogen removal efficiency, minimize NO and N(2)O emissions and obtain through OLAND a plant‐wide net energy gain from sewage treatment. Blackwell Publishing Ltd 2012-05 2012-04-16 /pmc/articles/PMC3821686/ /pubmed/22452819 http://dx.doi.org/10.1111/j.1751-7915.2012.00341.x Text en Copyright © 2012 The Authors. Microbial Biotechnology © 2012 Society for Applied Microbiology and Blackwell Publishing Ltd
spellingShingle Research Articles
Vlaeminck, S. E.
De Clippeleir, H.
Verstraete, W.
Microbial resource management of one‐stage partial nitritation/anammox
title Microbial resource management of one‐stage partial nitritation/anammox
title_full Microbial resource management of one‐stage partial nitritation/anammox
title_fullStr Microbial resource management of one‐stage partial nitritation/anammox
title_full_unstemmed Microbial resource management of one‐stage partial nitritation/anammox
title_short Microbial resource management of one‐stage partial nitritation/anammox
title_sort microbial resource management of one‐stage partial nitritation/anammox
topic Research Articles
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC3821686/
https://www.ncbi.nlm.nih.gov/pubmed/22452819
http://dx.doi.org/10.1111/j.1751-7915.2012.00341.x
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