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pH and microbial community determine the denitrifying activity in the presence of nitrate-containing radioactive waste

An important fraction of the currently stored volume of long-lived intermediate-level radioactive waste in Belgium contains large amounts of NaNO(3) homogeneously dispersed in a hard bituminous matrix. Geological disposal of this waste form in a water-saturated sedimentary formation such as Boom Cla...

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Autores principales: Mijnendonckx, Kristel, Bleyen, Nele, Van Gompel, Axel, Coninx, Ilse, Leys, Natalie
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Frontiers Media S.A. 2022
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9634998/
https://www.ncbi.nlm.nih.gov/pubmed/36338040
http://dx.doi.org/10.3389/fmicb.2022.968220
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author Mijnendonckx, Kristel
Bleyen, Nele
Van Gompel, Axel
Coninx, Ilse
Leys, Natalie
author_facet Mijnendonckx, Kristel
Bleyen, Nele
Van Gompel, Axel
Coninx, Ilse
Leys, Natalie
author_sort Mijnendonckx, Kristel
collection PubMed
description An important fraction of the currently stored volume of long-lived intermediate-level radioactive waste in Belgium contains large amounts of NaNO(3) homogeneously dispersed in a hard bituminous matrix. Geological disposal of this waste form in a water-saturated sedimentary formation such as Boom Clay will result in the leaching of high concentrations of NaNO(3), which could cause a geochemical perturbation of the surrounding clay, possibly affecting some of the favorable characteristics of the host formation. In addition, hyper-alkaline conditions are expected for thousands of years, imposed by the cementitious materials used as backfill material. Microbial nitrate reduction is a well-known process and can result in the accumulation of nitrite or nitrogenous gases. This could lead to the oxidation of redox-active Boom Clay components, which could (locally) decrease the reducing capacity of the clay formation. Here, we compared nitrate reduction processes between two microbial communities at different pH related to a geological repository environment and in the presence of a nitrate-containing waste simulate during 1 year in batch experiments. We showed that the microbial community from in Boom Clay borehole water was able to carry out nitrate reduction in the presence of acetate at pH 10.5, although the maximum rate of 1.3 ± 0.2 mM NO(3)(−)/day was much lower compared to that observed at pH 9 (2.9 mM NO(3)(−)/day). However, microbial activity at pH 10.5 was likely limited by a phosphate shortage. This study further confirmed that the Harpur Hill sediment harbors a microbial community adapted to high pH conditions. It reduced twice as much nitrate at pH 10.5 compared to pH 9 and the maximum nitrate reduction rate was higher at pH 10.5 compared to that at pH 9, i.e., 3.4 ± 0.8 mM NO(3)(−)/day versus 2.2 ± 0.4 mM NO(3)(−)/day. Both communities were able to form biofilms on non-radioactive Eurobitum. However, for both microbial communities, pH 12.5 seems to be a limiting condition for microbial activity as no nitrate reduction nor biofilm was observed. Nevertheless, pH alone is not sufficient to eliminate microbial presence, but it can induce a significant shift in the microbial community composition and reduce its nitrate reducing activity. Furthermore, at the interface between the cementitious disposal gallery and the clay host rock, the pH will not be sufficiently high to inhibit microbial nitrate reduction.
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spelling pubmed-96349982022-11-05 pH and microbial community determine the denitrifying activity in the presence of nitrate-containing radioactive waste Mijnendonckx, Kristel Bleyen, Nele Van Gompel, Axel Coninx, Ilse Leys, Natalie Front Microbiol Microbiology An important fraction of the currently stored volume of long-lived intermediate-level radioactive waste in Belgium contains large amounts of NaNO(3) homogeneously dispersed in a hard bituminous matrix. Geological disposal of this waste form in a water-saturated sedimentary formation such as Boom Clay will result in the leaching of high concentrations of NaNO(3), which could cause a geochemical perturbation of the surrounding clay, possibly affecting some of the favorable characteristics of the host formation. In addition, hyper-alkaline conditions are expected for thousands of years, imposed by the cementitious materials used as backfill material. Microbial nitrate reduction is a well-known process and can result in the accumulation of nitrite or nitrogenous gases. This could lead to the oxidation of redox-active Boom Clay components, which could (locally) decrease the reducing capacity of the clay formation. Here, we compared nitrate reduction processes between two microbial communities at different pH related to a geological repository environment and in the presence of a nitrate-containing waste simulate during 1 year in batch experiments. We showed that the microbial community from in Boom Clay borehole water was able to carry out nitrate reduction in the presence of acetate at pH 10.5, although the maximum rate of 1.3 ± 0.2 mM NO(3)(−)/day was much lower compared to that observed at pH 9 (2.9 mM NO(3)(−)/day). However, microbial activity at pH 10.5 was likely limited by a phosphate shortage. This study further confirmed that the Harpur Hill sediment harbors a microbial community adapted to high pH conditions. It reduced twice as much nitrate at pH 10.5 compared to pH 9 and the maximum nitrate reduction rate was higher at pH 10.5 compared to that at pH 9, i.e., 3.4 ± 0.8 mM NO(3)(−)/day versus 2.2 ± 0.4 mM NO(3)(−)/day. Both communities were able to form biofilms on non-radioactive Eurobitum. However, for both microbial communities, pH 12.5 seems to be a limiting condition for microbial activity as no nitrate reduction nor biofilm was observed. Nevertheless, pH alone is not sufficient to eliminate microbial presence, but it can induce a significant shift in the microbial community composition and reduce its nitrate reducing activity. Furthermore, at the interface between the cementitious disposal gallery and the clay host rock, the pH will not be sufficiently high to inhibit microbial nitrate reduction. Frontiers Media S.A. 2022-10-21 /pmc/articles/PMC9634998/ /pubmed/36338040 http://dx.doi.org/10.3389/fmicb.2022.968220 Text en Copyright © 2022 Mijnendonckx, Bleyen, Van Gompel, Coninx and Leys. https://creativecommons.org/licenses/by/4.0/This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
spellingShingle Microbiology
Mijnendonckx, Kristel
Bleyen, Nele
Van Gompel, Axel
Coninx, Ilse
Leys, Natalie
pH and microbial community determine the denitrifying activity in the presence of nitrate-containing radioactive waste
title pH and microbial community determine the denitrifying activity in the presence of nitrate-containing radioactive waste
title_full pH and microbial community determine the denitrifying activity in the presence of nitrate-containing radioactive waste
title_fullStr pH and microbial community determine the denitrifying activity in the presence of nitrate-containing radioactive waste
title_full_unstemmed pH and microbial community determine the denitrifying activity in the presence of nitrate-containing radioactive waste
title_short pH and microbial community determine the denitrifying activity in the presence of nitrate-containing radioactive waste
title_sort ph and microbial community determine the denitrifying activity in the presence of nitrate-containing radioactive waste
topic Microbiology
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9634998/
https://www.ncbi.nlm.nih.gov/pubmed/36338040
http://dx.doi.org/10.3389/fmicb.2022.968220
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