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Cationic polyacrylamide copolymers (PAMs): environmental half life determination in sludge-treated soil

BACKGROUND: Cationic polyacrylamide copolymers (PAMs) are used for sludge dewatering in municipal waste water treatment and might enter the environment by spreading of the sludge on agricultural land. Concern has been expressed since little is known about the degradation of PAMs in soils. To obtain...

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Autores principales: Hennecke, Dieter, Bauer, Angela, Herrchen, Monika, Wischerhoff, Erik, Gores, Friedhelm
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Springer Berlin Heidelberg 2018
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC5959997/
https://www.ncbi.nlm.nih.gov/pubmed/29805950
http://dx.doi.org/10.1186/s12302-018-0143-3
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author Hennecke, Dieter
Bauer, Angela
Herrchen, Monika
Wischerhoff, Erik
Gores, Friedhelm
author_facet Hennecke, Dieter
Bauer, Angela
Herrchen, Monika
Wischerhoff, Erik
Gores, Friedhelm
author_sort Hennecke, Dieter
collection PubMed
description BACKGROUND: Cationic polyacrylamide copolymers (PAMs) are used for sludge dewatering in municipal waste water treatment and might enter the environment by spreading of the sludge on agricultural land. Concern has been expressed since little is known about the degradation of PAMs in soils. To obtain detailed information on the polymer’s fate in the soil compartment, the degradation of (14)C-radiolabelled PAM in an outdoor lysimeter was studied. RESULTS: No plant uptake and leaching of radioactivity was observed. There was practically no vertical movement of polymer and no transformation products found at the end of the study. For the top 10 cm soil layer, a mass balance was established throughout the study. About 10% of applied radioactivity was not extractable from soil even with a matrix destructive method, and this was concluded to be bound residue. Characterization of extractable radioactivity by means of GPC-analysis showed a significant decrease of the molecular weight of the PAM with time. The decrease in molecular weight indicates a breakdown of the polymer backbone (the C–C-chain), and is assumed to be primary degradation. The total radioactivity content in the 10 cm top soil layer was quantified every 6 months over a period of 3 years. The results show a significant decrease of the total radioactivity over time and this is defined as ultimate degradation following the definition of OECD and EPA. Based on the data, a half-life time of 2.0 × 10(3) days and a rate constant of 0.00035/day were calculated. With a χ(2) of 12.0 the results of the calculation are thus valid and reliable. The rate constant indicates a mineralization of 22.5% within a period of 2 years based on the total recovered radioactivity. This half-life time is solely based on mineralization and does not take into account the degradation of the polymer backbone, hydrolysis of the side chains, incorporation into the soil matrix, and thus is a conservative approach. CONCLUSIONS: (14)C-PAM degrades very slowly in soil after land-spreading as a component of sewage sludge. Even in a very conservative evaluation which only considered the loss of radioactivity, a half-life time of 5.4 years was determined. ELECTRONIC SUPPLEMENTARY MATERIAL: The online version of this article (10.1186/s12302-018-0143-3) contains supplementary material, which is available to authorized users.
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spelling pubmed-59599972018-05-24 Cationic polyacrylamide copolymers (PAMs): environmental half life determination in sludge-treated soil Hennecke, Dieter Bauer, Angela Herrchen, Monika Wischerhoff, Erik Gores, Friedhelm Environ Sci Eur Research BACKGROUND: Cationic polyacrylamide copolymers (PAMs) are used for sludge dewatering in municipal waste water treatment and might enter the environment by spreading of the sludge on agricultural land. Concern has been expressed since little is known about the degradation of PAMs in soils. To obtain detailed information on the polymer’s fate in the soil compartment, the degradation of (14)C-radiolabelled PAM in an outdoor lysimeter was studied. RESULTS: No plant uptake and leaching of radioactivity was observed. There was practically no vertical movement of polymer and no transformation products found at the end of the study. For the top 10 cm soil layer, a mass balance was established throughout the study. About 10% of applied radioactivity was not extractable from soil even with a matrix destructive method, and this was concluded to be bound residue. Characterization of extractable radioactivity by means of GPC-analysis showed a significant decrease of the molecular weight of the PAM with time. The decrease in molecular weight indicates a breakdown of the polymer backbone (the C–C-chain), and is assumed to be primary degradation. The total radioactivity content in the 10 cm top soil layer was quantified every 6 months over a period of 3 years. The results show a significant decrease of the total radioactivity over time and this is defined as ultimate degradation following the definition of OECD and EPA. Based on the data, a half-life time of 2.0 × 10(3) days and a rate constant of 0.00035/day were calculated. With a χ(2) of 12.0 the results of the calculation are thus valid and reliable. The rate constant indicates a mineralization of 22.5% within a period of 2 years based on the total recovered radioactivity. This half-life time is solely based on mineralization and does not take into account the degradation of the polymer backbone, hydrolysis of the side chains, incorporation into the soil matrix, and thus is a conservative approach. CONCLUSIONS: (14)C-PAM degrades very slowly in soil after land-spreading as a component of sewage sludge. Even in a very conservative evaluation which only considered the loss of radioactivity, a half-life time of 5.4 years was determined. ELECTRONIC SUPPLEMENTARY MATERIAL: The online version of this article (10.1186/s12302-018-0143-3) contains supplementary material, which is available to authorized users. Springer Berlin Heidelberg 2018-05-18 2018 /pmc/articles/PMC5959997/ /pubmed/29805950 http://dx.doi.org/10.1186/s12302-018-0143-3 Text en © The Author(s) 2018 Open AccessThis 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 Research
Hennecke, Dieter
Bauer, Angela
Herrchen, Monika
Wischerhoff, Erik
Gores, Friedhelm
Cationic polyacrylamide copolymers (PAMs): environmental half life determination in sludge-treated soil
title Cationic polyacrylamide copolymers (PAMs): environmental half life determination in sludge-treated soil
title_full Cationic polyacrylamide copolymers (PAMs): environmental half life determination in sludge-treated soil
title_fullStr Cationic polyacrylamide copolymers (PAMs): environmental half life determination in sludge-treated soil
title_full_unstemmed Cationic polyacrylamide copolymers (PAMs): environmental half life determination in sludge-treated soil
title_short Cationic polyacrylamide copolymers (PAMs): environmental half life determination in sludge-treated soil
title_sort cationic polyacrylamide copolymers (pams): environmental half life determination in sludge-treated soil
topic Research
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC5959997/
https://www.ncbi.nlm.nih.gov/pubmed/29805950
http://dx.doi.org/10.1186/s12302-018-0143-3
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