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Predicting biochemical oxygen demand in European freshwater bodies

Biochemical Oxygen Demand (BOD) is an indicator of organic pollution in freshwater bodies correlated to microbiological contamination. High BOD concentrations reduce oxygen availability, degrade aquatic habitats and biodiversity, and impair water use. High BOD loadings to freshwater systems are main...

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Autores principales: Vigiak, Olga, Grizzetti, Bruna, Udias-Moinelo, Angel, Zanni, Michela, Dorati, Chiara, Bouraoui, Fayçal, Pistocchi, Alberto
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Elsevier 2019
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6451040/
https://www.ncbi.nlm.nih.gov/pubmed/30970475
http://dx.doi.org/10.1016/j.scitotenv.2019.02.252
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author Vigiak, Olga
Grizzetti, Bruna
Udias-Moinelo, Angel
Zanni, Michela
Dorati, Chiara
Bouraoui, Fayçal
Pistocchi, Alberto
author_facet Vigiak, Olga
Grizzetti, Bruna
Udias-Moinelo, Angel
Zanni, Michela
Dorati, Chiara
Bouraoui, Fayçal
Pistocchi, Alberto
author_sort Vigiak, Olga
collection PubMed
description Biochemical Oxygen Demand (BOD) is an indicator of organic pollution in freshwater bodies correlated to microbiological contamination. High BOD concentrations reduce oxygen availability, degrade aquatic habitats and biodiversity, and impair water use. High BOD loadings to freshwater systems are mainly coming from anthropogenic sources, comprising domestic and livestock waste, industrial emissions, and combined sewer overflows. We developed a conceptual model (GREEN(+)(BOD)) to assess mean annual current organic pollution (BOD fluxes) across Europe. The model was informed with the latest available European datasets of domestic and industrial emissions, population and livestock densities. Model parameters were calibrated using 2008–2012 mean annual BOD concentrations measured in 2157 European monitoring stations, and validated with other 1134 stations. The most sensitive model parameters were abatement of BOD by secondary treatment and the BOD decay exponent of travel time. The mean BOD concentrations measured in monitored stations was 2.10 mg O(2)/L and predicted concentrations were 2.54 mg O(2)/L; the 90th percentile of monitored BOD concentration was 3.51 mg O(2)/L while the predicted one was 4.76 mg O(2)/L. The model could correctly classify reaches for BOD concentrations classes, from high to poor quality, in 69% of cases. High overestimations (incorrect classification by 2 or more classes) were 2% and large underestimations were 5% of cases. Across Europe about 12% of freshwater network was estimated to be failing good quality due to excessive BOD concentrations (>5 mg O(2)/L). Dominant sources of BOD to freshwaters and seas were point sources and emissions from intensive livestock systems. Comparison with previous assessments confirms a decline of BOD pollution since the introduction of EU legislation regulating water pollution.
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spelling pubmed-64510402019-05-20 Predicting biochemical oxygen demand in European freshwater bodies Vigiak, Olga Grizzetti, Bruna Udias-Moinelo, Angel Zanni, Michela Dorati, Chiara Bouraoui, Fayçal Pistocchi, Alberto Sci Total Environ Article Biochemical Oxygen Demand (BOD) is an indicator of organic pollution in freshwater bodies correlated to microbiological contamination. High BOD concentrations reduce oxygen availability, degrade aquatic habitats and biodiversity, and impair water use. High BOD loadings to freshwater systems are mainly coming from anthropogenic sources, comprising domestic and livestock waste, industrial emissions, and combined sewer overflows. We developed a conceptual model (GREEN(+)(BOD)) to assess mean annual current organic pollution (BOD fluxes) across Europe. The model was informed with the latest available European datasets of domestic and industrial emissions, population and livestock densities. Model parameters were calibrated using 2008–2012 mean annual BOD concentrations measured in 2157 European monitoring stations, and validated with other 1134 stations. The most sensitive model parameters were abatement of BOD by secondary treatment and the BOD decay exponent of travel time. The mean BOD concentrations measured in monitored stations was 2.10 mg O(2)/L and predicted concentrations were 2.54 mg O(2)/L; the 90th percentile of monitored BOD concentration was 3.51 mg O(2)/L while the predicted one was 4.76 mg O(2)/L. The model could correctly classify reaches for BOD concentrations classes, from high to poor quality, in 69% of cases. High overestimations (incorrect classification by 2 or more classes) were 2% and large underestimations were 5% of cases. Across Europe about 12% of freshwater network was estimated to be failing good quality due to excessive BOD concentrations (>5 mg O(2)/L). Dominant sources of BOD to freshwaters and seas were point sources and emissions from intensive livestock systems. Comparison with previous assessments confirms a decline of BOD pollution since the introduction of EU legislation regulating water pollution. Elsevier 2019-05-20 /pmc/articles/PMC6451040/ /pubmed/30970475 http://dx.doi.org/10.1016/j.scitotenv.2019.02.252 Text en © 2019 The Authors http://creativecommons.org/licenses/by/4.0/ This is an open access article under the CC BY license (http://creativecommons.org/licenses/by/4.0/).
spellingShingle Article
Vigiak, Olga
Grizzetti, Bruna
Udias-Moinelo, Angel
Zanni, Michela
Dorati, Chiara
Bouraoui, Fayçal
Pistocchi, Alberto
Predicting biochemical oxygen demand in European freshwater bodies
title Predicting biochemical oxygen demand in European freshwater bodies
title_full Predicting biochemical oxygen demand in European freshwater bodies
title_fullStr Predicting biochemical oxygen demand in European freshwater bodies
title_full_unstemmed Predicting biochemical oxygen demand in European freshwater bodies
title_short Predicting biochemical oxygen demand in European freshwater bodies
title_sort predicting biochemical oxygen demand in european freshwater bodies
topic Article
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6451040/
https://www.ncbi.nlm.nih.gov/pubmed/30970475
http://dx.doi.org/10.1016/j.scitotenv.2019.02.252
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