Monitoring induced denitrification during managed aquifer recharge in an infiltration pond

Managed aquifer recharge (MAR) is a well-known technique for improving water quality and increasing groundwater resources. Denitrification (i.e. removal of nitrate) can be enhanced during MAR by coupling an artificial recharge pond with a permeable reactive layer (PRL). In this study, we examined th...

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Detalles Bibliográficos
Autores: Grau Martinez, Alba, Folch Sancho, Albert|||0000-0002-8490-1038, Torrentó, Clara, Valhondo González, Cristina|||0000-0002-4009-5476, Barba Ferrer, Maria del Carme|||0000-0001-7513-3754, Domènech Ortí, Cristina, Soler Gil, Albert, Otero, Neus
Tipo de recurso: artículo
Fecha de publicación:2018
País:España
Institución:Universitat Politècnica de Catalunya (UPC)
Repositorio:UPCommons. Portal del coneixement obert de la UPC
Idioma:inglés
OAI Identifier:oai:upcommons.upc.edu:2117/119399
Acceso en línea:https://hdl.handle.net/2117/119399
https://dx.doi.org/10.1016/j.jhydrol.2018.03.044
Access Level:acceso abierto
Palabra clave:Denitrification
Groundwater recharge
Nitrate reduction
Multi-isotope analysis
Reactive layer
Mixing zone
Artificial recharge
Field and laboratory experiments
Aigües subterrànies -- Recàrrega artificial
Àrees temàtiques de la UPC::Enginyeria civil::Geologia::Hidrologia subterrània
Descripción
Sumario:Managed aquifer recharge (MAR) is a well-known technique for improving water quality and increasing groundwater resources. Denitrification (i.e. removal of nitrate) can be enhanced during MAR by coupling an artificial recharge pond with a permeable reactive layer (PRL). In this study, we examined the suitability of a multi-isotope approach for assessing the long-term effectiveness of enhancing denitrification in a PRL containing vegetal compost. Batch laboratory experiments confirmed that the PRL was still able to enhance denitrification two years after its installation in the infiltration pond. At the field scale, changes in redox indicators along a flow path and below the MAR-PRL system were monitored over 21¿months during recharge and non-recharge periods. Results showed that the PRL was still releasing non-purgeable dissolved organic carbon five years after its installation. Nitrate concentration coupled with isotopic data collected from the piezometer network at the MAR system indicated that denitrification was occurring in the saturated zone immediately beneath the infiltration pond, where recharged water and native groundwater mix. Furthermore, longer operational periods of the MAR-PRL system increased denitrification extent. Multi-isotope analyses are therefore proved to be useful tools in identifying and quantifying denitrification in MAR-PRL systems.