title: Impact of solid waste disposal on nutrient dynamics in a sandy catchment.
abstract: Groundwaters impacted by mature landfill leachate are generally enriched in ammonium. In order to assess the dynamics of ammonium exchanges between leachates and the water system inside a sandy permeable catchment we measured ammonium, nitrate and chloride concentrations in the stream and in sediment pore waters of the streambed of a landfill impacted aquifer. Geophysical investigation methods complemented the biogeochemical survey. The studied zone is a 23 km(2) catchment located in a coastal lagoon area sensitive to eutrophication risk. Ammonium concentrations in the river were up to 800 micromol l(-1) during low water period in summer. Three surveys of the river chemistry showed a regular increase in ammonium, nitrate and chloride concentrations along a 1 km section of the watercourse, downstream the landfill, implying that the leachate plume exfiltrates along this section. Sediment cores collected within this section showed all an increase in ammonium concentrations with depth in pore waters as a consequence of the landfill leachate dispersion, as attested by a simultaneous increase in chloride concentrations. Nitrate enrichment in the river water was due to nitrification of ammonium at the interface between groundwater and streamwater. The apparent nitrification rate obtained was within values reported for turbid estuaries, although the river contained very little suspended particulate matter. Actually, pore water chemistry suggests that nitrification occurred for the most part in subsurface permeable sediments, rather than in stream water. The overall topographic, hydrological, geochemical, and geoelectrical data set permit to estimate the extension of the chloride and ammonium plume. The estimation of the apparent ammonium plume velocity is 23 m year(-1) whereas the chloride plume velocity should be 50 m year(-1). The river is the outlet of the impacted groundwaters. Considering that the input of ammonium from the landfill is balanced by the present day output via the river, the residence time of ammonium in the aquifer is between 7 and 18 years.
authors.affiliation: Université de Bordeaux 1, CNRS UMR 5805 Environnements Paléoenvironnements Océaniques (EPOC), Avenue des Facultés, 33405 Talence, France.
authors.forename: Mathieu
authors.initials: M
authors.lastname: Canton
authors.forename: Pierre
authors.initials: P
authors.lastname: Anschutz
authors.forename: Véronique
authors.initials: V
authors.lastname: Naudet
authors.forename: Nathalie
authors.initials: N
authors.lastname: Molnar
authors.forename: Aurélia
authors.initials: A
authors.lastname: Mouret
authors.forename: Michel
authors.initials: M
authors.lastname: Franceschi
authors.forename: Fabien
authors.initials: F
authors.lastname: Naessens
authors.forename: Dominique
authors.initials: D
authors.lastname: Poirier
mesh_terms: D002712:Chlorides / Q000032:analysis; D004784:Environmental Monitoring; D005602:France; D019015:Geologic Sediments / Q000737:chemistry; D009566:Nitrates / Q000032:analysis; D052638:Particulate Matter / Q000032:analysis; D000644:Quaternary Ammonium Compounds / Q000032:analysis; D012037:Refuse Disposal; D045483:Rivers / Q000737:chemistry*; D014874:Water Pollutants, Chemical / Q000032:analysis*; D014881:Water Supply
chemical_list: D002712:Chlorides; D009566:Nitrates; D052638:Particulate Matter; D000644:Quaternary Ammonium Compounds; D014874:Water Pollutants, Chemical