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Non-steady state behaviour of heavy metals in contaminated freshwater sediments
Affiliation:1. State Key Laboratory of Resources and Environmental Information System, Institute of Geographical Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing 100101, China;2. State Key Laboratory of Geological Processes and Mineral Resources(GPMR), Faculty of Earth Sciences, China University of Geosciences, Wuhan, 430074, China;3. University of Chinese Academy of Sciences, Beijing 100049, China;1. Laboratoire de Planétologie et Géodynamique Bio-Indicateur Actuels et Fossiles, LPG-BIAF, CNRS - UMR 6112, Université d''Angers UFR Sciences, CNRS, 2 Boulevard Lavoisier, 49000 Angers, France;2. Laboratoire Littoral Environnement Télédétection Géomatique, LETG, CNRS – UMR 6554, Université de Nantes, Campus Tertre, BP 81227 44312 Nantes Cedex 3, France;3. LUSAC, EA 4253, Normandie Univ, Unicaen, 50100 Cherbourg, France;4. Cnam/Intechmer, 50100 Cherbourg, France;5. Laboratoire de recherche en Hydrodynamique, Énergétique et Environnement Atmosphérique, LHEEA, CNRS – UMR 6598, École Centrale de Nantes - SEM-REV, 1 Rue de la Noë, BP 92101 44321 Nantes Cedex 3, France
Abstract:The behaviour of heavy metals has been investigated in contaminated sediments of the river Meuse, The Netherlands. Due to temporal changes in temperature and degradability of organic matter, the depths of the redox boundaries fluctuate. This contributes to a non-steady state. As a result of oxidation processes, a distinct peak in heavy metal concentrations in pore water is measured at the sediment-water interface. Because the studied anoxic sediments contain low levels of sulphide, other solid phases are expected to be of importance in the binding of heavy metals. Furthermore, heterogeneity of the sediment and complexation with dissolved organic compounds may result in supersaturation of the anoxic pore waters with respect to discrete heavy metal sulphides, thus influencing heavy metal mobility. Calculations using concentration gradients of heavy metals indicate that diffusive fluxes between the sediment and the surface water contribute to concentrations in the surface water, although significant effects may be confined to specific locations.
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