• Aucun résultat trouvé

Colloid Characterization at the Sediment-water Interface of Vidy Bay, Lake Geneva performance and the SAGRAVE team who provided and operated the platform from which the dives were carried out. We also thank Ulrich Lemmin and Jean-Denis Bourquin for project coordination. The service of Mikhail Kranoperov (Russian Honorary Consulate) as liaison is greatly appreciated. Agathe Martignier and Frédéric Loosli for their expertise, along with Elena Gascon Diez and Mathieu Masson for their assistance in sampling.

References

Baker, J. E., Eisenreich, S. J., Eadie, B. J. (1991). Sediment trap fluxes and benthic recycling of organic carbon, polycyclic aromatic hydrocarbons, and polychlorobiphenyl congeners in Lake Superior. Environmental Science & Technology 25 (3), 500–509.

Bell, G. L., Eadie, B. J. (1983). Variations in the distribution of suspended particles during an upwelling event in Lake Michigan in 1980. Journal of Great Lakes Research 9 (4), 559–567.

Buffle, J., Chalmers, R. A., Midgley, D. (1991). Complexation Reactions in Aquatic Systems Analytical Approach. Chichester: Prentice Hall.

Buffle, J., Wilkinson, K. J., Joz-Roland, A. (1997). Different roles of pedogenic fulvic acids and aquagenic biopolymers on colloid aggregation and stability in freshwaters. Limnol-ogy and Oceanography 42, 1714–1724.

Buffle, J., Wilkinson, K. J., Stoll, S., Filella, M., Zhang, J. W. (1998). A Generalized De-scription of Aquatic Colloidal Interactions: The Three-colloidal Component Approach.

Environmental Science & Technology 32 (19), 2887–2899.

Chen, C.-S., Anaya, J. M., Zhang, S., Spurgin, J., Chuang, C.-Y., Xu, C., Miao, A.-J., Chen, E. Y.-T., Schwehr, K. A., Jiang, Y., Quigg, A., Santschi, P. H., Chin, W.-C. (2011).

Effects of engineered nanoparticles on the assembly of exopolymeric substances from phytoplankton. PLOS ONE 6 (7), e21865.

Chen, K. L., Mylon, S. E., Elimelech, M. (2006). Aggregation kinetics of alginate-coated hematite nanoparticles in monovalent and divalent electrolytes. Environmental Science

& Technology 40 (5), 1516–1523.

Chin, W.-C., Orellana, M. V., Verdugo, P. (1998). Spontaneous assembly of marine dis-solved organic matter into polymer gels. Nature 391 (6667), 568–572.

Crawford, R. J., Harding, I. H., Mainwaring, D. E. (1996). The zeta potential of iron and chromium hydrous oxides during adsorption and coprecipitation of aqueous heavy met-als. Journal of Colloid and Interface Science 181 (2), 561–570.

Davis, J. A., Gloor, R. (1981). Adsorption of dissolved organics in lake water by aluminum oxide. Effect of molecular weight. Environmental Science & Technology 15 (10), 1223–

1229.

44

References Ding, Y. X., Chin, W.-C., Rodriguez, A., Hung, C.-C., Santschi, P. H., Verdugo, P. (2008).

Amphiphilic exopolymers from Sagittula stellata induce DOM self-assembly and for-mation of marine microgels. Marine Chemistry 112 (1-2), 11–19.

Ding, Y. X., Hung, C.-C., Santschi, P. H., Verdugo, P., Chin, W.-C. (2009). Spontaneous Assembly of Exopolymers from Phytoplankton. Terrestrial, Atmospheric and Oceanic Sciences 20 (5), 741–747.

Elimelech, M., Nagai, M., Ko, C.-H., Ryan, J. N. (2000). Relative Insignificance of Min-eral Grain Zeta Potential to Colloid Transport in Geochemically Heterogeneous Porous Media. Environmental Science & Technology 34 (11), 2143–2148.

Everett, D. H., Koopal, L. K. (1972). Manual of symbols and terminology for physicochem-ical quantities and units. Appendix II: Definition, terminology and symbols in colloid and surface chemistry, Part I. International Union of Pure and Applied Chemistry.

Gascon Diez, E., Garcia Bravo, A., Porta, N., Masson, M., Graham, N. D., Stoll, S., Akht-man, Y., Amouroux, D., Loizeau, J.-L. (2013). Influence of a wastewater treatment plant on mercury contamination and sediment characteristics in Vidy Bay (Lake Geneva, Switzerland). Aquatic Sciences 76 (S1), 21–32.

Girardclos, S., Hilbe, M., Corella, J. P., Loizeau, J.-L., Kremer, K., DelSontro, T., Aran-tegui, A., Moscariello, A., Arlaud, F., Akhtman, Y., Anselmetti, F., Lemmin, U. (2012).

Searching the Rhone delta channel in Lake Geneva since François-Alphonse Forel.

Archives des Sciences, 103–118.

Girardclos, S., Schmidt, O. T., Sturm, M., Ariztegui, D., Pugin, A., Anselmetti, F. (2007).

The 1996 AD delta collapse and large turbidite in Lake Brienz. Marine Geology 241 (1-4), 137–154.

Haller, L., Amedegnato, E., Poté, J., Wildi, W. (2009). Influence of Freshwater Sediment Characteristics on Persistence of Fecal Indicator Bacteria. Water, Air, and Soil Pollution 203 (1-4), 217–227.

Herrero, A., Bateman, A., Medina, V. (2013). Sediment resuspension due to density currents caused by a temperature difference: application to the Flix reservoir (Spain). Journal of Hydraulic Research 51 (1), 76–91.

Jørgensen, B. B., Revsbech, N. P. (1983). Colorless Sulfur Bacteria, Beggiatoa spp. and Thiovulumspp., in O2and H2S Microgradients. Applied and Environmental Microbiol-ogy 45 (4), 1261–1270.

Colloid Characterization at the Sediment-water Interface of Vidy Bay, Lake Geneva Loizeau, J.-L., Rozé, S., Peytremann, C., Monna, F., Dominik, J. (2003). Mapping sediment

accumulation rate by using volume magnetic susceptibility core correlation in a contam-inated bay (Lake Geneva, Switzerland). Eclogae Geologicae Helvetiae 96, S73–S79.

Loosli, F., Stoll, S. (2012). Adsorption of TiO2 Nanoparticles at the Surface of Micron-Sized Latex Particles. pH and Concentration Effects on Suspension Stability. Journal of Colloid Science and Biotechnology 1 (1), 113–121.

Masson, M., Tercier-Waeber, M.-L. (2013). Trace metal speciation at the sediment–water in-terface of Vidy Bay: influence of contrasting sediment characteristics. Aquatic Sciences 76 (S1), 47–58.

Ohshima, H. (1995). Electrophoretic mobility of soft particles. Colloids and Surfaces A:

Physicochemical and Engineering Aspects 103 (3), 249–255.

Perret, D., Gaillard, J.-F., Dominik, J., Atteia, O. (2000). The Diversity of Natural Hydrous Iron Oxides. Environmental Science & Technology 34 (17), 3540–3546.

Poté, J., Goldscheider, N., Haller, L., Zopfi, J., Khajehnouri, F., Wildi, W. (2008). Origin and spatial–temporal distribution of faecal bacteria in a bay of Lake Geneva, Switzerland.

Environmental Monitoring and Assessment 154 (1-4), 337–348.

Precht, E., Huettel, M. (2004). Rapid wave-driven advective pore water exchange in a per-meable coastal sediment. Journal of Sea Research 51 (2), 93–107.

Rigaud, S., Radakovitch, O., Couture, R.-M., Deflandre, B., Garnier, C., Garnier, J. M.

(2013). Mobility and fluxes of trace elements and nutrients at the sediment–water in-terface of a lagoon under contrasting water column oxygenation conditions. Applied Geochemistry 31 (C), 35–51.

Rossé, P., Loizeau, J.-L. (2003). Use of single particle counters for the determination of the number and size distribution of colloids in natural surface waters. Colloids and Surfaces A: Physicochemical and Engineering Aspects 217, 109–120.

Santos-Echeandía, J., Vale, C., Caetano, M., Pereira, P., Prego, R. (2010). Effect of tidal flooding on metal distribution in pore waters of marsh sediments and its transport to water column (Tagus estuary, Portugal). Marine Environmental Research 70 (5), 358–

367.

Sauvain, L., Bueche, M., Junier, T., Masson, M., Wunderlin, T., Kohler-Milleret, R., Gascon Diez, E., Loizeau, J.-L., Tercier-Waeber, M.-L., Junier, P. (2013). Bacterial communi-ties in trace metal contaminated lake sediments are dominated by endospore-forming bacteria. Aquatic Sciences 76 (S1), 33–46.

Sayama, M., Risgaard-Petersen, N., Nielsen, L. P., Fossing, H., Christensen, P. B. (2005).

Impact of bacterial NO3 transport on sediment biogeochemistry. Applied and Environ-mental Microbiology 71 (11), 7575–7577.

Schnellmann, M., Anselmetti, F., Giardini, D., McKenzie, J. A. (2007). 15,000 Years of mass-movement history in Lake Lucerne: Implications for seismic and tsunami hazards.

Swiss Journal of Geosciences 99 (3), 409–428.

46

References Smith, D. C., Meinhard, S., Alldredge, A. L., Azam, F. (1992). Intense hydrolytic enzyme activity on marine aggregates and implications for rapid particle dissolution. Nature 359 (6391), 139–142.

Steinmann, P., Billen, T., Loizeau, J.-L., Dominik, J. (1999). Beryllium-7 as a tracer to study mechanisms and rates of metal scavenging from lake surface waters. Geochimica et Cosmochimica Acta 63 (11-12), 1621–1633.

Subramanian, S. B., Yan, S., Tyagi, R. D., Surampalli, R. Y. (2010). Extracellular polymeric substances (EPS) producing bacterial strains of municipal wastewater sludge: Isolation, molecular identification, EPS characterization and performance for sludge settling and dewatering. Water Research 44 (7), 2253–2266.

Tipping, E., Higgins, D. C. (1982). The effect of adsorbed humic substances on the colloid stability of haematite particles. Colloids and Surfaces 5 (2), 85–92.

Viana, P. Z., Yin, K., Rockne, K. J. (2012). Field Measurements and Modeling of Ebullition-Facilitated Flux of Heavy Metals and Polycyclic Aromatic Hydrocarbons from Sed-iments to the Water Column. Environmental Science & Technology 46 (21), 12046–

12054.

Walther, H. J. (1991). The Components of Aquatic Systems and their Ractivity. Complexa-tion ReacComplexa-tions in Aquatic Systems Analytical Approach. Chichester: Prentice Hall, 230–

230.

Wells, M. L. (1998). Marine colloids - A neglected dimension. Nature 391 (6667), 530–531.

Wessels, M., Bussmann, I., Schloemer, S., Schlüter, M., Böder, V. (2010). Distribution, mor-phology, and formation of pockmarks in Lake Constance, Germany. Limnology and Oceanography 55 (6), 2623–2633.

Yu, S., Chow, G. M. (2004). Carboxyl group (–CO2H) functionalized ferrimagnetic iron oxide nanoparticles for potential bio-applications. Journal of Materials Chemistry 14 (18), 2781–2786.

C HAPTER 3

D ISCRIMINATION B ETWEEN V ERTICAL AND L ATERAL S ED

-IMENTATION P ATHWAYS IN A C ONTAMINATED B AY

This chapter investigates the spatial and temporal sedimentation dynamics influencing Vidy Bay. These dynamics are studied to understand the sedimentation pathways in and around the bay and, in doing so, help suggest to the pathways of particle-bound contaminants.

This understanding is paramount when attempting to determine whether an accumulation around, or dispersal from, a point source is occurring and identifying the process of sediment focusing and contamiant accumulation.

Discrimination Between Vertical and Lateral Sedimentation Pathways in a Contaminated Bay

Discrimination Between Vertical and Lateral Sedimentation Pathways in a Contaminated Bay

Neil D. Graham1*, Janusz Dominik2, Jean-Luc Loizeau1

1Institute F.–A. Forel, Earth and Environmental Sciences Section, University of Geneva Route de Suisse 10, 1290 Versoix, GE, Switzerland

2Istituto di Scienze Marine – Consiglio Nazionale delle Ricerche, Arsenale – Tesa 104 Castello 2737/F, 30 122 Venezia, Italy

*Neil.Graham@unige.ch

An article of form similar to this chapter will be submitted for publishing.

50

3.1 Abstract

3.1 Abstract

Knowing the fate of particle-bound contaminants is important for mitigating potential en-vironmental, economic, and health impacts linked to these contaminants. Vidy Bay, Lake Geneva, Switzerland, is highly contaminated due to the outfall and overflow from the wastew-ater treatment plant of the City of Lausanne. This study investigated the spatial and temporal sedimentation dynamics influencing Vidy Bay to better understand particle-bound contam-inant pathways. The flux ratio of natural radionuclide tracers were used to quantify lateral advections and to estimate process-related residence times. To achieve this, a vertical sedi-mentation model, with a lateral component, was constructed using7Be/210Pbxsratios to dif-ferentiate between particle sources and calculate process-related and overall residence times related to the sedimentation processes of: adsorption and coagulation/aggregation, particle settling through the water column, and particle settling through the bottom boundary layer.

Results of the study indicated that: (i) sedimentation rates and lateral advections in-creased vertically with proximity to the sediment surface and laterally with proximity to shore, where the lateral component accounted for 48 % of collected sediments near the sedi-ment surface in the bay as compared to−2 % closer to the lake surface in the main basin, (ii) lateral inputs were greater during thermally unstratified conditions than during stratification, and (iii) overall annual mean residence times showed that both the process-related residence time in the bottom boundary layer and adsorption/coagulation in surface waters were dom-inant, while mean lacustrine seasonal residence times were predominantly controlled by coagulation/aggregation closer to shore and by particle settling through the water column at deeper sites. The proposed sediment component model provided refined process-related and overall residence times as compared to those previously published for Lake Geneva and similar systems. The overall annual residence time was found to be 53 d in the bay and 118 d in the adjacent main basin.