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G. PEC) at many sites during low waters and we recommand specific water monitoring during this period in order to evaluate ecotoxicological risk at the watershed scale. 9 Dissolved and particulate Cd fluxes The instantaneous (daily) dissolved and particulate Cd fluxes were calculated for each sampling site (Table 2). The CdD levels significantly increased between the CHA3 and the CHA4 sites, inducing a clear increase in CdD flux that was not proportional to water discharge, suggesting an additional point source within this section (Figure 7A).
1981). Metal Pollution in the Aquatic Environment. New York, Springer-Verlag, 486 pp. , Noel, J. & Truquet, I. (1991). Distribution of Cd and Hg in the Bay of Marennes-Oleron, Oceanologica Acta, 14, pp. 559-568. Goulletquer, P. & Heral, M. (1997). L. Mackenzie, Jr. G. , A. L. Hobart (Eds). The history, present condition and future of the molluscan fisheries of North and Central America and Europe Volume 3, Europe. NOAA Technical Report NMFS, 129, pp. 137-164. J. (1991). A primer on sediment-trace element chemistry.
The sum of river discharges in all segments represents the estimated instantaneous water discharge of the river section. The uncertainty on the measurements was estimated between 5 and 10% (Regional Environment Agency- DIREN). 3 Water sampling The general physical and chemical parameters (pH, conductivity, Eh and O2) were measured in-situ at each site. Temperature and conductivity were measured using a TetraCon 96® probe (PROFILINE, WTW). Oxygen saturation was determined by an ISY 52® probe. Determinations of pH and Eh were performed using a Sentix® 41 probe (PROFILINE, WTW).