Deciphering As and Cu cycling in sediment pore waters in a large marina (Port Camargue, southern France) using a multi-tracer (Fe, Mn, U, Mo) approach. (March 2016)

• Record Type: Journal Article
• Authors: Briant, Nicolas; Elbaz-Poulichet, Françoise; Freydier, Rémi; Bancon-Montigny, Chrystelle; Delpoux, Sophie
• Is Part Of: Applied geochemistry. Volume 66(2016:Mar.)
• Page Start: 242
• Page End: 249
• Publication Date: 2016-03
• Subjects: Pore water -- Copper -- Arsenic -- Diagenesis -- Redox tracers; Environmental geochemistry -- Periodicals; Water chemistry -- Periodicals; Geochemistry -- Social aspects -- Periodicals; Geochemistry -- Periodicals; 551.9
• DOI: 10.1016/j.apgeochem.2016.01.001
• Languages: English
• ISSNs: 0883-2927

Abstract

Abstract: The sediments of the Port Camargue marina (South of France) are highly polluted by Cu and As (Briant et al., 2013). The dynamics of these pollutants in pore waters was investigated using redox tracers (sulfides, Fe, Mn, U, Mo) to better constrain the redox conditions. In summer, pore water profiles showed a steep redox gradient in the top 24 cm with the reduction of Fe and Mn oxy-hydroxides at the sediment water interface (SWI) and of sulfate immediately below. Below a depth of 24 cm, the Fe, Mn, Mo and U profiles in pore waters reflected Fe and Mn reducing conditions and, unlike in the overlying levels, sulfidic conditions were not observed. This unusual redox zonation was attributed to the occurrence of two distinct sediment layers: an upper layer comprising muddy organic-rich sediments underlain by a layer of relatively sandy and organic-poor sediments. The sandy sediments were in place before the building of the marina, whereas the muddy layer was deposited later. In the muddy layer, large quantities of Fe and Mo were removed in summer linked to the formation of insoluble sulfide phases. Mn, which can adsorb on Fe-sulfides or precipitate with carbonates, was also removed from pore waters. Uranium was removed probably through reduction and adsorption onto particles. In winter, in the absence of detectable pore water sulfides, removal of Mo was moderate compared to summer. Cu was released into solution at the sediment water interface but was efficiently trapped by the muddy layer, probably by precipitation with sulfides. Due to efficient trapping, today the Cu sediment profile reflects the increase in its use as a biocide in antifouling paints over the last 40 years. In the sandy layer, Fe, Mn, Mo and As were released into solution and diffused toward the top of the profile. They precipitated at the boundary between the muddy and sandy layers. This precipitation accounts for the high (75 μg g −1 ) As concentrations measured in the sediments at a depth of 24 cm. Highlights: The mobility of As and Cu was studied in pore waters of strongly polluted sediments of a Mediterranean marina. The sediments comprised a sandy layer predating the building of the harbor and a muddy layer, which deposited later. Cu was released into solution at the sediment water interface but was efficiently trapped by the muddy layer. As was released into solution in the sandy layers and accumulated at the boundary between the muddy and sandy layers.