Tidal cycling of mercury and methylmercury between sediments and water column in the Venice Lagoon (Italy)
Highlights
► Mercury and methylmercury were investigated during two tidal cycles in Venice lagoon. ► Both species peaked at the sediment-water interface at late tidal flooding. ► Fluctuations were attributed to advection from sediment to water column and to desorption. ► Suspended particles may enhance dispersal of methylmercury during tidal flushing. ► Tide-driven mobilization of methylmercury is an important factor controlling mercury cycling.
Introduction
The Venice Lagoon is a complex and dynamic system where notable exchanges of materials and energy between the main land (continent) and the Adriatic Sea occur (Ravera, 2000). The lagoon is shallow (average water depth 1.2 m) and consists of intertidal or submerged mudflats, salt marshes and man-made navigation canals (Molinaroli et al., 2009, Pranovi et al., 2004). The sedimentary dynamic strongly depends on the tidal flushing, leading to highly heterogeneous deposition and erosion rates between canals and salt-marshes areas. Sediment dynamics is also influenced by human activities related to construction, tourism and clam harvesting activities (Degetto et al., 2005).
Venice Lagoon has been recognized as a mercury (Hg) contaminated area (Bloom et al., 2004a, Pavoni et al., 1992). The two chlor-alkali plants of the industrial area of Porto Marghera were identified as the main contributors to the contamination of the lagoon (Bellucci et al., 2002, Bloom et al., 2004b, Zonta et al., 2007). Until recently, antifouling paints used near the town of Chioggia (in the southern part of the lagoon) were another local source of mercury (Berto et al., 2006).
Many authors described the Venice Lagoon as a ‘biological reactor’, because of considerable nutrient input, shallow and seasonally warm water, and extensive wetlands. Bloom et al. (2004b) described it as a “methyl Hg incubator”, where even small inputs of inorganic Hg could result in high levels of monomethylmercury (MMHg) production; the most toxic and bioaccumulating species of Hg (Cheng et al., 2009, Sirot et al., 2008, Wheatley and Wheatley, 2000). However, only few studies performed in the Venice Lagoon did consider the influence of tides on the production and release of MMHg from sediments to the water column.
In a study conducted in the Canale SS Apostoli (City of Venice), Bloom et al. (2004b) showed that MMHg concentrations in unfiltered water varied only slightly during a tidal cycle, while total Hg (THg) was inversely correlated with tide height. In addition, the dynamics of total suspended solids (TSS) associated with tidal flushing was suggested as the vehicle for Hg dispersal from the sources to the whole of Venice's Lagoon (Berto et al., 2006) and may play an important role in the adsorption of dissolved Hg species produced in the surficial sediments (Bloom et al., 2004b).
In the present study, we considered the influence of the tidal flushing on the short term THg and MMHg concentration changes in the water column and sediment pore water. First, we determined the THg and MMHg concentrations in sediments and pore water in two different areas typical of the sedimentary dynamic of the lagoon, (i.e., a remote site adjacent to salt marshes and open site close to the Burano canal bordering a marshy area). We also used various tools to get instantaneous and time integrated information on the dissolved and particulate THg and MMHg distribution in the water column and the sediment pore waters. Second, we followed temporal variations in particulate and dissolved THg and MMHg concentrations in water column and at the sediment–water interface during two tidal cycles to evaluate the exchanges between the surficial sediments and the water column for both Hg species.
Section snippets
Environmental settings and sampling strategy
Two sites located in the northern part of the Venice Lagoon were sampled during two campaigns: October 30th, 2008 to November 4th, 2008 and September 8th to 18th, 2009. These sites were chosen because they were located in a fairly Hg contaminated part of the lagoon (Bloom et al., 2004b, Zonta et al., 2007). The first site (VE1 — 45°30′04.56″N, 12°25′04.31″E) was representative of a low-energy, depositional area and was in a subtidal area adjacent to the salt marshes around Torcello Island,
Sedimentological and geochemical parameters of sediments
At both sampling sites and considering 2008 and 2009 cores, the percentage clay fraction (< 2 μm) never exceeded 1%, indicating winnowing of the finest sediment fraction because of tide-driven and anthropogenic re-suspension of surface sediments. However, the low amount of clay measured in sediments cores could also result (at least partly) from some known limitations of the laser counting technique (Beuselinck et al., 1998, Goossens, 2008). Whichever the case, the selected sites are
Availability of mercury for methylation in Venice Lagoon sediments
The distribution of THg in solid sediments points to THg inputs from the continental side of the lagoon. This observation is consistent with earlier findings that evidenced a decreasing THg gradient from the inner border of the Lagoon toward the sea inlets. This contamination pattern reflects the increasing distance from the source of Hg contamination (i.e., Marghera industrial site) and the increased tidal erosion and grain size distribution due to the increased proportion of carbonates in
Conclusions
In this study, we confirmed that Hg methylation is very active in two areas of the Venice Lagoon with contrasting sedimentation characteristics. Hg methylation in sediments was restricted to the upper eight centimeters in a moderately erosive area (site VE2) and reached 22 cm in a low-energy, depositional area bordering salt marshes (site VE1). MMHg pore water profiles and time series showed that the iron reduction zone is the most important source of MMHg for the water column, although higher
Acknowledgments
This study was supported by the Swiss National Science Foundation (grant no. 200020-117942 and no. IZKOZ2_136134/1). We are greatly indebted to the boat pilot Loris Dametto (CNR-ISMAR) and Philippe Arpagaus (Institut F.-A. Forel) for their dedication during sampling campaigns. We also thank Dr. Davide Tagliapietra (CNR-ISMAR) for his help in field work and advice on the selection of sampling sites, Dr. Andrea Pesce (CNR-ISMAR) for providing logistical support for laboratory work, Dr. Daniel
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