Elsevier

Marine Chemistry

Volumes 130–131, 20 February 2012, Pages 1-11
Marine Chemistry

Tidal cycling of mercury and methylmercury between sediments and water column in the Venice Lagoon (Italy)

https://doi.org/10.1016/j.marchem.2011.12.003Get rights and content

Abstract

The sediment of Venice Lagoon regularly undergoes complex redistribution due to tidal forcing, which affects the cycling of contaminants such as mercury (Hg) between the sediment and the water column. We examined the distribution of total Hg (THg) and monomethylmercury (MMHg) in the water column, sediment and pore-water at two sites: VE1 (located in a depositional area adjacent to salt marshes) and VE2 corresponding to a moderately erosive, open area. We obtained instantaneous (using cores and micro-needle samplers) and time-integrated (using peepers) concentrations of the two mercury species in both dissolved and particulate forms. THg and MMHg concentrations were higher in the sediments at site VE1 (621.9 ± 213.7 ng g 1 and 1.25 ± 0.63 ng g 1 for THg and MMHg, respectively) than in those of the site VE2 (386.9 ± 92.7 ng g 1 and 0.53 ± 0.30 ng g 1). Hg concentrations in sediments were positively correlated with silts and organic matter content. Over two tidal cycles, the concentrations of THg and MMHg varied with the evolution of the tides. During the tidal flooding, both THg and MMHg peaked at the sediment–water interface and a moderate increase of dissolved MMHg was also observed in the water column. These fluctuations were observed during both tides and are suggestively related to advection of mercury species from surficial sediment pore-water to the water column and to desorption from suspended particles. The short-term increase in MMHg concentrations can result from in situ production, release from organic matter degradation, or from oxidative dissolution of redox-sensitive sulfide minerals and iron oxide reduction by micro-organisms; the two latter mechanisms being favored by redox oscillations in the surface sediment layers due to the tidal forcing. The decrease of both dissolved THg and MMHg concentrations at the sediment–water interface after high tide was attributed to a rapid adsorption onto particles. THg concentrations on suspended particles showed little variations during the tidal cycle with a minor peak at tide maximum, while MMHg concentrations on suspended particles slightly increased during ebb tide. MMHg concentrations on suspended particles were double than those in surface sediments, suggesting that tidal flushing may enhance dispersal of particle bound MMHg throughout the lagoon.

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

References (78)

  • J. Cheng et al.

    Assessing noxious effects of dietary exposure to methylmercury, PCBs and Se coexisting in environmentally contaminated rice in male mice

    Environ. Int.

    (2009)
  • M. Coquery et al.

    Speciation and sorption of mercury in two macro-tidal estuaries

    Mar. Chem.

    (1997)
  • S. Covelli et al.

    Benthic fluxes of mercury species in a lagoon environment (Grado Lagoon, Northern Adriatic Sea, Italy)

    Appl. Geochem.

    (2008)
  • S. Degetto et al.

    Critical analysis of radiochemical methodologies for the assessment of sediment pollution and dynamics in the lagoon of Venice (Italy)

    Environ. Int.

    (2005)
  • C. Domènech et al.

    Oxidative dissolution of pyritic sludge from the Aznalcóllar mine (SW Spain)

    Chem. Geol.

    (2002)
  • S. Guédron et al.

    Weathering versus atmospheric contributions to mercury concentrations in French Guiana soils

    Appl. Geochem.

    (2006)
  • S. Guédron et al.

    Mercury speciation in a tropical soil association; Consequence of gold mining on Hg distribution in French Guiana

    Geoderma

    (2009)
  • S. Guédron et al.

    Methylmercury in tailings ponds of Amazonian gold mines (French Guiana): field observations and an experimental flocculation method for in situ remediation

    Appl. Geochem.

    (2011)
  • S. Han et al.

    Sulfide and iron control on mercury speciation in anoxic estuarine sediment slurries

    Mar. Chem.

    (2008)
  • H. Hintelmann et al.

    Application of multiple stable mercury isotopes to determine the adsorption and desorption dynamics of Hg(II) and MeHg to sediments

    Mar. Chem.

    (2004)
  • D. Jezequel et al.

    Two-dimensional determination of dissolved iron and sulfur species in marine sediment pore-waters by thin-film based imaging. Thau lagoon (France)

    Estuarine Coastal Shelf Sci.

    (2007)
  • B. Lewis et al.

    Short-term and interannual variability of redox-sensitive chemical parameters in hypoxic/anoxic bottom waters of the Chesapeake Bay

    Mar. Chem.

    (2007)
  • J.F. Lopes et al.

    Influence of tides and river inputs on suspended sediment transport in the Ria de Aveiro lagoon, Portugal

    Phys. Chem. Earth Part B

    (2001)
  • E. Molinaroli et al.

    Relationships between hydrodynamic parameters and grain size in two contrasting transitional environments: the Lagoons of Venice and Cabras, Italy

    Sedim. Geol.

    (2009)
  • C.O. Moses et al.

    Pyrite oxidation at circumneutral pH

    Geochim. Cosmochim. Acta

    (1991)
  • B. Muresan et al.

    Monomethylmercury sources in a tropical artificial reservoir

    Appl. Geochem.

    (2008)
  • J.L. Parker et al.

    Preservation and storage techniques for low-level aqueous mercury speciation

    Sci. Total. Environ.

    (2005)
  • E. Precht et al.

    Rapid wave-driven advective pore water exchange in a permeable coastal sediment

    J. Sea Res.

    (2004)
  • F. Roos-Barraclough et al.

    An analytical protocol for determination of total mercury concentration in solid peat samples

    Sci. Total Environ.

    (2002)
  • S.E. Rothenberg et al.

    Mercury cycling in surface water, pore water and sediments of Mugu Lagoon, CA, USA

    Environ. Pollut.

    (2008)
  • J. Santos-Echeandía et al.

    Effect of tidal flooding on metal distribution in pore waters of marsh sediments and its transport to water column (Tagus estuary, Portugal)

    Mar. Environ. Res.

    (2010)
  • J. Schäfer et al.

    Mercury methylation in the sediments of a macrotidal estuary (Gironde Estuary, south-west France)

    Estuarine Coastal Shelf Sci.

    (2010)
  • A. Sfriso et al.

    Role of macroalgal biomass and clam fishing on spatial and temporal changes in N and P sedimentary pools in the central part of the Venice lagoon

    Oceanol. Acta

    (2003)
  • V. Sirot et al.

    Methylmercury exposure assessment using dietary and biomarker data among frequent seafood consumers in France: CALIPSO study

    Environ. Res.

    (2008)
  • H. Tamura et al.

    Spectrophotometric determination of iron(II) with 1,10-phenanthroline in the presence of large amounts of iron(III)

    Talanta

    (1974)
  • D. van Proosdij et al.

    Controls on spatial patterns of sediment deposition across a macro-tidal salt marsh surface over single tidal cycles

    Estuarine Coastal Shelf Sci.

    (2006)
  • B. Wheatley et al.

    Methylmercury and the health of indigenous peoples: a risk management challenge for physical and social sciences and for public health policy

    Sci. Total Environ.

    (2000)
  • R. Zonta et al.

    Sediment chemical contamination of a shallow water area close to the industrial zone of Porto Marghera (Venice Lagoon, Italy)

    Mar. Pollut. Bull.

    (2007)
  • A. Basu et al.

    Toxic metals in Venice lagoon sediments: model, observations, and possible removal

    Environ. Geol.

    (1994)
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