Norwegian Institute for Air Research
Netherlands Institute for Ecology
Tyndall Centre for Climate Change Research
Institute for Environmental Studies, Free University Amsterdam
University of Plymouth
Centre for Social and Economic Research on the Global Environment
Land-Ocean Interactions in the Coastal Zone
 


Contaminants: Budgets and Behaviours

Case Study 2 - Mercury in the Mediterranean

 
1. Introduction and background
 
Mercury occurs naturally as elemental mercury and as organic and inorganic species. A large fraction of mercury is strongly bound to sediments and organic matter, and thus unavailable to organisms. However, microorganisms can transfer inorganic mercury to methylmercury which is fat soluble and are able to pass cell membranes, accumulates in animals, and biomagnifies in the food web.

Scientists have found particularly high concentrations of mercury in the Mediterranean Basin. Marine animals found in the Mediterranean Basin have high mercury levels compared to similar species from most parts of the Atlantic because of the natural presence of mercury from volcanic activity. About half of world mercury resources are located in the Mediterranean area. Mining in the area has increased the release of mercury into the environment. The process of biomagnification in the Mediterranean Basin is evident (http://www.westonaprice.org/envtoxins/mercury.html). High levels of mercury are found in the Mediterranean tuna compared to similar species in most parts of the Atlantic, as well as in smaller species such as anchovy and sardines, and also in local marine birds and their eggs. An investigation of fishermen and their families in coastal villages on the north Tyrrhenian Sea found a correlation between the number of seafood meals and the mercury levels from hair samples.

The following document presents major findings of four ELOISE projects (MAMCS, MOE) and the MED-OCEANOR programme funded by the Italian National Research Council (CNR) to support part of field investigations of the MAMCS project. The projects provide major results of these projects on different patterns involved in the dynamics of atmospheric pollutants in the Marine Boundary Layer (MBL) of e.g. the Mediterranean Sea, chemical and physical mechanisms in the lower atmosphere and sea water, atmospheric transport and deposition as well as gaseous exchanges at the air–water interface with changing meteorological conditions, and sampling and analytical techniques used to determine ambient levels of trace contaminants in the air and water samples.

 
Projects Project Features
BEEP (IMPACTS) How biological markers may be used to determine the incidence of chemical contamination on marine organisms in monitoring programs

MAMCS (ELOISE)

The overall goal of the MAMCS project is to improve our understanding of the mechanisms which influence the dynamics of atmospheric mercury in the Mediterranean Sea region. MAMCS will also contribute to the improvement of policies and strategies for reduction of the risks associated with environmental pollution by mercury in EU member countries, particularly in Southern Europe . The Mediterranean Sea Region is characterized by a geological anomaly (it contains 65% of the world cinnabar (HgS) deposits). It also has higher seasonal temperature and levels of solar irradiation than areas previously modeled; factors which are believed to be behind many of the processes involved in the biogeochemical mercury cycle.
MOE (ELOISE) The general objective of MOE is to identify and quantify sources of atmospheric mercury (Hg) species focusing on production and fluxes of methylmercury (MeHg). The research addresses the relative importance of the atmospheric deposition of MeHg, in comparison to methylation/demethylation processes in terrestrial and aquatic ecosystems, in heavily impacted regions in Northern and Central Europe.
MERCYMS (ELOISE) The overall goal of MERCYMS is to fill the gaps firstly specificated and develop a Practical Working Tool (PWT) for a wide spectrum of users (i.e., policy makers, environmental planners) that would allow for assessment of different environmental conditions and socio-economic scenarios, the relationship between the atmospheric input of mercury and its compounds to the Mediterranean Sea and the formation/production of the most toxic forms of mercury (i.e., MMHg, DMHg) in the marine system which have a significant impact on human health and the environment.
Table 1. List of projects (both IMPACTS and ELOISE) that addressed the issue of mercury in the Mediterranean.
 
2. Sources of mercury in the Mediterranean
 
The biomagnification is probably due to the natural presence of mercury from volcanic activity. About half of world mercury resources are located in the Mediterranean area. Mining in the area has increased the release of mercury into the environment. Cinnabar, which has been known for 3000 years, represents the principal ore containing mercury. The world's most abundant deposits are located in the Mediterranean region, and mercury from sites such as Almaden (Spain), Idrja (Slovenia) and Monte Amiata (Italy) has been exploited since ancient times for gold and silver extraction. A significant increase in mercury emission to the atmosphere occurred during the industrial revolution due to fossil fuel combustion and other human activities. Main anthropogenic sources today are processing of mineral resources at high temperatures, such as combustion of fossil fuels, roasting and smelting of ores, kiln operations in cement industry , as well as incineration of wastes and production of certain chemicals. (Pacyna et al. 2001; Pirrone et al., 2003).
 
3. Cycling of mercury in the Marine Boundary layer
 
A lot of work has been carried out in order to contribute to the assessment of the biogeochemical cycling of mercury in the Mediterranean region. Mercury evasion derived from measurements of dissolved gaseous mercury (DGM) as well as speciated air measurements including reactive gaseous mercury (RGM) total particulate mercury (Hg-P) and gaseous elemental mercury (TGM) were performed at the Mediterranean Sea during three cruises. Using the DGM data and an empirical gas-exchange model (Wanninkhof, 1992) the data suggest that about 66 tonnes of mercury are released to the atmosphere from the Mediterranean Sea during the summer (Gårdfeldt et al., 2003). This emission is considerable in comparison to European anthropogenic emissions and should thus be taken into account in regional atmospheric modelling and assessment. Hence, it was found that Mediterranean Sea constitutes sources of airborne elemental mercury influencing the European domain.

The vertical profiles of DGM measured in the Mediterranean basin revealed that the concentration generally increases with depth (Ferrara et al. 2003). This finding indicates that DGM is produced not only in surface water as a consequence of photo-induced reactions, but also in deep water as a consequence of bacterial and/or geochemical activity. Volatile forms of mercury diffuse from the deep to the surface waters and then partially pass to the atmosphere. DGM concentrations and mercury evasion in surface water in the Western Mediterranean basin were lower than that observed in the Eastern basin. The maximum was found in the Strait of Sicily. The observed differences between the two basins may be explained by different biochemical scenarios. (Ferrara et al. 2003, Gårdfeldt et al. 2003).

Measurements performed during summer and early spring season at off shore as well as coastal sites consistently demonstrated that maximum solar radiation at midday coincided with maximum DGM concentration. During nights DGM concentrations were generally lower compared to the concentrations measured during daylight. Hence, a diurnal variation has been demonstrated in the off shore waters as well as the coastal sites investigated during the cruises (Andersson et al., 2004).

Results from MAMCS and MOE on simultaneous measurements on mercury in Europe, showed that observed concentrations of total gaseous mercury (TGM), particulate mercury (TPM), and reactive gaseous mercury (RGM) were generally slightly higher in the Mediterranean region than in Northwest Europe (Wangeberg et al., 2001).

The RGM formation in the Marine Boundary Layer (Sprovieri et al. 2003; Hedgecock et al. 2003; Hedgecock and Pirrone, 2001) is:

  • driving the deposition processes of RGM to the sea
  • affecting the cycling/exchange of Hg species between the atmosphere and the seawater
  • the key to all chemical processes in gaseous, aqueous and heterogeneous phases that may drive the formation of oxidized mercury and transform elemental Hg to oxidized Hg

Also physical processes are very important with reference to the gas-particle partitioning of gaseous mercury with suspended particulate matter in the atmosphere. Obviously this process depends very much by meteorology (temperature, relative humidity, radiation) and particle composition Enriched particles with EC are certainly the main factor that brings gaseous elemental mercury onto the particle and therefore is deposited faster to the surface.

As a part of the MED-OCEANOR project the spatial and temporal distributions of mercury species along a 6000 km cruise path in the western and eastern sector of the Mediterranean Sea were studied for the first time. Simultaneous measurements of two atmospheric mercury species Hg0 and RGM were performed in order to investigate the dynamic patterns of mercury in the Marine Boundary Layer. Hg0 ranged between 0.4 and 11.2 ng m −3 with an average of 1.9±1.02 ng m −3 over the entire period. Higher concentrations were observed in the Gulf of Naples due primarily to air masses transported from the mainland reflecting the contribution from anthropogenic sources. RGM concentrations varied from 0.2 to 30.1 pg m −3 with an average of 7.9 pg m −3. A diurnal cycle of the RGM concentration was observed during the entire sampling period with the maximum around midday and the minimum during the night; the oxidation by daytime oxidants, i.e., OH, may have determined the observed diurnal cycle of RGM concentration in the MBL. The data set has been used by Hedgecock et al. to validate the mercury chemical model developed in MAMCS. The model has aimed to evaluate the dynamics of mercury in the MBL of the Mediterranean Sea.

Ongoing research is performed in order to evaluate the relative contributions of all these mechanisms in the overall mercury cycle and the relative contribution of natural vs. anthropogenic vs. recycling mechanisms. Indeed the emission of natural sources is a crucial step in the assessment of the global cycle in the Mediterranean sea basin. The Hg emission from the top water microlayer to the atmosphere and emissions from contaminated soil as well as from volcanoes and other geothermal activities are very important. See also Special issues in Atmospheric Environment published in 2001 and 2003.

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