Abstract

Abstract. An assessment of current and future emissions, air concentrations, and atmospheric deposition of mercury worldwide is presented on the basis of results obtained during the performance of the EU GMOS (Global Mercury Observation System) project. Emission estimates for mercury were prepared with the main goal of applying them in models to assess current (2013) and future (2035) air concentrations and atmospheric deposition of this contaminant. The combustion of fossil fuels (mainly coal) for energy and heat production in power plants and in industrial and residential boilers, as well as artisanal and small-scale gold mining, is one of the major anthropogenic sources of Hg emissions to the atmosphere at present. These sources account for about 37 and 25 % of the total anthropogenic Hg emissions globally, estimated to be about 2000 t. Emissions in Asian countries, particularly in China and India, dominate the total emissions of Hg. The current estimates of mercury emissions from natural processes (primary mercury emissions and re-emissions), including mercury depletion events, were estimated to be 5207 t year−1, which represents nearly 70 % of the global mercury emission budget. Oceans are the most important sources (36 %), followed by biomass burning (9 %). A comparison of the 2035 anthropogenic emissions estimated for three different scenarios with current anthropogenic emissions indicates a reduction of these emissions in 2035 up to 85 % for the best-case scenario. Two global chemical transport models (GLEMOS and ECHMERIT) have been used for the evaluation of future mercury pollution levels considering future emission scenarios. Projections of future changes in mercury deposition on a global scale simulated by these models for three anthropogenic emissions scenarios of 2035 indicate a decrease in up to 50 % deposition in the Northern Hemisphere and up to 35 % in Southern Hemisphere for the best-case scenario. The EU GMOS project has proved to be a very important research instrument for supporting the scientific justification for the Minamata Convention and monitoring of the implementation of targets of this convention, as well as the EU Mercury Strategy. This project provided the state of the art with regard to the development of the latest emission inventories for mercury, future emission scenarios, dispersion modelling of atmospheric mercury on a global and regional scale, and source–receptor techniques for mercury emission apportionment on a global scale.

Highlights

  • Mercury (Hg) has been recognized as a toxic, persistent, and mobile contaminant

  • Mercury emissions to air from waste associated with sectors using mercury intentionally for the various countries were based on world region consumption data as well as on assumptions regarding rates of breakage, degrees of waste handling/incineration, and suitable emission factors

  • Monitoring the implementation of international agreements mercury emission reduction and its impacts on the environment and human health would require the improvement of various parameters, including emission inventories, model simulations of atmospheric deposition, and monitoring networks

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Summary

Introduction

Mercury (Hg) has been recognized as a toxic, persistent, and mobile contaminant. This contaminant does not degrade in the environment, and it is mobile because of the volatility of the element and several of its compounds. The major conclusion drawn from recent studies on the impacts of mercury on the environment and human health is that there is a need for international action to reduce emissions of and human exposure to mercury on a regional and global scale. A part of the emissions entering the atmosphere is locally deposited to aquatic and terrestrial ecosystems Another part is transported with air masses in directions dependent on many factors, including wind direction and speed and mercury behaviour during this transport. The Global Mercury Observation System (GMOS) project (http://www.gmos.eu) has undertaken studies addressing this question. Both monitoring and model simulations were used for this purpose. The main results from the assessment of current and future emissions, air concentrations, and atmospheric deposition of mercury worldwide are presented in this paper

Methodology
Database on activities
Definition of emission scenarios
Assessment of 2010 global emissions and emission factors
Assessment of global mercury emissions in the year 2035
Model description
ECHMERIT GLEMOS
Future changes in mercury deposition levels
Source apportionment of mercury deposition
Findings
Concluding remarks
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