Abstract

Abstract. Mercury transformation mechanisms and speciation profiles are reviewed for mercury formed in and released from flue gases of coal-fired boilers, non-ferrous metal smelters, cement plants, iron and steel plants, waste incinerators, biomass burning and so on. Mercury in coal, ores, and other raw materials is released to flue gases in the form of Hg0 during combustion or smelting in boilers, kilns or furnaces. Decreasing temperature from over 800 °C to below 300 °C in flue gases leaving boilers, kilns or furnaces promotes homogeneous and heterogeneous oxidation of Hg0 to gaseous divalent mercury (Hg2+), with a portion of Hg2+ adsorbed onto fly ash to form particulate-bound mercury (Hgp). Halogen is the primary oxidizer for Hg0 in flue gases, and active components (e.g., TiO2, Fe2O3, etc.) on fly ash promote heterogeneous oxidation and adsorption processes. In addition to mercury removal, mercury transformation also occurs when passing through air pollution control devices (APCDs), affecting the mercury speciation in flue gases. In coal-fired power plants, selective catalytic reduction (SCR) system promotes mercury oxidation by 34–85 %, electrostatic precipitator (ESP) and fabric filter (FF) remove over 99 % of Hgp, and wet flue gas desulfurization system (WFGD) captures 60–95 % of Hg2+. In non-ferrous metal smelters, most Hg0 is converted to Hg2+ and removed in acid plants (APs). For cement clinker production, mercury cycling and operational conditions promote heterogeneous mercury oxidation and adsorption. The mercury speciation profiles in flue gases emitted to the atmosphere are determined by transformation mechanisms and mercury removal efficiencies by various APCDs. For all the sectors reviewed in this study, Hgp accounts for less than 5 % in flue gases. In China, mercury emission has a higher Hg0 fraction (66–82 % of total mercury) in flue gases from coal combustion, in contrast to a greater Hg2+ fraction (29–90 %) from non-ferrous metal smelting, cement and iron and/or steel production. The higher Hg2+ fractions shown here than previous estimates may imply stronger local environmental impacts than previously thought, caused by mercury emissions in East Asia. Future research should focus on determining mercury speciation in flue gases from iron and steel plants, waste incineration and biomass burning, and on elucidating the mechanisms of mercury oxidation and adsorption in flue gases.

Highlights

  • Atmospheric mercury is one of the key focuses in the global environmental issues in recent years owing to its toxicity, persistence, and long-range transportability

  • This paper provides a critical review of mercury speciation in flue gases from major anthropogenic emission sources, and elaborates the process of initial mercury release in boilers, kilns or furnaces to its transformation in the flue gases across air pollution control devices (APCDs)

  • Mercury speciation profiles in the flue gas from coal combustion are summarized in Table 1, which considers the transformation of mercury species across different types of APCDs

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Summary

Introduction

Atmospheric mercury is one of the key focuses in the global environmental issues in recent years owing to its toxicity, persistence, and long-range transportability. L. Zhang et al.: Mercury transformation and speciation in flue gases ers, cement clinker production facilities, and smelting and roasting processes used in the production of non-ferrous metals (lead, zinc, copper and industrial gold), waste incineration facilities, in terms of their rapid growth, are on the list of key point sources in Annex D for Article 8 of the Minamata Convention (UNEP, 2013b). Our recent study updated the anthropogenic mercury emission inventory of China to the calendar year 2010 based on an abundant database of field measurements, and the REPs of the overall mercury speciation profile were 58 : 39 : 3 (Zhang et al, 2015). Mercury speciation profiles of major emission sources in the world have remarkable influences on the assessment of long-range transport of atmospheric mercury. Profiles of mercury speciation in different countries and regions are compared by sectors to assess their local and regional environmental impacts

Mercury speciation in flue gas from coal combustion
Mercury transformation across APCDs for coal combustion
Mercury speciation profile for coal-fired boilers
Mercury transformation in the dust collectors
Mercury transformation in purification systems
Mercury transformation in dedicated mercury removal systems
Mercury transformation in the acid plants
Mercury speciation profile for non-ferrous metal smelters
Cement clinker production processes
Mercury behavior in cement clinker production process
Mercury transformation during cement clinker production process
Mercury speciation profile for cement plants
Mercury speciation and transformation in flue gas from waste incineration
Mercury speciation and transformation in flue gas from biomass burning
Mercury speciation and transformation in flue gas from cremation
Mercury speciation and transformation in flue gas from PVC production
Findings
Conclusions
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