Overview
Background Info

   
   Background Information
 
 

Making progress in mercury management

Setting emission standards for this sector, developing implementation plans and measuring their efficacy is impeded by continuing uncertainties in key areas of mercury management: emissions measurement, availability of technologies for removing mercury and the variability in the presence and behaviour of mercury.

The electric power generation sector is engaged in a number of activities to try to reduce these uncertainties.

Improving emission measurements

For a number of years, companies have been working to improve emission estimates. This requires an understanding of the mercury content in coal and what happens to that mercury when the coal is burned. Activities to improve this understanding have been confounded by the variability in the levels of mercury found in coal and its complex chemistry. 

The coal mercury content can vary dramatically across coal types and within a single coal seam. Likewise, the chemical form in which mercury is emitted can be highly variable, depending on coal and ash characteristics, especially the sulphur and chlorine content, as well as operating conditions.

Mercury emissions can occur in three forms – particulate mercury, oxidized or reactive (ionic) mercury, and elemental mercury. The particulate mercury is a very small fraction of the total mercury.  The ratio of ionic mercury to elemental mercury depends upon the factors noted above. The form of the emissions is a key factor in determining viable management options.

Mercury is difficult to measure in coal-fired electricity generation stack gases because its concentrations are so low – near the minimum level for detection. For much the same reason, laboratory analyses for mercury in coal or ash samples frequently produce inconsistent results.

The Ontario Hydro Method for measuring mercury emissions in combustion gases (“stacks”) has been recommended by regulators across North America, but it is relatively expensive to be considered as a long-term measurement tool. Because of the low mercury concentrations variable results are produced during repeated tests, and present only a single point value (“snapshot”) as opposed to continuous measurements.  \Coal-fired utilities in Canada continue to invest substantial resources in measuring stack gases.

Continuous Emissions Monitoring systems (CEMs) are available, but their long-term reliability has not been demonstrated for the low mercury concentrations produced by coal-fired plants.

Companies have been investing in research to address these measurement issues, testing coal, ash and stack gases.  Activities in these areas will increase significantly with the launch of an intensive three-year Canadian Electricity Association Mercury Program for Coal-fired Electricity Generators. 

Reducing mercury emissions

Electric utilities have been actively taking steps to reduce mercury emissions as part of ongoing integrated air emission management programs. Many of the pollution control devices installed to capture other emissions (e.g. sulphur dioxide, nitrogen oxides, particulate matter and carbon dioxide) do capture some particulate and ionic mercury. It has been estimated that 40 percent of the mercury in coal is removed from coal-fired boilers in Canada in this fashion(1). However, a recent U.S. modeling study regarding the four most significant air pollutants from electric power generation has shown that "a mercury reduction strategy by itself would not significantly reduce emissions of the other three pollutants"(2).

The technology receiving the most attention for mercury removal is Activated Carbon Injection (ACI). It is still under study in various programs in the U.S. and elsewhere: the final test results on commercial volume emissions are expected in late 2003.  Installing ACI technology or adjusting air pollution control systems can be effective in capturing mercury in its ionic form. Neither of these options, however, captures elemental mercury effectively.

Regional differences in the mercury content of coals used in Canada and the lack of technical solutions for reduction in elemental mercury emissions mean there is currently no commercially demonstrated technology that can achieve uniform reductions in mercury emissions from all coal-fired boilers(3).

CEA members are monitoring and investing in a variety of U.S. mercury research programs including control technologies and their application to Canadian plants. The U.S. government is spending many millions of dollars on mercury research, including pilot programs for a variety of mercury capture technology options.  Important commercial demonstration projects will be completed in 2003.

(1) Smith, Ian in Record of the Meeting of the Multi-Stakeholder Advisory Group and the Mercury CWS Development Committee, June 4-5, 2001

(2) U.S. EPA, Analysis of Emissions Reduction Options for the Electric Power Industry, March 1999

(3) U.S. EPA Notice of Regulatory Finding

 

 

Understanding Mercury in Detail