Page 107 - New Trends In Coal Conversion
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70                                             New Trends in Coal Conversion


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          Amount of metals retained in  different fractions, %  60
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                  V   Cr  Mn  Fe  Co  Ni  Cu  Zn  As  Se  Cd  Sn  Sb  Hg  Ti  Pb
                                            Metals
                     Losses       Emissions       Fly ash      Bottom ash
         Figure 3.5 Distribution of trace elements between bottom ash, fly ash, and emissions during
         pulverized coal combustion.
         Data from Danihelka, P., Volna, Z., Jones, J.M., Williams, A., 2003. Emission of trace toxic
         metals during pulverised fuel combustion of Czech coals. International Journal of Energy
         Research 27, 1181e1203.

            As it has been mentioned previously, mercury is an element of special concern due
         to its very high volatility (Group 3), toxicity, persistence, and bioaccumulation in the
         environment. Several studies have demonstrated that mercury can reach the stack in
         gas phase (Ochoa-Gonz  alez et al., 2011), coal combustion processes being one of
         the major sources of mercury to the atmosphere. For this reason, special attention
         has been paid to mercury behavior during combustion processes. The release of mer-
         cury occurs under both reducing and oxidizing conditions and cannot be influenced by
         modifications of the combustion process (Sloss, 2002). Mercury chemistry in flue gas
         is complex because mercury interacts with acid gases (e.g., HCl, SOx) and unburned
         carbon in ash. Mercury is almost completely released from the organic and inorganic
                                                       0
         fraction during coal combustion in its elemental form (Hg ). During the cooling of the
         gases, mercury interacts homogenously with acid gases such as HCl and SOx and het-
                                                           2þ
         erogeneously with fly ash particles and oxidized mercury (Hg ). In addition, oxida-
         tion by postcombustion control techniques may occur, resulting in a complex
         chemistry. As a result, mercury can be found in three forms in the flue gas as follows:
                               0
                                                      2þ
         (1) elemental mercury (Hg ); (2) oxidized mercury (Hg ), mainly HgCl 2 , HgO, and
         HgSO 4 ; and (3) particulate-bound mercury (Hg p )(Fig. 3.6).
         3.4   Current legislation and the European pollutant
               release and transfer register


         Legislation on coal-fired plants is becoming increasingly stringent to the point in
         which almost all existing plants in the developed world are required to make either
         fuel adjustments and/or have retrofitted flue gas treatment systems. Emission limits
         for existing plants will continue to tighten until all older plants are replaced with
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