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Technologies for control of sulfur and nitrogen compounds and particulates  149

              pilot-scale combustion facility. Under the staged case, an usual NO x trend was obtained by
              the following measures: coal nitrogen can be rapidly converted to NO x and then reaches a
              peak concentration in the primary combustion zone, followed by a significant reduction in
              NO x in the reduction zone. The greater the staged level is, the earlier the reduction stage
              starts. With the increase in the staged degree, raising the O 2 concentration promotion causes
              a decrease in the rise of NO x emission. NO x emissions go up again when the oxidation of
              unknown intermediate compounds that contain nitrogen occurs (Fan et al., 2017). Fan con-
              clusions can be drawn from the tests: (1) In the staged cases, the NO x curves show significant
              reductions in NO x in the reduction zone; (2) The burnout air addition caused the NO x to rise
              again to some extent. The NO final emission level is determined by the burnout air injection
              point; (3) There exists an NO reducing saturation phenomenon in an overlong reduction
              zone; (4) There is no essential difference in the mechanism of NO formation and destruction
              between staged combustion under oxygen enrichment and air-staged combustion; (5) The
              low-level NO x emissions in the reduction zone would rise again to a larger value after
              burnout air addition.
           •  Other researchers (Zhao et al., 2017) made a study about particulate filter systems or cata-
              lysts. The de-NO x performance of the Cu-beta zeolite (BEA) selective catalytic reduction
              (SCR) catalyst with Ce and Nb as additives was investigated for catalytic reduction systems.
              The Cu-BEA catalyst with the Ce and Nb additives improved NO x conversion, compared
              with the Cu-BEA catalyst without additives. This result is related to the strength of the in-
              tensity ratio as (Cu2p3 B peak)/(Cu2p3 A peak) for the Ce and Nb added catalysts.
           •  Fern  andez-Miranda et al. (2016), also in this field of studies, evaluated SCR catalysts under
              an oxy-combustion atmosphere, focusing on the main differences in conventional air coal
              combustion. Under the conditions of this study, a higher oxidation reaction in the CO 2 -
              enriched atmosphere was observed. In these conditions, NO x conversion was less, producing
              an elevated concentration of NO and free NO 2. In oxy-combustion conditions, the high
              amount of CO 2 and H 2 O present make the active sites blocked for mercury adsorption.
           •  Regarding the supercritical coal-fired system, Chen (Chen et al., 2017) made a study about
              a 660 MW supercritical coal-fired power plant with a feedwater heater coupled with a
              steam ejector and applied to address the NO x removal problem under low load conditions.
              The model results obtained were successful to the point that a good NO x removal effi-
              ciency could be reached (70%). This method could be effective under extremely low loads,
              and NO x removal efficiency remained efficient when the unit approximated the 20% THA
              condition.



           6.2.2  SO x emission control technology
           6.2.2.1  What is SO x ?

           SO x represents both SO 2 and SO 3 emissions that are considered one of the criterion
           pollutants derived from anthropogenic activities established in the Clean Air Act of
           1970 (Roy and Sardar, 2015). Sixty-five million tons of SO 2 are emitted every year
           worldwide, which corresponds to 14% of the total criterion pollutant emissions derived
           from industrial activity and energy production. Most of them are SO 2 , which accounts
           for almost 95% of the share (Wang et al., 2005). SO 2 causes environmental damages
           and human health problems such as urban smog and acid rain. It also produces the
           acidification of soil and water (Roy and Sardar, 2015).
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