Mercury curing and removing method for coal-fired power plant and device thereof
A coal-fired power plant, removal technology, applied in the direction of chemical instruments and methods, separation methods, dispersed particle separation, etc., can solve problems such as environmental pollution, high investment costs, activated carbon regeneration, etc., to avoid secondary pollution and improve desulfurization efficiency , the effect of reducing mercury content
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Embodiment 1
[0035] The flue gas from the boiler passes through the SCR reactor 1 to remove nitrogen oxides, then passes through the air preheater 2, and then enters the dry electrostatic precipitator 3 to remove dust. The mercury collection reactor 4 of the sulfide solution with a pH value of 9 removes divalent mercury in the flue gas; the flue gas treated with mercury removal enters the desulfurization absorption tower 5 to remove sulfur dioxide and then emits it.
Embodiment 2
[0037] The flue gas from the boiler passes through the SCR reactor 1 to remove nitrogen oxides, then passes through the air preheater 2, and then enters the dry electrostatic precipitator 3 to remove dust. Divalent mercury in the flue gas is removed in the mercury collection reactor 4 of the sulfide solution with a pH value of 11; the flue gas treated with mercury removal enters the desulfurization absorption tower 5 to remove sulfur dioxide and then is discharged.
Embodiment 3
[0039] The flue gas from the boiler passes through the SCR reactor 1 to remove nitrogen oxides, then passes through the air preheater 2, and then enters the dry electrostatic precipitator 3 to remove dust. The flue gas after electrostatic dust removal enters the container at a flow rate of 3.5m / s Divalent mercury in the flue gas is removed in the mercury collection reactor 4 with a sulfide solution with a pH value of 10; the flue gas treated with mercury removal enters the desulfurization absorption tower 5 to remove sulfur dioxide and then is discharged.
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