Method for synchronously treating the combined pollution exhaust gas containing nitric oxide and sulfur dioxide
A waste gas and solution technology, applied in chemical instruments and methods, separation methods, air quality improvement, etc., can solve the problems of reduced absorption efficiency, inability to complex NO, etc., and achieve the effect of cost reduction
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Embodiment 1
[0039] The absorption experiment is carried out in a packed tower with a diameter of 2cm and a height of 100cm. The gas-liquid two-phase flow is countercurrent, the gas velocity of the empty tower is 0.1m / s, and the liquid spray density is 5m 3 / m 2 .hr, 500ml absorption liquid.
[0040] Among them: the concentration of ferrous sulfate is 0.02mol l -1 , EDTA concentration is 0.04mol l -1 , The pH is 6,
[0041] The gas flow rate is 200ml / minute and the temperature is 50℃;
[0042] The gas inlet composition is NO: 480ppm, SO 2 : 1500ppm, O 2 : 5.2%, the rest is nitrogen.
[0043] The absorption liquid enters the packed tower from the top of the tower to absorb NO and SO 2 , Flow into the circulation tank through the bottom of the tower, and then from the circulation tank into a fixed-bed reactor with a height of 50cm and a diameter of 2cm filled with coconut shell activated carbon for catalyst regeneration. The reaction temperature is 80℃, and the liquid in the regeneration tower T...
Embodiment 2
[0045] The reactor and operating conditions are the same as in Example 1, but there is still 0.03mol l in the absorption liquid -1 Calcium oxide, when the operation is stable, the gas outlet concentration is NO: 30ppm, SO 2 : 40ppm.
Embodiment 3
[0047] The reactor and operating conditions are the same as in Example 1, but there is still 0.03mol l in the absorption liquid -1 When the operation is stable, the gas outlet concentration is NO: 30ppm, SO 2 : 40ppm.
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