SO2 and NOx collaborative emission reduction method in sintering process
A technology for sintering process and preparation process, applied in separation methods, chemical instruments and methods, and dispersed particle separation, etc., can solve the problems of high cost of flue gas treatment and poor emission reduction effect, and achieve improved emission reduction efficiency and emission reduction efficiency. High and economical effect
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Embodiment 1
[0043] Such as figure 1 As shown, a method for synergistic emission reduction of SO2 and NOx in the sintering process of this embodiment, in the preparation process of sintering raw materials, multi-layer composite pellets are added, and the multi-layer composite pellets include inner layer pellets 100 and are arranged in the inner layer The outer coating layer 200 of the pellet 100; the ammonia inhibitor and the inner layer pelletizing material are added during the preparation of the inner pellet 100, and the ammonia inhibitor can release ammonia gas when it is decomposed by heat, and the ammonia inhibitor The N element content accounts for 0.02-0.15% of the mass of the inner layer pellets, in this embodiment it is 0.047%, and the mass ratio converted into urea is 0.1%; Covering layer 200; the particle size of the outer pelletizing material reaches -0.149mm particle size mass percentage content ≥ 95%; the inner layer pelletizing material particle size reaches -0.074mm particl...
Embodiment 2
[0069] The preparation method and sintering emission reduction method of the pellets in this embodiment are basically the same as in Embodiment 1, except that the N element content of the ammonia inhibitor in this embodiment accounts for 0.038% of the mass of the inner pellet 100, The mass ratio converted to urea is 0.08%, the detection of SO 2 , NO X and the concentration of dioxins are recorded in Table 4, and the desulfurization and denitrification rate and the emission reduction efficiency of dioxins are calculated.
Embodiment 3
[0071] The preparation method and sintering emission reduction method of the pellets in this embodiment are basically the same as in Embodiment 1, except that the N element content of the ammonia inhibitor in this embodiment accounts for 0.071% of the mass of the inner pellet 100, The mass ratio converted to urea is 0.15%, the detection of SO 2 , NO X and the concentration of dioxins are recorded in Table 4, and the desulfurization and denitrification rate and the emission reduction efficiency of dioxins are calculated.
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