Method for removing mercury from flue gas using sulphur-applying active carbon
A technology of sulfur activated carbon and activated carbon is applied in the field of mercury removal from flue gas, which can solve the problems of no proposed flue gas mercury removal technology, and achieve the effects of eliminating secondary pollution, high efficiency and reducing cost.
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Embodiment 1
[0021] A method for flue gas demercuration using sulfur-enriched activated carbon: firstly adopt the applicant’s application for “a mesoporous sulfur-endowed activated carbon for mercury removal and its preparation method” (CN 200810197620) and “coke-based modified carbon Preparatory material and sulfur-endowing activated carbon and its preparation method” (CN200810197619.0) The sulfur-endowing activated carbon prepared by the patented technology, that is, the carbon preparatory material prepared by using commercially available activated carbon or coke powder and sulfur-rich carbon resources dry distillate, has a temperature of 350-850 °C, with SO 2 The mixed gas or flue gas in the hot charcoal fixed bed undergoes hot charcoal reduction reaction to generate sulfur-endorsed activated carbon.
[0022] The particle size of the sulfur-endowing activated carbon powder prepared in this example is 25-212 μm, and the specific surface area of the sulfur-endowing activated carbon is 1...
Embodiment 2
[0029] A method for flue gas demercuration using sulfur-endowing activated carbon: the preparation method of sulfur-endowing activated carbon is the same as in Example 1. The particle size of the prepared sulfur-endowing activated carbon powder is 25-212 μm; the specific surface area of the sulfur-endowing activated carbon is 350-600 m 2 / g, the mesopore specific surface area ratio is 35-55%, and the sulfur content is 10-20%. The mercury concentration in the outlet flue gas reaches the mercury concentration in the inlet flue gas for the first time to reach the adsorption equilibrium, and the mercury equilibrium adsorption capacity is 8 ~12mg·g -1 . Mercury adsorption reaction rate is determined by the kinetic rate model described in Example 1, wherein, k is 0.0050~0.0100min -1 .
[0030] Using sulfur-endowing activated carbon powder as the adsorbent, the concentration of mercury in the upstream flue is 150-500μg / m 3 , the temperature is 25~50℃ and the flow rate is 700~15...
Embodiment 3
[0032] A method for flue gas demercuration using sulfur-endowing activated carbon: the preparation method of sulfur-endowing activated carbon is the same as in Example 1. The prepared sulfur-endowing activated carbon powder particle size is 25-212μm; the specific surface area of sulfur-endowing activated carbon is 600-1000m 2 / g, the mesopore specific surface area ratio is 55-75%, and the sulfur content is 5-10%. The mercury concentration in the outlet flue gas reaches the mercury concentration in the inlet flue gas for the first time to reach the adsorption equilibrium, and the mercury equilibrium adsorption capacity is 10 ~15mg·g -1 Mercury adsorption reaction rate is determined by the kinetic rate model described in embodiment 1, wherein, k is 0.0080~0.1000min -1 .
[0033] Using sulfur-endowing activated carbon powder as the adsorbent, the mercury concentration in the upstream flue is 500-1000μg / m 3 , the temperature is 50~75℃ and the flow rate is 1000~1800m 3 .m -2...
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Abstract
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