Abstract

Sulphur dioxide (SO2) is mostly emitted from coal-fueled power plants, from waste incineration, from sulphuric acid manufacturing, from clay brick plants and from treating nonferrous metals. The emission of SO2 needs to be abated. Both wet scrubbing (absorption) and dry or semi-dry (reaction) systems are used. In the dry process, both bubbling and circulating fluidized beds (BFB, CFB) can be used as contactor. Experimental results demonstrate a SO2-removal efficiency in excess of 94% in a CFB application. A general model of the heterogeneous reaction is proposed, combining the external diffusion of SO2 across the gas film, the internal diffusion of SO2 in the porous particles and the reaction as such (irreversible, 1st order). For the reaction of SO2 with a fine particulate reactant, the reaction rate constant and the relevant contact time are the dominant parameters. Application of the model equations reveals that the circulating fluidized bed is the most appropriate technique, where the high solid to gas ratio guarantees a high conversion in a short reaction time. For the CFB operation, the required gas contact time in a CFB at given superficial gas velocities and solids circulation rates will determine the SO2 removal rate.

Highlights

  • The de-SO2 efficiency is analyzed in a large-scale CFBC, with cheap Ca(OH)2 as alkali sorbent

  • Hydrated lime [Ca(OH)2 ] of particle size

  • Hydrated lime [Ca(OH)2] of particle size

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Summary

Introduction

SO2 is mostly related to energy generation from fossil fuels. The International Energy Agency (IEA) reported that fossil fuels account for over 80% of the word energy supply [1]. Of the energy is provided by coal and fuel oil. The combustion of fossil fuels is the dominant contribution for anthropogenic CO2 emission [2], the combustion-derived emissions of NOx and SO2 are important towards atmospheric pollution. The ultimate analysis of some fuels determines the composition and the extent of the possible SO2 problem.

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