Process for absorbing toxic gas
AssigneeSanitech, Inc.
InventorSidney G. Nelson
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AssigneeSanitech, Inc.
InventorSidney G. Nelson
Estimating the term…
A process for absorbing noxious components such as SO.sub.x, NO.sub.x, and HX from a gas such as a flue gas at temperature below 250.degree. C. is improved by contacting the gas with a conditioned solid acceptor that contains divalent metal oxide, hydroxide or both coated onto exfoliated vermiculite and/or expanded perlite. Before use (to enhance its absorption of noxious components) conditioning can be done by heating the hydrated acceptor at temperature of at least about 400.degree. C. for a short time.
In a process for removing sulfur oxides, nitrogen oxides, and hydrogen halides from a gas contaminated with same in which the gas is contacted at a temperature below 250.degree. C. with particulate solid acceptor comprising a mineral support having a coating containing divalent metal oxide, hydroxide, or both, the support being water-moistened particles selected from the group consisting of exfoliated vermiculite, expanded perlite, or a mixture thereof, the improvement which comprises:
Dependencies are inferred from the claim text.
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Comprising silica: perlite
Comprising compounds of alkali metals, alkaline earth metals or magnesium: oxides or hydroxides
Comprising inorganic material: comprising oxides or hydroxides of metals not provided for in group B01J20/04
Comprising inorganic material: comprising silica or silicate
Term ended 11 Mar 2006 (estimated)
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This invention relates to solid sorbent materials ("acceptors") for use in removing ("accepting") sulfur oxides, nitrogen oxides (NO.sub.x), hydrogen halides and/or other noxious components (e.g. hydrogen sulfide, carbonyl sulfide, sulfur trioxide, etc.) from a gas, particularly a waste gas stream, and to improvements in process for making, using and regenerating the acceptors. Of these contaminants the ones specially targetted here are SO.sub.2 and NO.sub.x (typified by NO.sub.2) as they as the most common and usually most difficult to remove virtually completely amongst those above specified.
Flue or vent gases from the combustion of fuels such as coal or residual oil, the pyrolysis of solid waste, and the venting of chemical processes has been a matter of increasing concern for many years. Components such as sulfur dioxide and nitrogen oxides (NO.sub.x) are accused of fostering acid rain, having toxic effect on human, lower animal and plant life, and being generally dangerous or obnoxious even in quite low concentrations.
As a result, many approaches have been proposed to cleanse the waste gases of their toxic components. Scrubbing with a compound in slurry form with water has been by far the most popular approach. Wet scrubbing systems, although effective in removing toxic gases, have been very expensive and highly corrosive and have often simply converted an air-pollution problem into a sludge-disposal or water-pollution problem. Even with wet scrubbing processes involving reactants that are regenerable, thus producing no waste sludge, problems have occurred. In the magnesium oxide wet scrubbing process, for example, major technical difficulties have been encountered in handling the corrosive liquid slurries, and large energy costs have been incurred in drying the slurries and in regenerating the magnesium oxide.
Two 20-gram quantities of acceptor (MgO coated onto exfoliated vermiculite) were conditioned by heating each at 550.degree. C. for 30 minutes, then cooled and moistened. Two other like batches simply were air dried for 2 hours. All were tested with a gas stream flowing at two liters per minute and containing 931 ppm of NO.sub.2, 210 ppm of NO, and the balance nitrogen. The NO.sub.2 removal even after two hours was extremely high for the conditioned acceptors and essentially zero for the unconditioned ones. About half of the NO was removed by the conditioned acceptors while significantly less NO was removed by the unconditioned ones.
The tests are summarized below; they demonstrate that conditioning definitely improves sorptive performance of the acceptor.
TABLE I ______________________________________ NO.sub.2 Removal Efficiency, Percent After After After Acceptor 2 min. 10 min. 120 min. ______________________________________ Unconditioned #1 67.8 46.3 0 Unconditioned #2 66.7 35.6 0 Conditioned #1 100.0 97.3 87.1 Conditioned #2 100.0 97.9 87.1 ______________________________________