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Published byDarlene Garrett Modified over 9 years ago
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Air Emissions Treatment
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Because air pollutants vary in size many orders of magnitude, many different types of treatment devices are required for emissions treatment.
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Air pollutant devices can be treated as black box separators, like we studied in Chapter 3. Recovery efficiency can be described by the equation: R 1 = (x 1 /x 0 ) x 100 R 1 = recovery of component 1, % x 1 = amount of pollutant collected by the device per unit time, kg/sec x 0 = amount of pollutant entering the device per unit time, kg/sec
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Example An air pollution control device removes a particulate that is being emitted at a concentration of 125,000 : g/m 3 at an air flow rate of 180 m 3 /sec. The device removes 0.48 metric toms per day. What are the concentration of the emission and the recovery of collection? Pollution control deviceFeed x 0 x 0Escaped x 2 x 2 Removed x 1 x 1 At steady state the mass balance is: Rate of particulates in = rate of particulates out Rate of particles in = rate of particles removed + rate of particles escaping
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Particulates in: 180 m 3 /sec x 125,000 : g/m 3 x 10 -6 : g/g = 22.5 g/sec Particles collected: 0.48 tons/day x 10 6 g/ton x 1 hr/3600 sec x 1 day/24 hr = 5.5 g/sec Mass balance: 22.5 = 5.5 + particles that escape Particles that escape = 17 g/sec Emission concentration: (17 g/sec x 10 6 : g/g)/ 180 m 3 /sec = 94,000 : g/m 3 Recovery: R = (x 1 x 100)/x 0 = (5.5 x 100)/22.5 = 24%
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Treatment Devices Settling Chambers The simplest of treatment devices. Wide spot in the exhaust flue that allows particles to settle out. Only very large particles (> 100 : m) will settle effectively.
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Cyclones
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Bag Filter or Bag House
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Spray Tower or Scrubber
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Electrostatic Precipitators
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Process Selection A)Settling Chamber B)Simple Cyclone C)High-efficiency Cyclone D)Electrostatic Precipitator E)Spray Tower wet scrubber F)Venturi Scrubber G)Bag Filter
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Control of Gaseous Pollutants Wet Scrubbers Adsorption Incineration or flaring Catalytic Combustion
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Wet Scrubber Venturi Scrubber
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Wet Scrubbers
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Adsorption
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Carbon Adsorption System
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Incineration and Flaring
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Control of Sulfur Oxides (SO x ) Emission of SO x one of the major causes of acid precipitation Major source of SO x is coal-fired power plants Several options for control: Change to Low-sulfur fuel Desulfurize the coal Sulfur in coal is either organic (usually about 60%) or inorganic (about 40%). The inorganic form is iron pyrite (FeS 2 ) that can be removed from the coal by washing. The removal of organic sulfur requires a chemical reaction that is accomplished best if the coal is gassified first. Gasified coal is like natural gas.
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SO x Control Options (continued) Tall Stacks Flue-Gas Desulfurization Contact with lime SO 2 + CaO CaSO 3 Contact with limestone SO 2 + CaCO 3 CaSO 4 + CO 2 Calcium sulfite (CaSO 3 ) and calcium sulfate (CaSO 4 ) are solids that have low solubilities so they can be removed from the water by settling, but then there is a disposal problem
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