Page 326 - Air pollution and greenhouse gases from basic concepts to engineering applications for air emission control
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10.6  Control of Volatile Organic Compounds                     303

            intermittent spikes each time the valves switch the direction of flow, because the
            untreated VOC in the gas present in the inlet bed when it is suddenly switched to
            the outlet.
              Again, the advantage of thermal oxidation in an incinerator is the high
            destruction efficiency that can be obtained by proper control of the combustion
            chamber design and operation. If temperatures are maintained above 980 °C,
            greater than 99 % hydrocarbon destruction is routinely achievable. This efficiency
            depends on residence time, temperature, and turbulence (the three Ts) in the
            combustion chamber.
              Thermal oxidizers can be costly to install because of required support equip-
            ment, including high pressure fuel supplies (for example, natural gas), and sub-
            stantial process-control and monitoring equipment. In addition, public perception of
            a new “incinerator” can make it difficult to locate and permit a new unit.




            10.6.5 Catalytic Oxidation

            In a catalytic oxidation process, catalysts such as Pt or Pd on a Al 2 O 3 support may
            give destruction and removal efficiencies of up to 95 % with small size. The
            catalytic oxidation units are, however, much more expensive in operation. The high
            cost is caused by frequent replacement of the catalyst after being poisoned by other
            pollutants such as soot, particles, chlorine, sulfur, silicon, vanadium, lead, and/or
            hydrocarbons with great molecular weight. Temperature excursions also reduce the
            lifetime of catalysts. Furthermore, secondary air pollution may be produced by
            catalytic oxidation. Gases other than VOCs may be converted to hazardous com-
            pounds that require further treatment downstream. From this point of view, catalytic
            VOC oxidization is most suitable for the cleaning gases with stable VOC
            properties.
              As seen in Fig. 10.9, catalysts are loaded on a catalyst bed in the incinerator. The
            support structure of catalysts is arranged in a matrix that provides high geometric
            surface area, low pressure drop, and uniform flow. Structures providing these
            characteristics include honeycombs, grids, and mesh pads. Either a monolith or a
            beads/pellets configuration can be employed, depending on the kinetics of VOC
            oxidation and the presence of other pollutants. Monolith is a cluster of parallel tubes
            and it is used for fast kinetics. Bead or pellet bed is preferred for slow kinetics and it
            is less sensitive to fouling or poisoning. The performances of thermal and catalytic
            oxidizers are often affected by the presence of CO. Oxidation of CO will be
            addressed separately.
              Thermal oxidation is not effective for engine exhaust gases mainly due to low
            gas temperatures and low concentration of the VOC emission from liquid fuel
            combustion. VOC emissions from engines are successfully oxidized in catalytic
            converters, where the catalysts are Pt, Pd, or Rh. Pd is more sensitive to poisoning
            by lead and sulfur. Most of the time, it is integrated in a three-way catalyst with CO
            oxidation and NO x reduction.
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