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Three technologies that are most commonly used to treat
halogenated VOCs in air emissions/off-gases are carbon
adsorption, catalytic oxidation, and thermal oxidation.
Carbon adsorption
is a remediation technology in which pollutants are removed from
air by physical adsorption onto the carbon grain. Carbon is
"activated" for this purpose by processing the carbon
to create porous particles with a large internal surface area
(300 to 2,500 square meters per gram of carbon) that attracts and
adsorbs organic molecules as well as certain metal and other
inorganic molecules.
Commercial grades of activated carbon are available for
specific use in vapor-phase applications. The granular form of
activated carbon is typically used in packed beds through which
the contaminated air flows until the concentration of
contaminants in the effluent from the carbon bed exceeds an
acceptable level. Granular activated carbon systems typically
consist of one or more vessels filled with carbon connected in
series and/or parallel operating under atmospheric, negative, or
positive pressure. The carbon can then be regenerated in place,
regenerated at an off-site regeneration facility, or disposed of,
depending upon economic considerations.
Catalytic oxidation
is a relatively new alternative for the treatment of VOCs in air
streams resulting from remedial operations. VOCs are thermally
destroyed at temperatures typically ranging from 600 to 1,000 °F
by using a solid catalyst. First, the contaminated air is
directly preheated (electrically or, more frequently, using
natural gas or propane) to reach a temperature necessary to
initiate the catalytic oxidation of the VOCs. Then the preheated
VOC-laden air is passed through a bed of solid catalysts where
the VOCs are rapidly oxidized. Oxidation of halogenated VOCs
produces acid vapor. Off gas scrubbing may be needed to control
the acid vapor.
In most cases, the process can be enhanced to reduce auxiliary
fuel costs by using an air-to-air heat exchanger to transfer heat
from the exhaust gases to the incoming contaminated air.
Typically, about 50% of the heat of the exhaust gases is
recovered. Depending on VOC concentrations, the recovered heat
may be sufficient to sustain oxidation without additional fuel.
Catalyst systems used to oxidize VOCs typically use metal oxides
such as nickel oxide, copper oxide, manganese dioxide, or
chromium oxide. Noble metals such as platinum and palladium may
also be used. However, in a majority of remedial applications,
nonprecious metals (e.g., nickel, copper, or chromium) are used.
Most commercially available catalysts are proprietary. Catalysts
that resist damage from halogenated VOC combustion are available,
but cost more than catalysts that are suitable for nonhalogenated
VOC combustion.
Thermal oxidation
equipment is used for destroying contaminants in the exhaust gas
from air strippers and SVE systems. Probably fewer than 100
oxidizers have been sold to treat air stripper effluents; most of
these units are rated less than 600 scfm. Typically, the blower
for the air stripper or the vacuum extraction system provides
sufficient positive pressure and flow for thermal oxidizer
operation.
Thermal oxidation units are typically single chamber,
refractory-lined oxidizers equipped with a propane or natural gas
burner and a stack. Lightweight ceramic blanket refractory is
used because many of these units are mounted on skids or
trailers. Thermal oxidizers are often equipped with heat
exchangers where combustion gas is used to preheat the incoming
contaminated gas. If gasoline is the contaminant, heat exchanger
efficiencies are limited to 25 to 35% and preheat temperatures
are maintained below 530 °F to minimize the possibility of
ignition occurring in the heat exchanger. Flame arrestors are
always installed between the vapor source and the thermal
oxidizer. Burner capacities in the combustion chamber range from
0.5 to 2 million Btus per hour. Operating temperatures range from
1,400 to 1,600 °F, and gas residence times are typically 1
second or less. Like catalytic oxidation, thermal oxidation of
halogenated VOCs produces acid vapor. Off gas scrubbing may be
needed to control the acid vapor.
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