1238 VAPOR AND GASEOUS POLLUTANT FUNDAMENTALS
with sulphuric acid produces the gaseous pollutants associ-
ated with this process, most notably hydrogen fluoride, and
silicon tetrafluoride. Both of these gases can be scrubbed in
aqueous medium, but each one causes a severe handling prob-
lem, after scrubbing. The HF is highly corrosive, and the SiF 4
combines with water to form a gelatinous mass which can
clog an improperly designed scrubber.
Another constraint is the extremely low effluent concentra-
tions allowed by law, about 0.02 mg/ft^3. Since each unit in the
process stream is a source, there are at least 250,000 ft^3 /min
which much be scrubbed down from 200–500 mg/ft^3. This is a
reasonable requirement, considering the toxicity of the pollut-
ants, but it is still a difficult objective to attain.
Teller claims to solve all these problems at once with a
cross flow scrubber and a high water flow rate. The device is
a baffled tank with wetted baffles so that any solids which do
not immediately dissolve will just drop to the bottom after
colliding and not clog the air ducts. The large water flow rate
keeps the fluorine concentration low, so that the same effi-
ciency (4.8 transfer units) typical of a countercurrent flow
scrubber can be maintained.
Cost factors cause the designer to look very hard at the
size of this system and its pumping costs. It is obvious that a
scrubber which has a greater than necessary number of trans-
fer units will be un-economical. Evan with a tight design on
both size and pressure drop, the enormous volumes of gas
can still make this system undesirable. A way must be found
to decrease the volume.
The best way to do this is by taking advantage of the
fact that not all the units produce pollutants at the same
INLET
FLUE GAS
CONTAINING
NOx
GAS PHASE
OXIDATION
NO
NO
NO
YES
YES
YES
ARE
NITROGEN
COMPOUNDS
REDUCED
ARE
NITROGEN
COMPOUNDS
REDUCED
OX IDATION-ABSORPTION-REDUCTION
OXIDATION-ABSORPTION
ABSORPTION-REDUCTION
ABSORPTION-OXIDATION
FIGURE 20 Classification system for wet NOx removal processes (Fawcett et al., 1977).
TABLE 17
Flue gas treating applications in the US and Japan
Process type For Units Per cent of total
1 Selective catalytic reduction NOx 70 63.7
2 Selective reduction Exxon Thermal DeNOx NOx 25 22.7
3 Shell/UOP selective NOx and SO 2 2 1.8
4 Shell/UOP selective reduction-adsorption NOx and SO 2 2 1.8
5 Wet oxidation-adsorption reduction NOx and SO 2 9 8.2
6 Wet adsorption-reduction NOx and SO 2 4 3.6
110 100
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