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14-68 EQUIPMENT FOR DISTILLATION, GAS ABSORPTION, PHASE DISPERSION, AND PHASE SEPARATION<br />

11 of Kister’s Distillation Design (McGraw-Hill, New York, 1992)<br />

leads to a similar conclusion for structured packings. For water-rich<br />

systems, packing HETPs tend to be much higher than for nonaqueous<br />

systems due to their high lambda or surface underwetting, as discussed<br />

above. High hydrogen concentrations (>30 percent or so in the<br />

gas) have also led to low packing efficiencies (Kister et al., Proc. 4th<br />

Ethylene Producers Conference, AIChE, New Orleans, La., p. 283,<br />

1992), possibly due to the fast-moving hydrogen molecule dragging<br />

heavier molecules with it as it diffuses from a liquid film into the<br />

vapor.<br />

Errors in VLE These affect packing HETP in the same way as<br />

they affect tray efficiency. The discussions and derivation earlier in<br />

this subsection apply equally to tray and packed towers.<br />

Comparison of Various Packing Efficiencies for Absorption<br />

and Stripping In past editions of this handbook, extensive data on<br />

absorption/stripping systems were given. Emphasis was given to the<br />

following systems:<br />

Ammonia-air-water Liquid and gas phases contributing; chemical<br />

reaction contributing<br />

Air-water Gas phase controlling<br />

Sulfur dioxide-air-water Liquid and gas phase controlling<br />

Carbon dioxide-air-water Liquid phase controlling<br />

The reader may refer to the data in the 5th edition. For the current<br />

work, emphasis will be given to one absorption system, carbon dioxide-air-caustic.<br />

Carbon Dioxide-Air-Caustic System The vendors of packings<br />

have adopted this system as a “standard” for comparing the performance<br />

of different packing types and sizes for absorption/stripping.<br />

For tests, air containing 1.0 mol % CO2 is passed countercurrently to<br />

a circulating stream of sodium hydroxide solution. The initial concentration<br />

of NaOH in water is 1.0 N (4.0 wt %), and as the circulating<br />

NaOH is converted to sodium carbonate it is necessary to make a<br />

mass-transfer correction because of reduced mass-transfer rate in the<br />

liquid phase. The procedure has been described by Eckert et al. [Ind.<br />

Eng. Chem., 59(2), 41 (1967); Chem. Eng. Progr., 54(1), 790 (1958)].<br />

An overall coefficient is measured using gas-phase (CO2) concentrations:<br />

moles CO2 absorbed<br />

KOGae = ������<br />

time-bed volume-partial pressure CO2 driving force<br />

(14-161)<br />

The coefficients are usually corrected to a hydroxide conversion of 25<br />

percent at 24°C. For other conversions, Fig. 14-14 may be used.<br />

Reported values of KOGa for representative random packings are given<br />

in Table 14-15. The effect of liquid rate on the coefficient is shown in<br />

Fig. 14-63.<br />

While the carbon dioxide/caustic test method has become accepted,<br />

one should use the results with caution. The chemical reaction masks<br />

TABLE 14-15 Overall Coefficients for Representative Packings<br />

CO2-air-caustic system<br />

Nominal size,<br />

mm<br />

Overall coefficient KOGa, kg⋅moles/(hr⋅m3⋅atm) Ceramic raschig rings 25 37.0<br />

50 26.1<br />

Ceramic Intalox saddles 25 45.1<br />

50 30.1<br />

Metal pall rings 25 49.6<br />

50 34.9<br />

Metal Intalox saddles (IMTP ® ) 25 54.8<br />

50 39.1<br />

NOTE: Basis for reported values: CO2 concentration in inlet gas, 1.0 vol %; 1N<br />

NaOH solution in water, 25 percent NaOH conversion; temperature = 24°C;<br />

atmospheric pressure: gas rate = 1.264 kg/(s⋅m2 ); liquid rate = 6.78 kg/(s⋅m2 ).<br />

SOURCE: Strigle, R. L., <strong>Packed</strong> Tower Design and Applications, 2d ed., Gulf<br />

Publ. Co., Houston, 1994.<br />

K Ga, lb-moles/hr, ft 3 , atm<br />

K Ga, lb-moles/hr, ft 3 , atm<br />

10<br />

5<br />

3<br />

2<br />

1<br />

.8<br />

.6<br />

.4<br />

.3<br />

.2<br />

0.1<br />

100 500 1000 2000 5000<br />

2<br />

Liquid rate, lbm/(hr•ft )<br />

(a)<br />

10<br />

5<br />

3<br />

2<br />

1<br />

.8<br />

.6<br />

.4<br />

.3<br />

.2<br />

0.1 100<br />

1<br />

'<br />

'<br />

p<br />

'<br />

'<br />

1<br />

2<br />

a<br />

r<br />

'<br />

'<br />

the effect of physical absorption, and the relative values in the table<br />

may not hold for other cases, where much of the resistance to mass<br />

transfer is in the gas phase. Background on this combination of physical<br />

and chemical absorption may be found earlier in the present section,<br />

under “Absorption with Chemical Reaction.”<br />

l<br />

l<br />

n<br />

i<br />

r<br />

a<br />

a<br />

r<br />

s<br />

'<br />

'<br />

2<br />

s<br />

c<br />

c<br />

g<br />

i<br />

h<br />

p<br />

h<br />

s<br />

l<br />

a<br />

g<br />

i<br />

g<br />

l<br />

r<br />

r<br />

i<br />

r<br />

i<br />

n<br />

i<br />

n<br />

n<br />

g<br />

g<br />

g<br />

s<br />

500 1000 2000 5000<br />

2<br />

Liquid rate, lbm/(hr•ft )<br />

FIG. 14-63 Overall mass transfer coefficients for carbon dioxide absorbed<br />

from air by 1N caustic solution. (a) 1-in Pall rings and Raschig rings. (b) 2-in Pall<br />

rings and Raschig rings. Air rate = 0.61 kg/s⋅m 2 (450 lb/hr⋅ft 2 ). To convert from<br />

lb/hr⋅ft 2 to kg/s⋅m 2 , multiply by 0.00136. To convert from lb-moles/hr⋅ft 3 atm to<br />

kg-moles/s⋅m 3 atm, multiply by 0.0045. [Eckert et al., Chem. Eng. Progr., 54(1),<br />

70 (1958).]<br />

(b)<br />

s<br />

s

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