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Solubilization-emulsification mechanisms of detergency

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C.A. Miller and K.H. Raney/Colloids Surfaces A: Physicochem. Eng. Aspects 74 (1993) 169-215 209<br />

mixed soils. Maximum <strong>detergency</strong> is reached<br />

near 40ºC with 10% oleyl alcohol in the soil<br />

while high levels <strong>of</strong> cetane removal are attained<br />

down to 20ºC with 25% oleyl alcohol present.<br />

The temperatures at the lower limit <strong>of</strong> the<br />

plateaus in <strong>detergency</strong> are the respective phase<br />

inversion temperatures. For C 12E 7, PIT values<br />

can be obtained from the curves in Fig. 15.<br />

Above the PIT, soil removal remains at a high<br />

level until the cloud point <strong>of</strong> the surfactant is<br />

reached. As implied in the oil drop-contacting<br />

section, the formation <strong>of</strong> an intermediate liquid<br />

crystalline phase plays the key role in the<br />

soilremoval process in the plateau regime.<br />

The relative amount <strong>of</strong> polar soil also affects<br />

the rate <strong>of</strong> soil removal. Despite being removed<br />

at a comparable level to that <strong>of</strong> the 3/1<br />

cetane-oleyl alcohol soil after 10 min at 50ºC,<br />

the 9/1 soil is actually removed much more<br />

quickly, as indicated in Fig. 50. This very fast<br />

removal can be attributed to that soil having a<br />

PIT <strong>of</strong> approximately 50ºC with C 12E 7. A 1/1<br />

cetane-oleyl alcohol soil is removed very slowly<br />

at 50ºC, although a high level <strong>of</strong> removal is<br />

ultimately attained. Removal <strong>of</strong> the hexadecane<br />

soil reaches a plateau at a lower level since the<br />

washing temperature is well below the optimum<br />

<strong>detergency</strong> temperature for its removal by C 12E 7,<br />

i.e. approximately 80ºC.<br />

Fig. 50. Kinetics <strong>of</strong> n-hexadecane removal for mixed<br />

n-hexadecane-oleyl alcohol blends [12]. Reprinted<br />

with permission <strong>of</strong> the American Oil Chemists'<br />

Society.<br />

Similar results to those described for<br />

hexadecane-oleyl alcohol soils were obtained<br />

for hexadecane-oleic acid soils having the same<br />

ratio <strong>of</strong> nonpolar and polar constituents. These<br />

studies were performed in the absence <strong>of</strong><br />

triethanolarnine to insure that the oleic acid was<br />

in the non-ionized state. Also, the oleic acid was<br />

tagged with 14C-labeled material to allow<br />

measurement <strong>of</strong> its removal as well as that <strong>of</strong><br />

hexadecane. The results for 3/1 cetane-oleic acid<br />

soil are shown in Fig. 51. High levels <strong>of</strong> soil<br />

removal were found over a wide temperature<br />

range from 20ºC to the cloud point <strong>of</strong> the<br />

surfactant. As with the oleyl alcoholcontaining<br />

soils, optimum removal was found between the<br />

PIT and cloud point temperature. Interestingly,<br />

the data show that the removal <strong>of</strong> oleic acid<br />

paralleled that <strong>of</strong> cetane, although at levels<br />

10-20% higher. This behavior results from the<br />

higher ratio <strong>of</strong> oleic acid to hexadecane found in<br />

the intermediate liquid crystalline phase<br />

compared to that in the original soil.<br />

Presumably, preferential removal <strong>of</strong> oleyl<br />

alcohol would have been found in the<br />

hexadecane-oleyl alcohol experiments if the<br />

alcohol had been radioactively tagged.<br />

11. Discussion<br />

As shown above, maximum removal <strong>of</strong> liquid<br />

hydrocarbon soil from synthetic fabrics in non-<br />

Fig. 51. Oil removal for mixed 3/1 n-hexadecaneoleic<br />

acid soil [12]. Reprinted with permission <strong>of</strong> the<br />

American Oil Chemists' Society.

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