Environmental Engineering Reference
In-Depth Information
TABLE 4.3
Measured Air-Water Partition Constants for Selected Compounds
in Natural Waters
Compound
Matrix Composition
K aw
Reference
Toluene
Distilled water
0.244
Yurteri et al. (1987)
Tap water
0.231
“Creek” water
0.251
Chloroform
Distilled water
0.125
Nicholson et al. (1984)
Natural lake water
0.121
CH 3 CCl 3
Distilled water
0.53
Hunter-Smith et al. (1983)
Seawater
0.94
CHClBr 2
Distilled water
0.036
Nicholson et al. (1984)
Natural lake water
0.034
CHBr 3
Distilled water
0.018
Nicholson et al. (1984)
Natural lake water
0.017
Hexachlorobenzene
Distilled water
0.054
Brownawell (1986)
Seawater
0.070
2,4,4 -Trichlorobiphenyl
Distilled water
0.00595
Brownawell (1986)
Seawater
0.00885
effects on Henry's constants in the presence of co-solvents such as methanol and iso-
propanol up to concentrations as large as 10 g/L (i.e., co-solvent mole fraction of
0.5
10 3 ) . It was observed that the effects were pronounced for very hydrophobic
solutes.A compound that interacts better with the co-solvent exhibits the effect at low
co-solvent concentrations than does a compound that is more hydrophilic. In gen-
eral, for any hydrophobic solute, the presence of a co-solvent increases the aqueous
solubility and lowers K aw . These conclusions have been substantiated by others who
determined the Henry's constants of volatile solutes such as toluene and chloroform
in distilled, tap, and natural lake waters. Table 4.3 is a summary of these observations.
The effects of inorganic salts on air-water partition constants are manifest through
their effects on the infinite dilution activity coefficients that are described in Chap-
ter 3. Most hydrophobic organic compounds show the salting-out behavior, whereby
the mole fraction solubility in water is decreased (or activity coefficient is increased).
Consequently, the air-water partition constant decreases in the presence of salts. A
number of investigators have found that, for example, the partition constant for chlori-
natedVOCs such as chlorofluorocarbons (CFCs) and chlorobiphenyls in seawater are
20-80% greater than the values determined in distilled or deionized water (Table 4.3).
×
E XAMPLE 4.6 K aw AND I ONIC S TRENGTH
Determine K aw for phenanthrene in an industrial wastewater with 1 M total ion
concentration at 292 K.
 
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