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Handbook of Solvents - George Wypych - ChemTech - Ventech!

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1578 Hanadi S. Rifai, Charles J. Newell, Todd H. Wiedemeier<br />

23.1.2.6 Volatilization<br />

Volatilization causes contaminants to transfer from the dissolved phase to the gaseous<br />

phase. In general, factors affecting the volatilization <strong>of</strong> contaminants from ground water<br />

into soil gas include the contaminant concentration, the change in contaminant concentration<br />

with depth, the Henry’s Law constant and diffusion coefficient <strong>of</strong> the compound, mass<br />

transport coefficients for the contaminant in both water and soil gas, sorption, and the temperature<br />

<strong>of</strong> the water. 21<br />

The Henry’s Law constant <strong>of</strong> a chemical determines the tendency <strong>of</strong> a contaminant to<br />

volatilize from ground water into the soil gas. Henry’s Law states that the concentration <strong>of</strong> a<br />

contaminant in the gaseous phase is directly proportional to the compound’s concentration<br />

in the liquid phase and is a constant characteristic <strong>of</strong> the compound: 11<br />

Ca = HCl<br />

[23.1.12]<br />

where:<br />

H Henry’s Law constant (atm m 3 /mol)<br />

Ca concentration in air (atm)<br />

Cl concentration in water (mol/m 3 )<br />

Values <strong>of</strong> Henry’s Law constants for selected chlorinated solvents are given in Table<br />

23.1.2. As indicated in the table, values <strong>of</strong> H for chlorinated compounds also vary over several<br />

orders <strong>of</strong> magnitude. Chlorinated solvents have low Henry’s Law constants, with the<br />

exception <strong>of</strong> vinyl chloride. Volatilization <strong>of</strong> chlorinated solvents compounds from ground<br />

water is a relatively slow process that generally can be neglected when modeling<br />

biodegradation.<br />

Table 23.1.2. Physical properties for chlorinated compounds<br />

Constituent<br />

CAS<br />

#<br />

Molecular<br />

weight<br />

M W,<br />

g/mol Ref<br />

D air,<br />

cm 2 /s<br />

Diffusion coefficients<br />

in air in water<br />

Ref<br />

D wat,<br />

cm 2 /s<br />

Ref<br />

log Koc<br />

(@20-25°C)<br />

Partition<br />

log(L/kg)<br />

Bromodichloromethane 75-27-4 163.8 22 2.98E-02 22 1.06E-05 22 1.85 22<br />

Carbon tetrachloride 56-23-5 153.8 22 7.80E-02 22 8.80E-06 22 2.67 22<br />

Chlorobenzene 108-90-7 112.6 22 7.30E-02 22 8.70E-06 22 2.46 22<br />

Chloroethane 75-00-3 64.52 22 1.50E-01 22 1.18E-05 22 1.25 22<br />

Chlor<strong>of</strong>orm 67-66-3 119.4 22 1.04E-01 22 1.00E-05 22 1.93 22<br />

Chloromethane 74-87-3 51 23 1.28E-01 22 1.68E-04 b 1.40 28<br />

Chlorophenol, 2- 95-57-8 128.6 22 5.01E-02 22 9.46E-06 22 2.11 22<br />

Dibromochloromethane 124-48-1 208.29 22 1.99E-02 22 1.03E-05 22 2.05 22<br />

Dichlorobenzene, (1,2)(-o) 95-50-1 147 22 6.90E-02 22 7.90E-06 22 3.32 22<br />

Dichlorobenzene, (1,4)(-p) 106-46-7 147 22 6.90E-02 22 7.90E-06 22 3.33 22<br />

Dichlorodifluoromethane 75-71-8 120.92 22 5.20E-02 22 1.05E-05 22 2.12 22<br />

Ref

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