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Handbook of Solvents - George Wypych - ChemTech - Ventech!

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1166 William R. Roy<br />

MPC, μg/L LC, mg/L Half-life, years<br />

Methyl isobutyl ketone<br />

Others<br />

143 10.0 5<br />

Carbon disulfide 830 1,000 10<br />

Diethyl ether 55,000 1,000 5<br />

Ethyl acetate 55,000 1,000 5<br />

Pyridine 207 1,000 20<br />

A mass-loading rate was conservatively calculated for each solvent as,<br />

Mlr = Q× Cl<br />

[17.2.1]<br />

where:<br />

Mlr the mass loading rate (mass/time/area),<br />

Q calculated leachate flux (131.7 kL/year/hectare), and<br />

Cl largest concentration <strong>of</strong> the solvent in leachate (mg/L)<br />

17.2.2 MOVEMENT OF SOLVENTS IN GROUNDWATER<br />

Ketones and alcohols have little tendency to be adsorbed by soil materials (see Section<br />

17.1), and would appear at the compliance point only a few years after liner breakthrough<br />

(Figure 17.2.2). Because the mass loading rates were held constant, the ketones and alcohols<br />

assumed maximum steady-state concentrations after approximately 40 to 50 years<br />

(Figure 17.2.3). These two classes <strong>of</strong> organic solvents degrade readily, reducing their<br />

downgradient concentrations. The distribution <strong>of</strong> the benzene derivatives at the compliance<br />

well depended substantially on their soil-water partition coefficients, their tendencies to de-<br />

Figure 17.2.2. The predicted distribution <strong>of</strong> methyl ethyl<br />

ketone (mg/L) in the aquifer 100 years after the leachate<br />

has broken through the liner (Griffin and Roy 3 ).<br />

Figure 17.2.3. The predicted concentrations <strong>of</strong> methyl<br />

ethyl ketone, methanol, benzene, 1,1,1-trichloroethane,<br />

ethyl acetate, and F-22 at the compliance point as a<br />

function <strong>of</strong> time (Roy et al. 1 ).

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