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changes continuously and the amount of contaminant adsorbed on the soil surface
is adjusted accordingly. If the supply of volatile liquid is large compared to the
total adsorption capacity of the soil, this adjustment is slow and evaporation
approaches an apparent steady state. In the depletion stage, the soil already enri-
ched in less volatile components loses the volatile components slowly. The soil
still contains a small proportion of the more volatile components and does not lose
them completely until all components have disappeared.
References
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Brown K (eds) Reactions and movement of organic chemicals in soils. Soil Science Society of
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Mackay D (1979) Finding fugacity feasible. Environ Sci Technol 13:1218-1223
Nye PH, Yaron B, Galin T, Gerstl Z (1994) Volatilization of multicomponent liquid through dry
soils: Testing a model. Soil Sci Soc Am J 58:269-278
Plimmer JR (1976) Volatility. In: Kearny PC, Kaufmann DD (eds) Herbicides: Chemistry,
degradation and mode of action, vol 2, 2nd edn. Marcel Dekker, New York, pp 891-934
Stumm W, Morgan JJ (1996) Aquatic chemistry, 3rd edn. Wiley, New York
Taylor AW, Spencer WF (1990) Volatilization and vapor transport processes. In: Cheng HH (ed)
Pesticides in the soil environment. Soil Science Society America, Madison, pp 213-369
Woodrow JE, Selber JN, Yong-Hwe K (1986) Measured and calculated evaporation losses of two
petroleum hydrocarbon herbicide mixtures under laboratory and field conditions. Environ Sci
Technol 20:783-786
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