A Method for Assessing Residual NAPL Based on Organic Chemical Concentrations in Soil Samples

Ground water contamination by non-aqueous phase liquid (NAPL) chemicals is a serious concern at many industrial facilities and waste disposal sites. NAPL in the form of immobile residual contamination, or pools of mobile or potentially mobile NAPL, can represent continuing sources of ground water contamination. In order to develop rational and cost-effective plans for remediation of soil and ground water contamination at such sites, it is essential to determine if non-aqueous phase liquid (NAPL) chemicals are present in the subsurface and delineate the zones of NAPL contamination. The presence of NAPL pools may be evident as a floating or sinking phase in monitoring wells. The residual NAPL contamination may be identified in soil samples if residual contents are high and contaminated zones in the soil cores are thick. However, visual identification may not be effective if residual contents are low or if the NAPL residual is distributed heterogeneously in the samples. The chemical analysis of soil samples provides a measure of the total chemical concentration in the soil but cannot determine directly whether NAPL is present in the samples. Qualitatively, soil analyses that exhibit chemical concentrations in the percent range or >10,000 mg/kg would generally be considered to indicate the presence of NAPL. However, the results of soil analyses are seldom used in a quantitative manner to assess the possible presence of residual NAPL contamination when chemical concentrations are lower and the presence of NAPL is not obvious. The assessment of the presence of NAPL in soil samples is possible using the results of chemical and physical analyses of the soil, and the fundamental principles of chemical partitioning in unsaturated or saturated soil. The method requires information on the soil of the type typically considered in ground water contamination studies and provides a simple tool for the investigators of chemical spill and waste disposal sites to assess whether soil chemical analyses indicate the presence of residual NAPL in the subsurface.

[1]  David K. Kreamer,et al.  Development of a Standard, Pure‐Compound Base Gasoline Mixture for Use as a Reference in Field and Laboratory Experiments , 1990 .

[2]  W. Fawcett,et al.  Double Layer Structure at the Mercury/Acetonitrile Interface, , 1973 .

[3]  S. Banerjee Solubility of organic mixtures in water. , 1984, Environmental science & technology.

[4]  C. T. Chiou,et al.  Water solubility enhancements of DDT and trichlorobenzene by some surfactants below and above the critical micelle concentration , 1989 .

[5]  D. Mackay,et al.  The multicomponent solubility of hydrocarbons in water , 1973 .

[6]  Michele M. Miller,et al.  Relationships between octanol-water partition coefficient and aqueous solubility. , 1985, Environmental science & technology.

[7]  W. Shiu,et al.  Preparation of aqueous solutions of sparingly soluble organic substances: I. Single component systems , 1988 .

[8]  S. Karickhoff,et al.  Organic Pollutant Sorption in Aquatic Systems , 1984 .

[9]  James W. Mercer,et al.  A review of immiscible fluids in the subsurface: properties, models, characterization and remediation , 1990 .

[10]  J. Gossett Measurement of Henry's law constants for C1 and C2 chlorinated hydrocarbons , 1987 .

[11]  P. S. C. Rao,et al.  Sorption and Transport of Hydrophobic Organic Chemicals in Aqueous and Mixed Solvent Systems: Model Development and Preliminary Evaluation , 1985 .

[12]  W. Shiu,et al.  Environmentally relevant physical-chemical properties of hydrocarbons: A review of data and development of simple correlations , 1988 .

[13]  W. Shiu,et al.  Preparation of aqueous solutions of sparingly soluble organic substances: II. Multicomponent systems — hydrocarbon mixtures and petroleum products , 1988 .