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Dense nonaqueous phase liquid

The majority of trichloroethylene present on soil surfaces will volatilize to the atmosphere or leach into the subsurface. Once trichloroethylene leaches into the soil, it appears not to become chemically transformed or undergo covalent bonding with soil components. When trichloroethylene was absorbed onto kaolinite and bentonite, the nuclear magnetic resonance (NMR) spectra showed no evidence of chemical reactions (Jurkiewicz and Maciel 1995). Because trichloroethylene is a dense nonaqueous phase liquid, it can move through the imsaturated zone into the saturated zone where it can displace soil pore water (Wershaw et al. 1994). [Pg.213]

Besides petroleum products, other hazardous substances (see Tables 18.7-18.9) are also stored in USTs. Among them, a common and important group is the dense nonaqueous phase liquids (DNAPLs). This group has some different physical properties from petroleum (especially gasoline) that make them behave differently in the way they move underground. This section presents the important factors associated with the cleanup of DNAPLs. [Pg.745]

Dense metal membranes, 15 800 Dense nonaqueous phase liquids... [Pg.251]

U.S. Environmental Protection Agency, 1992, Dense Nonaqueous Phase Liquids — A Workshop Summary. EPS/600/R-92/030, 81 pp. [Pg.207]

Palmer AN (1996) Rates of limestone dissolution and calcite precipitation in cave streams of east-central New York state, northern section. Geol Soc Am 28 89 Parker BL, Cherry JA, Chapman SW, Guilbeault MA (2003) Review and analysis of chlorinated solvent dense nonaqueous phase liquid distribution in five sandy aquifers. Vadose Zone J 2 116-137... [Pg.399]

In Situ Density Modification of Entrapped Dense Nonaqueous-Phase Liquids (DNAPLs) using Surfactant/Alcohol Solutions... [Pg.271]

Dense nonaqueous-phase liquids (DNAPLs) are widespread at contaminated sites, where they are often distributed deep in aquifers due to their high densities [US EPA, 1993], Surfactant-based remediation techniques have the potential to be very effective at removing DNAPLs from contaminated sites (e.g., [Pennell, et al., 1994 Baran, et al., 1994 Pennell, etal., 1997 Zimmerman, et al., 1999]). However, one risk associated with surfactant-based remediation of DNAPLs is the potential for unwanted... [Pg.271]

Kibbey, T. C. G. Ramsburg, C. A. Pennell, K. D. Hayes, K. F. Effects of Surfactant Properties on Equilibrium and Non-equilibrium Alcohol Partitioning into Dense Nonaqueous-Phase Liquids (DNAPLs) for In Situ Density Modification Applications, presented at the Fall American Geophysical Union national meeting, San Francisco, California, December, 1998. [Pg.283]

Fountain, J.C. Waddell-Sheets, C., Lagowski, A., Taylor, C., Frazier, D., and Byrne, M. (1995). Enhanced Removal of Dense Nonaqueous Phase Liquids using Surfactants -Capabilities and Limitations from Field Trials. In Surfactant-Enhanced Subsurface Remediation, ACS Symposium Series Emerging Technologies 594, Sabatini, D.A., Knox, R.D., Harwell, J.H., (ed.), American Chemical Society, 177-190. [Pg.305]

Fig. 1 Schematic illustration of slightly soluble in water dense nonaqueous phase liquid migration in the subsurface and plume formation of dissolved hydrocarbons... Fig. 1 Schematic illustration of slightly soluble in water dense nonaqueous phase liquid migration in the subsurface and plume formation of dissolved hydrocarbons...
The contaminant s aqueous solubility and density greatly influence its final disposition in water-solid systems. Dense nonaqueous phase liquids (DNAPLs) are chemicals with densities greater than water and typically low aqueous solubilities. DNAPLs naturally partition away from the aqueous phase and towards the solid phase, often pooling on top of an impermeable solid layer. On the other hand, light nonaqueous phase liquids (LNAPLs) possess densities less than water and have a tendency to pool on the water s surface where they may be prone to volatilization and photolysis reactions. Various liquid-solid partition coefficients have been... [Pg.229]

The system has two phases an excess oil phase and a water-external microemulsion phase. Because microemulsion is the aqueous phase and is denser than the oil phase, it resides below the oil phase and is called a lower-phase microemulsion. At a high salinity, the system separates into an oil-external microemulsion and an excess water phase. In this case, the microemulsion is called an upper-phase microemulsion. At some intermediate range of salinities, the system could have three phases excess oil, microemulsion, and excess water. In this case, the microemulsion phase resides in the middle and is called a middle-phase microemulsion (Healy et al., 1976). Such terminology is consistent with their relative positions in a test tube (pipette) with the water being the dense liquid. In the environmental sciences and engineering, however, a dense nonaqueous phase liquid (DNAPL) could be denser than water (UTCHEM-9.0, 2000). Fleming et al. (1978) used y, P, and a to name the lower-phase, middle-phase, and upper-phase microemulsions, respectively. [Pg.246]

Fountain, J.C. (1992) Field tests of surfactant flooding -mobility control of dense nonaqueous-phase liquids. In D.A. Sabatini and R.C. Knox (eds), Transport and Remediation of Subsurface Contaminants, ACS Symposium Series 491. American Chemical Society, Washington, DC, pp. 182-191. [Pg.337]

Holzmer, F.J., Pope, G.A. andYeh, L. (2000) Surfactant-enhanced aquifer remediation of PCE-DNAPL in low permeability sands. In G.B. Wickramanayake, A.R. Gavaksar and N. Gupta (eds), Treating Dense Nonaqueous Phase Liquids (DNAPLs) Remediation of Chlorinated and Recalcitrant Compounds. Battelle Press, Columbus, OH, pp. 187-193. [Pg.339]

Ground Water Issue Dense Nonaqueous Phase Liquids... [Pg.38]

Dense nonaqueous phase liquids (DNAPLs) are the chlorinated organic compounds that have a density higher than water. Because of this unique property, DNAPLs will pass through the vadose zone and contaminate groundwater. Some reside in... [Pg.497]

Successfiil inq>lemeiitation of such an approach would considerably reduce both the time and cost of in situ biotreatment. Pretceating groundwaters with sonication techniques would form VOCs that could be removed effectively by either bioremediation technologies or a dual vapor extraction technique (developed by Stanford University under the VOC-Arid Program, now part of Plumes Focus Area). Sonication could also be coupled widi technologies aimed at mobilizing dense nonaqueous phase liquids (DNAPLs) in the subsur ce, such as surfactant floodii. ... [Pg.26]


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See also in sourсe #XX -- [ Pg.626 , Pg.689 , Pg.745 , Pg.796 ]




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Dense nonaqueous liquids

Dense nonaqueous phase liquid DNAPL)

Dense nonaqueous phase liquids DNAPLs)

Dense nonaqueous phase liquids groundwater contamination

Dense phase

Liquid nonaqueous

Liquids dense

Nonaqueous

Nonaqueous phase

Nonaqueous phase liquid

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