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Polycyclic aromatic hydrocarbons solubility

Coal tar pitch volatiles, see Particulate polycyclic aromatic hydrocarbons (PPAH), as benzene solubles Cobalt metal, dust and fume (as Co)... [Pg.375]

Although these issues have already been briefly noted, they deserve a few additional comments. For freely water-soluble substrates that have low volatility, there are few difficulties in carrying out the appropriate experiments described above. There is, however, increasing interest in xenobiotics such as polycyclic aromatic hydrocarbons (PAHs) and highly chlorinated compounds including, for example, PCBs, which have only low water solubility. In addition, attention has been focused on volatile chlorinated aliphatic compounds such as the chloroethenes, dichloromethane, and carbon tetrachloride. All of these substrates present experimental difficulties of greater or lesser severity. [Pg.268]

Kamlet, M. J., Doherty, R. M., Carr, P. W., Mackay, D., Abraham, M. H., Taft, R. W. (1988) Linear solvation energy relationships. 44. Parameter estimation rules that allow accurate prediction of octanol/water partition coefficients and other solubility and toxicity properties of polychlorinated biphenyls and polycyclic aromatic hydrocarbons. Environ. Sci. Technol. 22, 503-509. [Pg.54]

May, W. E., Wasik, S. P., Freeman, D. H. (1978b) Determination of the solubility behavior of some polycyclic aromatic hydrocarbons in water. Anal. Chem. 50, 997-1000. [Pg.55]

May, W.E. (1980) The solubility behaviour of polycyclic aromatic hydrocarbons in aqueous systems. Petroleum Mar. Environ. Adv. Chem. Ser. 185, Chapter 7, Am. Chem. Soc., Washington DC. [Pg.612]

Schwarz, F.P. (1977) Determination of temperature dependence of solubilities of polycyclic aromatic hydrocarbons in aqueous solutions by a fluorescence method. J. Chem. Eng. Data 22, 273-277. [Pg.614]

Wang, L., Wang, X., Xu, O., Tian, L. (1986) Determination of the ra-octanol/water partition coefficients of polycyclic aromatic hydrocarbons by HPLC and estimation of their aqueous solubilities. Huanjing Kexue Xuebao 6, 491 497. [Pg.616]

De Maagd, P.G.-J., ten Hulscher, T.E.M., Van den Heuvel, H., Opperhuizen, A., Sijm, D.T.H.M. (1998) Physicochemical properties of polycyclic aromatic hydrocarbons aqueous solubilities, n-octanol/water partition coefficients, and Henry s law constants. Environ. Toxicol. Chem. 17, 252-257. [Pg.903]

Gridin, V.V., Litani-Barzilai, I., Kadosh, M., Schechter, I. (1998) Determination of aqueous solubility and surface adsorption of polycyclic aromatic hydrocarbons by laser multiphoton ionization. Anal. Chem. 70, 2685-2692. [Pg.905]

Haines, R.L.S., Sandler, S.L. (1995) Aqueous solubilities and infinite dilution activity coefficients of several polycyclic aromatic hydrocarbons. J. Chem. Eng. Data 40, 835-836. [Pg.906]

Paschke, A., Popp, P., Schuurmann, G. (1999) Solubility and partitioning studies with polycyclic aromatic hydrocarbons using an optimized SPME procedure. Fresenius J. Anal. Chem. 363, 426 -28. [Pg.913]

Reza, J., Trejo, A., Vera-Avila, L.E. (2002) Determination of the temperature dependence of water solubilities of polycyclic aromatic hydrocarbons by a generator column-on-line solid-phase extraction-liquid chromatographic method. Chemosphere 47, 933-945. [Pg.914]

DNAPLs are broadly classified on the basis of certain chemical properties such as density, viscosity, and solubility. Some of the more common DNAPLs are chlorinated solvents (i.e., trichloroethylene, TCE tetrachloroethylene, PCE and trichlo-roethane, TCA), creosote, and coal tar, that is, polycyclic aromatic hydrocarbons... [Pg.132]

Sverdrup, L.E., Nielsen, T., and Krough, P.H. Soil ecotoxicity of polycyclic aromatic hydrocarbons in relation to soil sorption, lipophilicity, and water solubility, Environ. Sci. Technoi, 36(ll) 2429-2435, 2002. [Pg.1730]

A combined effect of natural organic matter and surfactants on the apparent solubility of polycyclic aromatic hydrocarbons (PAHs) is reported in the paper of Cho et al. (2002). Kinetic studies were conducted to compare solubilization of hydro-phobic contaminants such as naphthalene, phenanthrene, and pyrene into distilled water and aqueous solutions containing natural organic matter (NOM) and sodium dodecyl sulfate (SDS) surfactant. The results obtained after 72hr equilibration are reproduced in Fig. 8.19. The apparent solubility of the three contaminants was higher in SDS and NOM solutions than the solubility of these compounds in distilled water. When a combined SDS-NOM aqueous solution was used, the apparent solubility of naphthalene, phenanthrene, and pyrene was lower than in the NOM-aqueous solution. [Pg.171]

Fig. 8.19 Solubility of polycyclic aromatic hydrocarbons (PAH) in sodium dodecyl sulfate (SDS, lOmg/L) and Sunwannee River natural organic matter (NOM, lOmg/L) solution. C denotes increased solubility in SDS and NOM solutions and is the solubility in water. (Cho et al. 2002)... Fig. 8.19 Solubility of polycyclic aromatic hydrocarbons (PAH) in sodium dodecyl sulfate (SDS, lOmg/L) and Sunwannee River natural organic matter (NOM, lOmg/L) solution. C denotes increased solubility in SDS and NOM solutions and is the solubility in water. (Cho et al. 2002)...

See other pages where Polycyclic aromatic hydrocarbons solubility is mentioned: [Pg.42]    [Pg.461]    [Pg.9]    [Pg.740]    [Pg.6]    [Pg.11]    [Pg.910]    [Pg.1394]    [Pg.1398]    [Pg.413]    [Pg.248]    [Pg.82]    [Pg.1649]    [Pg.1697]    [Pg.131]    [Pg.138]   
See also in sourсe #XX -- [ Pg.194 , Pg.195 ]




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