Thermodynamic and kinetic models for the extraction of essential oil from savory and polycyclic aromatic hydrocarbons from soil with hot (subcritical) water and supercritical CO2.

Mechanisms that control the extraction rates of essential oil from savory (Satureja hortensis) and polycyclic aromatic hydrocarbons (PAHs) from historically-contaminated soil with hot water and supercritical carbon dioxide were studied. The extraction curves at different solvent flow-rates were used to determine whether the extractions were limited primarily by the near equilibrium partitioning of the analyte between the matrix and solvent (i.e. partitioning thermodynamics, or the "elution" step) or by the rate of analyte desorption from the matrix (i.e. kinetics, or the "initial desorption" step). Two simple models were applied to describe the extraction profiles obtained with hot water and with supercritical CO2: (1) a model based solely on the thermodynamic distribution coefficient KD, which assumes that analyte desorption from the matrix is rapid compared to elution. and (2) a two-site kinetic model which assumes that the extraction rate is limited by the analyte desorption rate from the matrix, and is not limited by the thermodynamic (KD) partitioning that occurs during elution. For hot water extraction, the thermodynamic elution of analytes from the matrix was the prevailing mechanism as evidenced by the fact that extraction rates increased proportionally with the hot water flow-rate. This was also confirmed by the fact that simple removal calculations based on a single KD (for each essential oil compound) gave good fits to experimental data for flow-rates from 0.25 to 4 ml/min. In contrast, supercritical CO2 extraction showed only minimal dependence on flow-rate, and the simple KD model could only describe the initial 20-50% of the extraction. However, a simple two-site kinetic model gave a good fit for all CO2 flow-rates tested. The results of these investigations demonstrated that very simple models can be used to determine and describe extractions which are limited primarily by partitioning thermodynamics, or primarily by desorption kinetics. Furthermore, these results show that the time required for the recovery of essential oil from savory with hot water can be minimized by increasing flow-rate, with little change in the total volume of water required. In contrast, raising the flow-rate of supercritical CO2 has little effect on the mass of essential oils recovered per unit of time, indicating that optimal recovery of these compounds with supercritical CO2 (amount recovered for the lowest amount of CO2) requires longer extraction times rather than faster flow-rates.

[1]  S. Hawthorne,et al.  Solubility of Liquid Organic Flavor and Fragrance Compounds in Subcritical (Hot/Liquid) Water from 298 K to 473 K , 2000 .

[2]  E. Reverchon,et al.  Modeling of supercritical fluid extraction from herbaceous matrices , 1993 .

[3]  Steven B. Hawthorne,et al.  Selective extraction of oxygenates from savory and peppermint using subcritical water , 2001 .

[4]  S. Hawthorne,et al.  Comparison of hydrodistillation and supercritical fluid extraction for the determination of essential oils in aromatic plants , 1993 .

[5]  S. Hawthorne,et al.  Determining PCB sorption/desorption behavior on sediments using selective supercritical fluid extraction. 1: Desorption from historically contaminated samples , 1999 .

[6]  M. D. L. Castro,et al.  An approach to the static–dynamic subcritical water extraction of laurel essential oil: comparison with conventional techniques , 2000 .

[7]  S. Hawthorne,et al.  Determining PCB Sorption/Desorption Behavior on Sediments Using Selective Supercritical Fluid Extraction. 3. Sorption from Water , 1999 .

[8]  J. King Fundamentals and Applications of Supercritical Fluid Extraction in Chromatographic Science , 1989 .

[9]  S. Hawthorne,et al.  Effect of SFE Flow Rate on Extraction Rates: Classifying Sample Extraction Behavior , 1995 .

[11]  J. King,et al.  Supercritical carbon dioxide extraction of evening primrose oil , 1991 .

[12]  John J. Langenfeld,et al.  A model for dynamic extraction using a supercritical fluid , 1990 .

[13]  M. J. Cocero,et al.  Mathematical model of supercritical extraction applied to oil seed extraction by CO2+saturated alcohol — I. Desorption model , 2001 .

[14]  M. Poletto,et al.  Comparison of models for supercritical fluid extraction of seed and essential oils in relation to the mass-transfer rate , 1996 .

[15]  Janusz Pawliszyn,et al.  Kinetic model of supercritical fluid extraction , 1993 .

[16]  M. S. Krieger,et al.  Extraction of cloransulam-methyl from soil with subcritical water and supercritical CO2. , 2000, Journal of chromatography. A.

[17]  John J. Langenfeld,et al.  Kinetic study of supercritical fluid extraction of organic contaminants from heterogeneous environmental samples with carbon dioxide and elevated temperatures , 1995 .

[18]  M. Goto,et al.  Shrinking-core leaching model for supercritical-fluid extraction , 1996 .

[19]  Steven B. Hawthorne,et al.  Solubility of Liquid Organics of Environmental Interest in Subcritical (Hot/Liquid) Water from 298 K to 473 K , 2000 .

[20]  S. Hawthorne,et al.  The Effect of solubility on the kinetics of dynamic supercritical-fluid extraction , 1992 .

[21]  S. Hawthorne,et al.  Method for determining the solubilities of hydrophobic organics in subcritical water. , 1998, Analytical chemistry.

[22]  S. J. Park,et al.  Phase behavior of CO2/crude oil mixtures in supercritical fluid extraction system: Experimental data and modeling , 1995 .

[23]  M. J. Cocero,et al.  Mathematical model of supercritical extraction applied to oil seed extraction by CO2+ saturated alcohol – II. Shortcut methods , 2001 .

[24]  Miller,et al.  Supercritical fluid extraction and accelerated solvent extraction of dioxins from high- and low-carbon fly ash , 2000, Analytical chemistry.

[25]  T. Veress Sample preparation by supercritical fluid extraction for quantification. A model based on the diffusion-layer theory for determination of extraction time. , 1994, Journal of chromatography. A.

[26]  S. Hawthorne,et al.  PAH release during water desorption, supercritical carbon dioxide extraction, and field bioremediation. , 2001, Environmental science & technology.

[27]  S. Hawthorne,et al.  Comparisons of soxhlet extraction, pressurized liquid extraction, supercritical fluid extraction and subcritical water extraction for environmental solids: recovery, selectivity and effects on sample matrix. , 2000, Journal of chromatography. A.

[28]  S. Hawthorne,et al.  Determining PCB sorption/desorption behavior on sediments using selective supercritical fluid extraction. 2. Describing PCB extraction with simple diffusion models , 1999 .

[29]  M. Webster,et al.  Fate of Treated and Weathered Hydrocarbons in Soil—Long-Term Changes , 2000 .