Predicting the solubilization preference of natural phenols to different solvents Charis M. Galanakisa, Vlasis Goulasc, Vassilis Gekasc a Department of Environmental Engineering, Technical University of Crete, Chania, Greece ([email protected]) b Department of Agricultural Sciences, Biotechnology and Food Science, Cyprus University of Technology, Lemesos, Cyprus ([email protected]) ABSTRACT The current investigation reports the prediction of activity coefficients of 15 natural phenols (tyrosol, hydroxytyrosol, oleuropein, caffeic, cinnamic, p-coumaric, ferulic, gallic, p-hydroxybenzoic, phydroxyphenyl acetic, protocatechuic, rosmarinic, sinapic, syringic and vanillic acid) in 7 solvents (water, ethanol, methanol, acetone, dichloromethane, ethyl acetate and diethyl ether) and 3 extraction temperatures (298.15, 313.15 and 333.15 K), by using the Universal Functional-group Activity Coefficient (UNIFAC) model. Solvents were classified for their ability to dissolve phenols and compared with experimental data of the literature in order to observe if the solvent extraction of phenols in practice matches with our theoretical approach. Results indicated the superiority of alcohols and acetone for the recovery of phenols in line with experimental data of previous studies. Furthermore, activity coefficients values were found to increase with increasing temperature. The prediction model may be particularly useful for the recovery of targeted individual phenols in order to screen them for biological activities. Finally, recovery of phenols is proposed to conduct initially with a polar protic solvent (hydro-ethanolic mixture) and then to progress sequentially extraction steps with solvents of reducing polarity in order to separate the compounds of interest for each case. This study provides a knowledge base for the selection of the most appropriate solvents for a given phenolic compound. Keywords: UNIFAC; extraction efficiency; phenolic acids; solubility; activity coefficient INTRODUCTION Broadly distributed in the plant kingdom and abundant in our diet, phenols are today among the most discussed categories of natural antioxidants [1]. Phenols include one or more hydroxyl groups (polar part) attached directly to an aromatic ring (non polar part) and are often found in plants as esters or glycosides, rather than as free molecules [2]. This stereochemistry distinguishes phenols according to their polarity variance. The above property has been utilized for the recovery of phenols from natural sources, which is usually accomplished with solvent extraction. The yield of this process is strongly dependent on the nature of the solvent [3]. The tendency of each phenol to be solubilized, transferred or diffused into a given solvent is governed by thermodynamics. One of the primary thermodynamic factors describing this tendency is the activity coefficient, which generally affects reversibly the solubility of phenols in nonpolar solvents (smaller coefficient corresponds to better solubility) [1, 4]. The objective of the current study was to predict the activity coefficients of 15 natural phenols in 7 solvents and 3 assayed extraction temperatures, by using the UNIFAC (UNIQUAC Functional-group Activity Coefficient) model [5]. Thereafter, with regard to the denoted data, solvents were classified for their ability to dissolve phenols. This classification was compared with bibliographic data obtained for agricultural wastes extraction in order to discuss if the recovery of phenols in practice matches with theoretical approach. MATERIALS & METHODS UNIFAC model and thermodynamics framework This method estimates activity coefficients in nonelectrolyte liquid mixtures remote from critical conditions [5, 6]. The main characteristics specifying the results of the model are the geometry (shape and size), the structure (distribution in chemical groups and subgroups) and the energy interaction between these groups and the assayed molecule. The basic properties of the subgroups include the relative volume (Rk), relative 1 surface (Qk) and the interaction parameter αmk (in Kelvin units) between them. The properties Rk, Qk and αmk exist in bibliography for a numerous of subgroups [6]. The activity coefficient γi of an ingredient “i” is supplied by the following equation: ln γ i = lnγ i + ln γ i C R (1) where “C” is the parameter of the combinatorial part (with regard to the shape and the size of the molecules) and “R” is the parameter of the residual part (with regard to molecules interactions). The natural logarithms of γ i C and γ i R are calculated by the following equations: J J C ln γ i = 1 - J i + ln J i - 5 q i 1 - i + ln i Li Li (2), β β R ln γ i = q i 1 − ∑ θ k ik − eki ln ik sk sk k (3) The parameters Ji and Li are calculated by the following equations: Ji = ri ∑ rj x j (4), j Li = qi ∑qjxj (5), j The parameters ri και qi are the parameters of relative volume and relative surface for the chemical substances and arise summative from the parameters Rk and Qk of the subgroups: ri = ∑ v k Rk (i ) (6), k q i = ∑ v k Qk (i ) (7), k where vk(i) is the number of subgroups “k” of a group inside a molecule “i”. The other parameters of equation (3) for the residual part of activity coefficient are defined by the following equations: (i ) v Qk eki = k qi (8), β ik = ∑ e mi τ mk (9), θk m ∑x q e = ∑x q i i i j ki (10), j j s k = ∑ θ m τ mk m (11), τ mk = exp - α mk T (12) The above 12 equations can be solved when the molecular fractions of the components (xi) and the absolute temperature (T) are known, by using the values of Rk, Qk and αmk found in literature. Nevertheless, the UNIFAC model possesses several limitations that should be accounted during calculations, i.e. the pressure should be less than 5 bar, the temperature should be less than 150 oC, calculations are only applicable to condensable non electrolytes, while components should not contain more than 10 functional groups [7]. xlUNIFAC tally The solution of the aforementioned equations was processed by using the software xlUNIFAC (version 1.0, GNU Public Licence, GRL, USA). This software is a Microsoft Excel logistic tally designed for the calculation of activity coefficients and partial vapor pressures, while it provides the possibility to examine the 2 effect of each parameter [7]. Thereby, the data of mixture ingredients (i.e. natural phenols and solvents) were inserted in the program and afterwards the solvent activity coefficients were calculated. Fifteen phenols (coumaric acid, vanillic acid, caffeic acid, ferulic acid, hydroxytyrosol, sinapic acid, cinnamic acid, phydroxyphenyl acetic acid, p-hydroxybenzoic acid, tyrosol, protocatechuic acid, syringic acid, gallic acid, rosmarinic acid and oleuropein), 7 solvents (water, ethanol, methanol, acetone, dichloromethane, ethyl acetate and diethyl ether) and 3 temperatures (298.15, 313.15 and 333.15 K) were introduced into the program and calculated according to the corresponding subgroups. In the case that a subgroup was not included inside the tally, the values of Rk and Qk were found in literature. The calculation of oleuropein activity coefficient was performed by simulating a part of the molecule with maltose and the addition of corresponding Rk and Qk values (10.7985 and 8.752, respectively) given in the literature [8]. RESULTS & DISCUSSION The activity coefficients of natural phenols for different solvents at 298.15 K are shown in Table 1. As a general rule, the values obtained for all the phenols were lower in alcohols and acetone, and possessed more or less the same decimal magnitude. Particularly, the lower values for hydroxytyrosol, tyrosol, oleuropein, caffeic, p-hydroxybenzoic, p-hydroxyphenyl acetic, protocatechuic and rosmarinic acid were obtained in ethanol. Other phenolic acids like vanillic, ferulic, sinapic and syringic possessed the lower values for methanol, while gallic, cinnamic and coumaric were the only acids that did not show the lower value for alcohols but for water, dichloromethane and acetone, respectively. Besides, all the phenols possessed the higher value for diethyl ether, except for oleuropein, coumaric, p-hydroxyphenyl acetic and protocatechuic acid that showed the higher activity coefficient for water. Table 2 represents the activity coefficients for different solvents at 313.15 K. Phenols showed again similar sympathy to alcohols and acetone, while the lower values were observed for each individual compound in the same solvent as above. An exception was observed for gallic acid, as the lower value was obtained for ethanol instead of water. The higher values were generally observed for diethyl ether and water (9 and 6 compounds, respectively). The activity coefficients for different solvents at even higher temperature 333.15 K are shown in Table 3. The lower values were observed for each individual phenol in the same solvent as in previous temperatures, but gallic and rosmarinic acid preferred methanol and acetone, respectively. The higher values were one more time observed for diethyl ether and water (9 and 5 compounds, respectively). Besides, many coefficients were similar for two solvents at this case, i.e. values observed for coumaric acid in alcohols (2.210-1), for vanillic acid in dicholoromethane and ethyl acetate (8.8-8.910-1), for hydroxytyrosol in water and dichloromethane (3.3-3.4100), for cinnamic acid in water and ethyl acetate (1.3-1.4100) and for phydroxyphenyl acetic acid for methanol and acetone (2.110-1). With regard to the variation of activity coefficients among the 3 assayed temperatures, values obtained for water, ethanol, methanol, acetone and ethyl acetate were generally enhanced by increasing temperature. On the other hand, values obtained for dichloromethane and diethyl ether were decreased by increasing temperature. Table 1. Solvent activity coefficients at 298.15 K for different natural phenols. Natural Solvent activity coefficients phenol Water Ethanol Methanol Acetone (W) (E) (M) (A) Caffeic acid 1.910-1 8.410-3 2.910-2 2.610-2 Cinnamic acid 2.0103 2.9100 1.1100 8.310-1 1 -1 -1 Coumaric acid 1.710 1.410 1.510 1.310-1 Ferulic acid 1.3100 2.710-1 1.410-1 1.810-1 -4 -4 -2 Gallic acid 7.510 8.710 1.110 1.410-2 0 -1 -1 p-Hydroxybenzoic acid 3.510 1.410 2.010 2.210-1 p-Hydroxyphenyl acetic acid 8.8100 9.810-2 1.510-1 1.510-1 -1 -2 -1 Hydroxytyrosol 9.110 2.710 2.010 2.310-1 Oleuropein 1.0100 3.310-5 7.410-4 3.610-4 0 -2 -2 Protocatechuic acid 4.710 1.010 4.510 5.210-2 -2 -4 -2 Rosmarinic acid 3.910 8.410 1.610 1.510-3 Sinapic acid 4.3100 3.210-1 1.010-1 2.510-1 0 -1 -1 Syringic acid 1.910 4.910 1.510 4.110-1 Tyrosol 5.0100 2.710-1 6.710-1 7.110-1 0 -1 -1 Vanillic acid 2.810 2.810 1.910 3.210-1 Dichloromethane (D) 4.610-1 6.710-1 4.910-1 4.310-1 1.5100 1.1100 6.310-1 4.8100 6.510-3 1.2100 3.610-2 4.210-1 7.710-1 3.2100 9.710-1 Ethyl Acetate (EA) 5.510-2 1.3100 2.4 10-1 3.510-1 3.610-2 4.110-1 2.710-1 3.710-1 1.510-3 1.110-1 3.410-3 5.110-1 8.610-1 9.910-1 6.410-1 Diethyl Ether (DE) 9.5100 1.8100 3.6100 8.2100 7.2101 6.3100 4.2100 8.0101 5.110-1 2.0100 1.4102 1.8101 3.1101 1.9101 1.5101 3 Table 2. Solvent activity coefficients at 313.15 K for different natural phenols. Natural Solvent activity coefficients phenol Water Ethanol Methanol Acetone Dichloro(W) (E) (M) (A) methane (D) Caffeic acid 4.010-1 1.410-2 3.710-2 3.510-2 4.410-1 3 0 0 -1 Cinnamic acid 1.710 2.810 1.210 8.510 6.610-1 1 -1 -1 -1 Coumaric acid 2.3 10 1.710 1.910 1.310 4.810-1 Ferulic acid 1.8101 3.110-1 1.610-1 2.110-1 4.210-1 -3 -3 -2 -2 Gallic acid 2.610 1.810 1.510 2.210 1.4100 p-Hydroxybenzoic acid 5.1100 1.710-1 2.410-1 2.510-1 1.0100 1 -1 -1 -1 p-Hydroxyphenyl acetic acid 1.210 1.310 1.810 1.710 6.210-1 0 -2 -1 -1 Hydroxytyrosol 1.810 4.010 2.110 2.610 4.0100 Oleuropein 2.3100 5.310-5 8.310-4 4.810-4 7.010-3 -1 -2 -2 -2 Protocatechuic acid 1.110 1.610 5.610 7.010 1.1100 Rosmarinic acid 1.610-1 1.810-4 1.810-2 2.310-2 3.510-2 0 -1 -1 -1 Sinapic acid 6.810 3.610 1.210 2.910 4.010-1 0 -1 -1 -1 Syringic acid 3.110 5.510 1.710 4.610 7.410-1 Tyrosol 6.3101 3.110-1 6.710-1 7.110-1 2.8100 0 -1 -1 -1 Vanillic acid 4.210 3.310 2.110 3.710 9.310-1 Table 3. Solvent activity coefficients at 333.15 K for different natural phenols. Natural Solvent activity coefficients phenol Water Ethanol Methanol Acetone Dichloro(W) (E) (M) (A) methane (D) Caffeic acid 8.710-1 2.310-2 4.810-2 4.810-2 4.310-1 Cinnamic acid 1.4103 2.7100 1.3100 8.610-1 6.610-1 Coumaric acid 3.1101 2.210-1 2.210-1 1.810-1 4.710-1 1 -1 -1 Ferulic acid 2.610 3.710 1.910 2.410-1 4.010-1 Gallic acid 9.810-3 3.910-3 2.110-3 3.610-2 1.4100 0 -1 -1 p-Hydroxybenzoic acid 7.410 2.210 2.810 3.010-1 9.910-1 1 -1 -1 p-Hydroxyphenyl acetic 1.810 1.610 2.110 2.110-1 6.110-1 acid Hydroxytyrosol 3.4100 5.910-2 2.310-1 2.910-1 3.3100 Oleuropein 5.1100 9.210-5 9.410-4 6.810-4 7.610-3 -1 -2 -2 Protocatechuic acid 2.510 2.710 7.210 9.710-2 1.1100 -1 -3 -2 Rosmarinic acid 7.110 3.910 2.110 3.610-3 3.410-2 Sinapic acid 1.1101 4.210-1 1.310-1 3.210-1 3.910-1 0 -1 -1 Syringic acid 5.010 6.210 1.910 5.110-1 6.910-1 Tyrosol 7.8101 3.610-1 6.610-1 7.010-1 2.4100 0 -1 -1 Vanillic acid 6.510 3.910 2.410 4.210-1 8.910-1 Ethyl Acetate (EA) 7.710-2 1.3100 2.8100 4.110-1 6.010-2 4.910-1 3.310-1 4.610-1 2.310-3 1.610-1 6.710-3 6.110-1 9.910-1 1.0100 7.510-1 Diethyl Ether (DE) 9.5100 1.8100 3.6100 7.9100 7.0101 6.3100 4.2100 6.7101 5.310-1 2.0101 1.3102 1.7101 2.9101 1.6101 1.5101 Ethyl Acetate (EA) 1.110-1 1.3100 3.410-1 4.910-1 1.010-1 5.810-1 4.110-1 Diethyl Ether (DE) 9.3100 1.8100 3.6100 7.5100 6.7101 6.2100 4.2100 5.710-1 3.910-3 2.310-1 1.410-2 7.410-1 1.2100 1.1100 8.810-1 5.4101 5.410-1 1.9101 1.1102 1.5101 2.5101 1.4101 1.4101 The activity coefficient data predicted by UNIFAC model indicate that natural phenols possess a solubility preference basically to solvents with intermediate polarity (alcohols and acetone), rather than more polar water or less polar dichloromethane and diethyl ether. The solubility tendency can be explained by the stereochemistry of phenols (the polar and the non polar fragment inside their molecules) and the intermolecular forces (mainly hydrogen bonds) occurred between them and the solvents. This was more obvious in the case of room temperature (Table 1, 298.15 K). In particular, the phenols’ hydroxyl groups can develop hydrogen bonds with the electronegative oxygen of ethanol, methanol or acetone. The alcohols’ hydroxyl groups can also develop hydrogen bonds with the oxygen atoms occurred inside phenol molecules (like oleuropein, ferulic, rosmarinic, vanillic, syringic or synapic acid) and this observation can explain their preference either to polar protic (methanol or ethanol) instead of polar aprotic solvents (acetone). The preference of phenols between methanol and ethanol can be attributed to their non polar part and the aliphatic fragment of alcohols. Methanol contains a smaller and more flexible aliphatic fragment compared to ethanol and thus surrounds easier phenols with substituted carbons inside their aromatic ring. This hypothesis was rather obvious in the cases of ferulic, vanillic, syringic and synapic acids (3 or 4 substituted carbons). On the other hand, bigger molecules (like oleuropein and rosmarinic acid), phenols with two anti-diametric substituted carbons (like p-hydrobenzoic and p-hydroxyphenyl acetic acid) or longer aliphatic fragments (like tyrosol and hydroxytyrosol) preferred ethanol, as it could “cover” better the gaps between the hydrogen bonds. In the case of gallic acid where the aromatic ring is well surrounded by 3 hydroxyls and one carboxyl group, the preferred solvent was the polar protic water molecule. Besides, the only studied phenol that did not 4 contain a hydroxyl group (cinnamic acid) preferred the polar aprotic dichloromethane, eventually due to the dipole-dipole interactions developed between the more electronegative fragment of the solvent (chlorine atoms) and the more electropositive fragment of the acid (hydrogen protons). For higher temperatures, the obtained prediction data coincided to the above considerations, although the induced thermal effect changed activity coefficient values. A potential explanation could be related to the number of hydrogen bonding with water molecule that decreases upon a temperature increase [9]. The above hypothesis was impressed in the prediction data, as activity coefficients of phenols were generally increased in polar protic (water, methanol and ethanol) and aprotic (acetone and ethyl acetate) solvents as a function of temperature, but decreased (or not varied) in less polar (aprotic) dichloromethane and non polar diethyl ether. Besides, few exceptions observed for specific phenols predicted the reduction of hydrogen bonds with increasing temperature, i.e. the coefficient of non-hydroxyl groups’ coumaric acid was decreased in polar water and ethanol. Moreover, the increase of activity coefficients suggests that the solubility of phenols into the aforementioned solvents is decreased as a function of temperature. However, this hypothesis is in contrast to the experimental and theoretical data of other studies referring that the solubility of phenols (tyrosol, protocatechuic, syringic, gallic, vanillic and coumaric acid) in water is increased by enhancing the temperature from 298.15 to 223.15 K [2, 10, 11]. Likewise, the solubility of gallic acid in polar protic (methanol or ethanol) and aprotic (ethyl acetate) solvents has been shown to increase smoothly with temperature [12]. A possible explanation for this discordance could be that the temperature induced solubility is affected more by other factors, i.e. fusion enthalpy, which should be taken account during prediction of thermal solvent extraction. Nevertheless, the correlation between phenols solubility and thermodynamic properties is not always clear as it has been referred for the case of several flavonoids [13]. According to bibliographic data, theoretical approach generally coincides with experimental findings, as polar (protic or aprotic) solvents are in both cases the most popular choice. For example, olive mill waste is a typical agricultural by-product that is known to contain all the discussed phenols of the current study (except from rosmarinic acid) and has been utilized for their recovery by solvent extraction [14]. Particularly, ethyl acetate has also been used for the recovery of low molecular weight phenolic acids like caffeic, ferulic and coumaric from this waste, but other common phenols (oleuropein, protocatechuic, syringic and cinnamic acid) were not detected in the corresponding extracts [14, 15]. The most active phenols (tyrosol and hydroxytyrosol) were preferably recovered with polar aprotic ethyl acetate as compared to non-polar solvents, while extraction yield enhanced with increasing polarity of the medium [16-19]. The last observation led the researchers to investigate more the polar protic (i.e. hydro-alcoholic) solvents. For example, water-ethanol mixtures have been reported for their advanced recovery of oleuropein, hydroxytyrosol and tyrosol [20], while hydro-methanolic mixtures have been referred to extract phenols with the highest yield and widest array compared to ethanol and ethyl-acetate [15]. Besides, rosmarinic acid has preferably been recovered with ethanol from sage and lemon balm [21-22]. Moreover, Lafka et al. [23] investigated the extraction of phenolic compounds (hydroxytyrosol, tyrosol, caffeic, syringic, vanillic and coumaric acid) with several solvents (ethanol, hydro-ethanolic mixture, methanol and acetone) from winery waste. According to this study, ethanolic extract possessed the highest antioxidant activity, although the difference from methanol and acetone extracts was negligible indicating that the recovery yield was rather similar. This result is in accordance to the theoretical estimation that the assayed phenols possessed activity of the same decimal magnitude for the aforementioned polar solvents. CONCLUSION In this study a knowledge base for the extraction of 15 phenols from natural sources was developed, reliant on the UNIFAC model and the calculation of the corresponding activity coefficients in 7 solvents. Based on the activity coefficient data, solvents were classified for their ability to dissolve phenols in 3 different temperatures. Predictions indicated that the studied phenols are generally solubilized easier in polar protic mediums like ethanol and methanol, but gallic, cinnamic and coumaric acids preferred water, dichloromethane and acetone, respectively. Increasing temperature changed the activity coefficient values of phenols, which tend to coincide for different solvents at the temperature of 333.15 K and thus to decline the solvent recovery preference. Despite the rather simple theoretical consideration (lower activity coefficient correspond to solubility and solvent recovery preference), a comparison with extraction data found in literature showed that the developed knowledge base could be utilized in order to predict the appropriate solvent for each extraction process, as modeling predictions were generally in accordance to experimental findings. 5 REFERENCES [1] Boskou D. 2006. Sources of natural antioxidants. Trends in Food Science and Technology, 17(9), 505512. [2] Queimada A.J., Mota F.L., Pinho S.P. & Macedo E.A. 2009. Solubilities of biologically active phenolic compounds: measurements and modeling. Journal of Physical Chemistry B, 113(11), 3469-3476. [3] Oreopoulou V. 2003. Extraction of natural antioxidants. In Tzia C., Liadakis G. (Eds.). Extraction optimization in Food Engineering. Marcel Dekker Inc, New York, USA, pp. 329-346. [4] Buchowski H., Ksiazczak A. & Pietrzyk S. 1980. Solvent activity along a saturation line and solubility of hydrogen-bonding solids. Journal of Physical Chemistry, 84(9), 975-979. [5] Fredenslund A., Jones R.L., Prausnitz J.M. 1975. Group-contribution estimation of activity coefficients in nonideal liquid mixtures. AIChe Journal, 21(6), 1086-1099. [6] Fredenslund A., Gmehling J., Michelsen M.L., Rasmussen P. & Prausnitz, J.M. 1977. Computerized design of multicomponent distillation columns using the UNIFAC group contribution method for calculation of activity coefficients. Industrial and Engineering Chemistry Process Design and Development, 16 (4), 450-462. [7] Randhol P. & Engelien H.K. 2000. xlUNIFAC version 1.0, a computer program for calculation of liquid activity coefficients using the UNIFAC Model. http://www.pvv.org/~randhol/xlunifac/. [8] Cooke S.A., Jónsdóttir S.Ó. & Westh P. 2001. Phase equilibria of carbohydrates: the study of a series of glucose oligomers from glucose to maltopentaose in aqueous solution - Experimental versus predicted data using various UNIQUAC/UNIFAC models. Fluid Phase Equilibria, 194 (Sp. Iss. SI), 947–956. [9] Ju S-.P., Liao M.-L., Yang S-.H. & Lee W-.J. 2007. Hydrogen-bond dynamics of interior and surface moleculesin a water nanocluster: temperature and size effects. Molecular Physics, 105(4), 429-436. [10] Noubigh A., Abderrabba M. & Provost E. 2007. Temperature and salt addition effects on the solubility behavior of some phenolic compounds in water. The Journal of Chemical Thermodynamics, 39(2), 297303. [11] Noubigh A., Cherif M., Provost E., & Abderrabba M. 2008. Solubility of some phenolic compounds in aqueous alkali nitrate solutions from (293.15 to 318.15 K). The Journal of Chemical Thermodynamics, 40(11), 1612-1616. [12] Daneshfar A., Ghaziaskar H.S., Homayoun N. 2008. Solubility of gallic acid in methanol, ethanol, water, and ethyl acetate. Journal of Chemical and Engineering Data, 53(3), 776-778. [13] Chebil L., Humeau C., Anthoni J., Dehez F., Engasser J-.M. & Ghoul M. 2007. Solubility of flavonoids in organic solvents. Journal of Chemical Engineering Data, 52(5), 1552-1556. [14] Obied H.K., Allen M.S., Bedgood D.R., Prenzler P.D., Robards K. & Stockmann, R. 2005. Bioactivity and analysis of biophenols recovered from olive mill waste. Journal of Agricultural and Food Chemistry, 53(4), 823-837. [15] Obied H.K., Allen M.S., Bedgood D.R., Prenzler P.D., Robards K. 2005. Investigation of Australian olive mill waste for recovery of biophenols. Journal of Agricultural and Food Chemistry, 53(26), 99119920. [16] Visioli F., Romani A., Mulinacci N., Zarini S., Conte D., Vincieri F.F. & Gallic C. 1999. Antioxidant and other biological activities of olive mill waste waters. Journal of Agricultural and Food Chemistry, 47(8), 3397-3401. [17] Allouche, N. 2004. Toward a high yield recovery of antioxidants and purified hydroxytyrosol from olive mill wastewaters. Journal of Agricultural and Food Chemistry, 52(2), 267-273. [18] Japón-Luján R. & de Castro M.D.L. 2007. Static-dynamic superheated liquid extraction of hydroxytyrosol and other biophenols from alperujo (a semisolid residue of the olive oil industry). Journal of Agricultural and Food Chemistry, 55(9), 3629-3634. [19] Durling N.E., Cathpole O.J., Grey J.B., Webby R.F., Mitchell K.A., Food L.Y. & Perry N.B. 2007. Extraction of phenolics and essential oil from dried sage (Salvia officinalis) using ethanol-water mixtures. Food Chemistry, 101(4), 1417-1424. [20] Dastmalchi K., Dorman H.J.D., Oinonen P.P., Darwis Y., Laakso I. & Hiltunen R. 2008. Chemical composition and in vitro antioxidative activity of a lemon balm (Melissa officinalis L.) extract. LWTFood Science and Technology, 41(3), 391-400. [21] Lafka T-.I., Sinanoglou V. & Lazos E.S. 2007. On the extraction and antioxidant activity of phenolic compounds from winery wastes. Food Chemistry, 104(3), 1206-1214. 6
© Copyright 2026 Paperzz