Development Of Enriched Oil With Polyphenols Extracted From Olive Mill Wastewater Part 2

Jun 02, 2023

The enrichment of the olive oil sample with the dispersion was then investigated. There was a 42.2% increase in polyphenols (from 60.2 ± 5.6 to 104.1 ± 8.3 mg GAE/Kg after 0.5% enrichment of micellar dispersions). The enriched olive oil is shown in Figure 4,  which also shows how the organoleptic characteristics of the olive oil changed. Although a pleasant, fruity odor (aroma) was developed, turbidity was observed without the deposition of sediment.

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Samples of micellar dispersions showed a decrease in free radicals after sonication with increasing concentration (Table 1) by the DPPH method. The highest reductions were observed at the highest concentrations for all samples while the 75-son sample displayed the highest value. The 60-son sample shows lower toxicity than the rest of the samples,  while the 90-son sample displays the highest. Statistical analysis, however, showed that there was no significant difference (p > 0.05) between the three sonication duration levels. It should also be noted that the 60-son and 75-son samples show similar mean inhibitory concentration patterns. In general, the repulsive interactions between the ionic head groups of the surfactant molecules were reduced when salts were added to the surfactant solution. As a result, it was encouraged to form micelles, which might have had an impact on DPPH  free-radical scavenging activity [29]. The hydroxytyrosol and tyrosol phenolic compounds are the most prevalent ones in the OMW extracts. According to Karadag et al. [30], OMW’s high hydroxytyrosol content is a contributing factor to its strong antioxidant activities. In their investigation on the recovery of phenolic compounds from OMW, Yangui, and Abderrabba [31] concluded that the recovered polyphenols showed strong antioxidant activity and rapid DPPH free-radical scavenging activity.

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3.3. Quality Control of Enriched Olive Oils 

Olive oil, including both refined and virgin oil, should have an acidity of less than 1%, as specified by Commission Implementing Regulation No 299/2013 [18] (Appendix— Characteristics of Olive Oil). All samples fell within the specified range, as seen in Table 2. At 20 ◦C, the refractive index should range from 1.4677 to 1.4705. The values of L* and a*  factors did not change noticeably. After the 75- and 90-son samples were included, factor b* was altered. The specific extinction coefficients were constant with the control olive oil and with the remaining enrichment sample olive oil. The samples of enhanced olive oil had protective factors that were less than a mean value of 1. Each sample demonstrated pro-oxidant activity. However, a 60-son oil sample with an approximate value of 1 was shown to have the highest oxidant efficiency (0.96 ± 0.05).

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The exothermic peaks of the extracts used in this investigation were measured using DSC (Figure 5). Thermographic curves that reveal the temperature of the extrapolated commencement of the thermo-oxidation process can be used by DSC to derive oxidation kinetic parameters. The highest oxidation peak on the thermographic curve is Tmax. As the sample demonstrates a stronger resistance, the higher the Tmax value. The 60-son oil sample showed the most important antioxidant efficiency.

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Due to the preservation of the initial sample (control), a monthly decrease in the total polyphenol content is observed. The initial sample was used for the monthly sampling (Figure 6).

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After enrichment, the total polyphenol content increased significantly. The 75-son oil had a significant consistency in polyphenol content, whose growth percentage peaked after four months (Figure 7). The 60-son oil sample was still largely stable after four months, but the 90-son oil sample exhibited significant changes throughout the same period.

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After sonication, the number of free radicals in micellar dispersion‐enhanced samples decreased when the concentration increased (Table 3). The 75‐son oil sample exhibited the greatest reduction in free radicals compared to other samples. The toxicity of the 75‐son  sample was lower than that of the other samples. Compared to other samples, the 90‐son  oil sample exhibited the highest level of toxicity, although the 60‐son oil and control samples behaved similarly.

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Due to its textural and organoleptic properties, negative environmental effects, and management and disposal issues, olive oil wastewater has attracted attention [32]. High amounts of polyphenolic compounds and the organic load of olive oil waste could be the cause of phytotoxicity and changes in soil microbiota [33]. The addition of polyphenols from oil waste to several food matrices has increased both their antioxidant properties and sensory characteristics, although it presents disadvantages as a fertilizer and feed additive. Previous research has shown that a significant quantity of polyphenols remains in the by-products of olive oil production [34–37]. To optimize the reintroduction of polyphenolic compounds into the food chain, increase their value, and improve the waste management of the olive oil industry, the effective recovery of polyphenolic compounds has been the subject of substantial research [38].

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4. Conclusions 

In our study, the cloud point extraction method, which used lecithin as an emulsifier at a concentration of 3%, produced significant recovery efficiency of micellar dispersions. Micellar dispersion sample sizes decreased following sonication as the concentration increased. The concentration of total polyphenols in olive oil samples rose to 42.2% with the addition of 0.5% micellar dispersions. The 75-son oil sample initially showed stability, but the total polyphenol concentration increased significantly after four months. In addition,  a significant reduction in free radicals was observed in this sample compared to other samples. The oil from the 60-son sample demonstrated less toxicity than the other samples in terms of the mean inhibitory concentration in the free radicals. No specific organoleptic characteristics have been noted. The colors of the samples remained unchanged, no sediment was visible, and the aroma of the olive oil was fruity and pleasant. More research is required to optimize the extraction conditions of polyphenolic components from olive mill wastewater. Their use could lead to better waste management in the olive oil industry as well as improvements in the nutritional quality of food products.

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Author Contributions: Conceptualization, O.G., I.G.R., S.I.L., and V.A.; methodology, O.G., and V.A.;  validation, A.V., V.A., and K.K.; formal analysis, A.V., and V.A.; investigation, A.V., and V.A.; resources, O.G. and S.I.L.; data curation, O.G., I.G.R., S.I.L., and V.A.; writing—original draft preparation, O.G., I.G.R., S.I.L., and V.A.; writing—review and editing, O.G., I.G.R., S.I.L., K.K., and V.A.; visualization, V.A.; supervision, O.G., I.G.R., and S.I.L.; project administration, O.G.; funding acquisition, O.G., and S.I.L. All authors have read and agreed to the published version of the manuscript.

Funding: This research received no external funding.

Data Availability Statement: All the data are contained within the article.

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Acknowledgments: Authors would like to thank Spyros Konakis (Konakis Olive Oil & Olives, Neos Oropos, GR-48061, Preveza, Greece) for providing the sample of olive mill wastewater.

Conflicts of Interest: The authors declare no conflict of interest.

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