1. Introduction
Onions (
Allium cepa L.) are one of the most important and widely cultivated vegetables globally, ranking second after tomatoes in cultivation volume. Global onion production has increased by more than 25% in recent years [
1]. Current worldwide onion production is estimated at 93.23 million tons [
2]. This high production generates a substantial amount of onion solid waste (OSW), which includes the semi-dried edible outer layers, the dry layers, and the apical and basal trimmings, as well as undersized, deformed, infected, or broken bulbs [
3]. This waste stream creates both biological and environmental challenges. OSW is not appropriate as animal feed, cannot be used as fertilizer [
2], and should not be released into landfills due to its strong sulfurous aroma and the fact that it promotes microbial growth, such as of
Sclerotium cepivorum. Additionally, due to its high moisture content, incineration is economically unfavorable [
3,
4,
5].
Flavonoids constitute the largest phenolic group in onions [
6,
7,
8]. Red onions contain the highest flavonoid levels, followed by yellow onions [
3]. According to Chadorshabi et al. [
3], flavonoids in red onion skins range from 1.276 to 169 mg/g, and their amount is higher than that of white onion skin, with an average value of 0.08 mg/g. Flavonoids exhibit different biological activities such as antioxidant, antibacterial, antifungal, cardioprotective, anti-inflammatory, antiviral, neuroprotective, anti-obesity, anticancer, and antidiabetic effects [
3].
The first step in obtaining bioactive compounds from OSW is extraction, and both conventional and modern techniques have been explored. Conventional methods such as Soxhlet and maceration are effective but require long times and large solvent volumes [
9]. More advanced approaches, including microwave- and ultrasound-assisted extraction, have been optimized for quercetin recovery and improved efficiency [
10,
11]. Subcritical water extraction has also been applied, offering high yields under eco-friendly conditions [
12]. In parallel, green solvents such as deep eutectic mixtures have shown promise for selective recovery of flavonoids [
13]. Despite these advances, there are very few studies on pressurized liquid extraction (PLE), and none that combine PLE with encapsulation and direct application of OSW extracts in real food systems.
Green extraction techniques, whether applied independently or in combination with conventional methods, are increasingly recognized for their efficiently in recovering a wide range of bioactive substances [
14]. Among them, PLE applies elevated temperature and pressure to enhance solvent penetration, solubility, and mass transfer, thereby accelerating extraction and improving yields [
15]. When operated under near-subcritical conditions, PLE further increases efficiency while maintaining solvent safety and reproducibility [
16].
PLE outperforms conventional (e.g., Soxhlet, maceration) and many modern extraction techniques by combining high pressure and temperature to achieve faster extraction, lower solvent use, and higher yields with excellent reproducibility. Studies show PLE can recover up to 30–40% of plant material in minutes versus hours and with sixfold less solvent than Soxhlet, while outperforming supercritical CO
2 and ultrasound/microwave-assisted methods in efficiency and consistency [
15,
17,
18,
19,
20]. Although equipment cost and risk of thermolabile degradation are drawbacks, PLE’s balance of speed, efficiency, and scalability makes it superior for routine and industrial applications [
21]. As a result, PLE is regarded as a high-performance and eco-friendly technique for extracting bioactive compounds from natural sources, such as plants, offering broad potential applications in the food industry [
22].
The rising demand for plant-based products rich in bioactive compounds has increased the need for methods that enhance food stability and shelf life. To achieve this, plant extracts are often converted into powders using spray drying—a process that rapidly removes moisture by exposing the material to hot air, producing a stable powder with preserved physicochemical properties [
23]. This method also encapsulates sensitive compounds, protecting them from light, moisture, and oxygen [
24,
25]. Spray drying improves product stability, quality, and shelf life while reducing volume and weight, making storage and transport easier [
23]. The final product quality depends on the properties of the feed solution, spray dryer settings, and the type and ratio of carriers used [
26]. Common carriers include polysaccharides, proteins, and lipids, with β-cyclodextrin (β-CD), gum arabic (GA), and maltodextrin (MD) widely used for their solubility, low viscosity, affordability, and stabilizing properties [
23,
27].
The aim of this study is to develop and evaluate the potential use of OSW encapsulated extracts as natural antioxidants in food. The optimal conditions for PLE of OSW were identified with the use of response surface methodology (RSM). Key extraction parameters—solvent composition (ethanol–water), temperature, liquid-to-solid ratio, and extraction time—were optimized. The optimal extract was analyzed for total polyphenol content (TPC) and total anthocyanin content (TAC), as well as antioxidant activity using DPPH• and FRAP assays. Moreover, the optimized extract was encapsulated by spray drying in GA and analyzed for encapsulation efficiency (%), loading capacity (%), and process yield (%). High-performance liquid chromatography (HPLC) with diode-array detection (DAD) was applied to the resulting powder for the identification of individual polyphenolic compounds. Finally, the encapsulated extract was incorporated into a food system (mayonnaise), and oxidative stability was monitored over 14 days. According to the authors’ knowledge, no prior study has integrated PLE optimization, encapsulation, and direct application of OSW extracts in a real food system (mayonnaise).
2. Materials and Methods
2.1. Chemicals and Reagents
Polyphenolic standards of HPLC grade (≥99.0% w/w) were obtained from MetaSci (Toronto, ON, Canada). From Panreac (Barcelona, Spain), gallic acid (≥99.0% w/w), Folin–Ciocalteu reagent, ammonium iron(II) sulfate hexahydrate (≥99.0% w/w), ethanol (≥99.8% v/v), and thiobarbituric acid were sourced. Trolox (≥96.5% w/w) was purchased from Glentham Life Sciences (Corsham, UK). Sigma-Aldrich (Darmstadt, Germany) supplied TPTZ (≥98% w/w), DPPH (≥90.0% w/w), methanol (≥99.8% v/v), hydrochloric acid (37% w/w), and trichloroacetic acid (≥99.0% w/w). Iron(III) chloride hexahydrate (≥99.0% w/w) was obtained from Merck (Darmstadt, Germany). Penta (Prague, Czech Republic) provided ammonium thiocyanate (≥99.0% w/w), chloroform, formic acid (99.8%), and anhydrous sodium carbonate. Acetonitrile (99.9%) was purchased from Labkem (Barcelona, Spain), while dichloromethane and ethyl acetate were obtained from Carlo Erba (Vaulx-de-Reuil, France). Hydrogen peroxide (35%) was sourced from Chemco (Malsch, Germany). Deionized water used in all experiments was produced using a deionizing column.
2.2. Onion Solid Waste (OSW) Material
The red onions used for this study were purchased from a local market in Karditsa, Greece. The variety was “MIRSINI”, with a diameter greater than 75 mm, and the cultivation region was Viotia, Greece. The OSW (skins, outer fleshy scales, and apical and basal trimmings) were removed and immediately subjected to freeze-drying. The freeze-drying process was carried out using a BK-FD10P lyophilizer (Biobase, Jinan, China). Following drying, the material was ground using an electric milling device to reduce particle size, thus increase surface area, mass transfer and solvent penetration for more efficient extraction. The ground material was then sieved using an Analysette 3 PRO sieve shaker (Fritsch GmbH, Idar-Oberstein, Germany), resulting in a median particle size of 144 μm. The resulting powder was stored at −40 °C until used in the subsequent experiments.
2.3. Experimental Design
To optimize the extraction of total polyphenol content (TPC), total anthocyanin content (TAC), and antioxidant activity (measured via FRAP and DPPH
• assays) from OSW powder, a Response Surface Methodology (RSM) approach was applied using a Custom Quadratic design. This design, chosen for its efficiency and rapid data acquisition, allowed for thorough exploration of four key factors, each evaluated at three levels. A Pressurized Liquid Extraction (PLE) system (Fluid Management Systems, Inc., Watertown, MA, USA) was used to perform all extractions under a constant pressure of 1700 psi, as determined from preliminary testing. The independent variables included the solvent composition, specifically the aqueous ethanol concentration (
C, %
v/
v), reflecting solvent polarity (
X1); the liquid-to-solid ratio (
R, mL/g) (
X2), which is equivalent to the solvent-to-feed ratio (S/F) commonly used in extraction engineering; the extraction temperature (
T, °C) (
X3); and the extraction time (
t, min) (
X4). Each factor was tested at three coded levels: low (−1), medium (0), and high (+1), as shown in
Table 1. Solvent levels were selected to span a polarity gradient, while the remaining factor levels were established based on prior experimental results.
To ensure method reproducibility, 18 experiments were conducted—each one repeated three times and incorporating three central points. Mean values of all responses were computed for analysis. To enhance model accuracy, a stepwise regression approach was applied, removing non-essential terms to reduce variance. This yielded a second-order polynomial equation representing the effects and interactions of the independent variables:
where
Yk is the predicted response, while
Xi and
Xj denote the independent variables. The coefficients
β0,
βi,
βii, and
βij correspond to the intercept, linear terms, quadratic terms, and interactions, respectively.
2.4. Determination of Antioxidant Components by Spectrophotometric Methods
2.4.1. Total Polyphenolic Content (TPC)
The total phenolic content (TPC) was assessed using the Folin–Ciocalteu method [
28], with results reported as milligrams of gallic acid equivalents (GAE) per gram of dry weight (dw). A calibration curve ranging from 10 to 100 mg/L of gallic acid (R
2 = 0.9996) in water was employed for quantification. Briefly, 100 μL of the appropriately diluted extract was mixed with 100 μL of Folin–Ciocalteu reagent and allowed to react for 2 min. Next, 800 μL of a 5%
w/v sodium carbonate solution was added. The mixture was incubated for 20 min at 40 °C, shielded from light, and absorbance was then measured at 740 nm using a Shimadzu UV-1900i UV/Vis spectrophotometer (Kyoto, Japan). The 40 °C incubation was carried out using an Elmasonic P70H ultrasonic bath from Elma Schmidbauer GmbH (Singen, Germany). Each sample was analyzed in triplicate, and the average result was used for calculations.
2.4.2. Total Anthocyanin Content (TAC)
The total anthocyanin content (TAC) was determined using a previously described method [
29]. A 70 μL aliquot of the extract was combined with 930 μL of a hydrochloric acid solution (0.25 M in ethanol) in a 1.5 mL Eppendorf tube and vortexed. After 10 min, the absorbance was measured at 520 nm, with the ethanolic HCl solution serving as the blank. The concentration of total anthocyanins (
CTA) was then calculated as cyanidin-3-
O-glucoside equivalents (CyE) using Equation (2):
where
A is the absorbance at 520 nm, MW is the cyanidin-3-
O-glucoside molecular weight (449.2),
FD is the dilution factor, and
= 26,900.
Therefore, the TAC was determined as follows in Equation (3):
where
V denotes the volume of the extraction solvent (in L), and
w represents the dry weight of the sample (in g).
2.4.3. Ferric-Reducing Antioxidant Power (FRAP, PR) Activity
A previously established method, based on the common electron-transfer technique, was used to assess the antioxidant capacity of the extracts [
28]. This approach involved measuring the reduction in the iron oxidation state from +3 to +2. Briefly, 50 μL of the appropriately diluted sample was combined with 50 μL of FeCl
3 solution (4 mM in 0.05 M HCl) and incubated at 37 °C for 30 min. After 5 min, 900 μL of TPTZ solution (1 mM in 0.05 M HCl) was added, and the absorbance was recorded at 620 nm. Quantification was performed using a calibration curve prepared with ascorbic acid (50–500 μM in 0.05 M HCl, R
2 = 0.9997). The results were expressed as μmol of ascorbic acid equivalents (AAE) per gram of dry weight (dw). All measurements were carried out in triplicate, and mean values were reported.
2.4.4. DPPH• Radical Scavenging Activity
The DPPH
• scavenging assay, as described in a previous study [
28], was applied. To begin, 25 μL of the appropriately diluted sample extract was mixed with 975 μL of DPPH
• solution (100 μmol/L in methanol), and absorbance at 515 nm was recorded immediately and after 30 min. Quantification was based on a calibration curve constructed with ascorbic acid (100–1000 μmol/L in methanol, R
2 = 0.9926). Results were expressed as μmol of ascorbic acid equivalents (AAE) per gram of dry weight (dw). All measurements were carried out in triplicate, and mean values were reported.
2.5. Spray Drying Encapsulation
Prior to spray drying, the optimized onion solid waste (OSW) extract was mixed with gum arabic (GA) as the encapsulating agent. Since the optimal extract was obtained using ethanol, solvent removal was first performed with a Heidolph Laborota 4000/G3 rotary evaporator, equipped with Rotavac Valve Control (Heidolph Instruments GmbH & Co. KG, Schwabach, Germany). The resulting concentrate was resuspended in a 60:40 (v/v) ethanol–water solution, followed by a second evaporation step to ensure complete removal of ethanol. The remaining aqueous extract was subsequently mixed with GA at a sample-to-carrier ratio of 1:6 (w/w), determined based on the total polyphenol content (TPC) of the resuspended extract.
The spray drying process was carried out using a BUCHI mini-B-290 laboratory spray dryer (BUCHI, Flawil, Switzerland) equipped with a standard 1-mm nozzle. Operating parameters were adapted with slight modifications from the method described by [
30]. The inlet and outlet air temperatures were set to 170 °C and 95 °C, respectively. The solution was fed at a rate of 3.5 mL/min, with a spray air flow rate of 742 L/h and a pressure drop of 1.35 bar. The aspirator was operated at a gas flow rate of 35 m
3/h. After spray drying, the resulting powders were stored in sealed plastic containers and kept refrigerated until further analysis.
2.6. Microcapsule Characterization Metrics
2.6.1. Process Yield
The yield obtained from the spray-drying process was determined in accordance with Equation (4) [
31]:
where
mp is the mass of the powder obtained (g),
md is the dry matter of the extract in the volume used for drying (g), and
mc is the mass of carrier (g) incorporated into the extract prior to spray-drying.
2.6.2. Encapsulation and Loading Capacity
Encapsulation capacity was evaluated as the proportion of total to surface polyphenols in the microcapsules, following the procedure of Robert et al. [
32], while loading capacity was expressed as the amount of polyphenols retained in the microcapsules relative to their dry weight after spray drying [
33].
To determine total polyphenols (TP), 0.2 g of powder was mixed with 2 mL of a methanol–acetic acid–water solution (50:8:42,
v/
v/
v), vortexed for 1 min, and subjected to ultrasonic extraction at room temperature for 20 min. The extract was then centrifuged at 3000 rpm for 10 min, and the supernatant was analyzed using the Folin–Ciocalteu method [
23].
Surface polyphenols (SP) were obtained by mixing 0.2 g of powder with 2 mL of ethanol–methanol (50:50, v/v), followed by vortexing for 1 min and centrifugation at 3000 rpm for 10 min. The supernatant was filtered and analyzed in the same way as TP.
Encapsulation capacity (EC) was calculated according to Equation (5):
where TP is the concentration of total polyphenols (mg GAE/g) and SP is the concentration of surface polyphenols (mg GAE/g).
Loading capacity (LC) was determined using Equation (6):
where TP is the total polyphenols in the microcapsules (g), and MC is the microcapsule weight (g) after spray drying.
2.6.3. HPLC-DAD Quantification of Key Polyphenols
The analysis was conducted using a Shimadzu CBM-20A liquid chromatograph coupled with a Shimadzu SPD-M20A diode array detector (Shimadzu Europa GmbH, Duisburg, Germany), following the procedure described in a previous study [
28]. Separation was performed on a Phenomenex Luna C18 (2) column (100 Å, 5 μm, 4.6 × 250 mm; Phenomenex Inc., Torrance, CA, USA) maintained at 40 °C. The mobile phase consisted of (A) 0.5% aqueous formic acid and (B) 0.5% formic acid in acetonitrile/water (6:4,
v/
v). The gradient elution was programmed as follows: 0% B at the start, increased to 40% B, then to 50% B within 10 min, further raised to 70% B over the next 10 min, and maintained at 70% B for 10 min. The mobile phase flow rate was 1 mL/min. Compounds were identified by comparing their retention times and UV–Vis spectra with those of authentic standards. Quantification was based on calibration curves prepared with concentrations ranging from 0 to 50 μg/mL.
2.7. Integration into Mayonnaise Matrix
2.7.1. Mayonnaise and Mayonnaise Samples’ Preparation
Mayonnaise was prepared according to the formulation presented in
Table 2, using sunflower oil, olive oil, egg yolk, mustard, vinegar, lemon juice, salt, and pepper powder. Following preparation, different concentrations of the encapsulated OSW extract were incorporated into 100 g portions of mayonnaise, which were placed in sterile plastic containers. A 100 g sample size was selected to ensure homogeneous mixing and reproducible incorporation of encapsulated onion solid waste (EOSW) without compromising analytical accuracy. Each treatment was prepared in quintuplicate, providing five independent replicates per condition. This ensured reproducibility and sufficient material for repeated analyses across all time points. In addition, a post hoc power analysis of the main oxidative stability parameters (peroxide value and TBARS) confirmed that the selected sample size achieved statistical power > 0.8 at α = 0.05, demonstrating adequacy for detecting treatment effects. For comparison, two synthetic antioxidants—butylated hydroxytoluene (BHT) and potassium sorbate—were added at different concentrations (
Table 3). The concentrations used are based on preliminary experiments and the European (EU) Union Regulations and Greek Food and Beverage Code for mayonnaise. A control sample consisting of mayonnaise without antioxidant addition was also prepared. Each sample was prepared in quintuplicate, so as one sample could be used for each testing day.
All samples were stored at ambient temperature (25 ± 2 °C) in the dark for 14 days. On days 1, 3, 7, and 14, aliquots were withdrawn and analyzed to determine the oxidative stability of the formulations.
2.7.2. Determination of Oxidative Stability Parameters
At each sampling point, the pH and color of the mayonnaise samples were measured. Antioxidant activity and oxidative stability were further evaluated in both the polar and non-polar fractions. In the polar fraction, analyses included the determination of total polyphenol content (TPC) and DPPH• radical scavenging activity. In the non-polar fraction, DPPH• activity, peroxide value (PV), and thiobarbituric acid reactive substances (TBARS) formation were assessed.
The pH value of the samples was measured with an XS pH 60 VioLab Bench pH meter coupled with a 201 T DHS electrode (Capri, Italy). The color of the extracts was assessed using a method previously established by Cesa et al. [
34]. The CIELAB parameters (
L*,
a*, and
b*) were measured for the hydroalcoholic extracts with a colorimeter (Lovibond CAM-System 500, The Tintometer Ltd., Amesbury, UK). The color description is based on three parameters: The
L* value represents lightness, ranging from 0 (absolute black) to 100 (absolute white). The
a* value indicates the degree of greenness (positive values) or redness (negative values). Similarly, the
b* value reflects the extent of blueness (positive values) or yellowness (negative values). Color intensity is represented by
Cab or
C* (Chroma, saturation), which is calculated using the equation C* = (
a2 +
b2)
(1/2).
2.7.3. Polar Compound Determinations
One gram of mayonnaise was mixed with 2 mL of
n-hexane to dissolve the lipid fraction, followed by extraction with 2 mL of a methanol–water solution (60:40
v/
v). The mixture was vortexed thoroughly and centrifuged at 4500 rpm for 5 min. The resulting polar (hydrophilic) extract was then collected and used for total polyphenol and DPPH
• antioxidant analyses. The total polyphenol and DPPH
• protocols are described in
Section 2.4.1 and
Section 2.4.4, respectively.
2.7.4. Non-Polar Compound Determinations
For the determination of non-polar compounds, 1.5 g of mayonnaise was placed in a 2 mL Eppendorf tube and subjected to centrifugation at 10,000 rpm. This process facilitated the separation of the oil phase, which was subsequently collected for DPPH•, peroxide value (PV), and thiobarbituric acid reactive substances (TBARS) assays.
The radical scavenging activity of oils was evaluated using the DPPH
• assay in the lipophilic phase, following the procedure of [
33]. A 950 μL aliquot of DPPH
• solution (100 μM in ethyl acetate) was combined with 50 μL of oil diluted tenfold in ethyl acetate. Reduction of the DPPH
• radical to its non-radical form was monitored spectrophotometrically, and antioxidant capacity was quantified against a Trolox calibration curve (50–500 μM, R
2 = 0.999). Results were expressed as Trolox equivalent antioxidant capacity (TEAC, μM/kg oil).
Lipid peroxidation was assessed via peroxide value determination according to IDF method 74A:1991, with minor modifications [
33]. This method quantifies hydroperoxides through their reaction with Fe
2+ and thiocyanate, yielding a red Fe
3+–thiocyanate complex. For analysis, 20 μL of oil was dissolved in 1960 μL dichloromethane/ethanol (3:2,
v/
v), followed by the addition of 10 μL each of ammonium thiocyanate and ammonium iron (II) sulfate. After 5 min, absorbance was recorded at 500 nm. A hydrogen peroxide calibration curve (50–500 μM, R
2 = 0.995) was used for quantification, and values were expressed as mmol H
2O
2/kg oil.
Secondary oxidation products were determined by the TBARS assay [
35]. Oil samples (0.1 g) were incubated with 5 mL of TBA reagent (15 g trichloroacetic acid, 1.76 mL HCl, and 0.375 g TBA in 100 mL water) at 95 °C for 20 min. After cooling, 200 μL chloroform was added, and the mixture was centrifuged (4500 rpm, 10 min). The absorbance of the supernatant was measured at 532 nm, using water as the blank. Values were expressed as mmol malondialdehyde equivalents (MDAE)/kg oil, calculated from a calibration curve (15–300 μM, y = 0.0032x − 0.0004, R
2 = 0.9999).
2.8. Statistical Analysis
All statistical analyses were performed using JMP® Pro 16 (SAS Institute Inc., Cary, NC, USA). Data were first tested for normality using the Kolmogorov–Smirnov test. Differences among treatments were evaluated by analysis of variance (ANOVA), and means were compared using Tukey’s HSD test at a significance level of p < 0.05. Each extraction experiment was conducted in duplicate, and all measurements were obtained in triplicate. Results are expressed as mean ± standard deviation. Multivariate techniques, including partial least squares (PLS), principal component analysis (PCA), multiple correspondence analysis (MCA), and Pareto plot analysis, were further applied to explore variable relationships and identify the most influential extraction parameters.