1. Introduction
In Europe, the agri-food sector produces vast quantities of by-products each year, generating significant environmental and economic challenges. According to Eurostat, more than 59 million tonnes of food waste were generated in the European Union in 2022, with approximately 19% originating from food processing and manufacturing stages [
1,
2]. Among agri-food chains, the olive oil, wine, cereal, and dairy industries represent major contributors to the generation of these by-products. When inadequately managed, by-products such as olive mill wastewater (OMWW) and grape pomace (GP) contribute to greenhouse gas emissions, soil and water pollution, and high disposal costs [
3,
4,
5].
OMWW is a liquid by-product generated during the mechanical extraction of olive oil. Worldwide production is estimated to range from 10 to more than 30 million m
3 per year, with typical yields of approximately 1.2 m
3 per tonne of olives processed [
3,
5]. OMWW is characterized by a very high organic load and by elevated concentrations of polyphenolic compounds that confer strong antioxidant properties but are also phytotoxic and poorly biodegradable [
3,
4].
GP, the main solid by-product of winemaking, is produced in quantities estimated between 10.5 and 13.1 million annual tonnes, reflecting the global scale of wine production. Europe is the largest contributor, with Italy, France, and Spain accounting for approximately half of worldwide wine output [
6,
7]. GP contains substantial amounts of structural carbohydrates, organic acids, residual sugars, and phenolic compounds, which enhance its functional value while also limiting its direct disposal due to slow biodegradation and potential environmental impact [
8,
9].
The magnitude and the pronounced seasonality of OMWW and GP production highlight the urgent need for effective stabilization and valorization strategies. Within a waste-to-resource framework, their recycling constitutes a sustainable strategy for mitigating the environmental burden. Such an approach, designed to facilitate the transition toward a circular economy model, can reduce pollution, promote resource efficiency, and contribute to environmental protection, particularly in Mediterranean regions where olive oil and wine production are geographically concentrated.
A distinctive feature of these by-products is their richness in bioactive compounds, especially polyphenols, which have attracted increasing interest due to their antioxidant, antimicrobial, and anti-inflammatory properties, with documented benefits in both human and animal nutrition [
10,
11,
12,
13]. The total polyphenol content of OMWW typically ranges from 0.3–0.4 g L
−1 in untreated samples [
3,
14,
15], and may increase up to approximately 2.5 g L
−1 in acidified extracts [
16]. GP is similarly recognized as a rich source of phenolics, with reported values of 144–298 mg gallic acid equivalents (GAE) g
−1 dry matter (DM) in skins and 327–540 mg GAE g
−1 DM in seeds [
17,
18].
In recent years, the use of GP as a feed ingredient has been widely addressed in the context of agro-industrial by-product valorization in animal nutrition. Recent reviews consistently indicate that GP can be incorporated into ruminant diets at moderate inclusion levels without detrimental effects on animal performance, while potentially improving the antioxidant status and lipid composition of milk and meat [
7,
19].
Similarly, olive-derived byproducts obtained from OMWW have been explored as dietary supplements in ruminants and other livestock species, with reported positive effects of OMWW-derived phenolic compounds—particularly hydroxytyrosol and related secoiridoids—on redox balance and antioxidant capacity, without adverse effects on rumen fermentation, nutrient utilization, or productivity when administered at controlled doses [
20,
21].
In this context, effective valorization strategies for these by-products require technological approaches that stabilize chemically complex agro-industrial matrices while preserving their functional properties over time.
A major constraint to the direct use of raw by-products in ruminant feeding is their marked seasonality and perishability, which hinder continuous and standardized supply. Ensiling suitable mixtures of agro-industrial byproducts has therefore emerged as a practical and sustainable strategy to stabilize seasonal availability and facilitate on-farm use [
22,
23]. Silage is a well-established preservation technique based on controlled anaerobic fermentation, allowing year-round feed availability and increased dietary flexibility through the inclusion of heterogeneous raw materials [
24]. When properly managed, ensiled feeds have been associated with improved nutrient utilization, digestibility, and productive performance in ruminants [
25].
In fact, it is well known that under anaerobic conditions of the ensiling process, lactic fermentation rapidly lowers pH, inhibits spoilage microorganisms, and contributes to preserving nutritional quality. However, factors such as composition of the ingredients, moisture content, buffering capacity, and fermentation kinetics affect the silage quality and its suitability for ruminant feeding [
23,
26,
27], factors that become particularly critical when complex mixtures rich in phenolic compounds are ensiled. In this regard, integrating OMWW and GP together with other agricultural byproducts such as straw and cheese whey into mixed silages could, therefore, extend shelf life and support sustainable feeding strategies.
Beyond their direct dietary application, GP and olive-derived by-products have also been evaluated within silage systems. Available studies indicate that their inclusion in silage formulations does not negatively affect fermentation quality or animal performance when applied at moderate inclusion levels [
28,
29]. Moreover, mixed silage systems combining GP, OMWW, and other byproducts have shown adequate fermentation characteristics and stability, supporting their practical applicability [
28,
30].
However, despite these promising findings, information on the optimization of co-ensiling strategies involving heterogeneous agro-industrial by-products remains limited, particularly with respect to the combined use of GP and OMWW under farm-scale conditions. The high variability in chemical composition and phenolic content of these substrates may influence fermentation dynamics, nutrient availability, and microbial activity, highlighting the need for targeted studies focusing on the stability of bioactive compounds and the functional quality of silages obtained from complex by-product mixtures.
In a previous laboratory-scale study, we demonstrated that ensiling raw mixed by-products (straw, GP, OMWW, and cheese whey), without preliminary fractionation or processing, was technically feasible and resulted in nutritionally stable silages retaining antioxidant properties over time, constituting a potential source of antioxidant compounds for ruminants [
28].
Building on these findings, the present study aimed to further explore integrated, multi-by-product silage systems, combining either GP or OMWW with wheat straw and cheese whey, by evaluating their quality under farm-scale silage conditions (≈300 kg bales). Chemical composition, fermentation parameters, and antioxidant capacity were monitored over a 150-day maturation period. The working hypothesis was that these formulations could produce nutritionally stable feed while retaining significant antioxidant potential over time, making them suitable for sustainable ruminant nutrition.
2. Materials and Methods
2.1. Chemicals
Methanol (HPLC grade, ≥99.9%), chloroform (≥99%), n-hexane (≥99%), diethyl ether (≥99%), formic acid (≥98%), phosphoric acid (85%), sulfuric acid (≥98%), sodium hydroxide (≥98%), potassium hydroxide (≥98%), and glacial acetic acid (≥99%) were purchased from Merck KGaA (Darmstadt, Germany). Trolox (6-hydroxy-2,5,7,8-tetramethylchroman-2-carboxylic acid, ≥97%), 2,2-diphenyl-1-picrylhydrazyl (DPPH, ≥95%), 2,2′-azino-bis(3-ethylbenzothiazoline-6-sulfonic acid) diammonium salt (ABTS, ≥98%), fluorescein sodium salt (≥95%), 2,2′-azobis(2-amidinopropane) dihydrochloride (AAPH, ≥98%), Folin–Ciocalteu reagent, gallic acid (≥98%), nonadecanoic acid (C19:0, ≥99%), and standard lactic acid (≥98%) were obtained from Sigma-Aldrich (Steinheim, Germany). Ammonium chloride (≥99%), phenol (≥99%), sodium hypochlorite (≥98%), and potassium persulfate (≥98%) were purchased from VWR International Eurolab S.L. (Barcelona, Spain), while sodium carbonate (≥99%), potassium phosphate monobasic/dibasic (≥99%), and acetic acid (≥99.8%) were supplied by PanReac AppliChem (Barcelona, Spain).
The short-chain fatty acid (SCFA) standard mix (TraceCERT®, CRM46975, 10 mM in water) and the 37-component fatty acid methyl ester (FAME) mix (CRM47885) were purchased from Supelco (Bellefonte, PA, USA). Reference phenolic and antioxidant standards, including catechin, epicatechin, caffeic acid, ferulic acid, rutin, naringenin, quercetin, kaempferol, myricetin, cyanidin-3-glucoside, malvidin-3-glucoside, delphinidin-3-glucoside, petunidin-3-glucoside, resveratrol, oleuropein, verbascoside, and aesculetin (≥98% purity), were obtained from Extrasynthèse (Genay, France) or Sigma-Aldrich (Steinheim, Germany). All reagents and solvents were of analytical or chromatographic grade and used without further purification.
2.2. Experimental Design and Silage Preparation
Two experimental silages were prepared using agro-industrial by-products, primarily grape pomace (GP) and olive mill wastewater (OMWW), co-ensiled with wheat straw, cheese whey, and molasses (
Table 1).
GP was obtained from a winery in Basilicata (southern Italy) after the pressing of
Vitis vinifera L. (cv. Primitivo). OMWW was collected from the milling of
Olea europaea L. (cv. Coratina) using a three-phase extraction system. Both by-products were transported chilled to a private farm located in southern Italy, where all subsequent silage preparation and ensiling procedures were carried out. At the farm, the by-products were thoroughly mixed with chopped wheat straw (
Triticum durum L., 3–4 cm pieces), cheese whey (CW), and molasses (Mol) using a feed mixer wagon to prepare the experimental silages. For SIL-2, the solid-to-liquid ratio was adjusted to 60:40 following Kafantaris et al. [
31], whereas SIL-1 was prepared at a 70:30 ratio (
Table 1). A commercial freeze-dried inoculum of
Lactiplantibacillus plantarum (14/DCSL CECT 4528; 250 × 10
9 cfu g
−1; Lactosil, CSL, Zelo Buon Persico, Lodi, Italy) was added in accordance with the manufacturer’s instructions to promote lactic acid fermentation and ensure proper stabilization of the silage mass.
Lactiplantibacillus plantarum was selected as a homofermentative lactic acid bacterium due to its well-documented ability to rapidly dominate the epiphytic microbiota and promote fast acidification of silage [
32].
2.3. Sampling and Sample Preparation
Silage samples were collected at multiple time points to monitor quality over storage. On day 0 (D0), immediately after silage preparation, samples were collected to represent the initial composition of each formulation. Subsequent samplings were performed at D15, D30, D60, and D150. At each sampling time point, three different bales per treatment were randomly selected. Each bale was considered an independent experimental unit, and different bales were used at each time point. From each selected bale, silage samples (~1 kg) were collected from different regions (top and bottom, approximately 30 cm from the surface, and central core) to account for within-bale variability. The subsamples collected from each bale were combined to obtain one representative sample for that bale. Each representative sample was subsequently divided into four subsamples. One subsample was used immediately for analyses on fresh matter, while the remaining three were processed for specific determinations: one was oven-dried at 60 °C, one was lyophilized, and one was stored at −20 °C until further analyses.
All analytical determinations were conducted on adequately homogenized samples.
2.4. Chemical Analyses
pH was measured on a 1:10 (
w/
v) water extract with a digital meter (SevenCompact™ S220, Mettler Toledo, Schwerzenbach, Switzerland). Buffering capacity was assessed by titration with 0.1 N NaOH as described by Playne and McDonald [
33]. Ground material (1 mm) was analyzed for dry matter (DM) (method 950.46), crude protein (CP) (990.03), ether extract (920.39), and ash (920.153) according to AOAC [
34]. Fiber fractions neutral detergent fiber (NDF), acid detergent fiber (ADF), and acid detergent lignin (ADL) were determined using the Van Soest method [
35]. Water-soluble carbohydrates (WSC) were quantified from frozen samples (−20 °C) following Dubois et al. [
36]. Ammonia nitrogen (NH
3–N) and lactic acid were determined by colorimetric assays according to Weatherburn [
37] and D’Alessandro et al. [
28], respectively. For both analyses, the extraction procedures were modified in this study to optimize homogenization and sample clarification. Briefly, 500 mg of fresh silage were extracted with 4–5 mL of deionized water using an Ultra-Turrax homogenizer (IKA Werke GmbH & Co. KG, Staufen, Germany) for 3 min, followed by 10 min sonication at room temperature and two centrifugation steps (5000 and 15,000 rpm, 10 min each, 4 °C). For NH
3–N determination, the clarified supernatant was acidified with 7.2 N H
2SO
4 and analyzed by the phenol–hypochlorite reaction as described by Partovi et al. [
38]. For lactic acid determination, the clarified extract was diluted (1:50) with deionized water and analyzed following the colorimetric procedure reported by D’Alessandro et al. [
28]. Accordingly, lactic acid was quantified using a dedicated colorimetric assay and was not included in the GC–MS analysis. Concentrations were calculated from calibration curves prepared with ammonium chloride and lactic acid standards, respectively, and expressed on a dry-matter basis.
2.5. Short-Chain Fatty Acids (SCFA)
The analysis of short-chain fatty acids (SCFA) was carried out according to D’Alessandro et al. [
28] with modifications in the extraction procedure. Briefly, 500 mg of fresh silage was extracted with 7.5 mL of distilled water under magnetic stirring for 15 min, centrifuged for 10 min at 4200 rpm and 4 °C, and 2.5 mL of the supernatant was acidified to pH 1 with 1.5 mL of 25% H
3PO
4. Five milliliters of methanol were then added to the samples, and the mixture was transferred into GC vials. Extracts were analyzed immediately or stored at −80 °C until analysis.
Gas chromatography–mass spectrometry (GC–MS) analysis was performed using a Trace 1610 GC system equipped with a TriPlus™ RSH SMART autosampler (Thermo Fisher Scientific, Rodano, Milan, Italy) and a TSQ™ 9610 triple quadrupole mass spectrometer (Thermo Fisher Scientific, Austin, TX, USA). Separation was achieved on a BP21 capillary column (30 m × 0.25 mm i.d., 0.25 µm film thickness; Trajan, Ringwood, Australia). One microliter of extract was injected in split mode (75:1). The oven temperature was programmed from 40 °C (1 min) to 160 °C at 10 °C/min, with a total run time of 21 min. Helium was used as carrier gas at a constant flow of 1.2 mL/min, and the MS was operated in full-scan mode (m/z 30–450).
Quantification was performed by external calibration using a commercial SCFA standard mixture (Supelco, Bellefonte, PA, USA; TraceCERT
®, CRM46975, 10 mM in water). Calibration curves were constructed using seven concentration levels obtained by serial dilution of the standard mixture in methanol. Owing to the different concentration ranges of individual SCFAs, separate calibration curves were applied, covering concentration ranges between 0.001 and 3 mM. Linearity was confirmed for all analytes, with coefficients of determination (R
2) ≥ 0.99. Compound identity was confirmed by comparison with authentic standards and the NIST mass spectral library. Representative GC–MS chromatograms of SCFA silage samples are provided in the
Supplementary Materials (Figures S1 and S2).
2.6. Lipid Extraction and FAME Derivatization
Lipids were extracted from 2 g of silage following mechanical homogenization using an Ultra-Turrax system, with a chloroform–methanol mixture (2:1,
v/
v) and converted to fatty acid methyl esters (FAMEs) according to Patel et al. [
39], with minor adaptations for silage matrices. After phase separation and washing with phosphate buffer, the organic layer was collected, evaporated under nitrogen, and weighed to determine total lipid content. Aliquots of the lipid extract (15 mg) were transmethylated with methanolic NaOH and methanolic HCl, spiked with nonadecanoic acid (C19:0) as internal standard, and the resulting FAMEs were extracted in hexane, evaporated, and re-dissolved in 250 µL of hexane for GC–MS analysis. Quantification was performed by external calibration using a 37-component FAME mix (Supelco, Bellefonte, PA, USA). Six calibration points were prepared by serial dilution of the stock solution up to 1:32. Calibration levels were obtained through a combination of dilution factors (1:4 to 1:32) and injection volumes (1–4 µL) to cover a wide dynamic range of analyte concentrations. Each calibration point and all samples were spiked with nonadecanoic acid (C19:0) from a 1 g L
−1 stock solution to reach a final concentration of 8 ppm after solvent evaporation and reconstitution in 250 µL of hexane. Calibration curves were constructed from the ratio of analyte to internal standard peak areas versus concentration and showed good linearity for all analytes (R
2 > 0.99). FAME identity was confirmed by comparison of retention times and mass spectra with authentic standards and the NIST mass spectral library.
2.7. FAME Analysis by GC–MS
The analysis of FAME was performed according to Sánchez-Parra et al. [
40] using a Trace 1610 gas chromatograph (Thermo Fisher Scientific, Rodano, Milan, Italy) coupled to a TSQ™ 9610 triple quadrupole mass spectrometer and equipped with a TriPlus™ RSH SMART autosampler (Thermo Fisher Scientific, Austin, TX, USA). Separation was achieved on a CP-Sil 88 fused silica capillary column (60 m × 0.25 mm i.d., 0.25 µm film thickness; Agilent Technologies, Santa Clara, CA, USA).
Samples (1.0 µL) were injected in split mode (5:1) at an injector temperature of 225 °C, using helium as carrier gas at a constant flow of 1.0 mL min−1. The oven temperature program was: initial 100 °C (2 min), ramped to 180 °C at 3 °C min−1 (2 min hold), then to 225 °C at 2.5 °C min−1 (2 min hold), for a total run time of approximately 48 min. The MS was operated in electron-impact ionization mode (EI, 70 eV) with a source temperature of 220 °C and transfer line at 230 °C, scanning the range m/z 45–350.
Data acquisition and processing were performed using Xcalibur software (version 4.6.67.17, Thermo Fisher Scientific, Austin, TX, USA). Representative GC–MS chromatograms obtained from FAME analyses are reported in the
Supplementary Materials (Figures S3 and S4).
2.8. Hydrophilic Extraction
Lyophilized and finely ground silage samples (200 mg) were weighed into Eppendorf tubes and extracted according to Tuárez-García et al. [
41]. Briefly, 1 mL of methanol: water (80:20,
v/
v) solution containing 1% formic acid was added to each sample, followed by vortex mixing for 10 s and sonication for 10 min. Samples were then centrifuged for 15 min at 4 °C at maximum speed. The supernatant was separated from the pellet, and the extraction procedure was repeated on the remaining pellet under the same conditions. The two supernatants were combined and adjusted to a final volume of 2 mL in a volumetric flask. One milliliter of the final extract was used for antioxidant activity assays, while the remaining 1 mL was used for phenolic compound identification and quantification by UHPLC-MS/MS. Total phenolic content (TPC) was determined using the Folin–Ciocalteu method [
42].
2.9. Antioxidant Activity
Antioxidant capacity was evaluated by ABTS, DPPH, and ORAC assays following the procedure described by Tuárez-García et al. [
41], using the hydrophilic extract described in
Section 2.8, suitably diluted when necessary to fall within the linear range of each assay. Results were expressed as g Trolox equivalents per kg DM.
2.10. Polyphenolic Analysis
The analysis of phenolic compounds was carried out using a UHPLC-MS/MS system, equipped with Vanquish Flex UHPLC (Thermo Fisher Scientific, Germering, Germany) coupled to triple quadruple TSQ Fortis™ Plus (Thermo Fisher Scientific, CA, USA). Analyses were performed on the hydrophilic extracts obtained as described in
Section 2.8. The separation of phenolic compounds was carried out on a Zorbax SB-C18 RRHD column (100 × 2.1 mm, i.d. 1.8 μm (Agilent, Santa Clara, CA, USA)) with a guard column of the same stationary phase maintained at 40 °C. The analytical procedure was carried out according to the method described by Pereira-Caro et al. [
43]. Mass spectrometric detection was performed in negative and positive ionization modes. Compounds were identified by comparison of retention times and mass signals with those of injected analytical standards. Standard solutions of phenolic compounds were prepared in methanol:water (80:20,
v/
v). Stock solutions were diluted and pooled to obtain mixed standard solutions at a final concentration of 200 mg/L for each compound. Nine working solutions, ranging from 0.01 to 50 mg/L, were prepared to construct the calibration curves. Phenolic compounds were quantified based on the theoretical exact mass of their molecular ions using external calibration curves. When authentic reference standards were unavailable, quantification was performed using calibration curves of structurally related compounds. Calibration ranges were selected according to the expected concentration levels in samples and showed good linearity (R
2 > 0.99). Detailed information on phenolic compound identification and quantification is provided in
Tables S5 and S6. Representative UHPLC-MS/MS chromatograms used for polyphenol identification are reported in the
Supplementary Materials (Figures S5 and S6).
2.11. Statistical Analysis
Data are presented as mean ± standard deviation (SD) of three independent biological replicates (bales) per treatment and sampling time. When applicable, analytical measurements were conducted in replicate and averaged prior to statistical analysis. Data were analyzed by two-way analysis of variance (ANOVA) according to the following linear model:
where
represents the observed value of each variable,
the overall mean,
the fixed effect of treatment (SIL-1, SIL-2),
the fixed effect of ensiling time (0, 15, 30, 60, 150 days),
the interaction between treatment and time, and
the random error term associated with independent bale-level replicates.
Assumptions of ANOVA (normality and homogeneity of variance) were verified prior to analysis. When significant effects were detected, mean separation was carried out using Tukey’s HSD post hoc test.
Effect sizes were estimated using partial eta squared (η2p) for the two-way ANOVA factors (treatment, time, and treatment × time interaction), and eta squared (η2) for one-way ANOVA analyses, based on the corresponding sums of squares from the ANOVA models, to quantify the proportion of variance explained by each factor. Statistical significance was set at p < 0.05, p < 0.01, and p < 0.001. All analyses were performed using R software (version 3.6.3; R Core Team, Vienna, Austria).
4. Discussion
Silage represents a fundamental and cost-effective feed resource for ruminants, providing both energy and protein while allowing long-term preservation of forages as well as agro-industrial residues. However, silage nutritional quality and fermentation performance remain critical determinants of animal productivity and health. High-quality silage, with proper fermentation process, supports efficient rumen function, milk production, and growth [
26,
29,
44]. In this context, the use of selected starter cultures is a key strategy to control fermentation dynamics and ensure consistent silage quality. Among lactic acid bacteria,
Lactiplantibacillus plantarum (formerly
Lactobacillus plantarum) is widely adopted as a starter culture in silage production due to its homofermentative metabolism, capacity for rapid lactic acid production, and effectiveness in suppressing spoilage microorganisms, thereby improving nutrient preservation and silage stability.
These properties have been extensively documented [
32,
45,
46]. Accordingly,
Lactiplantibacillus plantarum was selected in the present study to promote controlled fermentation in silages composed of agro-industrial substrates, where rapid stabilization is crucial for preserving functional compounds. Moreover, the present approach builds on previous investigations conducted on similar silage systems based on the same agro-industrial by-products [
28,
47], extending earlier laboratory-scale findings to farm-scale conditions. When agro-industrial by-products are used for ensiling, additional factors influence silage success, including their chemical composition (soluble carbohydrates, fiber fractions, and phenolic content), moisture level, and palatability. Proper dry matter adjustment and co-ensiling with complementary raw materials are therefore essential to optimize fermentation quality and feed acceptance [
48,
49,
50].
In this study, the two silage formulations based on OMWW or GP reflected the distinct chemical characteristics of their raw matrices and confirmed the central role of by-product selection in shaping the nutritional and functional properties of the final silage. In SIL-2, higher dry matter (DM) and structural fiber contents (NDF and ADF) were consistent with the greater inclusion rate of straw (60% vs. 10% in SIL-1). Conversely, SIL-1 exhibited a higher crude protein concentration, attributable to the contribution of GP, which is typically richer in nitrogenous compounds (10–15% DM) [
28,
51]. These differences were further supported by high η
2p values for DM, CP, NDF, and ADF, indicating a strong influence of treatment on silage chemical composition. These compositional values fall within ranges considered suitable for ruminant silages, ensuring appropriate retention times and stimulation of cellulolytic activity [
26].
From a nutritional perspective, the higher dry matter and fiber contents of SIL-2 suggest greater structural effectiveness for rumen function, whereas the higher crude protein level in SIL-1 better contributes to meeting the protein requirements of ruminants, which are recommended at 12–16% DM for lactation or growth in cows [
52].
The temporal variations in crude protein and DM content observed during ensiling were consistent with expected fermentation dynamics and microbial activity during silage storage. These processes typically lead to partial proteolysis and the conversion of soluble sugars into organic acids [
23].
Considering the structural fiber parameters, such as ADF, the differences between the two silages changed throughout the ensiling process. SIL-2 consistently exhibited higher ADF values, with a slight decline over time, whereas SIL-1 remained relatively stable (
Supplementary Table S1). These trends suggest distinct lignocellulosic degradation dynamics, likely linked to physicochemical properties of the respective matrices and the temporal evolution of the microbial community during fermentation [
49] (
Supplementary Table S1). The limited overall changes observed in crude protein and fiber fractions may reflect the primary role of
Lactiplantibacillus plantarum, which mainly affects fermentation dynamics rather than the structural composition of the biomass [
45,
46].
Differences in lipid profiles between formulations can be attributed primarily to the distinct composition of the ensiled substrates. The inclusion of GP in SIL-1 likely contributed to higher concentrations of medium-chain saturated fatty acids (C10:0, C14:0) and unsaturated fatty acids, including linoleic acid (C18:2), which is abundant in grape seeds and skins [
53,
54]. The presence of these lipid precursors may influence both microbial activity and the biochemical pathways involved in lipid metabolism during fermentation [
55]. Conversely, the relatively higher levels of arachidic acid (C20:0) detected in SIL-2 are consistent with residual lipids derived from olive processing associated with OMWW inclusion [
15].
Significant treatment × time interactions for specific fatty acids, including capric (C10:0) and palmitic (C16:0) acids, suggest that compositional differences between silages were more pronounced during the initial stages of ensiling and tended to decrease or even reverse as fermentation progressed. These temporal variations likely reflected the influence of lipolytic activity and microbial biohydrogenation processes occurring during storage [
56,
57] (
Supplementary Table S1). Overall, these compositional dynamics pointed to a qualitatively more favorable lipid profile in SIL-1, which appeared to be a more suitable substrate for balancing the dietary fiber fraction in ruminant rations (
Supplementary Table S1).
Fermentative parameters represent essential indicators of silage quality and preservation potential. The decrease in pH below 4.0 within the first weeks of storage, observed in both formulations, indicated a successful fermentation process, suitable for suppressing the growth of undesirable microorganisms [
23,
26]. Nevertheless, slightly lower pH values and higher buffering capacity in SIL-1 suggest greater resistance to pH fluctuations, likely due to the intrinsic physicochemical properties and organic acid composition associated with the inclusion of GP.
Higher initial water-soluble carbohydrate levels in SIL-2, along with their rapid decline during early ensiling, indicate swift utilization of fermentable substrates, consistent with intense lactic acid bacterial activity [
49,
58]. Ammonia nitrogen concentrations peaked around D30 more markedly in SIL-2, indicating extensive protein deamination during the initial fermentation phase, followed by subsequent stabilization [
23]. Overall, these dynamics aligned with those typically observed in well-preserved silages, where pH values below 4.0, progressive depletion of WSC, and controlled NH
3–N accumulation collectively ensured proper fermentation and long-term preservation [
22,
27,
59].
The SCFA profile further highlighted functional differences between the two silage formulations. SIL-2 displayed higher lactic acid concentrations, indicative of dominant homolactic fermentation and rapid acidification [
26]. Conversely, SIL-1 showed higher proportions of acetic, propionic, and isobutyric acids, reflecting a greater contribution of heterolactic fermentation. These non-lactic acids may confer enhanced aerobic stability owing to their antifungal properties of non-lactic volatile acids [
49,
59].
Over time, SCFA profiles converged toward a stable fermentative state [
23,
27,
58], with relatively high η
2p values indicating a strong influence of ensiling time on several SCFAs. Polyphenols may also have influenced silage microbial ecology through selective antimicrobial effects against spoilage microorganisms, while promoting the establishment of specific fermentative communities [
60,
61]. Such interactions between microbial metabolism and phenolic composition could have contributed to the divergent fermentation trajectories observed between SIL-1 and SIL-2, particularly during the early stages of ensiling.
Total phenolic content (TPC) and antioxidant activity are key indicators of the functional quality of silages, as they reflect the presence of bioactive compounds capable of mitigating oxidative stress and supporting animal health. In silages prepared from agro-industrial by-products, both the qualitative composition and the stability of polyphenols depend on the characteristics of the starting substrate, the ensiling process, and interactions with the matrix. Monitoring TPC and antioxidant activity over time, therefore, provides insights into the preservation of these compounds and their potential nutritional and functional relevance for ruminants.
In the present study, the significantly higher TPC observed in SIL-1 compared with SIL-2 confirms the major contribution of GP as a source of bioactive phenolics. In addition, the greater stability of the TPC in SIL-1 during storage highlights the higher resilience of the polyphenolic fraction associated with this matrix. The absence of a significant main effect of time on TPC, together with a significant treatment × time interaction, suggests matrix-dependent differences in polyphenol stability during ensiling [
62]. Specifically, SIL-1 showed greater stability, whereas SIL-2 exhibited an early decline in TPC. Similar patterns have been reported in polyphenol-rich silages, where phenolic compounds may undergo oxidation, partial degradation, or binding to the lignocellulosic matrix during fermentation [
63]. From a functional perspective, these results indicate that GP-derived polyphenols are more effectively preserved throughout storage. In contrast, phenolics associated with OMWW appear more susceptible to early structural or chemical modifications, likely due to their different chemical nature and matrix interactions [
64].
The greater stability observed in SIL-1 may also be related to microbial-mediated transformations occurring during ensiling. Lactic acid bacteria are known to possess enzymatic activities such as glycosidases and esterases that can modify polyphenols during fermentation [
60]. In particular, esterases may promote the release of bound phenolic acids from the lignocellulosic matrix, while glycosidases can hydrolyze flavonoid glycosides into more bioactive aglycone forms [
60,
65]. These mechanisms may partially explain the persistence of flavan-3-ols and phenolic acids observed in SIL-1 throughout storage.
Antioxidant capacity represents a key functional attribute of silages, reflecting the persistence of compounds capable of mitigating oxidative stress in ruminants. In silages derived from agro-industrial by-products, antioxidant potential is largely driven by the type and stability of polyphenolic compounds during storage.
Antioxidant capacity followed trends similar to those of the TPC pattern, reinforcing the functional relevance of polyphenol preservation. Both ABTS and DPPH radical-scavenging activities were consistently higher in SIL-1, whereas ORAC remained relatively stable over time. This pattern suggests that the GP-based matrix not only provides higher antioxidant capacity but also better preserves stable antioxidant compounds during ensiling. This behavior is likely attributable to the persistence of more stable flavan-3-ols and phenolic acids, whereas more labile fractions, such as certain glycosylated flavonoids, may contribute to the observed decline in ABTS activity [
43,
66,
67].
Previous studies have reported a strong positive correlation between TPC and antioxidant activity in silages enriched with vitivinicultural by-products [
68,
69], supporting the interpretation that polyphenol stability is a major driver of antioxidant potential. Importantly, silages with higher antioxidant capacity may contribute to improved oxidative status in animals by preserving or supplementing antioxidants such as α-tocopherol and β-carotene. Fermentation conditions and the use of specific lactic acid bacteria strains can further enhance antioxidant potential by protecting bioactive molecules and stimulating endogenous antioxidant enzymes, including catalase and glutathione peroxidase [
70]. Conversely, the ensiling process can also result in the loss of certain antioxidants, underscoring the importance of optimized silage preparation [
70].
Overall, the combination of high TPC and sustained antioxidant capacity characterizes SIL-1 as a silage with a superior functional profile throughout storage. The functional characteristics may have relevant implications for ruminant nutrition. Previous studies on silages enriched with GP and olive-derived by-products have reported improvements in systemic antioxidant status, oxidative stability, and milk fatty acid composition in lactating animals receiving bioactive silage-based diets [
71]. Although the present study did not include in vivo animal evaluations, the compositional and antioxidant features observed suggest a potential application of these silages as functional feed ingredients.
During ensiling, polyphenolic compounds exhibited distinct, class-specific dynamics strongly influenced by the composition of the starting matrix. In SIL-1, flavan-3-ols, including catechin and (epi)catechin, reached peak concentrations between D15 and D30, followed by a gradual decline.
In contrast, flavonols showed distinct temporal patterns: quercetin reached high concentrations at D15 and again at D150, whereas quercetin-3-glucoside peaked at D15 and progressively declined toward D150. These observations suggest that fermentation processes may facilitate the release of bound phenolics and promote the conversion of glycosylated forms into more bioactive aglycones [
72,
73]. Similar transformations have been reported in fermented grape-derived matrices, where microbial and enzymatic activities enhance the release of phenolics associated with plant cell wall components [
74,
75]. Progressive hydrolysis of glycosylated flavonoids may further contribute to the accumulation of aglycones, which generally exhibit higher antioxidant activity and bioavailability [
60,
76].
Anthocyanins displayed non-linear dynamics with moderate variations over time, reflecting their inherent oxidative lability. Among hydroxybenzoic acids, gallic and ellagic acids increased progressively, indicating greater stability and a sustained contribution to the antioxidant capacity of the silage [
66]. Despite an overall reduction in total polyphenol content from 52 to 36 mg/100 g DM during storage, SIL-1 retained a broad and diversified polyphenolic profile, with representative fractions persisting until the end of ensiling, highlighting its functional resilience. Differences in temporal behavior among phenolic subclasses likely reflect intrinsic chemical stability during fermentation. Anthocyanins are generally more susceptible to oxidation and degradation, whereas hydroxybenzoic acids and some flavan-3-ols exhibit greater resistance [
60,
77,
78], explaining their persistence during prolonged storage.
In SIL-2, the significant reduction in hydroxycinnamic acids during the early stages of ensiling (D15–D30), followed by a partial recovery at D150, reflects the lower stability of this phenolic subclass. In contrast, the hydroxybenzoic acid fraction decreased sharply from D0 and remained low thereafter [
64]. The rapid degradation of secoiridoids, including oleuropein and its derivatives, during the early stages of ensiling highlights a substantial structural loss typical of OMWW-based matrices [
62].
The marked reduction of secoiridoids observed in SIL-2 is consistent with previous findings on olive by-products, in which oleuropein and related derivatives undergo rapid microbial and enzymatic hydrolysis during fermentation [
61,
79]. In fermented olive matrices, β-glucosidases and esterases produced by lactic acid bacteria and yeasts can convert oleuropein into simpler derivatives, such as hydroxytyrosol and tyrosol [
79]. Although these transformation products were not specifically targeted in the present analytical approach, the observed decrease in secoiridoids likely reflects similar bioconversion processes occurring during ensiling. Overall, total polyphenol content decreased by more than 70% (from 22.1 to 6.3 mg/100 g DM) by 150 days, corresponding to a contraction of the phenolic profile and a potential reduction in the antioxidant and antimicrobial functionality of the silage [
68].
From a functional perspective, the phenolic composition differed markedly between the two silage types, reflecting the chemical characteristics of their respective raw materials. SIL-1, produced from GP, was characterized by high levels of flavan-3-ols (catechin and epicatechin), flavonols (quercetin and its glycosides), proanthocyanidins, and phenolic acids (gallic and ellagic acids). These compounds are widely recognized for their strong antioxidant potential, relative stability during fermentation, and possible nutraceutical effects [
67,
69]. Together, they confer SIL-1 a more complex and quantitatively richer phenolic profile, consistent with the higher in vitro antioxidant activity observed.
Conversely, SIL-2, prepared with OMWW, displayed a less diverse and quantitatively lower phenolic profile. This profile was dominated by secoiridoids (oleuropein and its derivatives) and hydroxycinnamic acids, which are highly susceptible to degradation during ensiling [
62,
64]. The rapid loss of these compounds, evident from the early stages of fermentation, resulted in a reduction in residual phenolic content and overall antioxidant capacity relative to SIL-1.
A non-monotonic trend was observed for isoeugenol, whose concentration decreased during the early stages of ensiling (D0–D30) and subsequently increased as fermentation progressed beyond 30 days. This pattern can be plausibly explained by the interplay between microbial transformation processes and the gradual release of phenolic compounds from the silage matrix. Isoeugenol, a phenylpropanoid compound, is known to undergo microbial oxidation during anaerobic and microaerobic conditions. Previous studies have reported its conversion into intermediate compounds such as vanillin, potentially via isoeugenol-diol, followed by further transformation into metabolites including vanillic acid and guaiacol [
80,
81]. These pathways involving oxidative and reductive reactions mediated by bacteria and fungi may account for the initial decrease in free isoeugenol during the early fermentation phase.
In parallel, polymerization or dimerization reactions of phenylpropanoids under fermentative conditions have been described, potentially contributing to a reduction in the detectable free isoeugenol fraction. At later stages of ensiling (D30–D150), the partial increase in isoeugenol concentration may be associated with its gradual release from bound or conjugated forms within the lignocellulosic silage matrix, promoted by ongoing enzymatic activity and microbial adaptation, resulting in a dynamic balance between degradation and formation processes. Similar delayed releases of phenolic compounds during prolonged fermentation have been attributed to progressive modifications of plant cell walls and to esterase-mediated cleavage of esterified phenolics, particularly in silages rich in fibrous substrates [
82,
83].
It should also be noted that downstream metabolites of isoeugenol were not specifically targeted in the present analytical approach. Consequently, some transformation products may have occurred only as transient intermediates or may have been further metabolized, preventing their accumulation at detectable levels. Overall, the non-monotonic behavior of isoeugenol likely reflects a dynamic equilibrium between degradation, transformation, and gradual release processes, which are characteristic of complex, multi-substrate fermentation systems [
80,
81]. Collectively, these findings indicate that the choice of agro-industrial by-products plays a key role in shaping the chemical composition, affecting not only total polyphenol content but also the stability, temporal dynamics, and diversity of bioactive phenolic metabolites throughout storage. This pattern is further supported by the generally high η
2 values, indicating strong time-related effects across most phenolic subclasses.
These compositional features ultimately contribute to the functional quality of the final silage, with potential implications for the antioxidant status of ruminants and animal-derived products, as reported for diets supplemented with agro-industrial residues [
84].
Despite the promising results obtained, some limitations should be acknowledged. Although the experimental design was conducted at farm scale with biological replicates, the silage formulations investigated represent specific combinations of agro-industrial by-products selected through preliminary evaluations. Further studies, including a broader range of formulations, would help assess the general applicability of these findings. Moreover, this work primarily focused on chemical composition, fermentative parameters, and in vitro antioxidant properties, while the effects on animal performance are currently being addressed in complementary in vivo trials. Finally, the inherent variability of agro-industrial by-products may influence silage quality under different production conditions and should therefore be considered when extrapolating these results.