Open Access Article
Kieu Dang Minh Nhuta,
Dao Pham Duy Quang
a,
Phung Van Trunga,
Tran Hoai Cuonga,
Pham Thi Nhat Trinh*b,
Nguyen Thi Nhu Quynhc,
Cao Van Duc and
Le Tien Dung
*a
aInstitute of Advanced Technology, Vietnam Academy of Science and Technology (VAST), 1B TL29, Ho Chi Minh, Vietnam. E-mail: ltdung@iat.vast.vn
bDepartment of Natural Science, Tien Giang University, 119 Ap Bac, My Tho, Dong Thap, Vietnam. E-mail: phamthinhattrinh@tgu.edu.vn
cFaculty of Pharmacy, Lac Hong University, Dong Nai, Vietnam
First published on 17th March 2026
Post-distillation residues (PDR) from Vitex rotundifolia essential-oil production represent an underutilized biomass stream that can retain medium- and high-polarity constituents. Here, PDR and raw fruits were extracted with 30–96% ethanol under matched ultrasound-assisted extraction conditions and evaluated by TPC/TFC and four bioactivity assays (DPPH, ABTS, NO inhibition, and xanthine oxidase). Among residue-derived extracts, R70 showed the best overall performance (DPPH and ABTS IC50 = 24.87 and 24.90 µg mL−1; NO IC50 = 104.99 µg mL−1), comparable to the corresponding raw extract (E70; NO IC50 = 102.86 µg mL−1). Untargeted UHPLC-QTOF-MS/MS enabled curated tentative annotation of 88 metabolites in R70, dominated by flavonoids, phenolic derivatives, terpenoids, and oxylipins, and four representative known constituents (casticin, quercitrin, vitexilactone, and agnuside) were isolated and structurally confirmed. A comparative greenness screening showed improved mass-based metrics for the residue-based route (PMI/E-factor 1409/1407 vs. 1925/1921 for the raw-material route), while per-batch energy-related indicators were higher (climate change 3.63 vs. 2.49 kg CO2-eq), highlighting a material-energy trade-off. Overall, PDR can serve as a viable secondary feedstock for recovering non-volatile bioactive constituents, and the environmental performance of residue valorization is condition-dependent.
The post-distillation residue (PDR) represents a major portion of the original plant mass and is expected to retain medium- and high-polarity constituents that do not evaporate during essential-oil extraction. Valorizing this residue aligns with green chemistry and circular-bioeconomy principles, which emphasize resource efficiency, waste reduction, and multi-product recovery.10–12
In practice, however, the chemical composition and bioactivity of V. rotundifolia residues remain poorly characterized, and no systematic comparison with extracts obtained from raw fruits has been reported.
Most earlier investigations have emphasized essential-oil constituents or extracts from raw fruits, whereas the chemical and sustainability potential of the post-distillation residue remains insufficiently understood. In particular, it is still unclear whether bioactive constituents persist after hydrodistillation, how chemically rich residue-derived extracts are when examined using LC-MS/MS metabolite profiling, and how residue valorization influences material efficiency and energy-related environmental impacts.
To address these issues, we systematically compared extracts obtained from raw fruits and post-distillation residues of V. rotundifolia using ethanol at different concentrations. Phenolic content and antioxidant and anti-inflammatory activities were quantified to identify extracts of interest. Untargeted UHPLC-QTOF-MS/MS profiling was performed to map the chemical space of the most active residue extract, followed by isolation and structure elucidation of major constituents. Finally, a greenness assessment incorporating PMI, E-factor, and life-cycle-inspired indicators was conducted to evaluate the sustainability of valorizing PDR as a feedstock for natural-product extraction.
Earlier work on Vitex rotundifolia has primarily focused on volatile constituents (essential oils) or extracts prepared directly from raw fruits, whereas the chemical space and bioactivity retained in the post-distillation residue have rarely been examined in a condition-matched manner. In particular, comprehensive LC-MS/MS-based profiling of residue-derived non-volatile metabolites and a side-by-side comparison of residue and raw-material extracts across solvent strengths remain limited in the literature.
In this study, we provide a condition-matched comparison of ethanol extracts from raw fruits and post-distillation residues across 30–96% ethanol, integrating multi-assay bioactivity profiling, untargeted UHPLC-QTOF-MS/MS annotation of the most active residue extract, isolation/structure elucidation of representative constituents, and a life-cycle-inspired, per-batch greenness screening (PMI, E-factor and selected impact indicators). This integrated workflow is intended to evaluate residue valorization potential and to identify key material-energy trade-offs, rather than to claim chemical novelty of individual compounds or unconditional environmental superiority.
Chemicals for phytochemical assays: Folin–Ciocalteu reagent (Merck, Germany), gallic acid (99.5%, Merck), quercetin (Merck), aluminum chloride, sodium carbonate, sodium hydroxide, sodium nitrite, sulfuric acid (Xilong, China).
Chemicals for antioxidant assays: 1,1-diphenyl-2-picrylhydrazyl (DPPH, Merck), ABTS (2,2′-azino-bis(3-ethylbenzothiazoline-6-sulfonic acid)), potassium persulfate.
Chemicals for NO inhibition experiment: sulfanilamide and N-(1-naphthyl)ethylenediamine dihydrochloride (NED).
Reagents and materials for chromatographic separation: silica gel 60 (Merck), C18 reversed-phase silica gel (Merck), Sephadex LH-20 (Merck), macroporous resin D101.
Other materials: dimethyl sulfoxide (DMSO, Fisher, USA), analytical-grade distilled water, and standard alkanes (C8–C30) for GC–MS retention index calibration.
UV-visible spectrophotometer: UV-1800 (Shimadzu, Japan), used for measuring absorbance in TPC, TFC, DPPH, and ABTS assays.
Gas chromatography–mass spectrometry (GC–MS): GC-2030 system coupled with GCMS-QP2020 detector (Shimadzu, Japan), equipped with Rxi-5MS capillary column (30 m × 0.25 mm, 0.25 µm film thickness), used for essential oil analysis.
Nuclear magnetic resonance (NMR) spectrometer: 1H-NMR (500 MHz) and 13C-NMR (125 MHz), used for structural elucidation of isolated compounds (measured at the Central Analytical Laboratory, Ho Chi Minh City, Vietnam).
Raw data were processed in SCIEX OS (v1.2.0.4122) for peak detection, alignment, deconvolution, and extraction of precursor/MS/MS spectra. All reported features were supported by MS/MS spectra. Putative annotations were assigned by direct MS/MS library comparison against MoNA and MassBank, accepting candidate precursors within ≤10 ppm. For each library hit, the number of matched diagnostic fragments (n_frag) was recorded and used to support a confidence tier; annotations were retained when the MS/MS spectra were chemically interpretable and showed library-consistent fragment evidence.23 All assignments are reported as putative identifications (MSI level 2).24 To improve transparency and mitigate false positives, an internal confidence tier was applied: high (|Δppm| ≤ 5 and n_frag ≥ 8), medium (|Δppm| ≤ 10 and n_frag = 4–7), and low (|Δppm| ≤ 10 and n_frag < 4). These annotations provide dereplication-level chemical context and are not intended as definitive identification or quantification. For each annotated feature, Δppm, n_frag, and confidence tier are reported in Table S4.
:
1), ethyl acetate, and methanol. This process yielded four fractions: the n-hexane fraction (VRH, 3.92 g), the n-hexane:ethyl acetate fraction (VRHEA, 5.67 g), the ethyl acetate fraction (VREA, 2.05 g), and the methanol fraction (VRM, 2.69 g).
The VRHEA fraction (5.67 g) was further fractionated on a normal-phase silica gel column using a gradient elution of n-hexane and ethyl acetate (from 9
:
1 to 6
:
4, v/v). Eight subfractions were obtained (VRHEA1- 8), among which VRHEA5 (144.1 mg) and VRHEA2 (357.5 mg), showing well-resolved spots on TLC, were selected for further purification. Compound VR1 (87.2 mg) was crystallized directly from VRHEA5. VRHEA2 underwent successive purification steps using silica gel columns with n-hexane:ethyl acetate and chloroform:methanol systems, ultimately yielding compound VR2 (13.7 mg).
The methanol-soluble fraction (VRM, 2.69 g) was fractionated on a D101 macroporous resin column using a gradient elution from water to 100% methanol, resulting in five subfractions: VRM1 (5342.2 mg), VRM2 (640.3 mg), VRM3 (850 mg), VRM4 (612.8 mg), and VRM5 (146.4 mg). VRM3 was further processed by silica gel column chromatography, from which subfraction VRM3.5 was purified using Sephadex LH-20 (MeOH 100% as eluent), followed by reversed-phase silica gel chromatography (MeOH–H2O = 1
:
2, v/v) to yield compound VR3 (19.5 mg). Similarly, VRM3.4 was separated on Sephadex® LH-20 eluting with MeOH to obtain compound VR4 (48.1 mg).
All isolated compounds (VR1–VR4) were monitored for purity by thin-layer chromatography using multiple solvent systems and visualized under UV light or by sulfuric acid staining. The structures of the four isolated constituents were established from their full NMR spectrum (Fig. S1–S8) and verified by comparison with literature-reported NMR values.
Assumptions and limitations. Because the target marker content in PDR was not quantified, no product-based functional unit (e.g., per gram of casticin) was applied; therefore, the environmental indicators are reported as per-batch, process-level comparisons. Electricity consumption was calculated from equipment rated power and operating time for each unit operation, and solvent losses were estimated based on measured volumes before and after recovery steps. To improve transparency, the inventory assumptions (electricity, solvent use and losses) are summarized in the SI, and a brief scenario check is provided to illustrate how solvent-recovery and energy-integration assumptions influence the direction and magnitude of the results.25–27
Additional inventory transparency (screening-level): the full process-step inventory of electricity, water and ethanol inputs for Route A and Route B is reported in Tables S7A–S7C. Transport distances were not included at this screening level, and no stochastic uncertainty analysis was performed; instead, a simple ±20% scenario check (electricity and solvent recovery/loss) is provided in Table S7C to illustrate robustness of comparative trends.
Concentration – response data for antioxidant (DPPH, ABTS) and enzyme/inflammation assays (XO, NO) were analyzed by non-linear regression using OriginPro 2019 for IC50 estimation. Multiple-group comparisons used one-way ANOVA followed by Tukey's HSD post-hoc test. Pairwise comparisons (when applicable) used two-tailed Student's t-test. Statistical significance was set at p < 0.05. PCA and Pearson correlation coefficients (r) were performed in OriginPro 2019. LCA inventories were compiled per batch and characterized using Mobius with EF 3.1 characterization factors.
| RT (min) | RI | Compound | Content (%) | |||
|---|---|---|---|---|---|---|
| Adam | Cacld. | EO3 | EO4 | EO5 | ||
| a Only compounds with content >1% in at least one distillation time or relevant to bioactivity (e.g., α-pinene, 1,8-cineole) are listed. RT = retention time. Detail compounds was shown in Table S1. | ||||||
| 7.633 | 932 | 926 | α-Pinene | 0 | 0 | 5.69 |
| 12.86 | 1026 | 1025 | 1,8-Cineole | 0 | 0 | 3.00 |
| 28.792 | 1346 | 1344 | α-Terpinyl acetate | 12.20 | 5.90 | 8.56 |
| 31.019 | 1417 | 1415 | trans-Caryophyllene | 1.24 | 0.67 | 1.13 |
| 33.668 | 1452 | 1461 | α-Humulene | 0.96 | 0.59 | 0.91 |
| 33.81 | 1522 | 1517 | δ-Cadinene | 1.42 | 0.81 | 1.39 |
| 40.001 | 1649 | 1643 | cis-Guaia-3,9-dien-11-ol | 6.70 | 6.49 | 0 |
| 40.146 | 1749 | 1751 | α-Bisabolol oxide A | 3.97 | 3.98 | 3.74 |
| 40.319 | 1987 | 1982 | Manool oxide | 21.35 | 21.74 | 18.44 |
| 40.784 | 2043 | 2045 | Kaurene | 9.33 | 8.89 | 16.50 |
| 40.99 | 2184 | 2184 | Sandaracopimarinal | 18.94 | 18.93 | 10.29 |
| 41.188 | n.a | 2573 | 4,16-Androstadien-3-one | 1.65 | 1.58 | 2.79 |
| Oxygenated compounds | 53.34 | 56.04 | 49.08 | |||
| Non-oxygenated compounds | 44.67 | 41.95 | 49.64 | |||
As hydrodistillation primarily removes volatile constituents, the resulting residue is expected to retain non-volatile metabolites, providing the rationale for the subsequent comparative extraction, bioactivity screening, and LC-MS/MS dereplication of the PDR. The essential-oil composition and antibacterial screening results (Tables 1 and 2) are included solely to document the distillation step and to describe the volatile fraction removed during processing. No causal linkage between individual volatile constituents and antibacterial effects is inferred in the present study; the main focus is the non-volatile fraction retained in PDR and its recovery under the tested extraction conditions.
| Sample | S. aureus (mm) | MRSA (mm) |
|---|---|---|
| a Values represent the average diameter (mm) of the inhibition zone against tested bacteria (n = 4). Larger diameters indicate stronger antibacterial activity. | ||
| EO3 | 8.2 ± 0.1 | 5.2 ± 0.2 |
| EO4 | 8.1 ± 0.2 | 9.1 ± 0.1 |
| EO5 | 14.9 ± 0.1 | 4.7 ± 0.2 |
| Gentamicin | 21.6 ± 0.2 | 22.1 ± 0.2 |
| DMSO 100% | 0.0 | 0.0 |
| Sample | Source | EtOH (%) | Yield (%) | TPC (mg GAE per g) | TFC (mg QE per g) | IC50 (µg mL−1) | |||
|---|---|---|---|---|---|---|---|---|---|
| DPPH | ABTS | NO | XO | ||||||
| a TPC = Total phenolic content (mg gallic acid equivalents per gram dry extract); TFC = Total flavonoid content (mg quercetin equivalents per gram); DPPH, ABTS = Antioxidant activity; NO: nitric oxide; XO: xanthine oxidase; values are mean of 3 replicates. | |||||||||
| R30 | Residue | 30 | 11.84 | 97.55 | 239.99 | 43.79 | 65.51 | 142.14 | 193.18 |
| R50 | Residue | 50 | 10.91 | 109.39 | 298.90 | 27.74 | 29.54 | 150.93 | 182.24 |
| R70 | Residue | 70 | 10.53 | 149.03 | 413.97 | 24.87 | 24.90 | 104.99 | 146.86 |
| R96 | Residue | 96 | 9.69 | 100.43 | 179.48 | 62.50 | 76.32 | 184.03 | 117.62 |
| E30 | Raw | 30 | 8.67 | 100.00 | 269.72 | 39.04 | 46.92 | 120.15 | 196.58 |
| E50 | Raw | 50 | 7.08 | 136.69 | 351.66 | 27.91 | 40.73 | 141.85 | 188.16 |
| E70 | Raw | 70 | 6.69 | 155.67 | 426.29 | 25.26 | 28.35 | 102.86 | 138.07 |
| E96 | Raw | 96 | 7.54 | 159.38 | 451.73 | 22.71 | 25.38 | 92.70 | 108.77 |
| Vitamin C | 5.37 | ||||||||
| Trolox | 2.87 | ||||||||
| Dexamethasone | 0.49 | ||||||||
| Allopurinol | 1.68 | ||||||||
Across all extraction conditions, raw-material extracts generally exhibited higher TPC and TFC than residue-derived samples. Among them, E96 yielded the highest phenolic (159.38 mg GAE per g) and flavonoid content (451.73 mg QE per g), whereas R70 represented the strongest extract from the residue series (TPC: 149.03 mg GAE per g; TFC: 413.97 mg QE per g). These results confirm that although essential-oil distillation removes volatile constituents, substantial amounts of medium- and high-polarity phytochemicals remain available for recovery.
Antioxidant activities showed a similar pattern. R70 displayed the strongest activity among residue extracts (DPPH IC50 = 24.87 µg mL−1; ABTS IC50 = 24.90 µg mL−1), whereas E96 remained the most potent overall (22.71 µg mL−1 and 25.38 µg mL−1, respectively). As noted previously,28–30 the antioxidant capacity does not always scale proportionally with TPC/TFC, indicating the influence of compound subclass distribution and structural features.
Cell viability assays in RAW264.7 cells indicated that all extracts maintained ≥80% viability up to 200 µg mL−1, while moderate cytotoxicity was observed at 400 µg mL−1 for selected samples (Table S6); NO inhibition was therefore interpreted within non-cytotoxic concentration ranges.
To explore relationships among extracts, PCA was conducted using six normalized variables (TPC, TFC, DPPH, ABTS, NO, XO). The score plot (Fig. 1A) suggests that R70 and E70 have broadly similar phytochemical and bioactivity profiles, whereas E96 is positioned separately, consistent with its high phenolic/flavonoid content. Given the limited number of samples, the PCA is used here as an exploratory visualization rather than a definitive classification model.
![]() | ||
| Fig. 1 Principal component analysis (PCA) of extract phytochemical and bioactivity variables. PC1 = 68.12%, PC2 = 17.71%. (A): PCA score plot. (B): PCA biplot. | ||
In the biplot (Fig. 1B), PC1 (68.12%) largely reflects covariation between TPC/TFC and the antioxidant/NO variables, while PC2 (17.71%) is influenced more strongly by XO inhibition. These loading patterns indicate that XO behaves partly independently from the other assays under the tested conditions.
Pairwise relationships were further examined using Pearson correlation analysis (Fig. 2 and Table S3). TPC and TFC correlated strongly and negatively with DPPH (r = −0.76, −0.90) and ABTS (r = −0.77, −0.90). Moderate correlations were also observed with NO inhibition, whereas XO inhibition showed weak or nonsignificant correlations (r < 0.35).
![]() | ||
| Fig. 2 Pearson correlation heatmap with two-tailed significance values (p < 0.05). Color scale indicates correlation strength. | ||
Together, these exploratory multivariate and correlation analyses support selecting R70 as a balanced residue-derived extract under the tested solvent conditions for subsequent chemical profiling and isolation, while acknowledging that broader validation across independent batches would be required for predictive modeling.31–33
| No. | Compound | m/z [M–H]− | m/z_calc | Error ppm | Matched fragments | Key fragments |
|---|---|---|---|---|---|---|
| 1 | 3,4-Dihydroxybenzoic acid | 153.0193 | 153.0193 | 0.12 | 31 | 109.029; 80.026; 65.039 |
| 2 | Trihydroxyoctadecadienoic acid (oxylipin) | 327.2177 | 327.2176 | 0.04 | 34 | 309.206; 291.195; 171.102 |
| 3 | Polyhydroxylated tetradecahydropicene | 503.3349 | 503.3378 | −5.68 | 34 | 485.324; 457.327; 71.012 |
| 4 | Hexacyclic diterpenoid dicarboxylic acid | 485.3265 | 485.3260 | 0.05 | 11 | 94.98; 80.96; 59.01; 151 |
| 5 | Monoterpenoid bicyclic | 293.1744 | 293.1758 | −4.67 | 15 | 59.013; 61.987; 192.114 |
| 6 | Furan–spiro-oxolane diterpenoid | 361.1659 | 361.1656 | 0.66 | 28 | 299.165; 343.962; 57–67 |
| 7 | Caffeoyl quinic acid isomer | 191.0556 | 191.0561 | −2.18 | 27 | 191; 85–127 |
| 8 | Quercetin | 301.0347 | 301.0353 | −1.99 | 111 | 151.001; 179.006 |
To improve transparency and mitigate potential false positives, an internal confidence tier was applied based on mass accuracy and the number of matched diagnostic fragments: high (|Δppm| ≤ 5 and n_frag ≥ 8), medium (|Δppm| ≤ 10 and n_frag = 4–7), and low (|Δppm| ≤ 10 and n_frag < 4). For each annotated feature, Δppm, n_frag, and confidence tier are reported in Table S4.
All annotations are reported at MSI level 2 and are intended to provide dereplication-level chemical context rather than definitive structural confirmation or quantification, in accordance with established reporting recommendations for non-targeted LC-MS workflows.23,34,35
Table S4 represents a curated subset of chemically interpretable and class-consistent features. Signals with low-quality MS/MS spectra or conflicting library matches were excluded to enhance annotation robustness.
The relative class distribution is consistent with previous phytochemical reports on Vitex rotundifolia, which describe flavonoids, iridoids, and terpenoid derivatives as major constituents of the species.36–39 Notably, despite hydrodistillation removing volatile monoterpenes and sesquiterpenes, a diverse spectrum of non-volatile phenolic and terpenoid metabolites remained detectable in the post-distillation residue.
This retained chemical diversity is consistent with the observed extract-level antioxidant and NO-inhibitory screening activities and supports the feasibility of recovering bioactivity-relevant metabolite classes from PDR.
Seventeen phenolic-type metabolites were annotated, including simple phenolic acids and caffeoylquinic acid derivatives. Such phenolic structures are widely associated with antioxidant capacity in plant extracts.15,28
Thirteen non-volatile terpenoid metabolites were identified, including diterpenoid and triterpenoid derivatives previously reported in Vitex species.5 Their detection after hydrodistillation indicates that structurally complex, less-volatile constituents persist in the residue matrix.
Additionally, several oxylipins and hydroxy fatty-acid derivatives were observed. These lipid-derived metabolites have been increasingly recognized as plant signaling molecules and may contribute to extract-level bioactivity profiles.41
Collectively, these metabolite classes represent well-documented phytochemical constituents of Vitex rotundifolia, and their presence in the PDR extract indicates that essential-oil removal does not exhaust the non-volatile chemical space of the material.
Accordingly, the present profiling is intended to confirm the recoverability and compositional continuity of established metabolite classes in PDR, rather than to claim structural novelty. In combination with extract-level bioactivity screening and process-level environmental assessment, these data support the feasibility of valorizing post-distillation biomass as a secondary feedstock within circular extraction strategies, while acknowledging that compound-level quantification and mechanistic validation would require further investigation.
Collectively, the LC-MS/MS dereplication indicates that non-volatile, bioactivity-relevant metabolite classes persist in PDR after hydrodistillation, supporting feasibility of secondary-feedstock recovery rather than demonstrating mechanistic causality or chemical novelty.
Compound VR1 (87.2 mg) was obtained from VRHEA5. Its 13C-NMR spectrum showed 19 carbon signals, including four methoxy carbons (55–60 ppm) and a characteristic C-4 carbonyl (178.97 ppm). The 1H-NMR displayed aromatic protons between 6.5–8.0 ppm and a diagnostic singlet at 6.51 ppm (H-8), indicating substitution on C-5/C-6/C-7. An ABX coupling system at 7.72, 6.96, 7.68 ppm matched H-6′, H-5′, H-2′ of a 3′,4′-disubstituted B-ring. Four methoxy singlets (3.88–3.99 ppm) showed HMBC correlations confirming substitution at C-4′, C-7, C-3, C-6. Additional HMBC correlations between H-6′ with C-2/C-4′; H-8 with C-6/C-7/C-9/C-10 reinforced the structure. The NMR data were entirely consistent with published values for casticin.42
Compound VR2 (13.7 mg) from VRHEA2 showed four methyl singlets (0.93–1.03 ppm), typical for a labdane skeleton. The 1H-NMR displayed resonances at δ 4.78 and 5.86 ppm, characteristic of methylene and olefinic protons in an α,β-unsaturated γ-lactone. A signal at δ 5.83 collapsed under selective decoupling, confirming coupling within the lactone system. The 13C-NMR revealed 22 carbons, including γ-lactone signals at δ 174.0, 170.9, 73.1, and an acetoxyl group. The combined spectral features matched literature data for vitexilactone.36
The 1H NMR spectrum of compound VR3 (19.5 mg) showed four downfield OH singlets (>9 ppm) and an ABX pattern at 6.86–7.30 ppm corresponding to B-ring protons. H-6 and H-8 doublets (6.20, 6.38 ppm, J = 2.0 Hz) indicated a 5,7-disubstituted A-ring. Sugar signals included an anomeric proton at 5.25 ppm (J = 1.5 Hz), confirming α-L-rhamnose, and a methyl carbon at 17.44 ppm. The 13C-NMR showed 21 carbons consistent with a flavonol glycoside. The data matched published NMR for quercitrin.43
VR4 (48.1 mg) exhibited hallmark iridoid signals in 1H NMR spectrum: δ 6.36 (H-3) and 5.13 (H-4) for an enol/olefin pair, with singlets at 5.85 and 6.37 ppm (H-7, H-10). Sugar signals (3.38–3.88 ppm) included δ 4.73 (H-1′, J = 8 Hz), indicating β-glucopyranoside. Aromatic protons at 6.88 and 7.96 ppm suggested a caffeoyl moiety. The 13C-NMR spectrum showed characteristic iridoid carbons and ester carbonyls. NMR data were fully consistent with literature reports for agnuside.6
Antioxidant and NO-inhibitory effects of VR1–VR4 are presented in Fig. 5. VR3 (quercitrin) exhibited the strongest antioxidant capacity (ABTS IC50 = 12.76 µM; DPPH IC50 = 16.05 µM), consistent with the radical-scavenging properties of polyhydroxylated flavonols.44 VR1 (casticin) and VR4 (agnuside) exhibited the strongest NO inhibition (IC50 = 31.05 and 28.41 µM), reflecting their ability to modulate inflammatory pathways.45,46 VR2 displayed moderate activities.
Bioactivities of natural isolates were lower than dexamethasone (IC50 = 0.49 µM), but VR3 showed antioxidant potency comparable to quercetin and superior to vitamin C.47
Collectively, these data indicate that R70 owes much of its bioactivity to its flavonoid and iridoid constituents. While the isolated compounds are well-known metabolites previously reported from Vitex species, their recovery from the post-distillation residue matrix demonstrates that PDR can retain and serve as a practical secondary source of representative bioactive constituents after essential oil removal.
![]() | ||
| Fig. 7 System boundary diagram comparing two isolation processes of casticin: Route A from raw material and Route B from post-distillation residue. Inputs include raw material (Route A only), solvents, and electricity. Outputs comprise solid waste, liquid waste, and life cycle assessment (LCA) indicators. Route A was adapted from (Hu et al., 2007),50 while Route B corresponds to the present work. | ||
| Impact category | Unit | Route A | Route B |
|---|---|---|---|
| Acidification | mol H+ eq | 0.015158 | 0.02245088 |
| Climate change | kg CO2-eq | 2.493344 | 3.626899 |
| Climate change – biogenic | kg CO2-eq | 0.448918 | 0.6509545 |
| Climate change – fossil | kg CO2-eq | 1.93927 | 2.825364 |
| Climate change – land use and LU change | kg CO2-eq | 0.105182 | 0.1505962 |
| Ecotoxicity, freshwater | CTUe | 0.0432112 | 0.0621488 |
| Ecotoxicity, freshwater – inorganics | CTUe | 0.024813 | 0.0355113 |
| Ecotoxicity, freshwater – organics | CTUe | 0.0183982 | 0.0266375 |
| Eutrophication, freshwater | kg P eq | 0.00367948 | 0.00548383 |
| Eutrophication, marine | kg N eq | 0.00581644 | 0.00865242 |
| Eutrophication, terrestrial | mol N eq | 0.0476776 | 0.0693922 |
| Human toxicity, cancer | CTUh | 3.05 × 10−6 | 4.30 × 10−6 |
| Human toxicity, cancer – inorganics | CTUh | 2.16 × 10−6 | 3.04 × 10−6 |
| Human toxicity, cancer – organics | CTUh | 8.91 × 10−7 | 1.26 × 10−6 |
| Human toxicity, non-cancer | CTUh | 8.79 × 10−6 | 1.26 × 10−5 |
| Human toxicity, non-cancer – inorganics | CTUh | 5.10 × 10−6 | 7.29 × 10−6 |
| Human toxicity, non-cancer – organics | CTUh | 3.68 × 10−6 | 5.31 × 10−6 |
| Ionising radiation | kBq U235 eq | 0.00758526 | 0.01028072 |
| Land use | Pt | 4.3635 | 6.2219 |
| Ozone depletion | kg CFC-11 eq | 1.91 × 10−6 | 2.71 × 10−6 |
| Particulate matter | kg PM2.5 eq | 0.000585124 | 0.000835195 |
| Photochemical ozone formation | kg NMVOC eq | 0.006673 | 0.009448905 |
| Resource use, fossils | MJ | 65.63016 | 97.35076 |
| Resource use, minerals and metals | kg Sb eq | 0.00438966 | 0.00582282 |
| Water use | m3 | 1.99894 | 3.079166 |
| Impact category | Unit | Route A | Route B |
|---|---|---|---|
| Acidification | mol H+ eq | 0.015158 | 0.022451 |
| Climate change | kg CO2-eq | 2.493344 | 3.626899 |
| Climate change – biogenic | kg CO2-eq | 0.448918 | 0.650955 |
| Climate change – fossil | kg CO2-eq | 1.93927 | 2.825364 |
| Resource use, fossils | MJ | 65.63016 | 97.35076 |
| Water use | m3 | 1.99894 | 3.079166 |
![]() | ||
| Fig. 8 Comparative per-batch impacts (climate change, fossil resource use, water use) for Route A and Route B under the stated system boundaries and assumptions. | ||
Route A generated a total climate change impact of 2.49 kg CO2-eq, whereas Route B reached 3.63 kg CO2-eq per batch. The higher burden in Route B was driven primarily by increased electricity and ethanol requirements during re-extraction, consistent with prior observations that valorizing waste streams may increase energy demand unless optimized.51,52
Fossil-derived emissions also followed this trend (2.83 vs. 1.94 kg CO2-eq). Biogenic emissions were higher in Route B (0.65 vs. 0.45 kg CO2-eq), reflecting the organic load remaining in residues, in agreement with earlier studies reporting substantial biogenic fractions in post-distillation biomass.53–55
Route B also required more water (3.67 vs. 2.88 m3), mainly due to ethanol dilution and washing operations, a trend consistent with hydrophilic solvent systems in green extraction workflows.56 Acidification potential similarly increased (0.022 vs. 0.015 mol H+-eq), largely linked to electricity and ethanol production. Although UAE shortens extraction time and reduces solvent,56,57 its electricity demand contributes to the LCA footprint. Renewable or hybrid energy integration (e.g., solar-UAE) could mitigate this burden.
Route B consumed 97.35 MJ of fossil energy, compared to 65.63 MJ in Route A. This illustrates the classic green-chemistry trade-off between circularity and processing intensity:12 although Route B avoids harvesting fresh biomass, the benefit is partly offset by energy needs. Still, Route B aligns with several principles of green chemistry,10 including prevention, renewable feedstocks, and – when optimized – energy efficiency.
Overall, Route A was more energy-efficient per batch of casticin produced, whereas Route B offered meaningful valorization of herbal residues that would otherwise be discarded. Process optimization – including ethanol recycling, heat integration, or renewable electricity – could markedly improve the sustainability profile of Route B.
In summary, the per-batch assessment highlights clear trade-offs in residue valorization: Route B improves material-efficiency metrics by reducing solvent mass and utilizing a waste stream, whereas energy-related indicators increase due to additional drying/extraction steps. Route B remains a practical valorization option, but its environmental advantage is not unconditional under the present assumptions. Instead, the analysis identifies improvement levers (solvent recovery, heat integration, and electricity source) that would be required to translate improved material efficiency into reduced life-cycle impacts.
Route A showed higher PMI due to large solvent volumes and three-stage maceration using 60% ethanol (>104 L). In contrast, Route B used UAE with 70% ethanol (1.4 L per 100 g residue), achieving significant reductions in solvent and water requirements.56,57 Despite UAE consuming 0.25 kWh of electricity, its process intensification effect lowered overall PMI, consistent with prior reports showing up to 50% PMI reduction versus maceration.56,59,60
The E-factor followed a similar trend: Route B generated less waste relative to product (1407 vs. 1921), aided by lower solvent mass and higher product recovery (0.11% vs. 0.104%). Importantly, using post-distillation residue avoids additional biomass extraction, improving circularity and reducing ecological harvesting pressure.
Together, PMI and E-factor (Table 7), combined with LCA metrics (Tables 5 and 6), reveal a clear mass – vs. – energy trade-off between the two routes.
| Parameter | Route A (raw fruit) | Route B (post-distillation residue) |
|---|---|---|
| PMI | 1925 | 1409 |
| E-factor | 1921 | 1407 |
| Extraction type | Maceration | UAE (ultrasound-assisted extraction) |
| Solvent volume | 104.4 L | 1.4 L |
| Yield (%) | 0.104% | 0.11% |
Route B remains a practical valorization option, but its environmental advantage is not unconditional under the present assumptions. Instead, the analysis identifies improvement levers (solvent recovery, heat integration, and electricity source) that would be required to translate improved material efficiency into reduced life-cycle impacts.10,12,62–64
Sensitivity check (screening-level): a ±20% variation in electricity consumption was applied as a simple robustness scenario; energy-related impact indicators scale proportionally and did not change the qualitative route comparison. Likewise, assuming a ±20% variation in solvent recovery/loss affects PMI and E-factor proportionally but does not reverse the observed mass-energy trade-off. Therefore, within reasonable laboratory-scale uncertainty bounds, the comparative trends are stable, while absolute values would require a more rigorous, product-normalized LCA.
Overall, the environmental assessment highlights a meaningful trade-off between resource efficiency and energy burden in waste-based extraction. The integrated use of mass-intensity, waste-generation, and life-cycle metrics provides a comprehensive evaluation of greenness and identifies actionable levers for process improvement.
Specific improvement levers that could markedly reduce the environmental footprint of Route B include: (1) solvent recovery and recycling (could reduce ethanol demand by 70–80%), (2) heat integration between distillation and drying operations, (3) renewable or grid-decarbonized electricity for UAE, (4) process intensification to minimize residue drying requirements.
In contrast, phytochemical investigations and comprehensive reviews have consistently emphasized that flavonoids, iridoid glycosides and labdane/abietane-type diterpenoids represent the key bioactive constituents of the genus Vitex.38,65,66 Representative compounds such as vitexin, orientin, aucubin and vitexilactone have been isolated from fruits, twigs or leaves of V. rotundifolia and shown to exhibit pronounced antioxidant or anti-inflammatory activities.7,39,67
Within this context, the untargeted LC-MS/MS profiling performed in the present study demonstrates that the post-distillation residue of V. rotundifolia retains a chemically rich metabolite spectrum, including flavonoids, phenolic acids, iridoid glycosides and non-volatile diterpenoids. These findings broaden the experimental evidence that non-volatile, medium-to-high polarity metabolites remain in the post-distillation residue and can be recovered under condition-matched extraction, complementing earlier studies focused primarily on essential oils.
Moreover, the concomitant presence of multiple metabolite classes (e.g., flavonoids, iridoid glycosides, and terpenoids) may contribute to the observed activities through complementary or additive effects, a common feature of complex botanical extracts. Consistent with prior reports on V. rotundifolia, whole extracts can modulate inflammatory markers in vitro, supporting a multi-target mode of action rather than the effect of a single dominant compound. In the present study, synergistic effects were not experimentally tested in this study; dedicated combination experiments would be required to demonstrate true synergy.38,39,65
This integrated utilization strategy broadens the chemical understanding of V. rotundifolia across volatile and non-volatile fractions and provides a basis for designing residue-utilization workflows with explicitly quantified trade-offs and transparent assumptions.
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