Next Article in Journal
In Vitro Regeneration Strategies in Woody Citrus of Northeast India (Citrus jambhiri and Citrus aurantifolia)
Previous Article in Journal
Arbuscular Mycorrhizal Fungi Modulate Variety-Specific Phosphate Transporter Gene Expression in Aerobic Rice Under Phosphorus-Limited Soil Conditions
Previous Article in Special Issue
Mangrove Against Invasive Snails: Aegiceras corniculatum Shows a Molluscicidal Effect on Exotic Apple Snails (Pomacea canaliculata) in Mangroves
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Repellent and Deterrent Oviposition Activity of Essential Oils from the Native Chilean Plant Drimys winteri Against Drosophila suzukii (Diptera: Drosophilidae)

1
Departamento de Ingeniería Química, Facultad de Ingeniería y Ciencias, Universidad de La Frontera, Avenida Francisco Salazar 01145, Casilla 54-D, Temuco 4811230, Chile
2
Laboratorio de Química Ecológica, Departamento de Ciencias Químicas y Recursos Naturales, Universidad de La Frontera, Avenida Francisco Salazar 01145, Casilla 54-D, Temuco 4811230, Chile
3
Centro de Investigación Biotecnológica Aplicada al Medio Ambiente (CIBAMA), Universidad de La Frontera, Avenida Francisco Salazar 01145, Casilla 54-D, Temuco 4811230, Chile
4
Doctorado en Ciencias de Recursos Naturales, Facultad de Ciencias Químicas y Recursos Naturales, Universidad de La Frontera, Avenida Francisco Salazar 01145, Casilla 54-D, Temuco 4811230, Chile
5
Scientific and Technological Bioresource Nucleus, BIOREN, Universidad de La Frontera, Avenida Francisco Salazar 01145, Casilla 54-D, Temuco 4811230, Chile
*
Authors to whom correspondence should be addressed.
Plants 2026, 15(11), 1676; https://doi.org/10.3390/plants15111676
Submission received: 25 April 2026 / Revised: 14 May 2026 / Accepted: 25 May 2026 / Published: 29 May 2026
(This article belongs to the Special Issue Application of Plant Extracts in Pest Control)

Abstract

Drosophila suzukii is one of the most destructive pests of soft fruits worldwide due to its high reproductive capacity, wide host range, and great adaptability. In this context, Drimys winteri, a tree native to southern Chile and Argentina, is recognized as a source of bioactive compounds with insecticidal and repellent properties. This study evaluated the repellent and oviposition-deterrent activity of essential oils (EOs) from the bark and leaf of D. winteri on D. suzukii. Chemical analysis by GC/MS showed that both EOs were dominated by monoterpenes, with α-pinene, β-pinene, and D-limonene being the major compounds, while the leaf EO exhibited greater chemical diversity and a higher proportion of sesquiterpenes. In choice bioassays, all treatments generated significant avoidance responses, with a preference for the control. The leaf EO showed the greatest repellent effect, exceeding 85% at 12 h and remaining above 80% at 96 h. In oviposition assays, the leaf EO significantly reduced egg laying at all concentrations, with negative oviposition preference index values indicating a consistent deterrent effect. Overall, the leaf EO of D. winteri showed repellent and oviposition-deterrent effects against D. suzukii under laboratory conditions.

1. Introduction

Drosophila suzukii (Matsumura) (Diptera: Drosophilidae), commonly known as the spotted wing drosophila (SWD), has emerged as one of the most destructive insect pests affecting fruit production globally. Native to Southeast Asia, it was first reported in Europe and North America in 2008 [1] and later detected in South America in 2013 [2]. In Chile, it was officially detected in 2017, when specimens were captured in traps placed in blackberry orchards along the Villarrica–Pucón International Highway, in the La Araucanía Region. This finding was confirmed by the Agricultural and Livestock Service (Servicio Agrícola y Ganadero—SAG), which prompted the implementation of national phytosanitary measures to prevent its spread [3].
The global invasion success of D. suzukii is largely attributed to its high ecological adaptability, reproductive capacity, broad host range, a wide variety of soft-skinned fruits, and strong passive and active dispersal abilities. The species can overwinter for extended periods and survive intercontinental transport in various developmental stages, including egg, larva, and adult, inside infested fruit or shipping containers [1,4,5,6,7,8]. Economically, the impact has been considerable. In the province of Trento, Italy, De Ros et al. [9] estimated losses of €3.3 million in crops, such as cherries, strawberries, raspberries, blueberries, and blackberries. In the United States, significant losses have also been reported. In Maine, in the northeastern part of the country, Yeh et al. [10] estimated losses of up to US$6.8 million in the blueberry industry, while in Minnesota, the raspberry industry reports annual losses of approximately US$2.35 million [11]. In South America, Benito et al. [12] estimated losses ranging from US$7.8 million in figs to US$21.4 million in peaches in Brazil. In Chile, although national-level losses have yet to be fully quantified, Buzzetti [13] reported losses of 10–15% of cherry production (1–2.7 t/ha), equivalent to US$5000–17,550/ha depending on the variety. In blueberries, damage affects approximately 8% of the fruit (1–1.5 t/ha), corresponding to losses of around US$4000/ha, with the potential to increase as pest pressure rises. In response, the Chilean government launched a two-year national project in 2021, investing CLP 360 million (approximately USD 493,000) to control this invasive pest in central production areas [14].
Current control strategies for D. suzukii are grounded in an integrated pest management (IPM) approach, which combines chemical, cultural, biological, and physical methods [15]. However, the heavy reliance on broad-spectrum synthetic insecticides presents several challenges. These compounds can negatively impact non-target organisms, including pollinators and beneficial arthropods; they may drive the evolution of pesticide-resistant populations and they raise concerns about chemical residues in fruit destined for export [9,16]. Moreover, these treatments are typically limited to managed crop areas, enabling rapid reinfestation from adjacent, untreated vegetation [17,18]. These limitations highlight the need for safer, eco-friendly pest control alternatives that align with sustainable agriculture principles and contribute to long-term food safety and security.
Essential oils (EOs) have gained increasing attention as promising alternatives to synthetic insecticides, primarily due to their biodegradability, reduced toxicity to non-target organisms, and rich composition of bioactive compounds [19,20]. These natural substances are complex mixtures of volatile secondary metabolites, such as terpenes, phenols, and aldehydes, synthesized by aromatic plants as part of their defense against herbivores and pathogens [21,22]. Their diverse biological activities—including insecticidal, repellent, antifeedant, and ovicidal effects—highlight their potential for inclusion in sustainable pest management programs [23,24].
Chile harbors a highly diverse native flora shaped by its unique geography and climatic range, from arid deserts to temperate rainforests. This botanical richness includes numerous native and endemic species known for producing bioactive secondary metabolites with potential applications in agriculture, medicine, and biotechnology [25,26,27,28,29]. Among these, EOs extracted from Pilgerodendron uviferum (Cupressaceae), Laureliopsis philippiana (Atherospermataceae), Adesmia boronioides (Fabaceae), and Drimys winteri (Winteraceae) have demonstrated insecticidal activity against agricultural pests and disease vectors [30]. Haplopappus foliosus (Asteraceae) EO also showed insecticidal activity against Drosophila melanogaster and interacted with acetylcholinesterase, suggesting a possible neurotoxic mechanism of action [29]. In this sense, Drimys winteri (J.R. Forst. & G. Forst.) commonly known as canelo, a tree species native to southern Chile and Argentina [31], exhibits interesting biological activities through its EOs. Recent studies have identified both bark- and leaf-derived EOs of D. winteri as rich sources of bioactive compounds with antifungal, antimicrobial, and insect-repellent properties [30,32,33,34]. These findings position D. winteri as a promising candidate for developing environmentally friendly pest control strategies.
This study aims to contribute to the development of safer and more sustainable pest management strategies by investigating the repellent potential of this native Chilean tree. Specifically, the repellent and oviposition deterrent activities of EOs extracted from D. winteri were assessed against D. suzukii using dual-choice bioassays. In addition, the chemical composition of these EOs was analyzed by gas chromatography–mass spectrometry (GC/MS).

2. Results

2.1. Chemical Profile of Drimys winteri Bark and Leaf Essential Oils

The GC/MS analysis (Table 1) enabled the identification of 21 compounds, accounting for 99.9% of the total relative abundance of the bark EO of D. winteri. The chemical profile was predominantly composed of monoterpenes, which represented 77.55% of the total composition. The major constituents were α-pinene (49.64%), followed by β-pinene (17.17%) and D-limonene (6.82%). Minor monoterpenes included 3-carene (1.62%) and p-cymene (1.86%). Sesquiterpenes accounted for 19.38% of the total composition. The most abundant compounds in this class were α-cubebene (6.75%) and β-cubebene (2.39%). Additional sesquiterpenes were detected in lower amounts, including γ-cadinene (1.30%), α- and γ-muurolene, santalene, caryophyllene, and oxygenated derivatives such as caryophyllene oxide and τ-cadinol, as well as drimenol (1.07%). Non-terpenoid compounds were represented by 2-piperizinopyridine, which accounted for 3.07% of the total relative area.
With respect to the leaf EO from D. winteri, a total of 31 compounds were identified, representing 98.63% of the total relative abundance. The chemical composition was also dominated by monoterpenes, which represented 69.69% of the total, with α-pinene (35.85%), β-pinene (17.61%), and D-limonene (6.77%) as the major constituents. Other monoterpenes, such as β-myrcene, α-phellandrene, γ-terpinene, and oxygenated derivatives including eucalyptol, borneol, terpinen-4-ol, and bornyl acetate, were detected in lower proportions. Sesquiterpenes accounted for 27.98% of the total composition, with elemol (7.07%), α-cubebene (2.21%), germacrene D (2.54%), and eudesmol isomers (α-, β-, and γ-eudesmol) among the most abundant compounds. Additional sesquiterpenes, including caryophyllene, humulene, cadinene derivatives, and spathulenol, were also identified in minor amounts. Diterpenes were present only in trace amounts (0.29%), represented by sandaracopimaradiene and α-kaurene. Non-terpenoid compounds and unidentified constituents accounted for 2.82% of the total relative area.

2.2. Choice Bioassay

In bark EO (T1), 92% of flies chose the control at 12 h (G = 47.55, df = 1, p < 0.0001), 76% at 48 h (G = 60.01, df = 1, p < 0.0001), and 71% at 96 h (G = 34.76, df = 1, p < 0.0001). Heterogeneity among replicates was detected in all evaluation periods (p < 0.05) (Figure 1A).
In leaf EO (T2), the percentage of flies choosing the control ranged from 91% at 12 h (G = 19.50, df = 1, p = 0.00001) to 94% at 48 h (G = 119.33, df = 1, p < 0.0001), without heterogeneity among replicates (p > 0.05), and 88% at 96 h (G = 79.9, df = 1, p < 0.0001), with significant heterogeneity (p < 0.05) (Figure 1B).
The mixture of bark and leaf EOs (1:1) (T3) showed a similar trend to that observed with the oils separately, though to a lesser degree. The percentage of flies choosing the control ranged from 80% at 12 h (G = 53.93, df = 1, p < 0.0001) without significant differences across replicates (p > 0.05), to 63% at 96 h (G = 12.13, df = 1, p < 0.001) with significant heterogeneity (p < 0.05) (Figure 1C).
The mixture of bark and leaf EOs (1.6:0.4) (T4) showed a similar trend to that observed with the mixture 1:1. At 12 h, 80% of flies chose the control over the treatment (G = 68.45, df = 1, p < 0.0001), while at 72 h, it reached 64% (G = 16.72, df = 1, p < 0.001) with significant heterogeneity among replicates (p < 0.05). At 96 h, no significant preference was observed (G = 2.00, df = 1, p = 0.157) (Figure 1D).
In treatment 5 (T5), the proportions of bark and leaf EOs were reversed (0.4:1.6). At 12 h, 91% of flies chose the control (G = 97.80, df = 1, p < 0.0001), decreasing to 80% at 48 h (G = 51.10, df = 1, p < 0.0001) and 76% at 96 h (G = 51.19, df = 1, p < 0.0001). Heterogeneity among replicates was not detected at 12, 24, 48, and 96 h (p > 0.05), but was detected at 72 h (p < 0.05) (Figure 1E).
In the negative control (acetone vs. acetone) (T6), flies showed no side preference between 12 and 72 h, with pooled G-tests indicating no deviation from a 50:50 distribution (all p > 0.23). Although significant heterogeneity among replicates was detected (all p-values ≤ 0.015), no directional bias was observed, indicating the absence of positional effects in the assay. At 96 h, the proportion deviated from 50:50 (p = 0.041) (Figure 1F).
All D. winteri EO treatments showed repellency percentages above 50% between 12 and 96 h (Figure 2, Table 2). The leaf EO (T2) showed the highest repellency, with values of 85.00 ± 10.00% at 12 h and 82.47 ± 6.63% at 96 h. However, no significant differences were detected between T2 and the other treatments (p > 0.05), except at 48 h, when it differed significantly from T3 and T4 (p < 0.05).

2.3. Oviposition Bioassay

The number of eggs laid on treated fruits with D. winteri leaf EOs was significantly lower than on control fruits at all concentrations tested. Significant differences were observed at 0.75 mg mL−1, with 2.76 ± 0.78 eggs in the treatment versus 6.68 ± 1.30 eggs in the control (Wilcoxon signed-rank test, Z = −2.37, p = 0.018); at 1.5 mg mL−1, with 0.64 ± 0.22 eggs in the treatment versus 11.32 ± 1.72 eggs in the control (Z = −4.05, p < 0.001); and at 3 mg mL−1, with 4.08 ± 0.98 eggs in the treatment versus 12.36 ± 1.84 eggs in the control (Z = −3.22, p = 0.001).
Oviposition preference index (OPI) was calculated (Figure 3). The OPI was significantly lower than zero at all tested concentrations (Wilcoxon signed-rank test: 0.75 mg mL−1, Z = −3.03, p = 0.002; 1.5 mg mL−1, Z = −3.91, p < 0.001; 3 mg mL−1, Z = −3.69, p < 0.001). The most negative mean OPI occurred at 1.5 mg mL−1 (−0.71 ± 0.11), followed by 3 mg mL−1 (−0.55 ± 0.11) and 0.75 mg mL−1 (−0.50 ± 0.14). No significant differences in OPI were detected among treatments (Kruskal–Wallis test, p = 0.118).

3. Discussion

In general, the bioactivity of EOs is linked to their chemical composition, which can vary even within the same species [35]. In this study, both bark and leaf EOs were dominated by monoterpenes, primarily α-pinene (49% in bark and 35% in leaf), followed by β-pinene (17% in both oils) and similar levels of D-limonene (~6.7%). Furthermore, the leaf EO exhibited greater chemical diversity than the bark EO, with more identified compounds (31 vs. 21) and a higher proportion of sesquiterpenes (28% vs. 19%). Among the sesquiterpenes identified in the leaf EO, elemol (7.07%) and the eudesmol isomers α-, β-, and γ-eudesmol (2.90%, 2.42%, and 2.95%, respectively) were noteworthy. Similar compounds were reported by Tampe et al. [32] in canelo leaf EOs from La Araucanía; however, in that study, these sesquiterpenes were the major compounds, whereas in the present study, α-pinene and β-pinene predominated.
Other studies conducted in different regions of Chile have also reported qualitative and quantitative differences in the EO chemical profiles of D. winteri [36,37,38,39,40,41]. For instance, Zapata et al. [37] described leaf EOs from south–central Chile as rich in γ-curcumene, limonene, myrcene, and trans-caryophyllene. In contrast, Becerra et al. [39] observed that oils from the Biobío Region were dominated by benzocycloheptene. Similarly, Muñoz et al. [41] found that monoterpenes predominated in leaf EOs from Chiloé Island populations, whereas sesquiterpenes and phenylpropanoids were more abundant in samples collected from continental areas near Santiago. Together, these findings highlight the chemical variability of D. winteri EOs and suggest that environmental and genetic factors may contribute to the occurrence of distinct chemotypes [34].
To date, no studies have evaluated the bioactivity of D. winteri EOs against D. suzukii. However, canelo EOs have been reported to exhibit repellent, insecticidal, and deterrent activity against insect pests [30,32,37,38]. In the present study, D. suzukii showed a clear preference for the control over raspberry jelly pots treated with D. winteri EOs, indicating an avoidance response to the treatments. The leaf EO (T2) produced the highest choice response toward the control, followed by the bark EO (T1) and the bark–leaf EO mixture (0.4:1.6) (T5), with more than 90% of flies choosing the control at 24 h and approximately 72% at 96 h. Lower choice responses were observed for the other bark–leaf EO mixtures (1:1) (T3) and (1.6:0.4) (T4), with approximately 80% at 24 h and 55% at 96 h. Similar avoidance responses have been reported by Renkema et al. [42], who observed variable levels of preference for untreated controls depending on the EO tested against D. suzukii.
Based on these results, the repellency percentage for each treatment was determined over time. T2 maintained the highest repellency throughout the evaluation period (85% at 12 h to 82% at 96 h), suggesting a more persistent repellent effect than the other treatments. Although T1 and T5 also showed high initial repellency, their effectiveness declined more rapidly. In contrast, T3 and T4 exhibited the lowest repellency. Similar observations were reported by Renkema et al. [42,43], who indicated that peppermint oil (Mentha × piperita) maintained 100% repellency against D. suzukii females up to 144 h after application, while geranium oil (Pelargonium asperum) showed a progressive decline in repellency, reaching approximately 35% at 96 h. In addition, Souza et al. [16] reported strong avoidance responses (~90%) in choice olfactometry assays, reflecting an immediate behavioral response of D. suzukii to the evaluated oils.
Olfactory cues are involved in oviposition site selection in D. suzukii [44], and exposure to aversive compounds can reduce this activity [45,46,47]. D. winteri leaf EO showed a deterrent effect under laboratory conditions, with negative Oviposition Index (OPI) values recorded at all evaluated concentrations. Egg deposition on treated fruits was reduced, and no significant differences were observed among concentrations, indicating comparable deterrent effects among them. Similar reductions in oviposition have been reported for other EOs against D. suzukii, including Baccharis spp. [48] and the EOs of Citrus reticulata and Melaleuca alternifolia [49], although the response varied among oils and concentrations. In our study, the 1.5 mg mL−1 treatment resulted in the lowest oviposition, with an average of 0.64 ± 0.22 eggs in treated fruits and 11.32 ± 1.72 eggs in control fruits. However, these differences were not statistically significant, possibly due to variability in the data. De Souza et al. [48] also found that the EOs of B. calvescens, B. mesoneura, and B. oblongifolia reduced oviposition on artificial fruits (≈7.6 eggs fruit−1) compared with the water (17.2 eggs fruit−1) and acetone (17.6 eggs fruit−1) controls.
The greater repellent and oviposition-deterrent activity observed may be associated with the chemical profile of the leaf EO. The main compounds identified, α-pinene and β-pinene, have been previously associated with insecticidal and oviposition-deterrent effects against D. suzukii in studies using Baccharis spp. EOs [48]. In addition, D-limonene has been identified as one of the most effective compounds associated with repellent responses in this species during choice and olfactory assays [50]. At the same time, EO bioactivity is not determined exclusively by major compounds, but also by interactions among constituents, including synergistic and antagonistic effects [19,35,51]. The canelo leaf EO had a greater proportion of sesquiterpenes than the bark EO (27.9% vs. 19.4%), including germacrene D, elemol, and the eudesmol isomers (α-, β-, and γ-eudesmol), none of which were detected in the bark EO. Although present in lower amounts than the dominant monoterpenes, these sesquiterpenes may contribute to EO bioactivity. Information regarding the effects of these sesquiterpenes against D. suzukii remains limited; however, Chu et al. [52] reported β-eudesmol as toxic to Drosophila melanogaster, suggesting that these compounds may also contribute to the behavioral responses observed in the present study.

4. Materials and Methods

4.1. Insects

The D. suzukii colony used in the bioassays was maintained in BugDorm insect-rearing cages (MegaView Science Co., Ltd., Taichung, Taiwan) at 22 ± 1 °C, 60% relative humidity, and a 12:12 h (L:D) photoperiod. Flies were provided with water through moist cotton and fed a modified artificial diet as described by Renkema et al. [43]. The diet consisted of agar, cornmeal, sugar, nutritional yeast, propionic acid, methyl paraben dissolved in 95% ethanol, and raspberry pulp.

4.2. Drimys winteri Essential Oils and Chemical Analysis

EOs from D. winteri bark and leaf were obtained by Campestre (Temuco, Chile), through steam distillation for 1.5 h from plant material collected in the La Araucanía Region, Chile. Each EO was analyzed with GC/MS (Thermo Focus GC, Thermo Fisher Scientific, Waltham, MA, USA). Each EO was diluted in hexane at 1 µg µL−1, and 1 µL of each one was injected, separately, into a capillary column BPX5 (30 m length, 0.25 µm film thickness, and 0.25 mm inner diameter). The operating conditions are described in Tampe et al. [32]. The Xcalibur software version 4.2.47 (Thermo Fisher Scientific Inc., Waltham, MA, USA) was used to acquire and process data. The compounds were identified by comparing their mass spectra with a library database (NIST ver. 2.0, NIST, Gaithersburg, MD, USA) and by comparing their Kovats indices with those reported in the literature [53,54].

4.3. Experimental Arena and Setup

The bioassays were conducted in clear acrylic boxes (37 cm long × 23 cm high × 23 cm wide) equipped with tight-fitting lids and white mesh on all four sides to ensure adequate ventilation. Each experimental arena contained two plastic cups positioned 25 cm apart. All assays were conducted in a climate-controlled room at 22 ± 1 °C, 60% relative humidity, and a 12:12 h (L:D) photoperiod.

4.3.1. Choice Bioassay

The bioassays were conducted to evaluate the behavioral response of D. suzukii to different D. winteri EO treatments. In each experimental arena, two plastic cups (150 mL) containing 15 g of raspberry jelly were used as an attractant for adult flies. The jelly consisted of agar (2 g), fructose (5 g), distilled water (200 mL), raspberry pulp (175 mL), and methyl paraben stock solution (2 mL). A cotton wick was placed in each cup to apply the treatments. The cotton wick received 2 mL of pure acetone (control), while the other received 2 mL of an EO solution diluted in acetone to a final concentration of 15 mg mL−1. Five treatments were evaluated: (T1) bark EO, (T2) leaf EO, (T3) a 1:1 (v/v) mixture of bark and leaf EOs, (T4) a bark: leaf EO mixture (1.6:0.4, v/v), and (T5) a bark:leaf EO mixture (0.4:1.6, v/v). Before each assay, the cups were placed under an extraction hood for 1 h to allow solvent evaporation. Subsequently, 25 unsexed adult flies (3–5 days old) were released into the center of the arena and allowed to move freely toward either cup. The number of flies present on each cotton wick (treatment or control) was recorded at 12, 24, 48, 72, and 96 h after release. To verify the absence of positional bias within the arena, choice assays were conducted using identical treatments on both sides. In these assays, 2 mL of pure acetone was applied to the cotton wick of each cup. Ten independent replicates were performed for each treatment and the negative control.

4.3.2. Oviposition Bioassay

The bioassays were conducted to evaluate the deterrent oviposition effect of D. winteri leaf EO on female D. suzukii. Based on the previous results, the leaf EO was selected because it showed the highest repellency over time. In each experimental arena, two natural raspberry fruits (cv. Heritage) were used as oviposition substrates. Raspberries were harvested before the trial to ensure firmness and uniform size. Three EO concentrations were tested (0.75, 1.5, and 3 mg mL−1). A volume of 500 μL of each EO solution diluted in acetone was applied to one fruit, while 500 μL of pure acetone was applied to the control fruit. Both treated and control fruits were kept for 1 h under a laminar flow hood to allow solvent evaporation. Each fruit was then placed inside a plastic cup (30 mL). In each arena, one treated and one control fruit were presented simultaneously, and 10 female and 5 male adult D. suzukii (5 days old) were released. After 24 h, the flies were removed, and the number of eggs laid on each fruit was counted under a stereoscopic magnifying glass (7–45× zoom). Each concentration was replicated twenty-five times.
The experimental workflow used in this study is shown in Figure 4.

4.4. Data Analysis

The statistical software SPSS version 26 (IBM Corp., Armonk, NY, USA) was used for data analysis. Before analysis, data were subjected to the Shapiro–Wilk test to assess normality. Since the data were not normally distributed, non-parametric tests were used. In the choice bioassay, the distribution of flies between the control and treated wicks was used to assess choice behavior. Choice data were analyzed in two complementary stages. First, goodness-of-fit tests (G-tests) were performed for each treatment to determine whether flies showed a significant preference for the treated stimulus over the control. When responses were consistent across replicates (heterogeneity test, p > 0.05), pooled G statistics were calculated. Repellency percentages were calculated for each replicate as shown in Equation (1), where C represents the number of individuals recorded in the control and T the number of individuals recorded in the treatment.
Repellency (%) = [C/(C + T)] × 100
Repellency values were compared among treatments using the Kruskal–Wallis test, followed by Bonferroni-adjusted pairwise comparisons when significant differences were detected.
For the oviposition bioassays, the oviposition preference index (OPI) was calculated as shown in Equation (2), where T represents the number of eggs laid on the treated substrate and C the number of eggs laid on the control substrate.
OPI = (T − C)/(T + C)
Differences in the number of eggs laid between treated and control substrates were evaluated using Wilcoxon signed-rank tests for paired samples, performed separately for each concentration. Differences in OPI among treatments were analyzed using the Kruskal–Wallis test. Additionally, Wilcoxon signed-rank tests were conducted for each treatment to determine whether OPI values differed from a neutral response (OPI = 0).
All figures were generated using OriginPro 2024b (64-bit), version 10.1.5.132 (OriginLab Corporation, Northampton, MA, USA).

5. Conclusions

D. winteri EOs, particularly the leaf EO, showed repellent and oviposition-deterrent activity against D. suzukii under laboratory conditions. These effects may be linked to the leaf EO’s chemical profile, which is dominated by monoterpenes and contains a higher proportion of sesquiterpenes than the bark EO. The reduced attraction and oviposition on treated substrates suggest that the leaf EO may support the development of alternative pest management strategies. However, further studies are needed to identify the compounds responsible for the observed behavioral responses and to evaluate their efficacy and persistence under field conditions.

Author Contributions

Conceptualization, J.T. and M.R.; methodology, J.T. and M.R.; investigation, D.S. and C.R.; data curation, J.T., D.S. and J.E.; writing—original draft preparation, J.T.; writing—review and editing, J.T. and J.E.; visualization, J.T.; supervision, M.R. and A.Q. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Research and Development Agency (ANID), the Initiation in research project 11230746.

Data Availability Statement

The original contributions presented in this study are included in the article. Further inquiries can be directed to the corresponding authors.

Acknowledgments

The authors acknowledge the contribution of Helen Lowry, who edited the English in the manuscript.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Tait, G.; Mermer, S.; Stockton, D.; Lee, J.; Avosani, S.; Abrieux, A.; Anfora, G.; Beers, E.; Biondi, A.; Burrack, H.; et al. Drosophila suzukii (Diptera: Drosophilidae): A decade of research towards a sustainable integrated pest management program. J. Econ. Entomol. 2021, 114, 1950–1974. [Google Scholar] [CrossRef]
  2. Deprá, M.; Poppe, J.L.; Schmitz, H.J.; De Toni, D.C.; Valente, V.L.S. The first records of the invasive pest Drosophila suzukii in the South American continent. J. Pest Sci. 2014, 87, 379–383. [Google Scholar] [CrossRef]
  3. Servicio Agrícola y Ganadero (SAG). Resolución Exenta N° 3672/2017: Establece Medidas Fitosanitarias de Emergencia Provisionales para la Plaga Drosophila suzukii (Matsumura). 2017. Available online: http://www.sag.cl/sites/default/files/resol._drosophila_suzukii_zero_5_ec_anasac_chile_s.a._resol._5863-2017.pdf (accessed on 16 February 2026).
  4. Lee, J.C.; Bruck, D.J.; Curry, H.; Edwards, D.; Haviland, D.R.; Van Steenwyk, R.A.; Walton, V.M. In focus: Spotted wing Drosophila suzukii across perspectives. Pest Manag. Sci. 2011, 67, 1349–1351. [Google Scholar] [CrossRef]
  5. Emiljanowicz, L.M.; Ryan, G.D.; Langille, A.; Newman, J. Development, reproductive output, and population growth of the fruit fly pest Drosophila suzukii (Diptera: Drosophilidae) on artificial diet. J. Econ. Entomol. 2014, 107, 1392–1398. [Google Scholar] [CrossRef] [PubMed]
  6. Asplen, M.K.; Anfora, G.; Biondi, A.; Choi, D.-S.; Chu, D.; Daane, K.M.; Gibert, P.; Gutierrez, A.P.; Hoelmer, K.A.; Hutchison, W.D.; et al. Invasion biology of spotted wing Drosophila suzukii: A global perspective and future priorities. J. Pest Sci. 2015, 88, 469–494. [Google Scholar] [CrossRef]
  7. Stockton, D.G.; Brown, R.; Loeb, G.M. Not berry hungry? Discovering the hidden food sources of a small fruit specialist, Drosophila suzukii. Ecol. Entomol. 2019, 44, 810–822. [Google Scholar] [CrossRef]
  8. Thistlewood, H.M.A.; Rozema, B.; Acheampong, S. Infestation and timing of use of non-crop plants by Drosophila suzukii (Matsumura) (Diptera: Drosophilidae) in the Okanagan Basin, Canada. Can. Entomol. 2019, 151, 34–48. [Google Scholar] [CrossRef]
  9. De Ros, G.; Grassi, A.; Pantezzi, T. Recent trends in the economic impact of Drosophila suzukii. In Drosophila suzukii Management; Springer: Cham, Switzerland, 2020; pp. 11–28. [Google Scholar] [CrossRef]
  10. Yeh, D.A.; Drummond, F.A.; Gómez, M.I.; Fan, X. The economic impacts and management of spotted wing Drosophila suzukii: The case of wild blueberries in Maine. J. Econ. Entomol. 2020, 113, 1262–1269. [Google Scholar] [CrossRef] [PubMed]
  11. DiGiacomo, G.; Hadrich, J.; Hutchison, W.D.; Peterson, H.; Rogers, M. Economic impact of spotted wing Drosophila suzukii (Diptera: Drosophilidae) yield loss on Minnesota raspberry farms: A grower survey. J. Integr. Pest Manag. 2019, 10, 11. [Google Scholar] [CrossRef]
  12. Benito, N.P.; Lopes-da-Silva, M.; Santos, R.S.S. Potential spread and economic impact of invasive Drosophila suzukii in Brazil. Pesqui. Agropecu. Bras. 2016, 51, 571–578. [Google Scholar] [CrossRef]
  13. Buzzetti Morales, K. The spotted wing Drosophila in the south of the world: Chilean case and its first productive impacts. In Invasive Species-Introduction Pathways, Economic Impact, and Possible Management Options; IntechOpen: London, UK, 2020. [Google Scholar] [CrossRef]
  14. AgroPages. Chile Approves Project to Combat Drosophila suzukii. 2021. Available online: https://news.agropages.com/News/NewsDetail---39604.htm (accessed on 8 January 2026).
  15. Cruz-Esteban, S. Advances in the management of Drosophila suzukii population: From olfactory and visual stimuli to development of push–pull systems. Front. Ecol. Evol. 2026, 14, 1746696. [Google Scholar] [CrossRef]
  16. de Souza, M.T.; de Souza, M.T.; Morais, M.C.; de Oliveira, D.C.; de Melo, D.J.; Figueiredo, L.; Zarbin, P.H.G.; Zawadneak, M.A.C.; Bernardi, D. Essential oils as a source of ecofriendly insecticides for Drosophila suzukii (Diptera: Drosophilidae) and their potential non-target effects. Molecules 2022, 27, 6215. [Google Scholar] [CrossRef]
  17. Van Timmeren, S.; Isaacs, R. Control of spotted wing Drosophila suzukii by specific insecticides and by conventional and organic crop protection programs. Crop Prot. 2013, 54, 126–133. [Google Scholar] [CrossRef]
  18. Haye, T.; Girod, P.; Cuthbertson, A.G.S.; Wang, X.G.; Daane, K.M.; Hoelmer, K.A.; Baroffio, C.; Zhang, J.P.; Desneux, N. Current SWD IPM tactics and their practical implementation in fruit crops across different regions around the world. J. Pest Sci. 2016, 89, 643–651. [Google Scholar] [CrossRef]
  19. Regnault-Roger, C.; Vincent, C.; Arnason, J.T. Essential oils in insect control: Low-risk products in a high-stakes world. Annu. Rev. Entomol. 2012, 57, 405–424. [Google Scholar] [CrossRef]
  20. Isman, M.B. Botanical insecticides in the twenty-first century-fulfilling their promise? Annu. Rev. Entomol. 2020, 65, 233–249. [Google Scholar] [CrossRef] [PubMed]
  21. Bakkali, F.; Averbeck, S.; Averbeck, D.; Idaomar, M. Biological effects of essential oils-a review. Food Chem. Toxicol. 2008, 46, 446–475. [Google Scholar] [CrossRef]
  22. Lahlali, R.; El Hamss, H.; Mediouni-Ben Jemâa, J.; Barka, E.A. Editorial: The use of plant extracts and essential oils as biopesticides. Front. Agron. 2022, 4, 921965. [Google Scholar] [CrossRef]
  23. Isman, M.B.; Grieneisen, M.L. Botanical insecticide research: Many publications, limited useful data. Trends Plant Sci. 2014, 19, 140–145. [Google Scholar] [CrossRef] [PubMed]
  24. Nerio, L.S.; Olivero-Verbel, J.; Stashenko, E. Repellent activity of essential oils: A review. Bioresour. Technol. 2010, 101, 372–378. [Google Scholar] [CrossRef]
  25. Velásquez, P.; Montenegro, G. Chilean Endemic/Native Plant Resources as Functional and Superfoods. In Superfood and Functional Food—An Overview of Their Processing and Utilization; InTech: London, UK, 2017. [Google Scholar] [CrossRef]
  26. Salehi, B.; Sharifi-Rad, J.; Herrera, J.; Salazar, L.; Delporte, C.; Valenzuela Barra, G.; Cazar, M.E.; López Belchí, M.; Ramírez-Alarcón, K.; Cruz-Martins, N.; et al. Ethnopharmacology, phytochemistry and biological activities of native Chilean plants. Curr. Pharm. Des. 2021, 27, 953–970. [Google Scholar] [CrossRef]
  27. Otero, M.C.; Fuentes, J.A.; Atala, C.; Cuadros-Orellana, S.; Fuentes, C.; Gordillo-Fuenzalida, F. Antimicrobial Properties of Chilean Native Plants: Future Aspects in Their Application in the Food Industry. Foods 2022, 11, 1763. [Google Scholar] [CrossRef] [PubMed]
  28. Rubio, J.; Robles-Kelly, C.; Silva-Moreno, E.; Carrasco, H.; Olea, A.F. Assessment of phytochemical composition and antifungal activity of micropropagated Drimys winteri plants. Plants 2025, 14, 3215. [Google Scholar] [CrossRef]
  29. Silva, V.; Muñoz, E.; Flores, S.; Reyes, C.; Bravo, N.; Levipan, H.A.; Montenegro, I.; Alarcón, J.; Santander, R.; Madrid, A. Chemical profile and bioinsecticidal nanoemulsion of Haplopappus foliosus essential oil: Mechanistic insights into pest management using a Drosophila model. Plants 2026, 15, 1282. [Google Scholar] [CrossRef] [PubMed]
  30. Giordani, C.; Spinozzi, E.; Baldassarri, C.; Ferrati, M.; Cappellacci, L.; Santibañez Nieto, D.; Pavela, R.; Ricciardi, R.; Benelli, G.; Petrelli, R.; et al. Insecticidal activity of four essential oils extracted from Chilean Patagonian plants as potential organic pesticides. Plants 2022, 11, 2012. [Google Scholar] [CrossRef] [PubMed]
  31. Hoffmann, A.; Fraga, C.; Lastra, C.; Veghazi, E. Plantas Medicinales de Uso Común en Chile; Fundación Claudio Gay: Santiago, Chile, 1992; p. 78. [Google Scholar]
  32. Tampe, J.; Espinoza, J.; Chacón-Fuentes, M.; Quiroz, A.; Rubilar, M. Evaluation of Drimys winteri (canelo) essential oil as insecticide against Acanthoscelides obtectus (Coleoptera: Bruchidae) and Aegorhinus superciliosus (Coleoptera: Curculionidae). Insects 2020, 11, 335. [Google Scholar] [CrossRef]
  33. Bruna, F.; Fernández, K.; Urrejola, F.; Touma, J.; Navarro, M.; Sepúlveda, B.; Larrazabal-Fuentes, M.; Paredes, A.; Neira, I.; Ferrando, M.; et al. The essential oil from Drimys winteri possesses activity: Antioxidant, theoretical chemistry reactivity, antimicrobial, antiproliferative, and chemical composition. Front. Nat. Prod. 2022, 1, 958425. [Google Scholar] [CrossRef]
  34. Navarro, M.; Urrejola, F.; Espinoza, M.; Silva, S.; González, S.; Utreras, D.; Fernández, K.; Bravo, J. Biological activity of the essential oil of Drimys winteri. Front. Chem. 2024, 12, 1321300. [Google Scholar] [CrossRef]
  35. Isman, M.B. Bioinsecticides based on plant essential oils: A short overview. Z. Naturforsch. C 2020, 75, 179–182. [Google Scholar] [CrossRef]
  36. Barrero, A.F.; Herrador, M.M.; Arteaga, P.; Lara, A.; Cortés, M. Chemical composition of the essential oil from Drimys winteri Forst. wood. J. Essent. Oil Res. 2000, 12, 685–688. [Google Scholar] [CrossRef]
  37. Zapata, N.; Lognay, G.; Smagghe, G. Bioactivity of essential oils from leaves and bark of Laurelia sempervirens and Drimys winteri against Acyrthosiphon pisum. Pest Manag. Sci. 2010, 66, 1324–1331. [Google Scholar] [CrossRef] [PubMed]
  38. Zapata, N.; Smagghe, G. Repellency and toxicity of essential oils from the leaves and bark of Laurelia sempervirens and Drimys winteri against Tribolium castaneum. Ind. Crops Prod. 2010, 32, 405–410. [Google Scholar] [CrossRef]
  39. Becerra, J.; Bittner, M.; Hernández, V.; Brintrup, C.; Becerra, J.S.; Silva, M. Actividad de aceites esenciales de canelo, queule, bailahuén y culén frente a hongos fitopatógenos. Bol. Latinoam. Caribe Plantas Med. Aromat. 2010, 9, 212–215. Available online: http://www.redalyc.org/articulo.oa?id=85615232008 (accessed on 2 April 2026).
  40. Verdeguer, M.; García-Rellán, D.; Boira, H.; Pérez, E.; Gandolfo, S.; Blázquez, M.A. Herbicidal activity of Peumus boldus and Drimys winteri essential oils from Chile. Molecules 2011, 16, 403–411. [Google Scholar] [CrossRef] [PubMed]
  41. Muñoz, O.; Christen, P.; Cretton, S.; Barrero, A.F.; Lara, A.; Herrador, M.M. Comparison of the essential oils of leaves and stem bark from two different populations of Drimys winteri, a Chilean herbal medicine. Nat. Prod. Commun. 2011, 6, 879–882. [Google Scholar] [CrossRef]
  42. Renkema, J.M.; Wright, D.; Buitenhuis, R.; Hallett, R.H. Plant essential oils and potassium metabisulfite as repellents for Drosophila suzukii (Diptera: Drosophilidae). Sci. Rep. 2016, 6, 21432. [Google Scholar] [CrossRef]
  43. Renkema, J.M.; Buitenhuis, R.; Hallett, R.H. Reduced Drosophila suzukii Infestation in Berries Using Deterrent Compounds and Laminate Polymer Flakes. Insects 2017, 8, 117. [Google Scholar] [CrossRef]
  44. Revadi, S.; Vitagliano, S.; Rossi Stacconi, M.V.; Ramasamy, S.; Mansourian, S.; Carlin, S.; Vrhovsek, U.; Becher, P.G.; Mazzoni, V.; Rota-Stabelli, O.; et al. Olfactory responses of Drosophila suzukii females to host plant volatiles. Physiol. Entomol. 2015, 40, 54–64. [Google Scholar] [CrossRef]
  45. Wallingford, A.; Connelly, H.L.; Dore Brind’Amour, G.; Boucher, M.T.; Mafra-Neto, A.; Loeb, G.M. Field evaluation of an oviposition deterrent for management of spotted-wing Drosophila suzukii and potential nontarget effects. J. Econ. Entomol. 2016, 109, 1779–1784. [Google Scholar] [CrossRef]
  46. Wallingford, A.; Hesler, S.P.; Cha, D.H.; Loeb, G.M. Behavioral response of spotted-wing Drosophila suzukii Matsumura to aversive odors and a potential oviposition deterrent in the field. Pest Manag. Sci. 2016, 72, 701–706. [Google Scholar] [CrossRef]
  47. Wallingford, A.; Cha, D.H.; Linn, C.E.; Wolfin, M.S.; Loeb, G.M. Robust manipulations of pest insect behavior using repellents and practical application for integrated pest management. Environ. Entomol. 2017, 46, 1041–1050. [Google Scholar] [CrossRef]
  48. de Souza, M.T.; de Souza, M.T.; Bernardi, D.; de Melo, D.J.; Zarpin, P.H.G.; Zawadneak, M.A.C. Insecticidal and oviposition deterrent effects of essential oils of Baccharis spp. and histological assessment against Drosophila suzukii (Diptera: Drosophilidae). Sci. Rep. 2021, 11, 3944. [Google Scholar] [CrossRef] [PubMed]
  49. Bedini, S.; Cosci, F.; Tani, C.; Pierattini, E.C.; Venturi, F.; Lucchi, A.; Ioriatti, C.; Ascrizzi, R.; Flamini, G.; Ferroni, G.; et al. Essential Oils as Post-Harvest Crop Protectants against the Fruit Fly Drosophila suzukii: Bioactivity and Organoleptic Profile. Insects 2020, 11, 508. [Google Scholar] [CrossRef] [PubMed]
  50. Wang, Q.; Xu, P.; Sanchez, S.; Duran, P.; Andreazza, F.; Isaacs, R.; Dong, K. Behavioral and physiological responses of Drosophila melanogaster and D. suzukii to volatiles from plant essential oils. Pest Manag. Sci. 2021, 77, 3698–3705. [Google Scholar] [CrossRef]
  51. Hummelbrunner, L.A.; Isman, M.B. Acute, sublethal, antifeedant, and synergistic effects of monoterpenoid essential oil compounds on the tobacco cutworm (Spodoptera litura). J. Agric. Food Chem. 2001, 49, 715–720. [Google Scholar] [CrossRef]
  52. Chu, S.S.; Jiang, G.H.; Liu, Z.L. Insecticidal compounds from the essential oil of Chinese medicinal herb Atractylodes chinensis. Pest Manag. Sci. 2011, 67, 1253–1257. [Google Scholar] [CrossRef] [PubMed]
  53. Babushok, V.I.; Linstrom, P.J.; Reed, J.J.; Zenkevich, I.G.; Brown, R.L.; Mallard, W.G.; Stein, S.E. Development of a database of gas chromatographic retention properties of organic compounds. J. Chromatogr. A 2007, 1157, 414–421. [Google Scholar] [CrossRef]
  54. Adams, R.P. Identification of Essential Oil Components by Gas Chromatography/Mass Spectrometry, 4th ed.; Allured Publishing Corporation: Carol Stream, IL, USA, 2007. [Google Scholar]
Figure 1. Percentage of D. suzukii choosing the control (white bars) or D. winteri EO treatments (black bars) in choice bioassays. The negative control contained acetone only. Bioassays were evaluated at 12, 24, 48, 72, and 96 h. Numbers in parentheses indicate the number of responding flies. Asterisks indicate significant differences based on G-tests: **** p < 0.0001, *** p < 0.001, * p < 0.05.
Figure 1. Percentage of D. suzukii choosing the control (white bars) or D. winteri EO treatments (black bars) in choice bioassays. The negative control contained acetone only. Bioassays were evaluated at 12, 24, 48, 72, and 96 h. Numbers in parentheses indicate the number of responding flies. Asterisks indicate significant differences based on G-tests: **** p < 0.0001, *** p < 0.001, * p < 0.05.
Plants 15 01676 g001
Figure 2. Repellency (%) of D. suzukii under different D. winteri EO treatments over time (12–96 h). Values represent mean ± SE. The horizontal dashed line at 50% indicates no preference for either stimulus.
Figure 2. Repellency (%) of D. suzukii under different D. winteri EO treatments over time (12–96 h). Values represent mean ± SE. The horizontal dashed line at 50% indicates no preference for either stimulus.
Plants 15 01676 g002
Figure 3. Oviposition preference index (OPI) of D. suzukii females exposed to raspberry fruits treated with D. winteri leaf EO (0.75, 1.5, and 3 mg mL−1). Negative OPI values indicate avoidance of treated fruits, whereas positive values indicate preference. The dashed line represents OPI = 0 (no preference). Asterisks indicate significant differences from zero based on Wilcoxon signed-rank tests (** p < 0.01, *** p < 0.001) and × indicates outliers. Each treatment included 25 independent replicates.
Figure 3. Oviposition preference index (OPI) of D. suzukii females exposed to raspberry fruits treated with D. winteri leaf EO (0.75, 1.5, and 3 mg mL−1). Negative OPI values indicate avoidance of treated fruits, whereas positive values indicate preference. The dashed line represents OPI = 0 (no preference). Asterisks indicate significant differences from zero based on Wilcoxon signed-rank tests (** p < 0.01, *** p < 0.001) and × indicates outliers. Each treatment included 25 independent replicates.
Plants 15 01676 g003
Figure 4. Experimental workflow of the study, including EO extraction, chemical characterization, and choice bioassays conducted with D. suzukii. The figure was created with BioRender.com.
Figure 4. Experimental workflow of the study, including EO extraction, chemical characterization, and choice bioassays conducted with D. suzukii. The figure was created with BioRender.com.
Plants 15 01676 g004
Table 1. Chemical composition of Drimys winteri bark and leaf essential oils.
Table 1. Chemical composition of Drimys winteri bark and leaf essential oils.
CompoundRTRIBark (%)Leaves (%)Identification
α-Pinene11.8593749.6435.85RI, MS
2-Piperizinopyridine12.20-3.071.45MS
β-Pinene13.1797917.1717.61RI, MS
β-Myrcene13.96991-1.84RI, MS
α-Phellandrene14.251005-2.05RI, MS
3-Carene14.4610111.62-RI, MS
β-Cymene14.8810231.86-RI, MS
Eucalyptol14.951032-0.99RI, MS
D-Limonene15.08-6.826.77MS
γ-Terpinene16.141060-1.18RI, MS
(+)-2-Bornanone18.3211430.27-RI, MS
(−)-Borneol19.291166-0.20RI, MS
Terpinen-4-ol19.951177-0.98RI, MS
(−)-Bornyl acetate22.7112840.110.18RI, MS
Elemene isomer24.371344-0.45RI, MS
α-Cubebene24.7613516.752.21RI, MS
α-Copaene25.46-2.490.53MS
β-Cubebene25.7613892.39-RI, MS
β-Elemene25.811391-1.48RI, MS
β-Maaliene26.3214050.34-RI, MS
Caryophyllene26.5114190.341.60RI, MS
Santalene26.5814200.49-RI, MS
β-Copaene26.801432-0.24RI, MS
Cadina-3,5-diene27.261458-0.22RI, MS
Humulene27.351454-0.39RI, MS
γ-Muurolene27.9014770.39-RI, MS
Germacrene D28.001481-2.54RI, MS
Bicyclogermacrene28.371495-1.06RI, MS
α-Muurolene28.4714990.72-RI, MS
γ-Cadinene28.7715131.30-RI, MS
Cadina-1(10),4-diene28.96-2.261.95MS
Elemol29.491549-7.07RI, MS
Spathulenol30.211576-0.23RI, MS
Caryophyllene oxide30.2915810.57-RI, MS
γ-Eudesmol31.421631-2.95RI, MS
τ-Cadinol31.7516400.20-RI, MS
β-Eudesmol31.801649-2.42RI, MS
α-Eudesmol31.941653-2.90RI, MS
Drimenol34.3217611.070.89RI, MS
Cembrene37.841939-0.12RI, MS
Sandaracopimaradiene38.181960-0.02RI, MS
α-Kaurene39.892041-0.16RI, MS
Monoterpenes--77.569.69-
Sesquiterpenes--19.3827.98-
Diterpenes--00.29-
Others--2.981.36-
RT—retention time (min); RI—Kovats retention index; %—considering detected compounds; MS—mass spectra. Compounds written in bold correspond to the most abundant compounds detected in bark and leaf EOs from D. winteri.
Table 2. Repellency (%) of D. suzukii in response to different treatments (T1–T6) over time (12–96 h).
Table 2. Repellency (%) of D. suzukii in response to different treatments (T1–T6) over time (12–96 h).
Time (h)
1224487296
T184.67 ± 10.09 a83.29 ± 6.12 a76.38 ± 7.46 ab74.06 ± 7.70 ab72.56 ± 7.15 a
T285.00 ± 10.00 a94.85 ± 2.35 a92.40 ± 2.62 a85.30 ± 5.81 a82.47 ± 6.63 a
T372.94 ± 9.00 ab76.81 ± 4.73 ab65.00 ± 5.07 b70.15 ± 4.90 ab59.77 ± 9.52 a
T469.42 ± 10.77 ab74.62 ± 4.84 ab64.45 ± 7.67 b62.44 ± 8.28 ab53.90 ± 9.71 a
T581.66 ± 9.74 a84.19 ± 3.69 a82.73 ± 4.37 ab73.18 ± 5.04 ab76.49 ± 3.07 a
T642.08 ± 6.40 b50.46 ± 5.16 b47.50 ± 8.49 b46.22 ± 9.58 b43.53 ± 9.78 a
Values are shown as mean ± SE (n = 10). Different letters within the same column indicate significant differences among treatments based on the Kruskal–Wallis test followed by Bonferroni multiple comparisons. T6 represents the negative control.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Tampe, J.; Sandoval, D.; Espinoza, J.; Ruiz, C.; Quiroz, A.; Rubilar, M. Repellent and Deterrent Oviposition Activity of Essential Oils from the Native Chilean Plant Drimys winteri Against Drosophila suzukii (Diptera: Drosophilidae). Plants 2026, 15, 1676. https://doi.org/10.3390/plants15111676

AMA Style

Tampe J, Sandoval D, Espinoza J, Ruiz C, Quiroz A, Rubilar M. Repellent and Deterrent Oviposition Activity of Essential Oils from the Native Chilean Plant Drimys winteri Against Drosophila suzukii (Diptera: Drosophilidae). Plants. 2026; 15(11):1676. https://doi.org/10.3390/plants15111676

Chicago/Turabian Style

Tampe, Jocelyne, Dante Sandoval, Javier Espinoza, Camila Ruiz, Andrés Quiroz, and Mónica Rubilar. 2026. "Repellent and Deterrent Oviposition Activity of Essential Oils from the Native Chilean Plant Drimys winteri Against Drosophila suzukii (Diptera: Drosophilidae)" Plants 15, no. 11: 1676. https://doi.org/10.3390/plants15111676

APA Style

Tampe, J., Sandoval, D., Espinoza, J., Ruiz, C., Quiroz, A., & Rubilar, M. (2026). Repellent and Deterrent Oviposition Activity of Essential Oils from the Native Chilean Plant Drimys winteri Against Drosophila suzukii (Diptera: Drosophilidae). Plants, 15(11), 1676. https://doi.org/10.3390/plants15111676

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop