Introduction

The introduction of chemical plant protection products into the natural environment results in the disruption of biological balance, and poses a great threat to human health, animals and the environment. They cause major damage to ecosystems and groundwater. In addition, chemical methods contribute to the destruction of useful fauna as well as contamination of agricultural products (Nicolopoulou-Stamati et al. 2016; Carvalho 2017). Due to the unfavorable effect of pesticides, non-chemical methods play an increasingly important role in pest control. The use of natural compounds in place of synthetic insecticides can reduce environmental pollution, and they are safe for human and animals health (Liao et al. Statistical analysis

Statistical analyses were based on two-factor and three-factor analysis of variance models and Tukey’s multiple T tests, at the assumed significance level of α = 0.05. ANOVA with Repeated Measures Analysis of Variance was used for data obtained from the measurements in subsequent time points (from the same objects) (data are correlated). Analysis of variance models with the main effects of the studied factors and their interactions with the final indication of the calculated probabilities related to the applied F test functions (F–Snedecor or Fisher–Snedecor) were applied. Tukey’s multiple comparison HSD tests enabled detailed comparative analyses of means by separating statistically homogeneous medium groups (homogeneous groups). The detailed data of the statistical analysis are presented in Table (Supplementary data).

Results

Oviposition preference of Acrobasis advenella females

In total, during the experiment, A. advenella females laid 2751 eggs (average 137.55 eggs/female). No eggs were found on fruits treated with acetone extracts. Statistical analysis of the results did not confirm a significant difference in the number of laid eggs in relation to the diluent (aqueous extracts and essential oils) (Table: Supplementary data). There was also no interaction between the applied diluent and the plant species used for spraying the inflorescences. However, plant species had a significant impact on the choice of females (F8.160 = 20.4910; P = 1 × 10−7). The highest number of eggs was laid by females on fruits treated with C. citratus (32.36%) (Fig. 1). A large number of them were also recorded on fruits sprayed with O. vulgare (19.68%), but this difference was not statistically significant compared to control (17.15%). Significantly fewer eggs were observed on fruits treated with other plant species. The lowest number of eggs was found on fruits treated with T. vulgare (2.43%) and S. hortensis (3.89%).

Fig. 1
figure 1

Mean percentage (± SE) of eggs laid by females of Acrobasis advenella on infructescences of Aronia melanocarpa treated with different species of plant extract (N = 20). Bars marked by different letters are significantly different (Tukey’s HSD test P ≤ 0.05)

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Effects of essential oils and extracts on free choice test of Acrobasis advenella larvae

The results showed that plant species had a significant influence on the selection of feeding site by larvae (F7.192 = 45.255; P = 1 × 10−7) (Fig. 2). Most larvae selected control inflorescences (27.35%), while from the remaining ones they chose C. citratus (25.68%) and O. vulgare (19.84%) most willingly. The lowest number of larvae was observed on inflorescences treated with T. vulgare (2.09%), A. millefolium (4.19%) and S. hortensis (4.69%). Statistical analyses did not show statistically significant differences in the selection of feeding site by particular larval stages (L1–L4) (Table: Supplementary data).

Fig. 2
figure 2

Mean percentage (± SE) of Acrobasis advenella larvae on inflorescences of Aronia melanocarpa treated with different species of plant extract (N = 360). Bars marked by different letters are significantly different (Tukey’s HSD test P ≤ 0.05)

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A.advenella larvae had the possibility to change the feeding site. At all time points, the number of larvae in non-treated inflorescences (control) and soaked in solutions of C. citratus and O. vulgare increased, reaching the highest value on C. citratus and control after 24 h (Fig. 3). The highest changes (increase or decrease) were most noticeable after 12 h from the beginning of the experiment (Fig. 3). After 2 and 5 h, the lowest number of larvae inhabited inflorescences soaked with T. vulgare and A. millefolium. After 12 h, all larvae left the inflorescences treated with T. vulgare, and several still inhabited the inflorescences soaked with S. hortensis and A. millefolium. Although part of the caterpillars changed their feeding sites during the experiment, statistical analysis did not confirm that time significantly influenced the choice of location by larvae, but multivariate statistical analysis showed that there are interactions between the species of plants used in the experiment and time (F21.576 = 33.528; P = 1 × 10−7). The experiments also showed that the type of diluent used (essential oil, water and acetone extract) had no effect on the choice of larvae (Table: Supplementary data).

Fig. 3
figure 3

Mean percentage (± SE) of larvae of Acrobasis advenella on inflorescences of Aronia melanocarpa treated with different species of plant extract after 2, 5, 12 and 24 h (N = 360)

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Discussion

Essential oils (EOs) contain organic compounds that are plant secondary metabolites. Chemically, these substances are mixtures of compounds such as monoterpenes, sesquiterpenes, phenols, aldehydes, alcohols or other compounds (Olayemi 2017). Plant volatiles can contain many components. Generally, oil is determined by one, two or three of its main active compounds, but it also happens that the residual oil components are important (Mossa 2016; Moghaddam and Mehdizadeh 2017). Chemical variations in EO composition are rather common even within the same species. Mainly, it depends on the type of genotype, plant organ, harvest, geographical region, season, plant nutritional status and climatic conditions—temperature, humidity and light intensity (Webster et al. 2010; Dhifi et al. 2016).

Volatiles emanating from plants play different ecological and behavioral roles in the life of insects. They can contribute to indicate food, decide about mating sites and control reproduction processes; furthermore, they are involved in food selection and acceptance of individual plants or only their parts, but also plants that are inappropriate for adult or larval food. Female insects also use plant volatiles to select oviposition sites (Nansen and Phillips 2003; Borrero-Echeverry et al. 2018). Oviposition by females is particularly important for the survival of their progenies, mainly because the quality of food and its availability to larvae are determined by oviposition of the female on a suitable host plant (Honda 1995). Antifeedants inhibit insect feeding, through sensory perception, but they do not directly kill insects (Li et al. 2005). Female moths select plants for oviposition based on visual, olfactory and gustatory information (Fei et al. 2017). These cues that induce or inhibit oviposition play an important role in the survival of herbivorous insects, since hatching larvae have often restricted activity. Moreover, they play a role in host selection, because choosing oviposition site depends on the presence or absence of stimulants or deterrents (Renwick and Radke 1988; Renwick 1994). Essential oils of the family Lamiaceae, including, Satureja, Thymus and Origanum contain mainly aromatic monoterpenes, carvacrol, thymol and p-cymene (Tabari et al. 2015). Insecticidal and acaricidal activities are often attributed to these compounds (Bakkali et al. 2008; Senthil-Nathan 2015). According to Honda (1995), secondary compound from plants also stimulates or inhibits oviposition of females. The reduction in fecundity may be due to the direct effect of essential oils, disruption of reproductive behavior by compounds in EOs or a combination of these two processes on adults. Essential oils often have stronger insecticidal activity than any of their individual constituents (Tak et al. 2016). Kim et al. (2010) demonstrated that the essential oil from O. vulgare was more effective against Tribolium castaneum (Herbst) than carvacrol, i.e., its pure secondary metabolite. On the other hand, it has been observed that complex essential oil compounds are more effective than pure EOs (Bakkali et al. 2008). Our results showed that O. vulgare extracts and EOs were rather attractant both for the females and larvae of A. advenella. Thymol may contain up to 80% of the main compounds of thyme essential oils (Archana et al. 2011). For example, Tabari et al. (2015) reported that carvacrol and thymol showed strong acaricidal activity against Dermanyssus gallinae (De Geer). Park et al. (2017) demonstrated that thymol exhibited insecticidal activity against Pochazia shantungensis Chou & Lu adults and nymphs. In our experiment, by far the strongest repellent activity was shown by the tansy, but a low percentage of larvae were found on plants treated with extracts and oils from S. hortensis. Magierowicz et al. (2019) proved that carvacrol was the dominant substance in S. hortensis essential oil (73.24%). We have noted that they are characterized by insecticidal activity against A. advenella. S. hortensis essential oil reduced the occurrence of moths’ longevity and increased mortality of larvae. Shahab-Ghayoor and Saeidi (2015) reported significant inhibition of Plodia interpunctella (Hübner) feeding even at low concentrations of the summer savory EO.

Essential oils and extracts belonging to plants of the families Poaceae and Lamiaceae are commonly used as insect repellents. Cymbopogon citratus is one of the most widely used natural repellents against various insect pests, but mainly it has been used to control mosquitoes and houseflies (Aidaross et al. 2005; Pushpanathan et al. 2006; Maia and Moore 2011). Lemon grass exerts both repellant and toxic effects against insects. Geranial (a-citral) and neral (b-citral) are the two main active components of lemon grass oil, but other compounds, which are often present in small amounts, such as geraniol and citronellol, are also known repellents (Baldacchino et al. 2013). Extracts from C. citratus exhibited high toxicity against Anopheles arabiensis Patton (Karunamoorthi and Ilango 2010). The repellent effect of C. citratus was also noted against Coleoptera insects, such as Sitophilus oryzae L. (Saljoqi et al. 2006) and Sitophilus zeamais Motschulsky (Parugrug and Roxas 2008). Rafeeq et al. (2016) also reported the repellent effect of C. citratus against Luprops tristis F., and the rate of this effect was higher with increasing oil dose. Hussein et al. (2015) observed that lemon grass extract and essential aromatic oil reduced the population of Tuta absoluta Povolny on tomato plants. In the available literature, we have not found information about attractiveness of C. citratus for insects. Our results showed that both adults and larvae of A. advenella definitely and preferably chose plants treated with lemon grass. Females laid the highest number of eggs on these plants, and they had the highest percentage of all A. advenella larval stages. The oldest larvae selected significantly more frequently inflorescences treated with C. citratus than controls, and therefore it could be a potential attractant for A. advenella. However, further studies are necessary to confirm the attractiveness of C. citratus EO in higher concentrations. Our results also showed that extracts and essential oils of O. vulgare were frequently chosen by A. advenella. However, this EO is also an effective repellent against pests (Yazdani et al. 2014; Nasr et al. 2017).

Studies by many authors have proved that plants of the Asteraceae family are a potential source of biopesticides with insecticidal properties (Umpiérrez et al. 2012; Czerniewicz et al. 2018). Extracts and essential oil from T. vulgare exhibit strong insecticidal and antifeedant effects (Panasiuk 1984; Schearer 1984; Hough-Goldstein and Hahn 1992). Mainly, these activities depend on their chemical composition. There are about 30 chemotypes of tansy in the world, but β-thujone is the main component of its essential oil (Kleine and Müller 2011). Szołyga et al. (2014) showed that T. vulgare EO and its main components, α- and β-thujone inhibited growth, slowed development, and increased mortality of young larvae (10-day-old) of Alphitobius diaperinus Panzer. On the other hand, they also acted as strong attractants, but the younger larvae were more susceptible to all tests than the older ones. Many authors emphasize that larvae become less susceptible to essential oils and their active ingredients with age (Mondal and Khalequzzaman 2010; Szczepanik et al. 2012), but our results did not show statistically significant differences in the selection of feeding site by particular larval stages (L1–L4). In addition, during all time points of the experiment, we showed that the lowest number of A. advenella larvae was obtained for inflorescences treated with T. vulgare plant extracts. T. vulgare definitely had the strongest repellent effect for larvae and females, although the statistical analysis did not confirm this. Gabel and Thiery (1994) reported a similar result that T. vulgare EO had a deterrent effect on oviposition and it inhibited the mating behavior in the moth Lobesia botrana (Den. and Schiff.). They showed that egg laying was reduced by 30–80% and the longevity of adults was decreased. In addition, tansy essential oil had an oviposition deterrent effect on Choristoneura rosaceana (Harris) females (Larocque et al. 1999). According to Szołyga et al. (2014), stronger action of EOs may be the result of the dose applied. Hough-Goldstein (1990) tested an aqueous extract of T. vulgare against Colorado potato beetles in laboratory choice tests. Tansy showed the most potent antifeedant effect compared to other test plants. The authors proved that the extracts deterred feeding by both larval and adult Colorado potato beetles (Leptinotarsa decemlineata Say). Moreover, Hough-Goldstein and Hahn (1992) reported that aqueous extract of tansy exerted antifeedant effects on Plutella xylostella L. larvae. Additionally, cabbage leaves treated with tansy extract caused longer growth of P. xylostella larvae. According to Ertürk et al. (2004), the alcohol extract of T.vulgare showed the strong deterrent effect against the larvae of Yponomeuta malinellus Zell., but it did not show toxicity effect against the pupae and larvae of Y. malinellus.

Previous studies have reported that the use of Asteraceae plants with repellent properties could be a useful method of reducing aphid populations. Halbert et al. (2009) found high repellency of A. millefolium essential oil against corn leaf aphids (Rhopalosiphum maidis Fitch). Czerniewicz et al. (2018) also demonstrated that repellent properties were enhanced with increasing EO concentrations. These authors showed that, among the used oils, A. millefolium oil had the highest settling inhibitory activity against M. persicae. Ebadollahi and Ashouri (2011) reported the essential oil from A. millefolium was highly effective against adults of Plodia interpunctella (Hübner), and the mortality values reached 100% after 48 h. Our results also showed that yarrow extracts had rather repellent properties and it was the second most rarely chosen plant species.

Research shows that the effect of compounds contained in essential oils is very diverse. Some substances can simultaneously attract and deter various insect species. Substances that occur in large quantities do not necessarily determine the acceptance of the insect. Biopesticides are a promising source of pest control compounds. They have aroused great interest in recent years as potential sources of natural insect control agents mainly due to the insects repelling properties. A thorough investigation of attractive components in plant volatiles would allow the development of effective plant protection products. Attractants would help in catching male and female moths, monitoring the population and eventually reducing the number of pests. The use of plant extract or EO as biopesticides can reduce damage to chokeberry by lowering the number of eggs laid and reducing A. advenella population. The application of natural pesticides can be combined with different biological methods in an integrated management strategy against A. advenella. This approach could also reduce the use of synthetic insecticides. However, further research is necessary to investigate the impact of extracts and essential oils of plant species that have the strongest effect on A. advenella in field conditions.