3.1 Exploitation of chemical communication
In the framework of biocontrol, researches are looking closely at odor. Those emitted by plants first, since they are what enable pest insects to locate them in the landscape and colonize them (Conti et al., 2021; Vargas, Rivera-Pedroza, García, & Jahnke, 2023). Those emitted by insects then, and in particular by females to attract males during reproduction (Lucie Conchou et al., 2019). These odors are called pheromones when they concern exchange between individuals belonging to the same species (Lucie Conchou et al., 2019; B. Nielsen, O. Rampin, N. Meunier, & V. Bombail, 2015). We talk of allelochemical substances to describe the exchanges between individuals of different species, and more specifically of kairomones, when these substances benefit the one who receives the message (B. Nielsen et al., 2015). In recent years, the development of strategies based on semiochemistry has increased considerably, as they are considered effective tools for manipulating the behavior of insects targeting plants with the aim of improving the biological control of crop pests (Conti et al., 2021). However, feeding and/or oviposition by herbivorous insects induces changes in a plant's ecophysiological traits and their emission of VOCs, either as herbivore-induced plant volatiles (HIPVs) or oviposition-induced plant volatiles (OIPVs) (Conti et al., 2021). In this work we interest on the study of the qua-trophic relationship between Punica granatum, A. punicae, natural enemy (ladybird), and pest protector (ant), under field conditions to detect a new way of research for pests protects plants.
3.1.1 The triggering systemic acquired resistance (SAR) in the host plant
The fruit cropping system is localized in the central-western agroclimatic subzone of the Al Baha region and the central and northern areas of the Makkah Region, including the very large Taif governorate. Fruits are grown on more than 35% of the cultivated land. Farms in the Al Baha and Taif regions now see more than 200,000 pomegranate trees produce 30,000 tons of fruit each year (according to the approximate statistics of the Pomegranate Cooperative Society in the Al-Baha and Taif region) (Alghamdi, Aly, & Ibrahim, 2022). The work of identifying aphids associated with plants growing in Taif governorate made it possible to establish a list of the main species encountered during the study period (Alotaibi et al., 2023). Among these aphids, A. punicae Passerini (SUB9563655) is a specialist in Punica granatum. A. punicae is the most important and destructive for the pomegranate tree. This pest could cause heavy yield losses, in some cases reaching 24 tons/ha in the absence of chemical intervention. Plant protection systems based on the intervention threshold can lead to the avoidance of some systematic treatments applied by farmers in the region against these pests.
3.1.2 Open-loop stripping systems-DVB
The effects of cascading in ecological systems that operate across three or more trophic levels can either be based on resources (bottom-up) or natural enemies (top-down). These effects are often considered separately due to their complexity, and their relative strength when acting simultaneously is not known (Senft, Clancy, Weisser, Schnitzler, & Zytynska, 2019). In this work, we studied three field ecological systems based on natural resources (bottom-up), starting with plant-aphid (S1-DVB), plant-aphid-ant (S2-DVB), and plant-aphid-ant-ladybird (S3-DVB) interactions.
During the quadruplet interaction between host plants, pests, protectors, and predators in our setup, herbivores resulted in the appearance volatile lists, which were collected from branches by OLS systems, and identified by GC-MS. Significant differences can be observed in the volatile compounds of field-infected pomegranates with aphids and their predator and protector when analyzed. 30 VOCs were detected in the samples that were trapped from different stages of AIP from all ecologies systems. Plants damaged by A. punicae change their odor emission, as well as the variety of substances classes of VOCs. In most treatments, alkanes, aldehydes, ester, benzene derivatives, and terpenes were the most likely VOCs released from field AIP in the presence or absence of predator or protector. The headspace of AIP (S1-DVB) consisted of benzene derivatives (53.44%), alkanes (43.62%), monoterpenes (5.07%), sesquiterpenes (5.14%), and alcohol (1.94%). In response to adding the ants to the AIP, the headspace profile of the tripartite community (S2-DVB) showed a high level of ketones (75.04%) and alkanes (19.84%) while monoterpenes, sesquiterpenes, and aldehydes disappeared. The profiles of the quadripartite community of AIP that contains ants and ladybirds (S3-DVB) show a decrease of 12.92% in alkanes and an absence of sesquiterpenes (Table S1, Figures 1a and 1b).
Several compounds are present in all samples trapped by DVB and identified by GC-MS. The pomegranate that is damaged by A. punicae (n=15) has the ability to alter its smell. According to the findings, the presence of ants reduces the number of VOCs (n=4), but the presence of ladybirds increases the number of detected VOCs (n=17) as compared to plants affected by A. punicae (Table S1). According to the OLS system, the AIP's qualitative odor composition mainly consists of o-xylene, p-xylene, 1-methyl-3-tert-butylbenzene, m-ethylcumene, 2-methylnaphthalene, 3-carene, (+)-4-carene, benzaldehyde, 2,2,4-trimethyl-pentane, tridecane, caryophyllene, beta-farnesene. Furthermore, the addition of ants changes the profile of the compounds detected. They were essentially formed of o-xylene, p-xylene, 4-heptanone, and unknown alkane-2. After adding ladybird, the number of VOCs detected increased again to 7, and 17 for the OLS system, after 24 and 48 hours of contact. After 48 hours of ecological interaction, OLS discovered new VOCs and the disappearance of others, which had a composition of 99.73% (Table S1, Figures 1a and 1b).
3.2 Analysis of the VOCs profiles from the qua-trophic relationship
The VOC profiles of the three ecologic interactions systems, S1 (two-trophic relationship aphid-plant), S2 (tri-trophic relationship aphid-plant-ant), and S3 (qua-trophic relationship aphid-plant-ant-ladybird), allowed the identification of 30 compounds. Of these 30 compounds, only one p-Xylene was present in all three treatments, while 1-methyl-3-tert-butylbenzene, m-ethylcumene, 3-carene, and (+)-4-carene, alpha-methylbenzeneacetaldehyde, unknown alkane-3, unknown alkane-4, 2,2,4-trimethyl-pentane, caryophyllene, and β -farnesene were only present in the headspace of system S1 (Table S1, Figures 1a and 1b). Ester, ketone, or N-compounds were not present in system S1's headspace, but they were present in other systems (Table S1, Figures 1a and 1b).
The GC/MS analysis showed that the emission of VOCs is highly influenced by ecological interaction. The ecology interaction system (S1-DVB) has ten components, which include 1-methyl-3-tert-butylbenzene, m-ethylcumene, and caryophyllene. In the presence of ants, the major compounds are 4-heptanone and unknown alkane-2. After 24 hours of the presence of ladybird, tricyclene was the main VOC, followed by limonene, and unknown alkane-3 after 48 hours.
3.3 Statistical analysis of fundamental ecological relationships and their impact on the implementation of biological control.
Analysis of HIPVs shows significant differences between the VOCs detected by OLS analysis systems, which were identified by GC-MS. Several compounds were present in all samples that were trapped from different stages of AIP. HIPVs obtained by OLS analysis (n=15), and it shows that β-farnesene was exclusively detected in the HIPVs from AIP. To understand the smell profile of plants attacked by pests and identify behaviorally active components for predators, it's important to use complementary methods, as our results demonstrate. The headspace profiles of AIP and AIP with ants and ladybirds were different due to VOCs. Figure 2c show a heat map graphically displaying results from hierarchical clustering of volatile compounds from AIP without and with ants and ladybirds detected by OLS systems.
This work was conducted to determine the closeness of individual compounds to all ecosystem systems' interactions infested pomegranate with A. punicae, triplet interactions between AIP and ants, and quadruplet interactions between AIP, ants, and ladybirds. Distances between samples and assays were calculated for hierarchical clustering using Pearson's correlation distance. Each volatile compound has a peak area detected by GC-MS, presented on a color scale that illustrates the differences between the replicates of all ecosystem systems interactions. The heat map indicated that the detected compounds and the difference between all ecologies interaction systems are based on the scale of color, and each color corresponds to one detected VOC. The value of the compound is represented by red, orange and dark blue for the maximum (2), average (0) and minimum (–2) (Figure 2c). In addition, principal component analysis (PCA) was performed. The PCA score plot (Figures 2a and 2b) reveals that all OLS analysis ecologic interaction systems are separated. However, the separation shows four different groups based on their profiles of VOCs using significant differences (p < 0.05), relationship between VOCs of AIP and AIP with ants and ladybirds, as shown in Figures 2a and 2b.
To accurately assess the closely connected substances on the topographic plot, all the information provided by the fingerprint analysis technique was used for qualitative characterization. In the fingerprint (Figure 2), each column displays the signal peaks of each sample, and each row displays the same volatile compound for every sample. Additionally, the color of it indicates the amount of volatile compounds, with a brighter color signified a higher content. As illustrated in Figure 2, there was a significant variation in the content of VOCs in the samples of all four groups.
The PCA obtained using the VOCs of the three study systems (Figure 3) showed that all ecology interactions (S1-DVB, S2-DVB, and S3-DVB) are able to form distinct groups on the first plane of the PCA. The specific profiles of each group were observed to have marked chemical variability (Table S2, Figure S1), which allowed for group separation on the PCA. The two dimensions (F1 and F2) of the PCA explain 73.8% of the total data variability (45.9% for the F1 axis and 27.9% for the F2 axis). The first axis, F1, allows for the separation of G-4 rich in 1-ethyl-3-methylbenzene (Bio3), 1,3,5-trimethylbenzene (Bio4), methyl salicylate (Bio10), sabinene (Bio12), limonene (Bio14), unknown alkane-3 (Bio20), pentadecane (Bio24), heptadecane (Bio25), 1-methyl-1H-imidazole (Bio26), and unknown-1 (Bio30), such as PIN48An48Lb48-DVB, located on the right side of the PCA, represented in the positive region of F1. The second dimension of the PCA, F2, allowed to distinguish two groups, G-2 and G-3, which were richer respectively in methyl methanoate (Bio9), unknown alkane-2 (Bio19), and 4-heptanone (Bio8), namely respectively PIN48An24-DVB and PIN24An24Lb24-DVB. The groups that are found in the negative region of F2. However, the first group G-1 was separated by F1 and F2 in the left positive region of F2, which was characterized as being richer in 1-methyl-3-tert-butylbenzene (Bio5), m-ethylcumene (Bio6), 3-carene (Bio11), (+)-4-carene (Bio15), 2,2,4-trimethyl-pentane (Bio18), unknown alkane-6 (Bio22), and caryophyllene (Bio27), namely PIN24-DVB (Figure S1).