1. Introduction
Spodoptera frugiperda (Lepidoptera: Noctuidae), commonly known as the fall armyworm, is a migratory agricultural pest originating from tropical and subtropical regions of the Americas [
1,
2,
3]. Its global significance stems from robust reproductive, adaptive, and migratory capacities, posing a formidable threat to crop production worldwide [
4,
5]. In January 2019,
S. frugiperda infiltrated China's Yunnan Province from Myanmar for the first time, identified as the "maize type," currently posing a severe threat to Chinese food crop production safety [
6,
7]. Subsequently in April 2019 the pest invaded Hainan Province, which is a tropical area with the same climate with the origin of this pest, swiftly affecting nearly all maize planting areas and resulting in substantial losses [
8,
9].
The significant impact on agriculture has prompted comprehensive efforts to monitor, prevent, and control
S. frugiperda in China. Comprehensive utilization of agricultural control technology, biological control technology, physical control technology, and chemical control technology has been made to reduce the adverse effects of this pest on Chinese agricultural development[
10]. Despite its preference for Poaceae plants, this polyphagous pest has demonstrated the ability to feed on a diverse range of plant taxa, including herbs, vines, and woody vegetation, with reports of up to 353 species from 76 families as potential hosts [
11,
12]. Particularly concerning is the possibility that, with enhanced agricultural control measures, the pest may evolve into a major threat to forestry vegetation. Previous studies have identified various host plants, including woody species from families such as Arecaceae, Euphorbiaceae, and Fabaceae[
12]. Experimental evidence, such as larvae feeding on tea plant leaves, further emphasizes the potential risk of
S. frugiperda to woody plants after principal crop harvests[
13]. Despite these findings, a lack of researchs remain regarding the specific adaptations of
S. frugiperda to woody species.
Hainan Province is a tropical region with the same tropical and subtropical climate as the origin of this pest in the Americas. The six trees advocated by Hainan Province, including
Areca catechu,
Cocos nucifera, (both are Arecaceae),
Hevea brasiliensis (Euphorbiaceae),
Dalbergia odorifera (Fabaceae),
Camellia oleifera (Theaceae) and
Aquilaria sinensis (Thymelaeaceae) [
14] have been expanded for planting. This not only improves the ecological and environmental quality, but also generates huge economic benefits. While possessing significant economic value, these trees have been reported to be susceptible damaged by Lepidoptera and Coleoptera pest [
15,
16]. Their main pests are described in
Table S1.
S. frugiperda as a Lepidoptera omnivorous pest, prompting concerns about the potential impact of infestation on these valuable trees.
This study aims to fill the current research gap by studying the potential threat posed by S. frugiperda to these six economically significant tree species in Hainan Province. A comprehensive understanding of the risk assessment associated with the pest's translocation among different hosts will inform Integrated Pest Management (IPM) strategies for S. frugiperda in both primary and alternate host plants.
2. Materials and Methods
2.1. Plants and Insects
Leaves from A. catechu, C. nucifera, D. odorifera and A. sinensis were sourced from the Yazhou Base of Sanya Academy of Tropical Agricultural Sciences, Sanya, Hainan Province, China (18.390246°N, 109.164020°E). Meanwhile, leaves of C.oleifera and H. brasiliensis were obtained from Danzhou Campus of Hainan University (19.507783°N, 109.495946°E). The maize (Zea mays) variety DK647, with seeds provided by Longping Biotech. Co., Ltd. (Sanya, China), served as the control treatment. The maize plants were cultivated in pots with nutrient soil (15 × 12 cm in diameter × height) in the greenhouse at the Yazhou Base of the Sanya Academy of Tropical Agricultural Sciences. All collected leaves were fresh and free from pest damage.
S. frugiperda eggs were originated from Longping Biotech. Co., Ltd (Sanya, China) and was consistently cultured in a climatic chamber (27 ± 1℃, 65 ± 3% RH, 16: 8h L:D). The eggs were placed in square plastic boxes (17.0 × 11.8 × 4.8 cm in length × width × height),covered with gauze to enhance insect respiration while prevent escape. Larvae in the 3rd instar were individually raised in cylindrical plastic boxes with lids (5.0 × 3.7 cm in diameter × height), each fitted with pinholes. The lids were punctured to facilitate adequate air circulation and simultaneously deter the larvae from escaping. After pupation, they were transferred to 100 mesh cages (Yiheng Scientific Instrument, Shanghai, China) (75 × 75 × 75 cm in length × width × height) for emergence, and a 10% honey water solution was provided to the adults for survival and reproduction. The 3rd instar larvae (7 days after hatching) were used for the experiment.
2.2. Feeding Patterns and Developmental Characteristics of S. frugiperda
The experiment encompassed seven treatments, involving the consumption of six distinct tropical tree species (
A. catechu,
C. nucifera,
H. brasiliensis,
D. odorifera,
C. oleifera,
A. sinensis), with
Z. mays served as the control treatment. Leaves from each treatment underwent washing and cutting into 1 cm² squares for convenient measurement of leaf area according to the grid method [
17]. Briefly, leaves were positioned on a transparent coordinate paper with a 1 mm
2 grid. The vacant squares within a 1 cm
2 area were counted, thus representing the leaf area (mm
2). Third instar larvae from the same batch were individually cultured in cylindrical plastic boxes (5.0 × 3.7 cm in diameter × height), each equipped with pinholes to facilitate insect respiration and prevent escape. One larva was placed per box, and 30 replicates were conducted for each treatment. Daily replacements of leaves and cleans of insect feces were performed, feeding quantity changed as the quantity consumed increased. Mortality rates and feeding leaf areas were documented daily. Measurements of weight and length were taken by electronic scales (d = 0.001) (PL203, Metler Toledo) and industrial microscope (SZX16, Olympus Corporation) as larvae progressed to the pre-pupal stage. The eclosion time and gender of the adults were also recorded. The entire experiment was conducted in a climate chamber (27 ± 1℃, 65 ± 3% RH, 16: 8h L:D).
2.3. Determination of Enzyme Activity
Superoxide dismutase (SOD), and peroxidase (POD) activities were quantified using kits (respectively A007, A001, A084; Nanjing Jiancheng Bioengineering Institute, Nanjing, China). For enzyme activity determination, three samples were randomly selected from each of the seven treatments. Due to the low survival rate of 3rd instar larvae feeding on A. catechu, C. oleifera and D. odorifera observed in the bioassay experiment, the S. frugiperda larvae, which ate different plant leaves for 7d after the 3th instar in a climatic chamber (27 ± 1 °C, 65 ± 3 % RH, 16: 8h L:D), were collected and used for test enzyme activity. Larvae before the 3th instar were reared with maize leaves.
Before collection, larvae were firstly washed by ultrapure water, the surface water were wiped with chipless paper, then the body weights were recorded. The samples were placed in centrifuge tubes and stored at -80°C until testing. Mechanical grinding on ice at 4°C was performed by mixing the insects with 0.9% saline in a 1:9 (w:v) ratio. After thorough grinding, the samples were centrifuged for 10 minutes at 2500 rpm, the resulting supernatant (10% homogenized supernatant) was used for enzyme analysis following the manufacturer's instructions. Optical density (OD) values were measured using a microplate spectrophotometer SpectraMax ABS (Molecular Devices, USA), enzyme activities were calculated using the corresponding formulas. The tests were carried out in accordance with the manufacturer's instructions [
18,
19,
20]. Corresponding formula:
where PC = Protein concentration; OD
A, OD
B, and OD
S represent the OD values detected by the corresponding tubes (Blank (B), standard (S), and assay (A)); Ps (Protein standard solution) = 0.524 g/l ; N = dilution times.
where SOD activity (U/mgprot) = the quantity of SOD per mg of histone corresponding to 50% SOD inhibition in 1 ml of reaction solution is one SOD viability unit (U); POD activity (U/mgprot) = amount of enzyme 1 mg of histone catalyzing 1 μg of substrate per minute at 37°C. In the formula, OD
C, OD
A = the OD values detected by the corresponding tubes (control (C) and assay (A)); 235.65 = the reciprocal of the slope (instructions indicate direct use); V
SD, V
F = Volume of SD or final reaction liquid taken for experimental use; T = reaction time.
2.4. S. frugiperda Feeding Preferences
Feeding preference experiments were conducted to further indicate the feeding selection for
S. frugiperda. Six distinct tree species were assessed using the leaf disk method [
17,
21]. Initially, a petri dish (90 mm in diameter) was evenly divided into six sectors of equal area. Leaves from various treatments were washed and cut into 1 cm² squares, which were randomly and sequentially positioned at the end of the dividing lines within the plastic petri dish. One 3rd instar larva of
S. frugiperda, starved for more than 6 hours, was introduced into the center of each dish, and the dish was covered to prevent escape. After 6 hours, the leaf disk areas consumed by larvae on different plants were assessed using the counting grid method [
17]. The feeding preference of larvae on different plants was quantified using the preference index, which was calculated as the percentage of the area of a plant's leaf disk consumed by larvae, relative to the sum of the areas of all leaf disks consumed. The preference performance was evaluated with 50 insects at a time and replicated three times. Experiments were conducted in a climatic chamber set at 27 ± 1℃, 65 ± 3% RH, and 16:8h L:D.
2.5. Data Analysis
Survival ratios of S. frugiperda among various plant treatments were analyzed using the Kaplan-Meier procedure and log-rank test. A full factorial LMER analysis, incorporating random factors for different plant treatments, time (days of measurement), and replications, was employed to analyze feeding leaf area, ANOVA with type III sum of squares (car package) was used for comparisons between treatments. For growth parameters, pupation rate, ecolosion rate, females rate between different treatments were subjected to analysis and comparison using the Chi-square test. Larval development time and pupal development time did not adhere to normal distribution were tested using the Kruskal-Wallis Test with Mann-Whitney U test. Enzyme activity assay data that did not conform to normal distribution were transformed using Blom in the normal score method. The remaining data, conforming to normality and homogeneous, were analyzed using one-way ANOVA with Tukey HSD test. All data are presented as mean ± standard error (SE). A significance level of P < 0.05 was considered for determining statistical significance. Data analysis was conducted using R 4.2.3.
4. Discussion
The bio-experimentation on this study revealed significant differences in the performance of S. frugiperda across various tropical tree species. Notably, A. sinensis emerged as the most vulnerable to S. frugiperda infestation, followed by H. brasiliensis and C. nucifera. In contract, A. catechu, D. odorifera and C. oleifera were at low risk by the infestation of S. frugiperda.
A. sinensis is the main incense in China. Currently, the world's resource endangered species of Aquilaria have been listed in Appendix II of the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) [
22]. It is an expensive and vital medicinal herb with an enormous financial value[
23].
A. sinensis has been reported to be mainly affected by three pests:
Heortia vitessoides (Lepidoptera),
Dyspessa monticola (Coleoptera), and
Anoplophora chinensis (Coleoptera) [
24]. Host plant choice significantly influences phytophagous insect growth and development, with suitable hosts leading to higher survival rates and shorter developmental periods [
25]. In current study, different host plants exerted distinct influences on the growth and development of
S. frugiperda. In the experiment, the parameters of daily survival rate, pupation rate (86.67%), eclosion rate (83.33%), females rate (24%) of
S. frugiperda with
A. sinensis were not significantly differences compared to the control group (maize). The parameters of leaf area consumption, larval development time (14.36 ± 0.32d), pupal development time (10.72 ± 0.13d) in
A. sinensis group were significantly inferior to maize group but performed well in comparison with other tree groups. Selectivity induced by plant volatiles plays a crucial role in determining feeding preference [
26,
27]. The observed feeding preference, as indicated by the preference index, also indicates
A. sinensis as the most vulnerable trees in high risk. Therefore, we infer that
A. sinensis is most likely to be victimized by
S. frugiperda among the six trees.
In contrast, H. brasiliensis (Euphorbiaceae) and C. nucifera (Arecaceae) presented varying degrees of susceptibility. Despite not reaching the performance level of Z. mays, S. frugiperda feeding on the leaves of these two plants demonstrated better development. The female ratios of adults in H. brasiliensis and C. nucifera groups were not significantly different from those of the control and A. sinensis. The parameters of daily survival rate, pupation rate (50.00%), eclosion rate (46.67%) for H. brasiliensis group were significantly lower than those of Z. mays and A. sinensis, and did not differ from C. nucifera, but were higher than those of the other three treatments. The parameter of leaf area consumption, larval development time (13.27 ± 0.57d), pupal development time (10.79 ± 0.21d) in H. brasiliensis group is significantly longer than Z. mays, not different from A. sinensis, but shorter than C. nucifera. In addition to these, the preference index (63.21 ± 4.796%) of H. brasiliensis is significantly largest among the six trees. The parameters of daily survival rate, pupation rate (76.67%), eclosion rate (46.67%) in C. nucifera group are similar to the H. brasiliensis group, inferior to Z. mays and A. sinensis but superior to the other groups, but do not perform as well as H. brasiliensis on larval development time (16.13 ± 0.55d), pupal development time (9.00 ± 0.15d), preference index (34.52 ± 4.464%). They do not perform as well as the control and A. sinensis groups, but S. frugiperda can equally survive by feeding on them, so they are potentially at risk of being victimized. Besides, the pronounced feeding preference of S. frugiperda for H. brasiliensis underscores its potential as a susceptible host. These results suggest C. nucifera and H. brasiliensis also pose risks, albeit to a lesser extent.
Larval mortality, as a crucial indicator of host suitability [
28], was notably higher in the
A. catechu,
C. oleifera, and
D. odorifera groups, which had zero survival rate (0%), so there's no data on pupal mean fresh weight, pupal development time, etc. indicating their unsuitability for
S. frugiperda survival. And their parameters of pupation rate (0% or 3.33%), eclosion rate (0%), and daily leaf area consumption also significantly lower, thus indicating that
A. catechu,
C. oleifera, and
D. odorifera are unsuitable for the survival of
S. frugiperda.
The activity of protective enzymes in insects is an important indicator for evaluating the physiological and biochemical responses of organisms to toxic substances [
29,
30,
31,
32]. Superoxide dismutase (SOD) and peroxidase (POD) play crucial roles as antioxidant enzymes, protecting the system from peroxidation and maintaining cellular redox balance [
33]. In our study, there were significant differences in SOD and POD activities in
S. frugiperda among different plant leaves. The SOD and POD enzyme activities of the
A. catechu treatment were significantly higher than those of the other treatments, and the SOD enzyme activities of the other leaf treatments were significantly higher than those of maize control treatment. However, except for the significantly lower POD enzyme activity of the
C. nucifera treatment group compared to the maize control treatment, there were no significant differences in POD enzyme activity among the other leaf treatments. This study further demonstrated the adaptability of
S. frugiperda to different tree species by detecting the activities of SOD and POD enzyme activities in the body that feed on different leaf treatments. The results of enzyme activity indicators show that, except for the strong toxicity of
A. catechu to
S. frugiperda, which is not suitable for the survival, other tree species may be eaten by
S. frugiperda, especially
C. nucifera.
Historically, omnivorous pests have exhibited a pattern of shifting to new host plants, eventually establishing themselves as dominant species. A case in point is the Colorado potato beetle, which originally infested wild lycophytes but swiftly transitioned to the potato as a primary host plant with the introduction of potato cultivation [
34,
35]. This phenomenon is not isolated, as other omnivorous pests like
Polyphagotarsonemus latus,
Caloptilia theory,
Lopholeucaspis japonica, and
Buzura suppressaria have been observed transitioning to tea trees after a period of acclimatization, becoming significant concerns for tea tree growers [
36]. Notably, the mirid bug outbreak correlated with the widespread adoption of Bt cotton in China serves as an illustrative example of the potential risks associated with large-scale planting of genetically modified (GM) crops [
37].
S. frugiperda, recognized as an omnivorous pest, is documented by the Center for Agriculture and Bioscience International (CABI) as a host for 353 species across 76 plant families [
38]. This extensive list, compiled by Montezano and others through a thorough literature review and a survey of the Brazilian ground [
12], reveals the broad range of plants susceptible to infestation by this pest. In previous results,
C. nucifera and
H. brasiliensis were identified as host plants in Brazil [
39,
40,
41], aligning with the findings of our study. Up to now, these plants were not reported as host plants of
S. frugiperda in China, suggesting that they may not have been scientifically investigated in the region. Notably, the specific adaptation of
S. frugiperda to
A. sinensis among those six trees examined in our experiment was not documented in previous surveys. The omission could be attributed to
A. sinensis being an economically significant evergreen tree species native to China [
42]. While there are no existing reports on whether
A. sinensis has been victimized by
S. frugiperda, the potential risk remains a matter of concern.
An intriguing discovery emerged during our investigation -
C. oleifera demonstrated inhibitory effects on the growth and development of
S. frugiperda, resulting in the mortality of all larvae within 10 days. This suggests that
C. oleifera may contain toxic substances with lethal effects on insects. Notably,
C. oleifera saponins are proposed as the potential agents responsible for this observed mortality, indicating their potential utility as natural plant-derived insecticides for controlling
S. frugiperda [
43]. The discovery of
C. oleifera's inhibitory effect on
S. frugiperda suggests a potential natural plant-derived insecticide. Further investigation into the toxic substances and mechanisms involved in this inhibition could contribute to the development of sustainable pest control strategies.