Jiayu Jia1†
Long Chen1†
Wenjing Yu1†Shouping Cai2Shunde Su2Xiangxi Xiao2Xinghao Tang2Xiangqing Jiang3Daoshun Chen3Yu Fang4Jinjin Wang1Xiaohua Luo5
Jian Li1Yunpeng Huang2*
Jun Su1*- 1Basic Forestry and Proteomics Research Center, College of Forestry, Fujian Provincial Key Laboratory of Haixia Applied Plant Systems Biology, Fujian Agriculture and Forestry University, Fuzhou, China
- 2Fujian Academy of Forestry, Key Laboratory of National Forestry and Grassland Administration on Timber Forest Breeding and Cultivation for Mountainous Areas in Southern China, Fuzhou, China
- 3Silviculture Department, Shaxian Guanzhuang State-Owned Forest Farm, Sanming, China
- 4Institute of Soil Fertilizer, Fujian Academy of Agricultural Sciences, Fuzhou, China
- 5Forest Fire Prevention Office, Forestry Bureau of Yuoxi County, Sanming, China
Introduction: Pine wilt disease (PWD) is responsible for extensive economic and ecological damage to Pinus spp. forests and plantations worldwide. PWD is caused by the pine wood nematode (PWN, Bursaphelenchus xylophilus) and transmitted into pine trees by a vector insect, the Japanese pine sawyer (JPS, Monochamus alternatus). Host infection by PWN will attract JPS to spawn, which leads to the co-existence of PWN and JPS within the host tree, an essential precondition for PWD outbreaks. Through the action of their metabolites, microbes can manipulate the co-existence of PWN and JPS, but our understanding on how key microorganisms engage in this process remains limited, which severely hinders the exploration and utilization of promising microbial resources in the prevention and control of PWD.
Methods: In this study we investigated how the PWN-associated fungus Aspergillus promotes the co-existence of PWN and JPS in the host trees (Pinus massoniana) via its secondary metabolite, sterigmatocystin (ST), by taking a multi-omics approach (phenomics, transcriptomics, microbiome, and metabolomics).
Results: We found that Aspergillus was able to promote PWN invasion and pathogenicity by increasing ST biosynthesis in the host plant, mainly by suppressing the accumulation of ROS (reactive oxygen species) in plant tissues that could counter PWN. Further, ST accumulation triggered the biosynthesis of VOC (volatile organic compounds) that attracts JPS and drives the coexistence of PWN and JPS in the host plant, thereby encouraging the local transmission of PWD. Meanwhile, we show that application of an Aspergillus inhibitor (chiricanine A treatment) results in the absence of Aspergillus and decreases the in vivo ST amount, thereby sharply restricting the PWN development in host. This further proved that Aspergillus is vital and sufficient for promoting PWD transmission.
Discussion: Altogether, these results document, for the first time, how the function of Aspergillus and its metabolite ST is involved in the entire PWD transmission chain, in addition to providing a novel and long-term effective nematicide for better PWD control in the field.
1 Introduction
Pine wilt disease (PWD) has brought great economic and ecological damage to Pinus spp. forests and plantations worldwide (Zhao et al., 2014). PWD is caused by the pine wood nematode (PWN) Bursaphelenchus xylophilus, which itself is transmitted by vector insects, namely the Japanese pine sawyer (JPS) Monochamus alternatus (Hu et al., 2013; Hirata et al., 2017; Carnegie et al., 2018; Wu et al., 2021). Infection with PWN will turn the host into a lure that attracts JPS to spawn, this leading to the PWN and JPS co-existing within the host pine tree, an essential precondition for PWD transmission (Li et al., 2022). In the last decade, tremendous effort has been expended towards developing effective strategies to impair the co-existence of PWN and JPS and thereby suppress the transmission PWD and potential outbreaks in stand. Microbes have proven substantial advantages for long-term pest control (Wang et al., 2017; Ponpandian et al., 2019; Cai et al., 2022; Pires et al., 2022; Tian et al., 2022); however, their efficacy is strongly affected by local environments and a highly structured microbial community, as well as microbe-specific biochemical metabolites. Accordingly, the high-efficiency use of microbes varies with different conditions, being context-dependent (Chaudhary et al., 2023; Poppeliers et al., 2023). Thus, exploring the biochemical basis enabling microbes to interfere with PWN and JPS co-existence is crucial for their use in effective long-term control of PWD.
Microbes are associated with PWN and play a crucial role in its invasion and pathogenicity (Zhao et al., 2014; Feng et al., 2022). The biological function of these PWN-associated microbes (PAMs) has been widely explored. Research has shown these PWN–PAM interactions can be beneficial (a mutualistic relationship), harmful (a parasitic/pathogenic relationship), or neutral (Zhao et al., 2014; Proenca et al., 2017a; Proenca et al., 2017b; Feng et al., 2022). These PAMs can also inactivate the PWN-induced resistance (mainly through the accumulation of reactive oxygen species [ROS]) in host pine trees, thus promoting the invasion and pathogenicity of PWN through adjustments to the microbial community or its members’ metabolites, including pathogenic factors, exoenzymes, and toxic secondary metabolites (Zhao et al., 2014; Li, 2018; Liu et al., 2019; Xue et al., 2019; Zhang, 2021; Feng et al., 2022; Li et al., 2022). Yet, because of the complex structure and function of microbial communities, our understanding of the key microorganisms and their functions that affect the invasion and pathogenicity of PWN is still limited. This greatly restricts the exploration and utilization of potent microbial resources in the prevention and control of PWD.
After infection by PWN, the biosynthesis of volatile organic compounds (VOCs) is strongly augmented in host pine trees, which lures JPS for feeding and spawning (Cheng et al., 2005). Several such VOC have been identified that are clearly capable of attracting JPS, including α-pinene, β-pinene, β-phellandrene, myrcene, and other terpene and sterols; some of them were successfully used to bait and trap JPS in the field (Teale et al., 2011). Previous studies have shown that PAM and host plant-associated microbes are directly or indirectly involved in the biosynthesis of the above VOCs via exoenzymes or metabolites (Alicandri et al., 2020). Hence, this hints that these PWN- and host-associated microbes might also affect the host preference of JPS, but this prospect warrants further exploration.
Based on above-mentioned lines of evidence, we hypothesized that a microbe can manipulate the co-existence of PWN and JPS through its metabolites, to influence PWD transmission. In our previous studies(Cai et al., 2022), by using metagenomic sequencing, we identified the key microorganism in host pine trees to be Aspergillus, whose abundance and activity are highly enriched during a PWN invasion and positively correlated with the amount and pathogenicity of PWN. Further, from correlations with metabolic data, it is evident that the pivotal metabolite of Aspergillus species, sterigmatocystin (ST), is highly induced by a PWN invasion, which might be the biochemical basis enabling Aspergillus to facilitate PWN invasion and pathogenicity. Given the above findings, the present study employed phenotypic, genetic, metabolic, and microbiological techniques to comprehensively clarify whether and how ST in the host plant Pinus massoniana enhances PWN invasion and pathogenicity; that is, by promoting host synthesis of VOC to attract JPS adults and ultimately sustaining the coexistence of PWN and JPS in their host, thus bolstering the transmission of PWD. Meanwhile, we speculated and tested whether the application of Aspergillus inhibitor (chiricanine A) could reduce the ST level in the host, to thus suppress PWN invasion and pathogenicity (Cai et al., 2022). The successful implementation of this project convincingly demonstrates the intrinsic biochemical mechanism of how key microorganisms, such as Aspergillus spp., are able to promote the transmission of PWD, which should encourage exploration of its application prospects in field settings.
2 Materials and methods
2.1 Plants and growth conditions
For the laboratory experiments, 2-year-old seedlings of P. massoniana were harvested from a nursery garden in a Shaxian Guanzhuang state-owned forest farm in Sanming, Fujian, China (26.5603°N, 117.7455°E). They were placed in growth chambers (light: dark = 16 h: 8 h, 70% humidity, 28°C in light and 24°C in dark) for 2 months before the experimental treatments began.
The field experiments were carried out in the same state-owned farm. This study area consisted of a 76-ha, 16-year-old pure P. massoniana plantation, where the annual average temperature and precipitation is 19.9°C and 1375.2 mm, respectively.
2.2 Inoculation of pine wood nematode
Adults of PWN were cultured as previously described (Cai et al., 2022). 1 mL of a PWN inoculation solution (5000 individuals/mL) was inoculated into P. massoniana seedlings as previously described, with 15 replicates (individual plants) used in each treatment. Double-distilled water served as the negative control.
2.3 Seedling injection with sterigmatocystin, A. arachidicola, A. sclerotioniger, and chiricanine A
Sterigmatocystin (cat no. 10048-13-2, Shanghai Yuanye Bio-Technology Co., Ltd, Shanghai, China) was first dissolved in methanol, to prepare a stock solution (1mg/mL), then diluted to 1/10, 1/100, and 1/1000 with methanol as the working solution. These working solutions were separately injected into P. massoniana seedlings (1 mL per individual), as previously described (Xiang et al., 2015). There was n = 15 per treatment, and a methanol solution served as the negative control.
Aspergillus arachidicola (CBS117610) and A. sclerotioniger (CBS115572) were ordered from the Westerdijk Fungal Biodiversity Institute (https://wi.knaw.nl/). Each was inoculated separately into P. massoniana seedlings (1 mL per individual), with n = 15 for each treatment and double-distilled water used as the negative control.
Under laboratory conditions, 2-year-old P. massoniana seedling were inoculated with PWN, then injected with a solution of 4 ppm chiricanine A (cat no. B35217-5mg, Shanghai Yuanye Bio-Technology Co., Ltd, Shanghai, China) and emamectin benzoate (cat no. 155569-91-8, Merck, Shanghai, China). These solutions were injected into P. massoniana seedlings (1 mL per individual) as previously described (Xiang et al., 2015); n = 10 for each treatment, for which a 4 ppm methanol solution served as the negative control. Plant samples were harvested at 14 dpi, then stored at –80°C for subsequent experiments. In the field testing chiricanine A and 2% emamectin benzoate (EB) solution (PD20110688, Syngenta, Shanghai, China) were used for the trunk injections. The injection dose was based on the DBH of each tree (1 mL/cm). High-pressure trunk drilling and injection equipment (cat no. ZYJ15B, Greenman, Beijing, China) was used to apply the injections, by following a standard protocol (dose injected into stem at 1 m above the ground at a 45° angle).
2.4 Quantification of ROS accumulation in the host plant P. massoniana
The ST-infected and negative control P. massoniana seedling samples in the laboratory experiments were harvested at 14 dpi. Their collected pine needles were immediately placed in liquid nitrogen and stored in a –80°C refrigerator. Then the amounts of ROS (cat no. ROS-1-Y, Comin Biology, Suzhou, China) and H2O2 (cat no. G0112W, Gris Biology, Suzhou, China) in these samples were measured by following the standard protocols of the above two kits. To ascertain differences among the means of the treatment groups, a one-way analysis of variance (ANOVA) along with Tukey’s test was employed.
2.5 Quantification of the relative PWN level
The amount of PWN in live plants was quantified by RT-qPCR (real-time quantitative polymerase chain reaction). Whole 2-year-old seedlings in the laboratory were used for the PWN quantification. The total genomic DNA of each plant sample was extracted using the MoBio PowerSoil DNA isolation kit (cat no.12855-50, MoBio, USA), according to the manufacturer’s protocol. The quantity and quality of DNA were measured on a NanoDrop 2000 photometer (Thermo Fisher Scientific, USA), with DNA integrity determined by 1% agarose gel electrophoresis. The extracted DNA was then stored at –80°C until further use. Quantitative PCR were conducted using PWN-specific primers and a host-specific primer (one transcript from P. massoniana as the internal control) (Table S32), by using the Hieff™ qPCR SYBR Green Master Mix (Low Rox Plus, cat no. 11202ES08, Yeasen, Shanghai, China) on a QuantStudio 6 Flex PCR (ABI). The qPCR signals were normalized to those of the reference gene PST in pine trees, by applying the 2-ΔΔCT method (Fang et al., 2023). Biological triplicates with technical triplicates were used. One-way analysis of variance (ANOVA; Tukey’s test) was performed to determine the differences among groups.
2.6 Quantification of plant defense genes and aflR of Aspergillus spp.
Total RNAs were isolated from P. massoniana seedlings at 14 dpi by using the Trizol reagent (cat no. 15596026, Invitrogen, CA, USA). Each sample of total RNA (1 mg) was reverse transcribed by the PrimeScript™ RT reagent Kit with gDNA Eraser (cat no. RR047A, Takara, Japan). The resistance genes examined were the same as those investigated in our previous study (Cai et al., 2022).
The aflR gene was extracted and searched by BLAST in the available genomes of the Aspergillus series at Genome/NCBI (https://www.ncbi.nlm.nih.gov/genome). The sequences extracted from these genomes were aligned and consensus sequence used to design the primers online in Primer3 Plus (https://www.primer3plus.com). All the gene-specific primers used in this assay are listed in Table S32. RT-qPCR was carried out to quantify the gene expression level (as described in section 2.5). One-way analysis of variance (ANOVA; Tukey’s test) was implemented to determine the differences among the means of treatment groups.
2.7 Metabolome sequencing and analysis in the host plant P. massoniana
Sample preparation went as described in section 2.3, with three technical replications used. The metabolites were then extracted from each sample by following a previously described protocol (De Vos et al., 2007). The Ultra High Performance Liquid Chromatography (UHPLC) separation was carried out using an A Dionex Ultimate 3000 RS UHPLC (Thermo Fisher Scientific, Waltham, MA, USA) equipped with an ACQUITY UPLC HSS T3 column (1.8 μm, 2.1×100 mm, 186009468, Waters, Milford, USA) by the Oebiotech Company (Shanghai, China). Set to a flow rate of 0.35 mL/min, the mobile phases were 0.1% formic acid in water (A) (A117-50, Thermo Fisher Scientific, Waltham, MA, USA) and 0.1% formic acid in acetonitrile (B) (A998-4, Thermo Fisher Scientific, Waltham, MA, USA). The column temperature was set to 45°C, while the auto-sampler temperature was set to 4°C, and the injection volume was 5 μL (Chen et al., 2007; Theodoridis et al., 2008). Ensuing data were trimmed from different samples to distinguish the insect-induced metabolites. Next, commercial databases, including the Kyoto Encyclopedia of Genes and Genomes (KEGG; http://www.kegg.jp) and MetaboAnalyst (https://www.kegg.jp/) were utilized to search for ‘metabolitepathways’ (https://www.genome.jp/kegg/pathway.html).
2.8 Metagenome sequencing and analysis
For the microbiota within host pine tree, whole seedlings of P. massoniana (n = 5, containing PWN) after 14 dpi under the ST treatments were crushed in liquid nitrogen for their respective total DNA extraction, followed by metagenomic sequencing and analysis, as previously described (Bolger et al., 2014; Cai et al., 2022). Total genomic DNA was extracted from each sample by using the MoBio PowerSoil DNA Isolation Kit (12855-50, MoBio, United States) as per the manufacturer’s protocol. The DNA quantity and quality were measured on a NanoDrop 2000 spectrophotometer (Thermo Fisher Scientific, United States). This DNA was then sheared to 300-bp fragments by a Covaris ultrasonic crusher. To prepare each sequencing library, those fragments were treated by end repair, A tailing, and ligation of Illumina compatible adapters. Next all DNA sequencing libraries were deep-sequenced on an Illumina HiSeq platform at the Allwegene Company (Beijing, China). After every run, the image analysis, base calling, and error estimation were carried out using Illumina Analysis Pipeline v2.6. Quality control of the raw data, including the removal of adapter sequence and low-quality reads, was performed using Trimmomatic. High-quality sequences were compared with NR database and classified into different taxonomic groups, using the DIAMOND tool (Buchfink et al., 2015). Then MEGAHIT (Li et al., 2015) was used to assemble the sequencing data, and the contigs were annotated with Prodigal software (Hyatt et al., 2012) to predict the open reading frames (ORFs). After that, CD-HIT software (Li et al., 2001) constructed the non-redundant gene set. To compare the sequencing data with the non-redundant gene set, Bowtie (Langmead et al., 2009) was used, after which the abundance information of genes in the different samples was counted.
2.9 Volatile organic compound sequencing and analysis
For the VOC within the host pine tree, whole seedlings of P. massoniana (n = 5, with PWN) at 14 dpi under the ST treatments were examined, as previously described (Fang et al., 2023). First, 500 mg (1 mL) of sample powder was transferred immediately into a 20-mL headspace vial (Agilent, Palo Alto, CA, USA) that contained an NaCl-saturated solution, to inhibit any enzyme reactions. These vials were sealed using crimp-top caps with TFE-silicone headspace septa (Agilent). During the Solid Phase Microextraction (SPME) analysis, each vial was placed accordingly at 60°C for 5 min, then a 120 µm DVB/CWR/PDMS fibre (Agilent) was exposed to the headspace of a given sample for 15 min (also at 60°C).
After completing that sampling procedure, desorption of VOCs from the fiber coating was performed in the injection port of the GC apparatus (Model 8890; Agilent), at 250°C for 5 min, in the splitless mode. The identification and quantification of VOCs was carried out using an Agilent Model 8890 GC and a 7000D mass spectrometer (Agilent). The selected ion monitoring (SIM) mode was used for the identification and quantification of analytes by MS. The ensuing identified metabolites were annotated using KEGG Compound database (http://www.kegg.jp/kegg/compound/); annotated metabolites were then mapped to the KEGG Pathway database (http://www.kegg.jp/kegg/pathway.html). Pathways with significantly regulated metabolites mapped to them were then fed into MSEA (metabolite sets enrichment analysis), whose significance was determined by hypergeometric test’s P-values.
2.10 Insect host preference and diet quantification assay
Adults of JPS were collected from an experimental population reared at the Fujian Agriculture and Forestry University, Fuzhou, China. All experiments using them, as described below, were conducted in a growth chamber (light: dark = 12 h: 12 h, 70% humidity, 25°C).
The host performance assay was done as described in a previous study(Geneau et al., 2013), albeit with some minor changes. Healthy and vigorous JPS were collected and starved for 24 h before starting the treatments, using a total 18 JPS adults per treatment (9 males, 9 females). Entire P. massoniana seedlings that had been inoculated with ST or 4 ppm methanol solution were the experimental odor source or negative control, respectively. Biological triplicates with technical triplicates were used. The performance of JPS on the host pine plants was expressed as an attraction ratio: [no. of choices by JPS/total no. Of JPS adults] * 100%. To determine statistical differences between treatment groups, first a Kruskal–Wallis test was applied, and then pairwise comparisons were made using multiple Mann-Whitney tests.
The diet of JPS adults was quantified as the consumed area of P. massoniana bark by these insects. Healthy and vigorous JPS individuals were collected and starved for 24 h before starting the treatments. A total of 12 JPS adults (6 males, 6 females) were used per treatment. Fresh 2-year-old P. massoniana seedlings from the various treatments were fed to the JPS for 3 days; then, the feeding area of the JPS was rubbed with transparent sulfuric acid paper, and this measured on grid coordinate paper. One-way analysis of variance (ANOVA; followed by Tukey’s test) was performed to determine the differences among the means of treatment groups.
All the JPS adults from the same treatment of each diet quantification assay were pooled into a single sample, crushed in liquid nitrogen, and divided into three equal aliquots for further analysis. The activities of exo-β-1,4-glucanase/cellobiose hydrolase (cat no. G0533W, Gris Biology, Suzhou, China), endo-β-1,4-glucanase (cat no. G0534W, Gris Biology, Suzhou, China), and β-glucosidase (cat no. G0535W, Gris Biology, Suzhou, China) in each sample were measured by following the standard protocols of corresponding kits. One-way analysis of variance (ANOVA; Tukey’s test) was implemented to determine the differences among the means of treatment groups.
3 Results
3.1 Sterigmatocystin increases PWN pathogenicity by suppressing ROS accumulation in P. massoniana
Previous results shown that sterigmatocystin (ST) is highly positively associated with the pathogenicity of PWN. Here, we speculated that ST functions during the PWN invasion and pathogenic process (Figure 1A). First, after PWN invasion, the ST level was highly induced (5.2 times, P < 0.01). Different concentrations (0.1 mg/mL, 0.01 mg/mL, 0.001 mg/mL) of the exogenous ST treatment applied to PWN-carrying P. massoniana (PCP) could significantly (P < 0.05) increase the PWN amount in the host, by 9.6, 6.6, and 4.6 times, respectively (Figure 1B). Further, the death rate of host plants was measured at 2 months post-treatment with respect to different concentrations of ST (Figure 1C). Evidently, the death ratio was positively correlated with the exogenous ST amounts; hence, ST could enhance the pathogenicity of PWN. We also measured the ROS level in PCP under the three ST treatments, finding that the rate of ROS (Figure 1D) as well as H2O2 (Figure 1E) production in PCP was significantly reduced by ST (P < 0.05) and negatively correlated (P < 0.01) with the exogenous ST concentration; this weakened resistance in PCP, thus benefiting the PWN invasion and pathogenic process. Further multi-omics (transcriptomics, microbiomes, and metabolic) data revealed that ST was capable of suppressing ROS accumulation through the regulation of a vast array of related genes (c60547.graph_c0, c82953.graph_c0, c64867.graph_c0, c68789.graph_c0, c81022.graph_c0), microbes (Cladophialophora, Penicillium, Trichoderma, Achromobacter, Chitinophaga, and Flavobacterium), and metabolites (maltotriose, 1-hexadecanoyl-2-(9Z-octadecenoyl)-sn-glycero-3-phosphoethanolamine and myo-inositol) (Figure 1F). We also explored the ST-regulated metabolites from metabolic data. They were mostly enriched in arachidonic acid metabolism, flavonoid biosynthesis, phenylpropanoid biosynthesis, nucleotide metabolism, and Cyprinus carpio (common carp) pathways; this suggested secondary metabolites, ST inhibitors (stilbenoid), and VOCs (phenylpropanoids) were highly negatively (P = 0.021, r = -0.979), positively (P = 0.006, r = 0.994), and positively (P = 0.012, r = 0.989) correlated with the ST concentration, respectively (Figure 1G). Also, the richness of several genera of microbes (Enterobacter, Klebsiella, Pelagivirga, Herbaspirilum, Staphylococcus, Pseudovibrio, Rhizophagus, Cronobacter, Acinetobacter, Achromobacter) was correlated with the ST concentration, and most of them were predicted to regulate the VOC and flavonoid biosynthesis (Supplementary Figure S1).
Figure 1 Sterigmatocystin (ST) increases Pinewood nematode (PWN) pathogenicity by suppressing ROS accumulation in Pinus massoniana. (A) Relative ST concentrations in the host plant P. massoniana quantified before (PWN(-)) and after (PWN(+)) invasion by PWN. The seedlings were inoculated with an equal amount of PWN (5000 individuals), followed by 0.1 mg/mL (ST_H), 0.01 mg/mL (ST_M), 0.001 mg/mL (ST_L) or a 0 mg/mL (ST(-)) of ST as the treatment, after which the (B) relative PWN amount, (C) death rate, (D) rate of ROS production, and (E) rate of H2O2 production were quantified at 14 days post-infection. Data shown is the mean ± standard deviation (SD). (F) Correlations between ST and their correlated ROS, transcripts, microbes, and metabolites. Metabolite pathways of P. massoniana as induced by ST with a highly correlated concentration. Different lowercase letters above bar columns show significant differences between treatments at P < 0.05, based on a one-way ANOVA, with multiple comparisons made using Tukey’s test. G1–G5 denote different transcripts (c60547.graph_c0, c82953.graph_c0, c64867.graph_c0, c68789.graph_c0, c81022.graph_c0); Mb1–Mb6 correspond to different microbial genera (Cladophialophora, Penicillium, Trichoderma, Achromobacter, Chitinophaga, and Flavobacterium); Mt1–Mt3 indicate different metabolites [maltotriose, 1-hexadecanoyl-2-(9Z-octadecenoyl)-sn-glycero-3-phosphoethanolamine, and myo-inositol]. (G) KEGG enrichment map of metabolic pathways of metabolites found significantly related to ST. The abscissa represents the impact of each pathway and the ordinate represents the pathways’ name. Impact is expressed as the ratio of the number of differential metabolites to the number of metabolites annotated in a given pathway. The circle represents ST_H vs. ST(-), the square represents ST_M vs. ST(-), and the triangle represents ST_L vs. ST(-), whose sizes indicate the number of differentially expressed metabolites contained in that metabolic pathway. Coloring represents the P-values for the enrichment analysis.
3.2 Sterigmatocystin increases VOC accumulation in P. massoniana to attract Monochamus alternatus
VOCs have been proven to determine the host preference of JPS(Yan et al., 2008; Wang et al., 2016). Accordingly, here we first quantified the VOC amount of P. massoniana under each exogenous ST treatment. The latter significantly increased the total VOC amount within P. massoniana by 212, 182, and 105 times when compared to the negative control, respectively (P < 0.001; Figure 2A). Also, for 10 VOCs (trans-anethole; acetophenone, 4’-hydroxy-; humulene; niacinamide; 4a(2H)-naphthalenol, octahydro-4,8a-dimethyl-,(4.alpha.,4a.alpha.,8a.beta.)-; 6-octen-1-ol,3,7-dimethyl-, (R)-; alpha-pinene; butanoic acid,3-hydroxy-3-methyl-; phenol; beta-myrcene), their amounts were positively correlated with the ST concentration, including three reported JPS-attracting VOCs (acetophenone, alpha-pinene, beta-myrcene) (Li et al., 2015; Zhang, 2016) (Figure 2B). These results led us to speculate whether the exogenous ST treatment can lure JPS adults. So we conducted an olfactory experiment, which showed that exogenous ST treatment can significantly (P < 0.05) promote the selective ratio of JPS adults to the host pine tree, and that ratio increased with a higher ST concentration (Figure 2C). Host performance of insects were based on that this behavior is benefit to themselves (Li et al., 2007; Zhu et al., 2019; Togashi et al., 2022). Furthermore, we also observed whether feeding on ST-treated P. massoniana could benefit the development of JPS The consumption area of JPS larvae feeding upon ST-treated P. massoniana increased significantly (P < 0.05) over time, and the body weight of the 3rd instar along with the spawning ratio of JPS eggs were both significantly increased by 1.67 and 4.7 times vis-à-vis the negative control, respectively (Figures 2D–F). The EG (endo-1,4-β-D-glucanase), CBH (exo-β-1,4-D-glucanase) and β-GC (β-glucosidase) activity in the gut of the JPS adults that fed upon P. massoniana treated with ST were quantified as well, these increasing by 1.24, 1.21, and 1.54 times relative to the negative control, respectively (Figures 2G–I). Altogether, these results suggested ST is able to increase the VOC accumulation in P. massoniana, thus attracting the JPS, whose feeding and development obviously improves when eating ST-treated P. massoniana, which can therefore manipulate the host preference of JPS.
Figure 2 Sterigmatocystin (ST) increases VOC accumulation in Pinus Massoniana to attract Monochamus alternatus (JPS). (A) VOC amounts in host plant P. massoniana quantified 14 days after treatment with 0.1 mg/mL (ST_H), 0.01 mg/ml (ST_M), 0.001 mg/mL (ST_L), or 0 mg/mL (ST(-)) of ST. (B) VOC compounds of P. massoniana induced by ST with a high concentration correlation. (C) Selective ratio of JPS to different plant samples were plotted, with the P-value for the t test between samples treated with (ST (+)) and without ST(ST(-)) presented in white. The (D) consumption area and (E) body weight of 3rd instar JPS larvae, and the (F) spawning rate, (G) EG (endo-1,4-β-D-glucanase) activity, (H) CBH (exo-β-1,4-D-glucanase) activity, and (I) β-GC (β-glucosidase) activity in the gut of the JPS adults that fed upon plant samples treated with (ST (+)) and without ST(ST(-)); data shown are the mean ± standard error (SE). The * and *** represents significant differences between treatments at P < 0.05 and P < 0.001, respectively, based on a one-way ANOVA, with multiple comparisons made using Tukey’s test. VOC1–VOC10 indicate different volatile organic compound (trans-anethole; acetophenone, 4’-hydroxy-; humulene; niacinamide; 4a(2H)-naphthalenol, octahydro-4,8a-dimethyl-,(4.alpha.,4a.alpha.,8a.beta.)-; 6-octen-1-ol,3,7-dimethyl-, (R)-; alpha-pinene; butanoic acid, 3-hydroxy-3-methyl-; phenol; beta-myrcene). The ** represents significant differences between treatments at P < 0.01.
3.3 An associated microbe A. arachidicola, promotes PWN pathogenicity by increasing the sterigmatocystin accumulation in P. massoniana
Identify the vital effective microbe is crucial to achieving PWD control in the field. As an important metabolite in Aspergillus, ST is positively regulated by alfR. Although total species richness of Aspergillus harbored by the host plant was negligible influenced by PWN invasion and perhaps even slightly reduced (Figure 3A), evidently the alfR expression level was significantly induced (14.06 times, P < 0.001) by PWN (Figure 3B). We also found that only a few Aspergillus species (A. arachidicola, A. fischeri, A. taichungensis) were strongly (P < 0.001) increased or decreased (A. sclerotioniger, A. awamori, A. aculeatus) by PWN (Supplementary Figure S2). This prompted us to compare the functional differences between PWN-increased (A. sarachidicola) and -decreased (A. sclerotioniger) species and their associated microbes (Figure 3C). After introducing it into P. massoniana via PWN, it was found that A. arachidicola significantly induced the accumulation of ST in the host (2.61 times, P < 0.001) whereas A. sclerotioniger did not (Figure 3D). Further, the amount of PWN was respectively quantified in A. arachidicola- and A. sclerotioniger-infected PCP, which demonstrated the former can increase the PWN population size, whereas the latter cannot (Figure 3E). Comparing the survival ratio of PCP infected by different microbes showed that it was sharply reduced after 2 weeks of infection by A. arachidicola but not A. sclerotioniger (Figure 3F). Collectively, these results suggested that PWN-induced Aspergillus are sufficient to trigger ST accumulation that assists PWN invasion and pathogenicity.
Figure 3 Associated microbe Aspergillus arachidicola promotes PWN pathogenicity by increasing the sterigmatocystin (ST) accumulation in Pinus massoniana. (A) Richness of microbes belonging to the Aspergillus genus, (B) expression level of ST synthesis promoting gene aflR, (C) richness of A arachidicola and A sclerotioniger in plant samples before (PWN(-)) and after (PWN(+)), invasion by PWN invasion are plotted. Aspergillus arachidicola, A sclerotioniger, and inactivated A arachidicola (-) were co-incubated with sterilized PWN, then inoculated into P. massoniana and the (D) ST amount, (E) relative PWN amount, and (F) survival ratio of different host plants were measured. Data shown are the mean ± standard deviation (SD). The *** represents significant differences between treatments at P < 0.001, based on a one-way ANOVA, with multiple comparisons made using Tukey’s test; ‘n.s.’ denotes no significant differences found.
3.4 The fungal inhibitor chiricanine A can suppress the species richness of Aspergillus fungi in P. massoniana host, thus curtailing in vivo PWN population size or pathogenicity in both laboratory and field tests
The Aspergillus-inhibitor chiricanine A has long been used to suppress ST accumulation in numerous crops(Arias et al., 2014). Accordingly, we wondered whether chiricanine A could decrease the accumulation of ST by reducing the richness of PWN-induced Aspergillu species. We found that the application of chiricanine A significantly decreased (P < 0.001) the richness of PWN-induced Aspergillu spp. as well as the aflR expression level by 4 times and 1.77 times, respectively (Figures 4A, B). When compared with emamectin benzoate, currently the most efficacious nematicide, chiricanine A was able to inhibit PWN for much longer (Figure 4C). But when the host is inoculated with A. arachidicola or ST, either was clearly able to suppress that long-term effect of chiricanine A (Figures 4D, E).
Figure 4 The fungal inhibitor chiricanine A can suppress the richness of Aspergillus fungi in Pinus massoniana to limit in vivo PWN population or pathogenicity, in both laboratory and field testing. Under laboratory conditions, 2-year-old P. massoniana seedlings were inoculated with PWN, and then inoculated with chiricanine A solution or methanol (control). For these samples, the (A) richness of Aspergillus fungi highly induced and (B) aflR expression level in response to PWN invasion were quantified. Relative PWN amount in PWN-carrying P. massoniana treated with (C) emamectin benzoate and chiricanine A, as well as those (D) injected with A arachidicola or (E) ST at 8 weeks post-inoculation. In the field trial, a solution of chiricanine A or methanol (control) was injected into PWN-carrying P. massoniana, and its (F) survival ratio, (G) relative PWN amount, and the (H) richness of Aspergillus fungi highly induced and (I) aflR expression level in response to PWN invasion were quantified after the 1st and 2nd year post-injection. Data shown are the mean ± standard deviation (SD). The *** represents significant differences between treatments at P < 0.001, based on a one-way ANOVA, with multiple comparisons made using Tukey’s test.
We also tested the PWN-control functioning of chiricanine A in a 2-year field trial. The application of chiricanine A significantly increased the survival rate of PCP in both years vis-à-vis the control (1.17 and 1.33 times, P < 0.001) (Figure 4F). Yet, significant reductions in the amount of PWN (2.36 and 22.05 times, P < 0.001), richness of PWN-induced Aspergillus spp. (4.44 and 18.07 times, P < 0.001), and the aflR expression level (2.15 and 18.07 times, P < 0.001) of PCP occurred in both years relative to the control (Figures 4G–I). These results indicated that chiricanine A could serve as more efficient nematicide in the field by suppressing ST accumulation thereby performed a long-term control of PWD.
4 Discussion
A paramount prerequisite to manipulating functional microorganisms is identifying those vital effective microbes that drive ecological phenomena, and elucidating their underlying biochemical mechanisms (Ayilara et al., 2023). Associated microbes enable linkages between PWN, host pine, and JPS (Feng et al., 2022); however, our understanding of how microbes directly affect the “PWN- host-JPS” complex through their produced metabolites are largely unknown (Zhao et al., 2014; Santini and Battisti, 2019; Feng et al., 2022). Here, we demonstrated that PWN-associated fungi, Aspergillus spp., are able to promote PWN invasion and pathogenicity by increasing biosynthesis of a secondary metabolite, sterigmatocystin (ST), in the host plant P. massoniana, mainly via suppressed ROS accumulation in hosts against PWN. Further, ST accumulation triggers VOC biosynthesis for attracting JPS to spawn and this drives the coexistence of PWN and JPS in host trees, thereby encouraging transmission of PWD (Figure 5). Meanwhile, through the application of an Aspergillus inhibitor (Chiricanine A), we also showed that the absence of Aspergillus sharply restricts the development of PWN in P. massoniana (Figure 4), further proving that Aspergillus is vital and sufficient to promote PWD transmission.
Figure 5 Schematic diagram of the pine wood nematode-Monochamus alternatus symbiosis promoted by Aspergillus fungi in Pinus massoniana host trees via sterigmatocystin (ST).
Ophiostomatoids and molds are two major fungal families well known for being highly correlated with the propagation and distribution of the PWN (Feng et al., 2022). Although molds do play crucial roles in multiple processes of PWD epidemics (Guo et al., 2020), in a way unlike the known contributions of ophiostomatoids to PWN (important food resources) (An et al., 2022; Cai et al., 2022; Li et al., 2022), how molds are involved in PWD epidemics remains unclear. The present work, for the first time, clarifies how an important genus of molds, Aspergillus, contributes to the PWD epidemic via its secondary metabolite. The ST biosynthesis is conserved in Aspergillus (Sobolev et al., 2018) and promoted by aflR, and a pronounced positive correlation between ST and aflR expression was indeed observed in this study, but no correlation of ST with richness of Aspergillus spp. Although the absence of Aspergillus substantially restricts the PWN’s development in its host, among these identified Aspergillus species in the PWN-carrying P. massoniana, only three of them—A. fischeri, A. arachidicola, A. taichungensis—increased markedly in response to PWN invasion and were very likely transferred by PWN into host plants, in contrast to most of them (like A. sclerotioniger) decreasing considerably. These lines of evidence suggest PWN-associated Aspergillus fungi are able to reconstruct the host plant-associated microbial community to promote PWN development. This point is also supported by the diversity of the host plant-associated microbial community being severely reduced by the application of a low ST concentration yet increasing with higher ST concentrations. The above point can also explained by the various functions of Aspergillus species; most of the plant-associated Aspergillus are mutualists (El-Desoky et al., 2021; Cheng et al., 2022; Toth et al., 2022), one of the PWN-associated Aspergillus fungi, A. arachidicola, has been reported as being harmful to plant and beneficial for insect feeding (El-Desoky et al., 2021; Cheng et al., 2022).
Despite ST being detectable in various of crops and foods (Versilovskis and De Saeger, 2010), its functioning in plants has yet to be resolved. In this work, we demonstrated that ST was able to suppress ROS accumulation in the host pine tree via genetic, metabolic, and microbial level regulation processes. The richness of several genera of microbes—Enterobacter, Klebsiella, Pelagivirga, Herbaspirilum, Staphylococcus, Pseudovibrio, Rhizophagus, Cronobacter, Acinetobacter, and Achromobacter—was correlated with the ST concentration, and most of them were predicted to regulate the biosynthesis of VOCs and flavonoids. Further, these functional predictions were supported by the metabolic data. By quantifying the VOC amounts in host pine trees, we find that the total VOC amount is highly induced by ST (more than 100 times), yet only a few of them (mostly terpenes) are induced in a ST-dependent manner; this finding hints that ST might be a potential signal acting to regulate the host performance of insects. Although, some reported JPS-attracting VOCs (acetophenone, pinene, and myrcene) were among the above ST-induced metabolites, it was not clear whether these are all JPS-specific VOC, an aspect worth exploring further. Meanwhile, the amount of flavonoids was significantly increased by ST treatment, indicating that ST may serve as a signal to initiate the later stages of plant defense (Hedrich et al., 2016). Plant flavonoids have been widely demonstrated to be toxic to pests, including the Pine Wood Nematode (PWN) (Shen et al., 2022; Xie et al., 2022). However, over a long period of co-evolution, pests have developed efficient detoxification systems to counteract the toxic effects of secondary metabolites, including flavonoids (Souto et al., 2021). This suggests that the PWN may possess a highly effective detoxification system to survive the presence of flavonoids in the host plant. Further investigation into the detoxification system of the PWN against plant secondary metabolites would provide a valuable opportunity to shed light on the outbreak of PWD. Interestingly, we also found that synthesis of an ST inhibitor, stilbenoid (Sobolev et al., 2018), was promoted by ST, suggesting that plants may have a conserved system to respond to ST as a signal. Together, we hypothesize that ST can suppress the early stage of PWN resistance and reconstructs the microbial community in the host plant; it may also strongly activate the later stage of pest resistance (flavonoid accumulation) to limits competitors in the same niche, thereby promoting outbreaks of PWD in pine stands.
Emamectin benzoate (EB) is widely regarded as the most useful nematicide against the PWN, largely because it is environmentally friendly and has longer field residence time (i.e., at least 3 years) (Takai et al., 2004; Lu et al., 2020). However, continuous injection is required to maintain an effective dose of EB in a pine tree or whole stand (Rajasekharan et al., 2017; Lu et al., 2020; Chen et al., 2021; Hao et al., 2021). Although neither EB nor chiricanine A can completely eradicate the PWN population in host pines, we propose that chiricanine A has a PWN control efficiency on par with EB, but is able to suppress the PWN population for a longer time. As a plant metabolite, chiricanine A can also be synthesized manually (Park et al., 2011), which greatly reduces the cost of its application. Chiricanine A is plant-originating metabolic that has multiple biological functions: it can be utilized and metabolized by the recipient plant itself (Wang et al., 2018), which may affect its residence time within the host, an aspect that requires future research attention. As an Aspergillus inhibitor, chiricanine A is already widely used for eliminating Aspergillus spp. in the crops (Sobolev, 2008; Sobolev et al., 2011; Sobolev et al., 2016; Sobolev et al., 2018; Souto et al., 2021), but whether Aspergillus spp are the unique target of chiricanine A remains unknown. We know that ST is produced by various species of Aspergillus (Versilovskis and De Saeger, 2010), but it can also be produced by other mold species, including some members of Penicillium, Emiricella, Chaetomium, and Bipolaris genera, and most of them are pertinent to plant growth (Barnes et al., 1994; Rank et al., 2011). Plenty of above ST-producing microbes could be induced by PWN invasion, though in this study only Aspergillus was investigated. Although we show that applying chiricanine A could drastcially reduce the Aspergillus and ST levels in host pine trees, it is uncertain whether such chiricanine A applications can limit or benefit other microbes of host plants. In conclusion, we found a new plant-originating nematicide, chiricanine A, that has obvious advantages in terms of residence time to aid in the long-term control of PWN in pine stands, but the side effects of its and underline mechanistic action both require further attention.
Data availability statement
The original contributions presented in the study are included in the article/Supplementary Files, further inquiries can be directed to the corresponding author/s.
Author contributions
JJ: Writing – original draft. LC: Writing – original draft. WY: Writing – original draft. SC: Conceptualization, Writing – original draft. SS: Investigation, Writing – original draft. XX: Software, Writing – original draft. XT: Data curation, Writing – original draft. XJ: Methodology, Writing – review & editing. DC: Supervision, Writing – review & editing. YF: Formal Analysis, Writing – review & editing. JW: Writing – review & editing. XL: Project administration, Writing – review & editing. JL: Funding acquisition, Validation, Writing – review & editing. YH: Resources, Visualization, Writing – original draft. JS: Writing – original draft, Writing – review & editing.
Funding
The author(s) declare financial support was received for the research, authorship, and/or publication of this article. This work was supported by the Fujian Forestry Science and Technology Project (2021FKJ01, LZKG-202205) and the Forestry Peak Discipline Construction Project of Fujian Agriculture and Forestry University (72202200205).
Acknowledgments
We are very grateful to the Fujian Key Laboratory of Forest Cultivation and Forest Products Processing and Utilization, Fujian Forestry Bureau, for help in providing detailed information of the sampling areas in this study, and to Syngenta (China) Investment Co. Ltd. for technical support.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
Supplementary material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fpls.2023.1257744/full#supplementary-material
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Keywords: aspergillus, host performance, Monochamus alternatus, nematicide, pine wilt disease, pinewood nematode (Bursaphelenchus xylophilus), sterigmatocystin
Citation: Jia J, Chen L, Yu W, Cai S, Su S, Xiao X, Tang X, Jiang X, Chen D, Fang Y, Wang J, Luo X, Li J, Huang Y and Su J (2023) The novel nematicide chiricanine A suppresses Bursaphelenchus xylophilus pathogenicity in Pinus massoniana by inhibiting Aspergillus and its secondary metabolite, sterigmatocystin. Front. Plant Sci. 14:1257744. doi: 10.3389/fpls.2023.1257744
Received: 12 July 2023; Accepted: 24 October 2023;
Published: 08 November 2023.
Edited by:
Mohamed Mannaa, Cairo University, EgyptReviewed by:
Sara Fareed Mohamed Wahdan, Suez Canal University, EgyptTuyong Yi, Hunan Agricultural University, China
Copyright © 2023 Jia, Chen, Yu, Cai, Su, Xiao, Tang, Jiang, Chen, Fang, Wang, Luo, Li, Huang and Su. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Yunpeng Huang, hyp1234888@126.com; Jun Su, junsu@fafu.edu.cn
†These authors have contributed equally to this work