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Review

Research Progress in Chemical Control of Pine Wilt Disease

1
Key Laboratory of Forest Protection of National Forestry and Grassland Administration, Ecology and Nature Conservation Institute, Chinese Academy of Forestry, Beijing 100091, China
2
Forestry Bureau of Yuanzhou District, Yichun 336000, China
3
College of Forestry, Sichuan Agricultural University, Chengdu 611130, China
4
Forestry Bureau of Huoshan County, Lu’an 237200, China
5
Center of Biological Disaster Prevention and Control, National Forestry and Grassland Administration, Shenyang 110034, China
6
CAS Key Laboratory of Forest Ecology and Silviculture, Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, China
*
Author to whom correspondence should be addressed.
Forests 2026, 17(1), 137; https://doi.org/10.3390/f17010137
Submission received: 15 December 2025 / Revised: 14 January 2026 / Accepted: 15 January 2026 / Published: 20 January 2026
(This article belongs to the Section Forest Health)

Abstract

Pine wilt disease (PWD), caused by Bursaphelenchus xylophilus, is driven by a tri-component system involving the pinewood nematode, Monochamus spp. beetle vectors, and susceptible pine hosts. Chemical control remains a scenario-dependent option for emergency suppression and high-value protection, but its deployment is constrained by strong regional regulatory and practical differences. In Europe (e.g., Portugal and Spain), field chemical control is generally not practiced; post-harvest phytosanitary treatments for wood and wood packaging rely mainly on heat treatment, and among ISPMs only sulfuryl fluoride is listed for wood treatment with limited use. This review focuses on recent progress in PWD chemical control, summarizing advances in nematicide discovery and modes of action, greener formulations and delivery technologies, and evidence-based, scenario-oriented applications (standing-tree protection, vector suppression, and infested-wood/inoculum management). Recent studies highlight accelerated development of target-oriented nematicides acting on key pathways such as neural transmission and mitochondrial energy metabolism, with structure–activity relationship (SAR) efforts enabling lead optimization. Formulation innovations (water-based and low-solvent products, microemulsions and suspensions) improve stability and operational safety, while controlled-release delivery systems (e.g., micro/nanocapsules) enhance penetration and persistence. Application technologies such as trunk injection, aerial/Unmanned aerial vehicle (UAV) operations, and fumigation/treatment approaches further strengthen scenario compatibility and operational efficiency. Future research should prioritize robust target–mechanism evidence, resistance risk management and rotation strategies, greener formulations with smart delivery, and scenario-based exposure and compliance evaluation to support precise, green, and sustainable integrated control together with biological and other sustainable approaches.

1. Introduction

Pine wilt disease (PWD), caused by the pine wood nematode Bursaphelenchus xylophilus (Nematoda, Aphelenchidae), is one of the most severe invasive threats to pine forest ecosystems worldwide [1]. Since the early twentieth century, when the B. xylophilus spread from North America to East Asia, the disease has continued to cause outbreaks in Japan, China, South Korea, and several European countries, leading to large-scale pine mortality [2].
Species of the genus Pinus are important timber resources and are widely used in construction, furniture manufacturing, papermaking, and woodworking industries [3]. They are also a crucial component of forest ecosystems. As a core pillar of carbon sinks in Northern Hemisphere forests, pine forests account for 17.7% of the total global forest carbon stock and play a key role in maintaining ecological balance and conserving soil and water resources [4]. Consequently, pine wilt disease poses a substantial threat to global forest ecosystems and the timber trade.
As a major forestry country in Europe, France first detected this disease in November 2025 in the Seignosse (Landes) in southwestern France. This event indicates that the emergence of pine wilt disease in new regions may impose increased pressure on monitoring and control efforts, requiring advance assessment and response in the allocation of resources for quarantine, surveillance, and management [5]. Taking China as an example, since the disease was recorded firstly in Nanjing in 1982, PWD has spread rapidly and persisted across multiple regions, resulting in large-scale pine mortality and significant ecological and economic losses [6]. Owing to its long transmission chain and high management costs, this disease has long been regarded as a major challenge in global forest health management [7].
To address the increasingly severe threat posed by pine wilt disease, a range of management strategies have been explored and implemented in different regions, including physical removal, ecological regulation, biological control, and quarantine measures. However, owing to the concealed colonization and reproduction of the pathogenic nematode within host trees, the complexity of forest environments, and the narrow window for effective intervention, the efficacy of single control measures is often limited. Consequently, disease management has gradually shifted toward integrated and regional governance approaches that combine multiple technologies. Notably, the role and acceptance of chemical control in pine wilt disease management vary markedly among regions, which is closely associated with differences in forest management systems, pesticide registration frameworks, ecological risk tolerance, and operational conditions. In East Asian countries, where pine forests are intensively managed, disease outbreaks occur frequently, and rapid suppression is required, chemical control has traditionally played an important role in emergency response and the protection of standing trees [8]. In contrast, forest management in Europe follows a precautionary regulatory principle, with strict pesticide approval procedures and a strong emphasis on biodiversity conservation; accordingly, the use of chemical interventions is more cautious and highly context dependent, and such measures are generally regarded as supplementary tools within integrated forest pest management rather than as primary or routine solutions [9].
For example, chemical control has not yet been implemented in forest stands in European outbreak regions such as Portugal and Spain. Under the current International Standards for Phytosanitary Measures (ISPMs), sulfuryl fluoride is permitted only for post-harvest wood treatment, with its application scope being strictly limited [10]. Following the gradual phase-out of methyl bromide, heat treatment has become the preferred option for wood packaging and quarantine facilities [11]. To date, routine in-forest chemical control has been mainly practiced in China, while limited applications have been reported in some regions of South Korea; however, the safety of chemical agents remains a major public concern [12]. This reality highlights the strong regional specificity of chemical control strategies and underscores the importance of evaluating chemical interventions within differentiated governance and management contexts.
Within the above integrated management framework, chemical control remains an important technical component, particularly in high-risk areas and during the early stages of disease outbreaks, where its rapid onset of action, operational feasibility, and ability to directly protect living trees confer significant practical value. Accordingly, chemical measures should be selected and applied in a scenario-specific manner as part of integrated control programs. From a developmental perspective, chemical control of pine wilt disease has undergone several stages: early reliance on organophosphates and fumigants [13,14,15], followed by the widespread use of macrocyclic lactones and neonicotinoid insecticides, and more recently the emergence of modern nematicides with well-defined molecular targets and improved environmental profiles [16,17,18]. Bibliometric analyses indicate that, since the early twenty-first century, research output related to the chemical control of pine wilt disease has increased steadily, with research directions shifting markedly from empirical applications toward mechanism-driven, targeted, and sustainability-oriented strategies [19,20].
It should be emphasized that the applicability of chemical measures is constrained by registration approvals, application scenarios, and ecological exposure risks, and such measures should therefore be employed as stage-specific or conditional tools under a framework of risk–benefit assessment and regulatory compliance. Accordingly, this review does not regard chemical control as the sole or long-term dominant solution for pine wilt disease management; rather, it evaluates chemical interventions as stage-specific and conditional tools within integrated management systems under defined ecological and regulatory contexts. Against this background, the present review systematically summarizes recent advances in the chemical control of pine wilt disease, with a particular focus on four interrelated core areas: mechanism-driven discovery of novel nematicides, structure–activity relationship-guided molecular optimization, formulation innovation and nanodelivery technologies, and the optimization of precision application methods such as trunk injection and unmanned aerial vehicle spraying. Compared with existing reviews that primarily emphasize empirical applications or single technological aspects, this review offers three key innovations: (1) integration of molecular target discovery based on omics and structural biology with practical application technologies, thereby constructing a systematic “target–compound–formulation–application” framework; (2) incorporation of regional differences in governance systems between East Asia and Europe into evaluations of the efficacy and safety of chemical control, providing scenario-adapted technical references; and (3) critical examination of the ecological risks and governance dependency associated with chemical control, rather than a sole focus on its advantages, thereby laying a foundation for the development of balanced and sustainable integrated management strategies. By integrating historical development with contemporary ecological and regulatory considerations, this review provides an in-depth analysis of the scientific bottlenecks and future directions of chemical control within integrated management frameworks, aiming to offer comprehensive guidance for the development of more precise, efficient, and environmentally friendly control strategies. Looking ahead, effective management of pine wilt disease will require strengthened integration of chemical control with biological control and green prevention technologies, promoting the establishment of a diversified integrated management system centered on ecological safety to achieve long-term disease control and the sustainable development of forest ecosystems.
This review is structured around the transmission chain of the pinewood nematode, the vector beetle, and the host pine trees, and, in combination with typical scenarios such as standing tree protection, vector interruption, and infection source management, systematically examines the targets and mechanisms of chemical control, pesticide agents and formulation delivery, application technologies, and region-specific evidence, thereby providing a reference for precision chemical use and risk assessment within integrated management programs.

2. Development History of Chemical Control of PWD

From a broader perspective of nematode management research, the application of nematicides and their chemical lineages has evolved from early reliance on fumigants and broad-spectrum compounds toward approaches that emphasize target selectivity, environmental safety, and adaptation to specific application scenarios [21,22]. With the increasing rigor of ecological risk assessments and regulatory requirements, many systems have reduced dependence on high-risk compounds and placed greater emphasis on integrated management with non-chemical measures.
Within this context, chemical control of pine wilt disease exhibits distinct characteristics associated with the “pathogen–vector–host” triad. The pathogenic B. xylophilus colonizes and reproduces within the host tree and is transmitted by the vector beetle, making chemical interventions applicable both to the nematode itself (e.g., systemic treatment of standing trees) and to the suppression of vector populations or the narrowing of transmission windows. Additionally, chemical measures can be applied to infected trees or wood during quarantine and post-harvest treatments to reduce sources of infection [23].
Regarding vector control, some regions conduct forest or canopy applications during adult beetle emergence and supplementary feeding periods; however, types of chemical agents, registration approvals, and application scales vary considerably. These interventions are typically coupled with trapping, monitoring, and removal of infected trees, and non-target exposure risks must be carefully evaluated. For high-value individual trees, trunk injection is sometimes used to enhance persistence of the treatment [24,25,26]. The differences in chemical classes, registration status, and application scales among regions, along with the need to coordinate with infected tree removal and monitoring measures, underscore the importance of reducing reliance on a single chemical strategy while controlling potential ecological risks.
Within the research framework for pine wilt disease management, both the volume of chemical control-related literature and the focus of research have evolved significantly over time. To ensure the scientific rigor and reproducibility of the literature survey in this study, a standardized literature search and screening procedure was employed. Specifically, the Web of Science (WOS) Core Collection and the China National Knowledge Infrastructure (CNKI) databases were used as data sources, with keywords including “Bursaphelenchus xylophilus” and “chemical control” applied in the topic fields. All searches were conducted on 4 January 2026.
The inclusion criteria were studies explicitly involving chemical control of PWD (e.g., pesticide screening, modes of action, formulations/delivery, application methods, and efficacy evaluation) in either Chinese or English-language publications. Excluded were conference abstracts, news reports, patents, and publications with insufficient topical relevance. The process and key data are shown in Table 1.
To provide a more intuitive presentation of the literature search and screening logic, the above procedure is summarized in a flowchart (Figure 1).
Following this process, a total of 390 relevant Chinese- and English-language publications published between 1988 and 2025 were obtained, spanning from the late 1980s to the present. Bibliometric analysis indicates that, although the number of publications fluctuated slightly in certain years, the overall trend has shown a continuous increase (Figure 2). This trend requires interpretation in conjunction with the evolution of research topics.
The period from 1988 to 2000 represents the early exploratory stage, characterized by a relatively low publication volume. Research topics were primarily focused on traditional nematicides (e.g., fumigants, organophosphates), including laboratory toxicity testing and preliminary field applications, with the core objective of emergency response during the initial outbreaks of pine wilt disease. From 2001 to 2015, the field entered a rapid development stage, with steadily increasing publication output. The research focus shifted toward optimization of application techniques (e.g., trunk injection, unmanned aerial vehicle spraying) and the development of pesticide combinations, while also beginning to consider impacts on non-target organisms. This shift was closely associated with the expansion of outbreak areas during this period, the rising demand for refined control strategies, and innovations in application equipment. The period from 2016 to 2025 is defined as the high-quality development stage, characterized by a significant increase in publication volume. Research topics during this stage have become more diversified and environmentally oriented, with particular emphasis on the development of eco-friendly nematicides (e.g., bio-based nematicides, nano-formulated delivery systems), integration of chemical and biological control technologies, and assessment of pesticide residue risks. This trend reflects a shift in disease management concepts from “rapid emergency control” toward “green and sustainable management” (Table 2). The stage divisions are based on comprehensive summarization of changes in publication volume and keyword co-occurrence characteristics, representing descriptive categorizations rather than formal policy-based periods.
In summary, the continuous increase in publication volume not only reflects the growing importance of chemical control in pine wilt disease management, but also reveals the evolution of research topics in response to changing control needs, technological innovations, and environmental protection concepts. This provides clear literature support and directional guidance for the precise development and efficient application of chemical control technologies. From a historical perspective on pine wilt disease management, the rise and development of chemical control have undergone distinct transitional stages, which closely correspond with the observed trends in the literature.
In the early to mid-20th century, when the outbreak and transmission mechanisms of pine wilt disease were not yet well understood, control relied primarily on physical and silvicultural measures, such as felling and burning infected trees, and removing bark and roots to interrupt pathogen transmission pathways [13,27]. Such measures could be effective on a small scale or in areas with low incidence, but they were highly labor- and resource-intensive and insufficient for sustained control across large pine forests. As outbreaks expanded over broader geographical areas, the limitations of purely physical and silvicultural measures became increasingly apparent—they lacked curative effects against the nematode, and biological or ecological control approaches could not respond rapidly in large-scale epidemics. During urgent outbreak stages, efficient intervention measures were urgently needed to contain disease spread. Under this context, chemical control was systematically introduced into the pine wilt disease management system and quickly became a key component, laying the practical foundation for the subsequent emergence of related publications after 1988.
In the late 20th century (corresponding to the early exploratory stage of the literature, 1988–2000), chemical control entered the stage of basic management system construction, with research gradually focusing on the control of the vector pine sawyer beetle (Coleoptera: Cerambycidae) and forming multi-step pesticide application strategies targeting the “beetle–infected wood–diseased tree” pathway. On one hand, in standing tree control, trunk injection of agents such as fenitrothion or fenthion was applied to enable translocation through the tree’s conductive tissues, simultaneously killing nematodes and beetle larvae inside the tree. On the other hand, foliar spraying with fenitrothion or carbaryl was used to suppress adult beetle feeding and oviposition. For infected or dead trees, fumigants such as methyl bromide and aluminum phosphide were applied to efficiently eliminate nematodes and larvae in the wood, thereby blocking secondary transmission [28,29,30]. During the same period, chemical treatments targeting the B. xylophilus itself included inorganic or conventional nematicides such as fenamiphos, aldicarb, levamisole hydrochloride, and some pyrethroid formulations, which achieved temporary mitigation of outbreaks under certain conditions [14,15,31]. These practices correspond to the literature characteristic of this stage, which concentrated on laboratory toxicity testing and preliminary field applications of traditional nematicides.
From the early 21st century to 2015 (corresponding to the rapid development stage of the literature), chemical control entered a period of rapid expansion, with a continuous diversification of chemical agents and a shift in control targets from primarily the vector insect toward both the pathogenic nematode and the vector. Agents including fensulfothion, avermectin, beta-cypermethrin, emamectin benzoate (EB), thiacloprid, and fluopyram, were successively introduced or evaluated, showing enhanced direct toxicity against B. xylophilus and related nematodes and demonstrating promising prospects for both laboratory and field applications [25,32,33]. At the same time, trunk injection techniques were increasingly refined, and aerial application began to be used for medium- to large-scale forest management. These developments align closely with the bibliometric finding that research focus shifted toward application technique optimization and pesticide combination development, reflecting both the expansion of outbreak areas and the increasing need for precise control measures during this period.
From 2016 to the present (corresponding to the high-quality development stage of the literature), research on chemical control of pine wilt disease has further advanced toward greener and more precise strategies. The development of nano-formulations and novel dosage forms has improved active ingredient stability and targeted delivery efficiency, significantly enhancing control precision and pesticide utilization [26,34,35]. Concurrently, research has focused on eco-friendly agents (e.g., bio-based nematicides), integration of chemical and biological control technologies, and pesticide residue risk assessment [36]. These trends confirm the diversification and greening of research topics and reflect a paradigm shift in disease management from “rapid emergency control” toward “green and sustainable management”.
In summary, since the late 1980s, chemical control of pine wilt disease has evolved from an exploratory phase dominated by physical and silvicultural measures with chemical interventions as a supplement, through the establishment of a basic system supported by organophosphate and inorganic nematicides, to a comprehensive chemical control stage centered on high-efficiency specialized agents, combination formulations, and refined application techniques. This historical trajectory is highly consistent with the thematic evolution revealed by bibliometric analysis, reflecting the long-term core role of chemical control in integrated management of pine wilt disease and providing an important foundation of technical knowledge and practical experience for subsequent innovations based on molecular targets and novel formulations.

3. Classification of Nematicide Action Mechanism and Registration Status of Nematicides for B. xylophilus Control

3.1. Classification of Modes of Action of Existing Nematicides

According to the classification of nematicide modes of action by the Insecticide Resistance Action Committee [37], chemical agents used for pine wilt disease control can be categorized into multiple functional groups with distinct molecular targets or modes of action. Existing research has mainly focused on acetylcholinesterase (AChE) inhibitors (N-1A; N-1B), glutamate-gated chloride channel (GluCl) modulators (N-2), succinate dehydrogenase inhibitors (SDHIs, N-3), acetyl-CoA carboxylase (ACC) inhibitors (N-4), as well as several candidate agents with mechanisms not yet clearly defined (N-UN, N-UNX, N-UNE, N-UNF). The toxicological performance of these different target types against B. xylophilus and other plant-parasitic nematodes (e.g., Meloidogyne incognita and Ditylenchus destructor) provides diverse technical pathways for chemical control of pine wilt disease (Table 3). Table 3 also includes some low-risk or naturally derived formulations (e.g., fungal- or plant-based agents) to illustrate the comparison across different risk spectra, although the application evidence for these should be discussed separately from that of synthetic chemical agents.

3.1.1. AChE Inhibitors (N-1A; N-1B)

AChE inhibitors act by competitively or non-competitively inhibiting acetylcholinesterase activity in nematodes, leading to the accumulation of acetylcholine at synaptic junctions, continuous neuronal excitation, and ultimately paralysis and death [38]. Representative compounds include fenamiphos, aldicarb, and ethoprophos, which were widely used in the early stages for trunk injection treatments against B. xylophilus. These compounds also exhibit pronounced nematicidal activity against M. incognita and D. destructor [39,40]. However, their use has been progressively restricted due to environmental risks, limited persistence, and adverse effects on non-target organisms. Nevertheless, the well-defined neurotoxic mode of action and rapid efficacy of AChE inhibitors continue to provide reliable tools for emergency control and trunk injection applications. Through formulation optimization or low-dose combination strategies, it may be possible to extend their application lifespan and provide valuable reference frameworks for the design of novel neuro-targeting compounds.

3.1.2. GluCl Modulators (N-2)

This class of compounds primarily targets γ-aminobutyric acid (GABA)- and glutamate-gated chloride ion channels, inducing neuronal membrane hyperpolarization and consequently reducing nematode motility. Representative agents include avermectin and EB, which exhibit high toxicity against both B. xylophilus and M. incognita [25,41,42]. These compounds constitute one of the most widely applied categories of neurotoxic nematicides. Owing to their high target selectivity and broad-spectrum activity, GluCl modulators may further enhance application efficiency and targeting precision through improved trunk-injection formulations or integration with controlled-release delivery systems, thereby providing a stable and reliable technical basis for pine wood nematode management.

3.1.3. SDHIs (N-3)

SDHI nematicides exert their effects by inhibiting mitochondrial complex II (succinate dehydrogenase, SDH) in nematodes, thereby disrupting the tricarboxylic acid cycle and electron transport chain, leading to impaired energy metabolism and rapid mortality. The representative compound fluopyram exhibits markedly higher nematicidal activity than traditional agents (e.g., avermectin and EB), and can induce high mortality of B. xylophilus within a short period [43,44,45]. A new-generation SDHI compound, cyclobutrifluram, significantly suppresses egg production and hatching in B. xylophilus; when applied via trunk injection, it shows stable and reliable control efficacy and has progressed from laboratory studies to pilot-scale validation [34,46]. Owing to their well-defined target site, high potency, and relatively favorable safety profile toward non-target organisms, SDHI nematicides represent a core direction in chemical control research and development. With the advancement and deployment of novel high-activity molecules, SDHIs have the potential to become an integral component of standardized control technologies, providing a foundation for multi-target, high-efficiency management strategies.

3.1.4. ACC Inhibitors (N-4)

ACC is a key rate-limiting enzyme in fatty acid biosynthesis, and its inhibition disrupts lipid metabolism of nematode cell membranes. Spirotetramat is metabolized in plants to spirotetramat-enol, which exhibits pronounced inhibitory activity against Caenorhabditis elegans and plant-parasitic nematodes [47]. Studies on its efficacy against B. xylophilus remain at an early stage. As a non-neurotoxic class of compounds targeting a novel biochemical pathway, ACC inhibitors expand the range of available chemical control options. With further investigation into their modes of action and environmental adaptability, these compounds have the potential to support the development of low-toxicity, high-efficacy nematicides with differentiated mechanisms of action.

3.1.5. Agents with Unknown or Multiple Potential Modes of Action (N-UN/N-UNX/N-UNE/N-UNF)

Some nematicides and candidate molecules cannot yet be clearly classified within existing mode-of-action categories. Their biological effects may involve interference with neural signaling, metabolic inhibition, or cellular structure disruption. For example, certain sulfone-containing nematicides and plant-derived compounds exhibit significant nematicidal activity, but their specific molecular targets have not been systematically elucidated [48,49,50].
The unclear characterization of these agents’ modes of action arises from three main factors: (1) formulation complexity, particularly for natural product-based agents containing multiple active constituents, making it difficult to distinguish the contribution of individual components; (2) the widespread presence of true multi-target effects, which single-target validation methods fail to fully capture; and (3) research emphasis historically biased toward activity screening rather than systematic mechanistic studies, resulting in insufficient molecular biological and biochemical evidence. Consequently, the modes of action of such nematicides often remain at a speculative or inferred level.
Although their modes of action remain unclear, these multi-target or mechanism-unknown compounds exhibit substantial potential activity and broad-spectrum effects. Through systematic investigations into their molecular mechanisms and subsequent structural optimization, novel targets may be identified, providing innovative avenues for PWD management while also expanding the application potential of natural products and multifunctional compounds.

3.2. Current Registration Systems and Formulation Status for PWD

Different countries and regions have established significantly distinct registration systems, formulation compositions, and application practices for chemical control of PWD. These differences are not solely determined by pesticide development capacity or market supply but are shaped by the interplay of regulatory frameworks, risk perception and management objectives, and practical forestry conditions. At the regulatory level, pesticide registration generally emphasizes human health and ecological risk assessments, imposing varying restrictions on application scenarios, methods, and sensitive areas. From a management perspective, regional priorities differ: some focus on rapid suppression during outbreak periods, while others emphasize preventive quarantine and long-term ecological risk management. At the operational level, forest structure, accessibility, labor and mechanization capacity, and the maturity of infected-wood handling systems directly influence the feasibility and cost-effectiveness of chemical control measures. The combined effect of these factors determines country-specific differences in the number of registered nematicides, selection of active ingredients, and formulation structures.
In Europe, the number of registered chemical agents for controlling Monochamus spp. is limited, with EB being among the few approved active ingredients. Where permitted, EB is applied only in highly restricted contexts, such as trunk injection of selected high-value individual trees or trees located within narrowly defined risk buffer zones, reflecting a precautionary regulatory approach rather than a reliance on stand-scale chemical intervention in forest ecosystems [51]. These interventions are not implemented as routine field-level control measures but are instead regarded as auxiliary, situational tools, used in combination with sanitation felling, removal of infected wood, and quarantine treatment of timber and packaging materials [52].
In North America, pine wilt disease management emphasizes quarantine and the individual protection of high-value or landscape trees. Accordingly, systemic nematicides or insecticides (e.g., avamectin and EB) are primarily applied via trunk injection to target trees, reducing the risk of B. xylophilus infection or infestation by Monochamus spp. vectors [53,54].
Japan, as one of the earliest countries affected by pine wilt disease, has developed a relatively systematic registration system for dedicated products, covering multiple application scenarios, including trunk injection, aqueous applications, and fumigation. Registered products are mainly formulated as emulsifiable concentrates (EC), microemulsions (ME), and emulsions in water (EW), emphasizing the synergistic control of both B. xylophilus and adult Monochamus spp. vectors, reflecting an integrated chemical management strategy shaped by long-term practice [55].
South Korea’s registration system is generally similar to that of Japan but places greater emphasis on graded measures corresponding to different outbreak stages. The registered products include relatively more trunk injection and forest spray agents, with commonly used formulations including EC, suspension concentrates (SC), and wettable powders (WP), supporting multi-dimensional control of both vector insects and B. xylophilus [56].
In China, with the continuous intensification of national-level efforts to control pine wilt disease, the registration system for chemical control products has been rapidly expanded and refined [57]. According to the registration information summarized in the original sources, a total of 73 formulations are currently registered for pine wood nematode control in China (Table 4), covering a range of active ingredients, including avermectin, EB, and imidacloprid.
The formulation spectrum is relatively diverse, encompassing EC, ME, EW, soluble concentrates (SL), capsule suspensions (CS), SC, and aqueous solutions (AS). This multi-formulation registration structure supports different application scenarios, including trunk injection, spraying, and mechanized pesticide application (Table 4) [58,59].
Differences in formulation types and active ingredient selection among countries reflect variations in technological adaptability and management objectives. In the future, further improvements in control efficiency while maintaining ecological safety may be achieved through formulation innovation, dose optimization, and combined application strategies.

4. Innovative Development of B. xylophilus Control Agents and Formulation Application Technologies

4.1. Development of Novel Control Agents

Since 2015, methyl bromide has been banned due to its ozone-depleting effects [60]. Although alternative fumigants such as sulfuryl fluoride have partially alleviated B. xylophilus damage, issues remain, including the rapid development of resistance as well as environmental and human health risks [61,62]. Currently, under specific application scenarios, non-fumigant nematicides such as avermectin and its derivative EB have become core components of integrated control strategies; however, challenges related to resistance management and ecological safety persist [63,64]. Accordingly, building on the application basis of SDHI compounds, macrocyclic lactones, and other well-defined agents discussed in Section 2, recent research has increasingly shifted toward novel molecule design, structural optimization, and innovation in formulations and application technologies. These efforts aim to enhance nematicidal activity, extend residual efficacy, reduce non-target risks, and improve overall ecological safety.
Against the backdrop of rising demands for high efficacy, safety, and resistance management, chemical control research has gradually converged on a systematic development pathway encompassing “novel target identification–structure optimization–new molecule design–application validation.” Current studies primarily focus on activity optimization within SDHI compounds, as well as the development of new small-molecule nematicides based on active scaffolds such as oxadiazoles, isoxazoles, amides, and quinazolines. Oxadiazole and isoxazole derivatives are widely explored as new nematicide scaffolds, designed based on structural hypotheses potentially interfering with metabolism or key enzymatic processes, although specific molecular targets remain unclear. Quinazoline compounds are also considered to possess nematicidal potential, possibly acting through signaling pathway regulation; the incorporation of amide moieties is commonly used to enhance selectivity, physicochemical properties, and overall activity.

4.1.1. Existing Molecule Optimization and New Molecule Design

Structural optimization of existing nematicides and design of novel small molecules represent a key research direction in B. xylophilus chemical control, featuring a clear progression from “structural modification” toward “innovative design”.
Structural Optimization
With respect to optimization of existing compounds, abamectin—derived from structural modification at the C22 position of avermectin—exhibits markedly enhanced nematicidal activity. Improvements in molecular polarity and membrane permeability are considered the primary factors underlying its increased toxicity. Although this compound remains at the laboratory evaluation stage, its structural optimization strategy provides a valuable reference for the further development of other macrocyclic lactone nematicides [65].
Exploration of Novel Scaffolds
Oxadiazole/Isoxazole Compounds: Oxadiazole and isoxazole compounds containing N–O five-membered heterocycles have attracted considerable attention due to their favorable biological activities. At a concentration of 200 mg/L, compounds 4i and 4p exhibited corrected mortalities of 57.1% and 60.1%, respectively, after a defined exposure period, substantially higher than that of the commercial nematicide tioxazafen (13.5%) [66], indicating strong development potential for this scaffold. In addition, among 34 chalcone derivatives containing a 1,2,4-oxadiazole moiety designed by Luo Ling et al. [67], compounds A13 and A14 showed LC50 values of 35.5 mg/L and 31.8 mg/L against B. xylophilus, respectively. These activities were markedly superior to those of fosthiazate, avermectin and tioxazafen (all reference LC50 values > 100 mg/L).
Novel Amide-Based Nematicides: New amide-based derivatives incorporating oxazole moieties as core structural elements have demonstrated pronounced inhibitory effects on B. xylophilus egg hatching and larval feeding. Compound B21 exhibited an LC50 value of 3.2 mg/L. Although this activity was slightly lower than that of fluopyram (0.4 mg/L), it was substantially superior to that of the commercial nematicide tioxazafen (102.2 mg/L), highlighting its promising development potential [68]. These findings suggest that the amide functional group is a key structural motif for enhancing nematicidal activity, and that further modification may improve selectivity, physicochemical properties, and overall efficacy.
Quinazoline Derivatives: The mode of action of quinazoline compounds has not yet been fully elucidated, but they are hypothesized to exert toxicity through modulation of signaling pathways. In novel nematicide development, the introduction of electron-withdrawing substituents—such as chlorine, fluorine, or trifluoromethyl groups—at strategic positions can enhance binding affinity to potential targets and thereby increase biological activity. Laboratory studies have demonstrated relatively high activity for these derivatives; however, they remain largely at the preliminary screening or pot experiment stages. Further advancement will require integrated evaluation of toxicity, environmental behavior, and chemical stability to facilitate their translation into practical control agents [69,70,71].
Overall, this research direction has yielded multiple high-activity candidate molecules, but most remain at the laboratory stage. Future development must consider toxicity, environmental fate, and stability to achieve translation into practical nematicides.

4.2. Formulation Innovation and Delivery Technologies

In Section 2, we systematically reviewed the current formulation profiles of pesticides registered for PWD control across different countries, including EC, ME, EW, SC, SL, and CS, and clarified the applicability of different application methods in forestry practice. Building on this foundation, the present section focuses on recent advances in formulation improvement and delivery technologies, with the aim of exploring their innovative roles in enhancing pesticide bioavailability, improving uptake and translocation within host trees, reducing non-target exposure, and optimizing ecological safety. A systematic analysis of these technologies not only provides theoretical support for the efficient application of pine wood nematode control agents but also lays a solid foundation for the development of greener and more intelligent disease management strategies in the future.

4.2.1. ME and Other Water-Based Green Formulations

With the increasing emphasis on environmental friendliness and ecological safety in chemical control practices in forestry, the limitations of traditional emulsifiable concentrate (EC) formulations have become increasingly apparent. The high content of organic solvents in ECs is associated with environmental pollution and safety risks, leading to growing restrictions on their use [72]. In contrast, water-based green formulations such as ME, EW, and SC offer advantages including good dispersibility, high permeability, and strong environmental compatibility [73].
Studies have shown that abamectin microemulsions outperform EC formulations in terms of surface tension reduction, permeability, and wettability, resulting in lower losses of the active ingredient during application [74]. Moreover, both LC50 and LC90 values of the microemulsion are significantly lower than those of the EC formulation, indicating stronger nematicidal activity and higher utilization efficiency [41]. Similarly, comparative studies of different formulations of EB demonstrated that microemulsions and suspension concentrates exhibit significantly lower toxicity to non-target organisms than ECs and water-dispersible granules, suggesting that formulation optimization can enhance efficacy while simultaneously improving ecological safety [75].
Due to their small particle size and strong dispersibility, microemulsions facilitate improved uptake and translocation within host trees, thereby reducing active ingredient loss and increasing application efficiency [76]. In addition, water-based green formulations are readily compatible with nanocarriers, controlled-release technologies, and intelligent delivery systems, providing a technological foundation for the precise application and long-term control of pine wood nematode agents.
Overall, microemulsions and related water-based green formulations enhance bioavailability while reducing environmental risks and non-target exposure, offering a sustainable formulation pathway for pine wood nematode management and supporting the future development of green and intelligent control strategies.

4.2.2. Nanocarriers and Smart Release Systems

Nanotechnology, owing to its submicron size effects, high specific surface area, and excellent drug-loading capacity, has gradually become an important direction in formulation innovation for pine wood nematode control agents [77]. Nanocarriers—including nanospheres, microcapsules, and mesoporous materials—can effectively protect active ingredients, improve aqueous dispersibility and stability, and enable controlled release and prolonged efficacy [78]. For example, mesoporous silica-loaded avermectin has been shown to extend cumulative release time to 12 days, effectively preventing photodegradation [34]. Avermectin encapsulated in bovine serum albumin nanocapsules significantly improved photostability and exhibited enhanced toxicity against B. xylophilus and M. alternatus [79]. Inorganic nanocarriers such as dendritic mesoporous silica improve absorption efficiency in pine trees and allow more uniform tissue distribution [80], while biobased nanomaterials such as castor oil–derived waterborne polyurethane nanoemulsions enhance rainfastness and retention of clothianidin and are renewable, aligning with green development goals [81].
However, the application of nanotechnology in forest ecosystems still faces challenges, as its potential long-term ecological impacts have not been fully evaluated. Studies indicate that once nanomaterials enter soil, they may affect microbial community structure and function through direct contact or ion release. For instance, copper oxide nanoparticles can reduce peroxidase and polyphenol oxidase activities and alter microbial community composition [82]. A global meta-analysis further revealed that nanomaterials generally exert negative effects on soil microbial diversity and biomass, with stronger inhibitory effects on fungi than on bacteria, and such impacts may persist for months to years [83]. Nano-TiO2 can influence aquatic ecosystems by altering energy transfer within planktonic food webs [84], while the neurotoxicity of silver nanoparticles depends on coating materials and may induce neurodegenerative effects [85]. In addition, the adhesion properties of nanomaterials, ion release, and environmental pH changes can affect their stability and release behavior [86].
To address these ecological risks, recent studies have explored mitigation strategies at three levels: material selection, structural design, and risk assessment. Biodegradable or biobased nanomaterials can reduce long-term accumulation risks in the environment [87]. Surface modification and coating strategies can regulate nanomaterial interactions with biological systems to reduce non-target exposure [88]. Multi-scale ecotoxicology-based risk assessment frameworks are gradually being established to systematically evaluate environmental fate and ecological impacts of nanomaterials in soil and water [89].
In summary, future research should pursue a balanced strategy integrating “efficacy enhancement and risk control.” This includes continued focus on the screening of green, low-toxicity nanomaterials and the development of intelligent, stimulus-responsive delivery systems [90,91], particularly enzyme-responsive nanopesticides capable of pathogen-specific recognition and precise release to further reduce non-target exposure [92,93]. At the same time, long-term monitoring of forest soil microbial community structure, enzyme activities, and carbon–nitrogen cycling should be strengthened to define safe application thresholds and environmental fate patterns, thereby providing a scientific basis for the sustainable application of nanoformulations in B. xylophilus management.

5. Application Technologies and Control Scenarios

Chemical control of PWD primarily involves trunk injection, ground and aerial spraying (including Unmanned aerial vehicle (UAV)-based applications), and fumigation of infected or cut timber. This section is organized around three application scenarios: standing tree protection, vector interruption, and infection source management, corresponding, respectively, to pathogen suppression, vector population reduction, and inoculum disposal. Each subsection summarizes the application background, key active ingredients and mechanisms, delivery methods and equipment, quantitative evidence, risk limitations, and technological innovations. Different application technologies differ significantly in delivery pathways, target specificity, operational conditions, and ecological risks. Their control efficacy depends not only on chemical properties but also on forest structure, topography, and vector activity rhythms. Therefore, comparing techniques in terms of efficacy duration, spatial coverage, and cost-effectiveness, and combining them appropriately according to control scenarios, is critical for constructing an integrated PWD management system.

5.1. Standing Tree Protection

Trunk injection is an important application scenario for in situ tree protection. It involves drilling near the cambium and delivering systemic pesticides into the xylem, where the active ingredients are translocated via transpiration, forming an internal distribution. The main advantage of this approach is the direct delivery of the pesticide to the pathogen’s niche within the host, providing a relatively long-lasting and stable protective effect [24,94].
Studies have shown that EB, avermectin, and similar systemic nematicides can maintain effective concentrations in the tree for approximately 6–12 months, continuously suppressing feeding, reproduction, and spread of B. xylophilus. At the same time, exposure of the tree’s internal tissues to insecticides may alter the habitat conditions for the vector, thereby indirectly affecting the survival of larvae of Monochamus spp. [95,96]. Compared with external applications such as spraying, trunk injection offers higher targeting, reducing drift and off-target losses, and thus lowering environmental exposure. However, reduced exposure does not equate to elimination of ecological risk; pesticide migration within and outside the tree can still impact non-target organisms. Combining formulation optimization, dose control, and leak management is necessary to reduce unintended exposure, along with scenario-specific risk assessment and monitoring. For example, field studies in Pinus massoniana forests evaluated the effect of EB trunk injection on soil arthropods and Hymenoptera communities. While overall community diversity remained stable, some functional groups, such as detritivores, showed detectable changes in diversity and composition, indicating that trunk injection requires component- and scenario-specific ecological monitoring and risk management [97].
Trunk injection is labor-intensive and low-throughput, making it unsuitable for rapid, large-scale control. Complex terrain and dense canopy cover can further limit its application. High or repeated doses may also induce phytotoxicity and cumulative mechanical damage, affecting long-term tree health [98,99]. Accumulated injection sites can have additional long-term effects on tree vitality.
Therefore, trunk injection is best applied as a scenario-dependent, targeted auxiliary measure, mainly for high-value individual trees, urban forests, and buffer zones in epidemic areas, rather than as a routine landscape-scale control method.

5.2. Vector Interruption

Ground and aerial applications mainly target adult and larval Monochamus spp. to indirectly suppress the spread of pine wood nematode. Because the insecticides cannot penetrate into the tree, their efficacy is mainly confined to the canopy and is affected by wind, canopy structure, and application parameters, resulting in uneven deposition and variable effectiveness.
UAV-based spraying has attracted attention in precision forestry due to its high maneuverability, low flight altitude, and adjustable spray swath and dosage, making it suitable for rapid operations in complex terrain. Studies show that UAV spraying during peak Monochamus spp. emergence significantly reduces adult density, thereby weakening nematode transmission chains [35].
However, UAV spraying provides only short-term protection, highly dependent on weather conditions, as rain and drift accelerate chemical loss. The effective duration of conventional aerial applications is typically 20–45 days, substantially shorter than that of trunk injection [100]. Additionally, UAV spraying covers large areas, posing environmental exposure and non-target risks, and cannot deliver chemicals into tree tissues to directly target B. xylophilus. Dense canopy cover may further limit deposition to lower layers, reducing efficacy in the understory [101,102].
Thus, UAV spraying is most suitable for rapid vector suppression during outbreak peaks and should be used in combination with other technologies rather than as a standalone long-term control strategy.

5.3. Infection Source Management

During epidemic outbreaks, dead, infected, and cut trees serve as major sources of B. xylophilus and Monochamus spp. vectors. Fumigation in closed environments with phosphine or sulfuryl fluoride effectively kills nematodes and insects inside timber, widely applied for centralized disposal of infected wood and quarantine purposes, making it a critical emergency control method [103].
Phosphine released from aluminum phosphide under warm and humid conditions penetrates wood efficiently; under 20 °C and 48 h in sealed containers, it achieves 99.99% mortality of B. xylophilus in shipping pine timber, with corrected mortality of Monochamus spp. larvae exceeding 98% [104]. However, phosphine is highly toxic by inhalation, and acute exposure can lead to respiratory irritation, pulmonary edema, cardiovascular dysfunction (e.g., hypotension, arrhythmias), neurological symptoms (e.g., headache, dizziness), gastrointestinal distress, and in severe cases collapse and death. These health effects have been documented in occupational and accidental exposure reports and toxicological assessments [105,106]. Fumigants can also disturb soil ecosystems, affecting non-target organisms and transiently altering soil biological community structure and function [107].
Sulfuryl fluoride, as a methyl bromide alternative, similarly demonstrates high nematicidal activity under ≥20 °C and CT ≥ 3000 g·h·m−3, achieving near-complete B. xylophilus mortality [10]. Yet, sulfuryl fluoride also poses health risks, with low occupational exposure limits (8 h TWA 5 ppm) and reported respiratory and neurological effects under inadequate ventilation or high-dose conditions [108,109].
Due to the dependence of fumigant efficacy on sealed conditions, its effective period is constrained by gas diffusion and safety requirements, making it unsuitable for open forest landscapes. High facility and safety management costs further limit large-scale deployment [110]. Overall, fumigation is most appropriate for sanitary disposal and quarantine of infected timber, not as a routine in-forest control measure.
In summary, trunk injection, UAV spraying, and fumigation each have distinct characteristics regarding efficacy duration, spatial coverage, and cost structure: trunk injection provides long-lasting protection but limited coverage; UAV spraying covers large areas but offers short-term efficacy; fumigation achieves high mortality in closed environments but has high costs and application constraints. To facilitate comparison, Table 5 provides a semi-quantitative assessment of these three techniques across efficacy duration, spatial coverage, and cost input.

5.4. Multi-Stage Differentiated Application Strategy

The occurrence and spread of PWD exhibit distinct stage-dependent dynamics, with varying control objectives and pesticide application requirements at different epidemic phases. Based on the goals of tree protection, vector suppression, inoculum removal, and ecological restoration, a full-cycle integrated application framework can be constructed [111].
Prevention Stage (Uninfected Areas): The primary goal is to reduce the risk of infection in susceptible stands. Trunk injection can establish a long-lasting internal chemical barrier within trees, enhancing host resistance to nematode invasion. Simultaneously, vector monitoring and trapping can provide early warning and risk mitigation, enabling proactive management of potential outbreaks [112].
Spread Stage: As Monochamus spp. activity intensifies, the focus shifts to interrupting the transmission chain. UAV applications during the peak emergence period of Monochamus spp. adults can effectively reduce adult densities, thereby weakening nematode dispersal pressure; however, their effect is mainly short-term and needs to be coordinated with trapping and other measures [101].
Outbreak Stage: When dead and infected trees accumulate rapidly, rapid removal of secondary inoculum sources becomes critical. At this stage, infected tree removal and fumigation are central. Using sulfuryl fluoride or aluminium phosphide under controlled conditions can efficiently eliminate both nematodes and vector insects within infected trees and stumps. When necessary, small-scale clear-cutting may be applied to quickly sever transmission pathways [28,61].
Recovery Stage: Following immediate control interventions, the focus shifts toward long-term forest stability and ecosystem recovery. Strategies include planting disease-resistant tree species, promoting mixed-species stands, and implementing silvicultural management practices to enhance structural stability and resilience, thereby providing a foundation for sustained control of PWD.
This multi-stage, differentiated application strategy integrates preventive, suppressive, and restorative measures to optimize chemical use, reduce environmental impact, and enhance the long-term effectiveness of pine wilt disease management.

6. Challenges and Scientific Bottlenecks

Although chemical control remains a core strategy for suppressing the spread of PWD due to its rapid action, controllable cost, and short-term irreplaceability by other approaches, long-term reliance on chemical agents has revealed structural bottlenecks across ecological, mechanistic, material, silvicultural, and system-level dimensions. Building on the framework outlined in previous sections, and integrating recent advances in new pesticide development, resistance evolution, green formulation design, and application technologies, this section systematically summarizes the key unresolved scientific challenges in chemical control of PWD.

6.1. RNAi-Based Strategies in Resistance Management and Integrated Chemical Control

The core mechanistic bottlenecks in chemical control of PWD include the potential accumulation of resistance and the slow pace of target innovation. The high virulence and rapid dispersal of B. xylophilus necessitate intensive chemical applications, which in turn exert continuous selection pressure on nematode populations, accelerating resistance evolution. Historically, the use of highly toxic pesticides not only caused ecological side effects but also amplified selective responses in both target and non-target organisms, exacerbating resistance issues. Resistance development is closely linked to target gene expression regulation, yet in B. xylophilus systems, cross-year and cross-region sensitivity monitoring frameworks are still lacking, and databases on target mutations, detoxification enzyme profiles, and resistance evolution dynamics remain incomplete.
Recent advances in computational chemistry, molecular docking, and virtual screening have facilitated the discovery of novel molecular scaffolds, such as SDHI lead compounds targeting succinate dehydrogenase [113,114] and novel natural product inhibitors targeting trehalose-phosphate synthase [115]. However, current targets remain concentrated on a limited set of key metabolic or neural proteins, resulting in concentrated resistance risk. Although structure–activity relationship (SAR) studies have revealed nematicidal mechanisms of coumarin-type natural products [116], a systematic strategy for target innovation has not yet been established.
Meanwhile, the development of RNA interference (RNAi) technology offers new avenues to enhance nematode sensitivity to chemical agents. Silencing neuroreceptor-related genes such as BxSnf7 or PxRdl2 can significantly increase the toxicity of corresponding pesticides against B. xylophilus [117,118]. Targeting key detoxification pathway genes—including UDP-glucosyltransferases (UGTs) [119,120], glutathione S-transferases (GSTs) [121], and aldehyde dehydrogenases (ALDHs) [122]—can effectively reduce the nematode’s detoxification capacity, thereby substantially enhancing pesticide lethality. In insect pest studies, upstream transcriptional regulators such as Nrf2 and AhR have been silenced to achieve coordinated downregulation of multiple detoxification genes, demonstrating potential for resistance reduction under experimental conditions [123,124].
However, in B. xylophilus the theoretical framework for integrating RNAi with chemical pesticides remains undeveloped, leaving resistance management strategies and pesticide optimization largely isolated and preventing the establishment of a synergistic control system.
Thus, a critical mechanistic bottleneck is how to integrate “target innovation—resistance evolution—RNAi-mediated gene regulation” into a unified conceptual framework (Figure 3). Within such a framework, target innovation provides novel sites of action, RNAi enhances nematode sensitivity via key gene regulation, and resistance monitoring and evolutionary dynamics analyses inform strategy optimization, collectively enabling a sustainable and precision-guided control system.
Future chemical control strategies for PWD should therefore rely on target innovation, computational chemistry-driven drug design, RNAi-enhanced sensitivity modulation, green and intelligent delivery systems, and multi-technology integrated management. Methods such as SAR analysis, molecular dynamics simulations, active pocket identification, and large-scale virtual screening can provide computable guidance for early-stage molecule optimization and selective modification. Concurrently, synergistic RNAi-chemical application models, intelligent delivery systems, and integrated governance measures can provide a comprehensive scientific foundation for precise, efficient, and eco-friendly B. xylophilus management.

6.2. Materials and Formulations

Although formulation innovation has advanced continuously, uncertainties remain regarding the ecological risks of materials and the real-world performance of formulations. Conventional EC face sustainability challenges due to solvent pollution, environmental residues, and toxicity, and are gradually being replaced by ME, SC, and other green formulations. However, whether these new formulations can maintain long-term stability, efficacy, and degradability within forest ecosystems remains poorly validated.
Nanocarriers, due to their high surface area, controlled release capacity, and enhanced bioavailability, are considered a key avenue for future nematicide delivery [125]. Nevertheless, the fate, accumulation, and transformation pathways of nanomaterials in forest ecosystems remain unclear, and a comprehensive ecological safety assessment framework addressing impacts on soil microbial communities, decomposer guilds, and root–soil interface processes is lacking. Key unknowns include whether nanomaterials may accumulate in soil, alter rhizosphere enzyme activity, or disrupt microbial networks.
Combined formulations, designed to enhance multi-target efficacy and cover multiple transmission nodes (e.g., nematodes and vector beetles), show potential [126]. However, quantitative data on synergistic interactions, efficacy strength, environmental residue behavior, and ecological risk are still limited. In other words, the pace of formulation innovation has outstripped ecological safety research, hindering the large-scale adoption of new formulations in forest management.

6.3. Persistence and Phytotoxicity

Forest environments are highly variable systems, leading to significant uncertainty in pesticide persistence, translocation, and mechanism of action. Although trunk injection can establish effective internal chemical barriers [33], long-term monitoring of persistence under different tree ages, site conditions, and seasonal variations is lacking. Current application cycles are often based on experience rather than predictive models, limiting precision application.
Pesticide translocation in trees is influenced by multiple factors—including transpiration rates, xylem structure, temperature, humidity, and tree health status—yet integrated models are lacking. This makes it difficult to determine the optimal application window, dosage thresholds, and injection frequency.
Phytotoxicity from trunk injection represents another critical bottleneck. Studies indicate that injection may cause cambial browning, vessel blockage, and tissue damage [98,99], but the underlying physiological mechanisms, dose–response relationships, pressure control principles, and species-specific sensitivities remain uncharacterized. The cumulative damage from repeated injections is particularly under-studied, hindering the standardization and refinement of trunk injection technology.
These uncertainties imply that current chemical control lacks predictable “in-forest behavior”, limiting the capacity for precision and efficient application.

6.4. System Integration and Synergy

The PWD transmission chain is complex, involving pinewood nematodes, vector beetles, weakened hosts, and deadwood. Current chemical control measures are unevenly effective across different nodes: trunk injection primarily targets the internal tree tissues; UAV spraying primarily targets adult beetles; fumigation targets infected logs and stumps. These techniques lack quantitative integration, preventing the establishment of a continuous, chain-wide defense.
Although combined formulations can partially cover multiple nodes, models to evaluate control strength at each node are missing, as is a theoretical framework to define minimum intervention thresholds for transmission chain disruption. Remote sensing, smart sensor networks, vector behavior regulation, and infected log management have been applied for PWD management, but deep integration with chemical control remains limited [112,127].
Essentially, current chemical control systems remain at a “multi-method parallel” stage rather than a truly cross-technology integrated stage. Lack of systematic linkage means chemical measures can only provide localized suppression rather than regional epidemic control.

7. Conclusions

Chemical control of PWD should be evaluated in the context of the “nematode–vector–host pine” transmission chain. Its use is most appropriate when linked to the three application scenarios—tree protection, vector suppression, and infection source management (Section 4), rather than as a standalone long-term dominant measure. Evidence also indicates that different techniques vary in delivery pathway, persistence, and non-target exposure risk, requiring synchronized trade-offs among efficacy, ecological and human health risk, operational feasibility, and regulatory compliance.
Importantly, chemical control in standing forests is generally not practiced in European PWD-affected countries such as Portugal and Spain, where management strategies primarily emphasize quarantine, sanitation felling, and vector regulation. In contrast, field-level chemical control is mainly applied in China, and to a lesser extent in the Republic of Korea, where large-scale forest stands, epidemic pressure, and regulatory frameworks have supported the development of scenario-specific chemical intervention strategies. Accordingly, chemical interventions should function as conditional, scenario-dependent tools integrated with quarantine, infected log management, and vector control to achieve stable suppression under controllable risk.

8. Future Outlook

Future chemical control strategies should be positioned as rapid suppression and targeted protection measures under specific scenarios, integrated with quarantine, infected log management, vector control, silvicultural practices, and biological control. Research should establish a verifiable evidence chain covering “targets–mechanisms–formulation/delivery–application scenario–ecological exposure and compliance evaluation”, supporting precise application and risk–benefit optimization.
Computational and target-oriented strategies have become central to the discovery and optimization of novel nematicides against B. xylophilus. By leveraging virtual screening, molecular docking, and homology modeling, researchers have identified promising lead compounds targeting critical enzymes such as AChE and cytochrome c oxidase subunit II (COX-2) [128]. Integrating comprehensive target databases with artificial intelligence–driven molecular design and structure optimization enables a closed-loop workflow—computational prediction, synthesis validation, and iterative refinement—that enhances screening efficiency and guides rational modification for improved potency and selectivity. Such approaches provide a systematic, mechanism-informed framework to accelerate early-stage nematicide development and support the transition from empirical screening to precision-guided chemical design.
Resistance management: RNAi and other molecular modulation strategies can complement chemical control to enhance efficacy and delay resistance, but target selection, delivery methods, field feasibility, and ecological safety require further evidence. A prudent approach is to evaluate synergistic boundaries with chemical agents across scenarios based on confirmed targets and resistance mechanisms.
Formulation and delivery: Water-based, low-solvent, and controlled-release formulations remain priorities. ME, SC, and biodegradable nanocarriers can improve stability and bioavailability [125], supporting reduced dosage and enhanced persistence. Simultaneously, studies on migration, accumulation, transformation, and degradation in forest ecosystems, as well as long-term impacts on soil microbial communities, enzyme activity, and rhizosphere processes, are necessary to establish scenario-specific ecological safety frameworks. For precision delivery, focus should include responsive release systems in specific phloem/xylem microenvironments, enhanced vascular bundle adhesion/penetration, and metabolically targeted release mechanisms.
Application and governance: Chemical measures should be deeply integrated with monitoring and multi-technology interventions. Remote sensing, UAV patrols, and intelligent sensor networks enable epidemic detection, transmission chain tracking, and risk zoning, supporting dynamic optimization of dosage, timing, and coverage [112,127]. Integrated interventions could combine tree protection via trunk injection, vector suppression during adult peaks, and infected log management, enhancing control stability and sustainability under regulatory and ecological constraints.
Long-term management: Chemical measures should complement biological control and other green technologies. Biological agents can act at both ends of the transmission chain: (i) directly suppressing nematodes via endoparasitic fungi [129,130] and (ii) suppressing vector beetle populations via parasitic wasps, parasitic beetles, or entomopathogenic fungi [131,132]. When combined with trapping, infected log management, and silvicultural adjustments, this can reduce chemical inputs while maintaining long-term stability [133].

Author Contributions

Conceptualization, D.G., T.L., Z.C. and Y.Y.; Validation, D.G., T.L., Z.C. and Y.Y.; Formal analysis, D.G., Y.L. (Yonghong Li) and S.H.; Data curation, D.G., T.L., X.C. and Y.L. (Yu Liang); Writing—original draft preparation, D.G.; Writing—review and editing, L.Y., L.W. and X.W.; Funding acquisition, L.Y. and X.W.; Supervision, X.W. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Central Public Interest Scientific Institution Basal Research Fund (CAFYBB2024QF033).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

No new data were created or analyzed in this study. Data sharing is not applicable to this article.

Conflicts of Interest

The authors declare no conflicts of interest.

Abbreviations

The following abbreviations are used in this manuscript:
PWDPine wilt disease
SARStructure–activity relationship
UAVUnmanned aerial vehicle
EBEmamectin benzoate
AChEAcetylcholinesterase
GluClGlutamate—Gated Chloride Channel
SDHISuccinate dehydrogenase inhibitor
ACCAcetyl-CoA carboxylase
SDHSuccinate dehydrogenase
ASAqueous solution
CSCapsule suspensions
ECEmulsifiable concentrate
EWEmulsion in water
MEMicroemulsion
SCSuspension concentrate
SLSoluble concentrates
WGWater-dispersible granules
RNAiRNA interference

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Figure 1. Flow diagram of the literature search and screening process.
Figure 1. Flow diagram of the literature search and screening process.
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Figure 2. Temporal distribution of published studies on chemical control of PWD (1988–2025).
Figure 2. Temporal distribution of published studies on chemical control of PWD (1988–2025).
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Figure 3. Conceptual framework for integrated resistance management and RNAi-chemical control in PWD.
Figure 3. Conceptual framework for integrated resistance management and RNAi-chemical control in PWD.
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Table 1. Summary of literature retrieval and screening strategy and key data for studies on chemical control of PWD.
Table 1. Summary of literature retrieval and screening strategy and key data for studies on chemical control of PWD.
Data SourceRetrieval StrategyInitial Retrieved Lit. (pcs)Screening BasisFinally Included Lit. (pcs)
WOSTS = “Bursaphelenchus xylophilus” OR “pine wood nematode” OR “pine wilt disease”
and
TS = “chemical control” OR “nematicide” OR “pesticide”
279Inclusion: Focus on chemical control technologies/pesticides/effects
Exclusion: Conference abstracts, duplicate publications, irrelevant themes
254
CNKI242Inclusion: Academic papers focusing on core content of chemical control
Exclusion: Patents, news, irrelevant chapters in reviews, duplicate publications
136
Total-521-390
Literature was retrieved from the Web of Science Core Collection and CNKI databases. The search and screening process was conducted up to 4 January 2026.
Table 2. Thematic evolution of chemical control research on PWD across different developmental stages.
Table 2. Thematic evolution of chemical control research on PWD across different developmental stages.
Research StageCore KeywordsPesticide Type KeywordsPrevention and Control Concept Keywords
1988–2000
Early Exploration
Traditional nematicides, Indoor toxicity determination, Preliminary field applicationFumigants, Organophosphates, Fenamiphos, AldicarbEmergency prevention and control
2001–2015
Rapid Development
Optimization of pesticide application technology, Research and development of pesticide mixtures, Impact on non-target organismsAvermectin, Beta-cypermethrin, Thiacloprid, FluopyramRefined prevention and control
2016–2025
High-quality Development
Greening, Synergistic technology, Residue risk assessment, New formulationsBio-based nematicides, Nano-drug delivery systemsGreen and sustainable management
Table 3. Classification of modes of action of nematicides published by the Nematode Working Group of the Action Committee on Pesticide Resistance (January 2026).
Table 3. Classification of modes of action of nematicides published by the Nematode Working Group of the Action Committee on Pesticide Resistance (January 2026).
Nematicide MOAMode of ActionChemical Structure GroupRepresentative Compounds
N-1A
N-1B
Nerve & Muscle. Acetylcholine (AChE) inhibitorsA. Carbamates
B. Organophosphate
Aldicarb
Fenamiphos
Ethoprophos
N-2Nerve & Muscle. Glutamate-gated chloride channel (GluCl) allosteric modulatorsAvermectinsAbamectin
Emamectin benzoate
N-3Respiration. Mitochondrial complex II electron transport inhibitors. Succinate-coenzyme Q reductase.Pyridinyl-ethyl-benzamides
Phenethyl pyridineamides
Fluopyram,
Cyclobutrifluram
N-4Growth & Development. Lipid synthesis, growth regulation. Inhibitors of acetyl CoA carboxylaseTetronic and Tetramicacid derivativesSpirotetramat
N-UNUnknown or Non-Specific. Compounds of unknown or uncertain MoAVarious chemistriesFluensulfone
Fluazaindolizine
N-UNXUnknown or Non-Specific. Compounds of unknown or uncertain MoA: Presumed multi-site inhibitor.Volatile sulphur generatorCarbon disulfide
Methyl bromide
N-UNBBacterial agents (non-Bt) of unknown or uncertain MoA.Bacterium or Bacterium-DerivedBacillus spp., e.g., firmus
Pseudomonas spp., e.g., chlororaphis
N-UNFUnknown or Non-Specific. Fungal agents of unknown or uncertain MoAFungus or Fungus-DerivedArthrobotrys spp., e.g., oligospora
Muscodor spp., e.g., albus
N-UNEUnknown or Non-Specific. Botanical or animal derived agents including synthetic, extracts and unrefined oils with unknown or uncertain MoA.Botanical or Animal-DerivedEssential oils
Pongamiaoil
Table 4. Summary of registered nematicides for B. xylophilus control in China (Data retrieved as of January 2026).
Table 4. Summary of registered nematicides for B. xylophilus control in China (Data retrieved as of January 2026).
NematicideNo. of NematicideNo. of Single
Nematicide
No. of Mixed
Nematicide
Formulation and Number a
Avermectin28280CS, 2; EC, 21; EW, 3; ME, 2
Emamectin benzoate42411SC, 1; EC, 7; EW, 3; ME, 25; SL, 5
Ivermectin110ME, 1
Imidacloprid101SL, 1
Matrine110AS, 1
Matrine extraction110SL, 1
a AS, aqueous solutions; CS, capsule suspensions; EC, emulsifiable concentrate; EW, emulsions in water; ME, microemulsion; SC, suspension concentrate; SL, soluble concentrate.
Table 5. Comparison of major chemical application technologies for pine wilt disease management.
Table 5. Comparison of major chemical application technologies for pine wilt disease management.
Application TechnologyEfficacy DurationSpatial CoverageCost ProfileTypical Application Scenario
Trunk injectionLong (months to >1 growing season)Tree-level (localized)High labor input; low retreatment frequencyHigh-value individual trees; urban forests; buffer zones
UAV sprayingShort (weeks, ~20–45 days)Stand- to landscape-levelLow per operation; high cumulative costRapid vector suppression during outbreak periods
FumigationVery short (no residual effect)Confined/enclosed spacesHigh infrastructure and safety costQuarantine treatment of infected wood and stumps
Note: The comparison is semi-quantitative and reflects typical operational conditions reported in the literature rather than site-specific performance.
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Gu, D.; Liu, T.; Chen, Z.; Yuan, Y.; Yu, L.; Han, S.; Li, Y.; Cheng, X.; Liang, Y.; Wang, L.; et al. Research Progress in Chemical Control of Pine Wilt Disease. Forests 2026, 17, 137. https://doi.org/10.3390/f17010137

AMA Style

Gu D, Liu T, Chen Z, Yuan Y, Yu L, Han S, Li Y, Cheng X, Liang Y, Wang L, et al. Research Progress in Chemical Control of Pine Wilt Disease. Forests. 2026; 17(1):137. https://doi.org/10.3390/f17010137

Chicago/Turabian Style

Gu, Die, Taosheng Liu, Zhenhong Chen, Yanzhi Yuan, Lu Yu, Shan Han, Yonghong Li, Xiangchen Cheng, Yu Liang, Laifa Wang, and et al. 2026. "Research Progress in Chemical Control of Pine Wilt Disease" Forests 17, no. 1: 137. https://doi.org/10.3390/f17010137

APA Style

Gu, D., Liu, T., Chen, Z., Yuan, Y., Yu, L., Han, S., Li, Y., Cheng, X., Liang, Y., Wang, L., & Wang, X. (2026). Research Progress in Chemical Control of Pine Wilt Disease. Forests, 17(1), 137. https://doi.org/10.3390/f17010137

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