Assessing the Role of Asymptomatic Infected Trees in Pine Wilt Disease Spread in Japan—Insights from Tree Health Monitoring

Abstract

To examine the role of asymptomatic infected trees in the spread of pine wilt disease (PWD), we established two study sites in a coastal black pine forest in 2020: one in a heavily damaged site and the other in a slightly damaged site. Half of the trees in each site were treated with a nematicide injection to suppress nematode activity. Tree health, assessed by resin exudation and external symptoms, was monitored for four years. In the slightly damaged site, asymptomatic infected trees emerged within 20 m of infected trees, and even with nematicide treatment, trees within 2 m of infected trees became asymptomatic infected. However, nematicide treatment allowed temporarily asymptomatic infected trees to survive or recover. These findings suggest that combining nematicide injection with the felling of neighboring infected trees can effectively suppress PWD.

1. Introduction

Pine wilt disease (PWD) is a severe epidemic that causes large-scale mortality in pine forests. First identified in Japan in the early 1900s, PWD has since spread to East Asian countries, Portugal, and Spain, causing severe economic and ecological damage [1,2,3,4,5,6]. The pathogen responsible for PWD is the pine wood nematode Bursaphelenchus xylophilus (Steiner and Buhrer), which is transmitted from wilted trees to healthy ones by pine sawyer beetles (Monochamus spp.) [7]. In East Asian countries such as Japan, South Korea, and the People’s Republic of China, Monochamus alternatus Hope is the primary vector of B. xylophilus [1,2]. The potential range of PWD is projected to expand further, raising concerns due to global warming and the increasing international movement of timber [8]. Rising temperatures may allow Monochamus beetles to expand their range to higher latitudes and elevations, thereby facilitating the spread of B. xylophilus. Additionally, warmer conditions may enhance the reproductive success of both the nematode and its insect vector, potentially accelerating disease transmission. In response, Nordic countries and the European Union have imposed strict bans on the import of pine wood, causing significant economic losses even in countries where the disease has not yet been reported [9]. In Japan, PWD was first detected in Kyushu in the early 1900s and has progressively expanded northward. As of 2024, PWD damage has been observed throughout Japan, except in Hokkaido [1,10].

The infection mechanism of PWD was elucidated in 1972 based on the life cycles of the pathogen nematode B. xylophilus and its vector, pine sawyer beetle (M. alternatus) [11,12]. After pupation, newly emerged M. alternatus adults feed on young twigs of healthy pines, creating feeding scars that serve as entry points for the nematode infection [13,14,15,16]. Once inside the tree, the nematodes spread through the parenchymal tissues, disrupting physiological functions and ultimately leading to tree death [17,18,19,20,21]. During the summer, M. alternatus uses recently wilted pine trees as oviposition hosts. The larvae develop inside the wood, and when the adults emerge in early summer the following year, they carry nematodes from dead wood to new host pines, initiating the next infection cycle [1,22,23,24].

Various control strategies have been developed and implemented to manage PWD, targeting both Monochamus beetles as nematode vectors and the nematode itself. Among these, the most common preventive measures are chemical spraying to prevent post-emergence feeding by M. alternatus adults [25,26,27] and preventive trunk injection of nematicides into pine trees to prevent nematode infection [28,29,30]. Eradication measures include felling and removing infected trees through mechanical shredding, fumigation with insecticides, or incineration [31]. Although the infection mechanism and control strategies have been well established, in practice, PWD remains difficult to control, resulting in the widespread distribution of infected trees [31,32,33]. In recent years, emerging technologies, including remote sensing and machine learning, have been developed to improve the accuracy of detecting infected trees and to monitor the expansion of PWD on a large scale [34,35,36].

Despite extensive efforts involving insecticide spraying and the felling of infected trees, PWD persists in pine forests, remaining a major obstacle to effective control. One of the primary factors responsible for this persistence is the presence of asymptomatic infected trees, also referred to as latent infected trees, which appear externally healthy despite harboring nematodes [37,38]. In susceptible pine species, nematode inoculation experiments have demonstrated that infected trees can survive for several years while harboring nematodes [39,40]. Notably, some trees have remained asymptomatic for up to 11 years [41]. Consequently, these asymptomatic infected trees are often overlooked and remain in the forest undetected because conventional control operations primarily target visibly wilted trees. Furthermore, as these trees develop symptoms, they release volatile terpenes and ethanol, attracting adult Monochamus beetles and facilitating nematode transmission to adjacent healthy trees [42,43]. This delayed disease onset, along with subsequent nematode transmission, poses a major problem for control and drives the continued spread of PWD.

Recent studies have provided further evidence that asymptomatic infected trees are critical factors in the spread of PWD. A trunk injection experiment conducted in Shizuoka Prefecture demonstrated that asymptomatic infected trees can act as new infection sources in the following year, highlighting the importance of their removal [44]. In Iwate Prefecture, a study on the distribution of asymptomatic infected trees and subsequent felling experiments suggested that their removal could contribute to suppressing the spread of PWD [45]. Similarly, field control efforts against PWD in South Korea underscored the problems posed by asymptomatic infected trees, emphasizing the difficulties in achieving effective disease management [46]. Furthermore, a recent study suggests that sexually mature M. alternatus beetles may feed on healthy trees near oviposition hosts during the egg-laying period, potentially transmitting nematodes and leading to the emergence of new asymptomatic infected trees [47].

This study aims to elucidate the role of asymptomatic infected trees in the progression and spatial distribution of PWD through a four-year tree vigor monitoring study initiated prior to infection onset. Special attention is given to identifying asymptomatic infected trees that become detectable following the oviposition period of M. alternatus beetles and examining their contribution to the spread of PWD. By elucidating their role in the infection cycle, we seek to develop more effective PWD management strategies.

2. Materials and Methods

2.1. Study Site

Two study sites were established in a coastal Pinus thunbergii Parl. forest in Kakegawa City, Shizuoka Prefecture, Japan (Figure 1). The study site consisted of a 46-year-old pure P. thunbergii stand in 2020, with broad-leaved shrubs such as Pittosporum tobira (Thunb.) W.T.Aiton present along the forest edges. A complete mapping of all healthy trees at the time of site establishment was conducted. One site, referred to as the “severely damaged site”, had already experienced extensive PWD-induced death, where previously infected trees had died and been removed, resulting in a more open canopy and reduced tree density. The second site, located approximately 500 m east of the severely damaged site, exhibited minimal PWD-induced damage at the time of study site establishment, with only four trees showing symptoms of PWD, such as dead or abnormal resin exudation. This site was, therefore, referred to as the “slightly damaged site.” Visual observations confirmed the progressive spread of PWD from the severely damaged site towards the slightly damaged site at the time of site establishment.

During the study period (2020–2023), the mean annual temperature at the site was 17.7 °C, with a recorded maximum of 34.6 °C and a minimum of −3.4 °C (“Omaezaki” AMeDAS weather station, Japan Meteorological Agency, Figure 1). In the severely damaged site, 102 trees (97 healthy and 5 abnormally resin exudation) that had survived the PWD outbreak were randomly selected for monitoring. Among them, 51 trees in the southern section were injected with a nematicide (morantel tartrate 20.0%, “Greenguard NEO”; Nisso Green Co., Ltd., Tokyo, Japan) on 26 March 2020, designated as the “nematicide treatment plot”. Trees with a DBH < 20 cm received 90 mL of nematicide per tree, while those with a DBH ≥ 20 cm received 180 mL. The remaining 51 trees in the northern section were left untreated, constituting the control plot. In the slightly damaged site, 100 trees were randomly selected, with 50 trees in the northern section designated as the “nematicide treatment plot”, where nematicide was applied under the same conditions as in the severely damaged site on the same date, while the remaining 50 trees constituted the control plot. This random selection ensured that the treatment and control plots were comparable in terms of initial tree health conditions and stand density. All trees in the two study sites were individually tagged with numbered tape for identification.

During the study period, felling operations to remove PWD-infected trees were conducted in May 2021 and May 2022. Additionally, to prevent feeding by M. alternatus adults, healthy pine stands were treated annually with aerial application of fenitrothion (MEP) microcapsule formulation (MEP 23.5%, “Sumipine MC”; Sumitomo Chemical Co., Ltd., Tokyo, Japan). The insecticide was applied once per year between mid- and late May at a rate of 60 L/ha using a five-fold dilution of the original MEP (23.5%) formulation. The application was adjusted based on PWD spread, with treatments continuing until 2021 in the severely damaged site and until 2023 in the slightly damaged site. Nematicide trunk injection was not conducted outside the designated experimental sites.

2.2. Tree Health Monitoring

The health status of all trees within the study sites was monitored monthly from March 2020 to November 2021 and subsequently three times per year from April 2022 to August 2023. Tree health monitoring was performed at least three times per year: once during the oviposition period of M. alternatus (July to August) [1,15,16], as well as once before and once after this period.

Tree health was evaluated using two criteria: external appearance and resin exudation. The external appearance was categorized into three classes through visual observation: healthy (green needles), discolored or partially wilted needles, and dead. Resin exudation was evaluated by drilling a hole into the cambium using either a 6 mm punch tool or a 3 mm electric drill. The amount of exuded resin was then assessed approximately 30 min after drilling. Resin exudation levels were categorized into five grades (+++, ++, +, −, and 0) following Oda’s method [48].

Some trees were accidentally felled during the study period. In such cases, the identification number of each felled tree was recorded, and resin exudation from the stump was assessed.

2.3. Statistical Analysis

In the slightly damaged site, the spatial relationship between oviposition target trees (i.e., trees targeted for oviposition by M. alternatus adults during the given year) and asymptomatic infected trees (i.e., trees that developed abnormal resin exudation after the oviposition period but remained asymptomatic before the following year’s oviposition period) was analyzed using the O-ring statistic [49]. The pair correlation function $O\left(r\right)=\lambda g\left(r\right)$ was calculated for both tree categories, and the degree of spatial clustering was evaluated by comparing the observed values to those of a null model. The null model was generated from 99 simulations of an inhomogeneous Poisson process with marks to produce the expected pair correlation function $O\left(r\right)$.

The null model encompassed all monitored trees. The area analyzed was 341 m² for the untreated (control) plot and 272 m² for the nematicide-treated plot. Deviations from random distribution were considered significant when the observed $O\left(r\right)$ exceeded the 95% confidence envelope of the null model. All spatial analyses were performed using the spatstat package in R (version 4.3.1) [50]. There is a possibility that asymptomatic infected trees emerging around oviposition target trees located outside the plot were inadvertently included in this analysis. Although this potential limitation was recognized, it is considered unlikely to have significantly affected the conclusions of this study.

Observation data were obtained from the slightly damaged site, where the initial occurrence of PWD-infected trees was monitored. Based on the oviposition period of M. alternatus (July to August) [1,15,16], trees were classified into four categories: healthy trees, oviposition target trees, current-year asymptomatic infected trees, and previous-year asymptomatic infected trees. Oviposition target trees were defined as those that died or weakened between July and August. Asymptomatic infected trees newly emerging in a given year were defined as trees that appeared healthy with normal resin exudation levels (plus or higher) until August but subsequently exhibited reduced resin exudation (minus or lower) while maintaining a healthy external appearance from September to the following June.

The bandwidth parameter $\sigma$ for the pair correlation function was optimized separately for each year and treatment plot based on the Berman–Diggle Cross-Validation Criterion [51]. The upper limit for the search range of $\sigma$ was set at 5 m, equivalent to half the length of the shorter side of the plot. The bandwidth that minimized the mean squared error was selected for the analysis.

3. Results

3.1. Relationship Between Initial PWD Damage, Nematicide Treatment, and Damage Progression

The annual progression of PWD damage in each study site differed depending on whether nematicide treatment was applied (Figure 2). In the severely damaged site, 60–80% of the trees died as a result of the 2020 PWD infection (observed from September 2020 to June 2021), followed by an additional 15–20% in 2021 (observed from September 2021 to April 2022). After the 2021 infection, almost all untreated (control) trees eventually died. In contrast, in the nematicide treatment plot, approximately 24% of the trees survived as of October 2021, although the proportion exhibiting abnormal resin exudation increased until the final monitoring date. Among these trees, approximately 16% remained alive until the end of the study period.

In the slightly damaged site, where PWD damage started to occur later, nematicide treatment not only prolonged the survival of asymptomatic infected trees but also restored their resin exudation to normal levels. PWD damage increased primarily in this site in 2022, with 24% of the trees in the untreated (control) plot and 16% in the nematicide treatment plot dying that year (Figure 2; July 2022). The proportion of asymptomatic infected trees in each plot peaked at 64% in October 2022.

By August 2023, all the trees in the untreated (control) plot had either died or developed resin exudation abnormalities, whereas 72% of the trees in the nematicide treatment plot remained healthy at the same time. Notably, in the nematicide treatment plot, although 64% of all monitored trees were classified as asymptomatic infected in October 2022, by May 2023, 82% of all monitored trees had recovered to a healthy state, exhibiting normal resin exudation and no external symptoms.

3.2. Spatial Overlap Between Oviposition Target Trees and Asymptomatic Infected Trees in the Slightly Damaged Site

Based on tree health monitoring, trees in the slightly damaged site were classified into four categories: oviposition target trees, newly emerged asymptomatic infected trees, previously emerged asymptomatic infected trees and healthy trees. Oviposition target trees were defined as those that were either dead or asymptomatic infected (i.e., those with a resin exudation value of minus or lower according to Oda’s method [48]) during the Monochamus beetle’s oviposition period (July to August) of the given year [1,15,16]. Newly emerged asymptomatic infected trees exhibited no resin exudation abnormalities until August of the given year but developed at least one instance of abnormal resin exudation between September and June of the following year. Previously emerged asymptomatic infected trees had become asymptomatic infected by June of the given year but later recovered and remained healthy. Healthy trees exhibited no external symptoms and maintained normal resin exudation levels (plus or higher) throughout the study period until June of the following year. Additionally, trees that felled during Monochamus beetle eradication efforts in May 2021 and May 2022, as well as those that accidentally felled, were excluded from subsequent plots. However, in the 2023 distribution map, tree classifications were based solely on assessments conducted in August 2023.

New asymptomatic infected trees emerged within a range of up to approximately 20 m from oviposition target trees, regardless of nematicide treatment (Figure 3). The spatial overlap between these two distributions—the locations of newly emerged asymptomatic infected trees and oviposition target trees—was analyzed using the pair correlation function $O\left(r\right)$ (Figure 4).

In the untreated (control) plot, no significant spatial association between the two tree categories was detected until 2021, as the observed $O\left(r\right)$ remained at 0 for all analyzable distances. However, as PWD damage intensified in 2022, newly emerged asymptomatic infected trees exhibited significant clustering around oviposition target trees.

In contrast, in the nematicide-treated plot, significant deviations from the null model were detected before 2021, preceding the severe outbreak of PWD. Clustering tendencies persisted throughout the study period. In 2020 and 2021, the observed $O\left(r\right)$ significantly exceeded the 95% confidence envelope of the null model, indicating a strong spatial association between newly emerged asymptomatic infected trees and oviposition target trees. In 2022, although a clustering tendency persisted, the observed $O\left(r\right)$ remained within the 95% confidence envelope.

4. Discussion

4.1. Suggestions for PWD Control

This study confirmed the presence of PWD-infected trees that develop symptoms after the oviposition period of M. alternatus adults, as suggested in previous research [37]. These trees play a critical role in the spread of PWD at the stand level. According to conventional theory [1,22], nematodes infect host pines via feeding scars created by immature M. alternatus adults shortly after emergence. The infected trees typically die in the summer of the same year and subsequently serve as oviposition hosts. However, trees exhibiting abnormal resin exudation (asymptomatic infected trees) and/or wilting symptoms from autumn to the following spring (trees that developed symptoms after an asymptomatic stage) (Figure 3) became new oviposition target trees in the following season, leading to the further progression of PWD. Nevertheless, they were omitted from control measures based on the conventional understanding of the infection cycle.

Felling-based control strategies, which involve removing dead trees by early summer of the following year, may overlook asymptomatic infected trees that develop symptoms after autumn. Failure to remove these trees can lead to the release of volatile terpenes and ethanol from weakened trees, attracting sexually mature M. alternatus adults and perpetuating PWD transmission [42,43]. This suggests that undetected asymptomatic infected trees are a key factor in the persistence of PWD outbreaks [38]. The observed expansion of PWD-induced death in 2023 in the untreated (control) plot of the slightly damaged site (Figure 3) further underscores the critical role of asymptomatic infected trees, as the number of PWD-affected trees increased rapidly within a short period.

Trunk injection of nematicides, such as morantel tartrate, which has been shown to suppress nematode multiplication for up to seven years, offers an additional benefit beyond its established preventive effect [28]. Even if nematode infection cannot be entirely prevented, nematicide treatment can extend the period from the onset of abnormal resin exudation to eventual tree death (Figure 2). When nematicide was applied across the stand before PWD invasion, some trees temporarily exhibited abnormal resin production but later recovered, with resin exudation returning to normal, and survived for up to three years (Figure 3).

In contrast, untreated asymptomatic infected trees did not recover normal resin exudation and died by the following summer (Figure 3). Despite two rounds of felling operations, PWD damage continued to spread. By 2023, all healthy trees in the untreated plot had disappeared, causing the complete collapse of the pine stand. These findings suggest that applying trunk injection prior to PWD onset in a stand can effectively reduce the occurrence of asymptomatic infected trees and mitigate the risk of severe outbreaks.

4.2. Suggestions for PWD Control Considering Asymptomatic Infected Trees

This study demonstrated that asymptomatic infected trees occur within a broader range—up to 20 m from oviposition target trees—than previously recognized [37,52]. The actual range, however, may extend further due to the influence of oviposition target trees in adjacent pine stands. Although few in number, several studies in which felling operations targeted asymptomatic infected trees have demonstrated their effectiveness in suppressing the spread of PWD. For example, at the front line of PWD spread in South Korea, all trees within a 20 m radius of an infected tree are felled to prevent the emergence of latent infections. This approach significantly mitigated PWD damage in several regions of South Korea [46]. In Japan, a similar strategy was applied in Iwate Prefecture, where all trees were subjected to resin exudation tests to identify asymptomatic infected trees. Felling both dead and asymptomatic infected trees led to a substantial reduction in PWD damage [45]. While the spatial distribution analysis in this study was constrained by the size of the experimental plots, our present results support the effectiveness of the felling radius (20 m) adopted in these control strategies. Additionally, because our study could not distinguish infections originating from oviposition target trees outside the experimental plots, the actual range of newly emerging asymptomatic infected trees may have been even broader. Future advancements in early infection detection technologies, such as UAV-based remote sensing [34,35,36], along with the potential use of pH indicators based on the observed decrease in plant pH in PWD-infected trees [53], could enhance the accuracy of asymptomatic infected tree identification over larger areas.

Even in plots where nematicide trunk injection was performed to maintain low levels of damage, asymptomatic infected trees tended to cluster at around 1.9 m from oviposition target trees. This proximity likely results in frequent feeding by M. alternatus adults [14,54], increasing the risk of multiple feeding scars and a higher frequency of nematode infections. However, none of the asymptomatic infected trees that emerged near oviposition target trees in nematicide-treated plots died the following year (Figure 3). This result suggests that nematicide treatment suppressed nematode multiplication, preventing asymptomatic infected trees from progressing symptoms to mortality.

Our findings suggest that preventive trunk injection of nematicide for all trees in areas not yet affected by PWD is a highly effective strategy. Even if trees become temporarily asymptomatic infected, the nematicide can promote recovery or prolong survival for several years. However, trees within a 2 m radius of initial infection sites—corresponding to neighboring trees in mature pine stands—are likely to remain at a high risk of nematode infection due to concentrated feeding by Monochamus beetles. Although trunk injection may help restore vigor and prevent mortality in asymptomatic infected trees, temporary declines in tree health (i.e., reduced resin exudation) may still attract Monochamus adults, increasing the risk of further spread of PWD.

For effective area-wide prevention of PWD, combining nematicide treatment with targeted felling of infected trees and their neighboring pines within a 2 m radius is likely to be a more effective strategy. This integrated approach could enhance PWD management and help maintain long-term forest health.