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Management of Forest Pests and Diseases—2nd Edition

A special issue of Forests (ISSN 1999-4907). This special issue belongs to the section "Forest Health".

Deadline for manuscript submissions: 30 November 2024 | Viewed by 17124

Special Issue Editors


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Guest Editor
National Institute of Forest Science, Seoul, Republic of Korea
Interests: climate change; entomology; ecological modeling; forest pests; population dynamics
Special Issues, Collections and Topics in MDPI journals

E-Mail Website
Guest Editor
Department of Forest Environment Protection, Kangwon National University, Chuncheon 24341, Republic of Korea
Interests: forest entomology; forest pests; urban tree; community ecology; insect diversity; environmental monitoring; forest disturbance

Special Issue Information

Dear Colleagues,

Forest insects as well as microorganisms are important parts of the forest ecosystem, acting as regulating factors in the nutrient cycle and energy flow. However, many pests and diseases severely impact these ecosystems, negatively impacting forestry economy, ecosystem services, biodiversity, etc. Recently, forest pests and diseases have mainly emerged as a result of habitat changes or climate change. International trade and travel increase the movement of organisms from their original habitat to new areas, inducing the dispersal of organisms as invasive species. Meanwhile, climate change, including temperature increase, changes the potential distribution area of species by changing their habitat condition. Therefore, surveillance and monitoring of their occurrences and assessment of their impacts on the forest ecosystem would be the first step towards sustainable forest ecosystem management. Surveillance and monitoring play a fundamental role in effective control and management strategies for pests and diseases. In addition, accumulated monitoring data are used for the development of new methods for monitoring, assessing impacts and developing management techniques.

To minimize the impacts of pests and diseases and provide a better understanding of the structure and processes of the management of forest ecosystems, this Special Issue is seeking studies from a broad range of research topics related to forest pests and diseases, including:

  • Report on new forest pests;
  • Monitoring;
  • Assessment;
  • Impacts;
  • Management;
  • Sustainable ecosystem management;
  • Invasive species;
  • Dispersal of invasive species;
  • Dispersal modeling;
  • Effects of climate change;
  • Habitat change;
  • Risk assessment

Prof. Dr. Young-Seuk Park
Dr. Won Il Choi
Dr. Jong-Kook Jung
Guest Editors

Manuscript Submission Information

Manuscripts should be submitted online at www.mdpi.com by registering and logging in to this website. Once you are registered, click here to go to the submission form. Manuscripts can be submitted until the deadline. All submissions that pass pre-check are peer-reviewed. Accepted papers will be published continuously in the journal (as soon as accepted) and will be listed together on the special issue website. Research articles, review articles as well as short communications are invited. For planned papers, a title and short abstract (about 100 words) can be sent to the Editorial Office for announcement on this website.

Submitted manuscripts should not have been published previously, nor be under consideration for publication elsewhere (except conference proceedings papers). All manuscripts are thoroughly refereed through a single-blind peer-review process. A guide for authors and other relevant information for submission of manuscripts is available on the Instructions for Authors page. Forests is an international peer-reviewed open access monthly journal published by MDPI.

Please visit the Instructions for Authors page before submitting a manuscript. The Article Processing Charge (APC) for publication in this open access journal is 2600 CHF (Swiss Francs). Submitted papers should be well formatted and use good English. Authors may use MDPI's English editing service prior to publication or during author revisions.

Keywords

  • forest management
  • invasive species
  • alien species
  • risk assessment
  • pests
  • insects
  • diseases
  • monitoring
  • assessment
  • ecology
  • effects of climate change
  • effects of environment change, outbreak, modelling

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Related Special Issue

Published Papers (8 papers)

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Editorial

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4 pages, 672 KiB  
Editorial
Management of Forest Pests and Diseases
by Won Il Choi and Young-Seuk Park
Forests 2022, 13(11), 1765; https://doi.org/10.3390/f13111765 - 27 Oct 2022
Cited by 5 | Viewed by 2452
Abstract
The occurrence patterns of forest insect pests and diseases have been altered by global events such as climate change. Recent developments in improved monitoring methods and tools for data analyses provide new opportunities to understand the causes and consequences of such changes. Using [...] Read more.
The occurrence patterns of forest insect pests and diseases have been altered by global events such as climate change. Recent developments in improved monitoring methods and tools for data analyses provide new opportunities to understand the causes and consequences of such changes. Using a variety of management tools, forest pest management programs can mitigate the influence of global changes on forest health. The goal of this Special Issue is to improve our understanding of the root causes of changes that have induced global changes. Fifteen papers are included in this Special Issue, covering several issues in forest pest management. One paper reviews the causes of Korean oak wilt, and another paper discusses fourteen invasive tree pests in Russia. The remaining thirteen papers cover issues related to the monitoring and management of forest pests. These studies provide a better understanding of the causes of change in the patterns of forest pests under the influence of global changes. These reviews also contribute to the development of forest-pest-management strategies to mitigate such impacts on forests due to global changes. Full article
(This article belongs to the Special Issue Management of Forest Pests and Diseases—2nd Edition)

Research

Jump to: Editorial

16 pages, 5395 KiB  
Article
Development of Integrated Control for Verticillium Wilt of Smoke Trees in Beijing
by Bimeng Li, Ruifeng Guo, Yize Zhao, Qiyan Li, Lizhou Song, Chong Shen, Chenming Du, Yuntao Gu, Guanghang Qiao, Liping Wang, Fei Yuan, Sanxiang Huang and Yonglin Wang
Forests 2024, 15(5), 776; https://doi.org/10.3390/f15050776 - 28 Apr 2024
Cited by 1 | Viewed by 1150
Abstract
Smoke tree (Cotinus coggygria) is an important ornamental tree that represents the autumnal landscape of red leaves in Northern China, especially in Beijing. However, Verticillium wilt, caused by the fungus (Verticillium dahliae), has resulted in a high mortality rate [...] Read more.
Smoke tree (Cotinus coggygria) is an important ornamental tree that represents the autumnal landscape of red leaves in Northern China, especially in Beijing. However, Verticillium wilt, caused by the fungus (Verticillium dahliae), has resulted in a high mortality rate for smoke trees, posing a serious threat to the highly valued landscape of red leaves in Beijing. To explore an efficient control measure for Verticillium wilt, we systematically analyzed the applicability and efficacy of multiple treatments for three consecutive years in Xiangshan Park and Badaling Forest Park. From 2021 to 2023, diseased smoke trees in Xiangshan Park were subjected to three application methods (agent irrigation, trunk injection, or a combination of the two) and five candidate agents, namely Bacillus subtilis, azoxystrobin, propiconazole, carbendazim, and prochloraz. Analyses of the data for three consecutive years revealed a decreasing trend in the annual disease incidence rate. Specifically, the combined application of agent irrigation and trunk injection exhibited the highest control effect and a significant improvement in the landscape of red leaves in Beijing. Furthermore, the combination of propiconazole via irrigation plus the trunk injection of carbendazim and prochloraz had the greatest control effect. These suppressive measurements were further used and demonstrated to be effective in Badaling Forest Park. Overall, our study provides an effective disease management means for controlling Verticillium wilt in smoke trees. Full article
(This article belongs to the Special Issue Management of Forest Pests and Diseases—2nd Edition)
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Figure 1

Figure 1
<p>Results of a three-year study for control of Verticillium wilt on smoke tree in Xiangshan Park. (<b>A</b>–<b>C</b>) Comparison of disease occurrence of smoke tree No. 26 (only one) in September 2021 (<b>A</b>), September 2022 (<b>B</b>), and September 2023 (<b>C</b>). (<b>D</b>) Red leaf of smoke tree No. 26 (only one) in 2023. (<b>E</b>–<b>G</b>) Comparison of disease occurrence of smoke tree No. 81 (only one) in September 2021 (<b>E</b>), September 2022 (<b>F</b>), and September 2023 (<b>G</b>). (<b>H</b>) Red leaf of smoke tree No. 81 (only one) in 2023.</p>
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<p>Relative disease index of smoke trees with different degrees of Verticillium wilt from 2021 to 2023. (<b>A</b>) Relative disease index of healthy smoke trees. (<b>B</b>) Relative disease index of mildly diseased smoke trees. (<b>C</b>) Relative disease index of severely diseased smoke trees. In June 2021, due to the severe incidence of Verticillium wilt in the smoke trees in treatment 9, the Xiangshan Park Administration undertook large-scale pruning efforts for smoke tree branches within this treatment, and therefore it does not have a reference value.</p>
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<p>Relative disease indices of each treatment on Verticillium wilt of smoke trees in different seasons within three years and the red leaf index in 2023. (<b>A</b>) Relative disease index of each treatment in spring, summer, and autumn 2021. (<b>B</b>) Relative disease index of each treatment in spring, summer, and autumn 2022. (<b>C</b>) Relative disease index of each treatment in spring, summer, and autumn 2023. (<b>D</b>) Red leaf index of each treatment in 2023. In June 2021, due to the severe incidence of Verticillium wilt in the smoke trees in treatment 9, the Xiangshan Park Administration undertook large-scale pruning efforts for smoke tree branches within this treatment, and therefore it does not have a reference value.</p>
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<p>Control effect of Verticillium wilt of smoke trees in Badaling. (<b>A</b>) Incidence rate reduction of each treatment from 2021 to 2023. (<b>B</b>) Relative disease indices of different treatments in 2023. (<b>C</b>) Relative disease indices of different application methods in 2023 (I indicates agent irrigation; T indicates trunk injection; and C indicates combined application). (<b>D</b>) Relative disease index of different degrees of disease in 2023.</p>
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<p>Results of a three-year study for control of Verticillium wilt on smoke tree in Badaling. (<b>A</b>–<b>C</b>) Comparison of disease occurrence of smoke tree No. 42 (only one) in September 2021 (<b>A</b>), September 2022 (<b>B</b>), and September 2023 (<b>C</b>). (<b>D</b>) Red leaf of smoke tree No. 42 (only one) in 2023. (<b>E</b>–<b>G</b>) Comparison of disease occurrence of smoke tree No. 49 (only one) in September 2021 (<b>E</b>), September 2022 (<b>F</b>), and September 2023 (<b>G</b>). (<b>H</b>) Red leaf of smoke tree No. 49 (only one) in 2023.</p>
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12 pages, 3375 KiB  
Article
Antifungal Activity of Culture Filtrate from Endophytic Fungus Nectria balsamea E282 and Its Fractions against Dryadomyces quercus-mongolicae
by Manh Ha Nguyen, Il-Kwon Park, Jong Kyu Lee, Dong-Hyeon Lee and Keumchul Shin
Forests 2024, 15(2), 332; https://doi.org/10.3390/f15020332 - 8 Feb 2024
Viewed by 1253
Abstract
A key role that fungal endophytes play in interacting with their host plant can be defined by the fact that they promote the growth of plants and enhance the tolerance of the host against plant pathogens using bioactive compounds that they produce. Several [...] Read more.
A key role that fungal endophytes play in interacting with their host plant can be defined by the fact that they promote the growth of plants and enhance the tolerance of the host against plant pathogens using bioactive compounds that they produce. Several studies utilizing endophytic fungi as a source of biological control against plant pathogens were conducted, and a representative example includes Aureobasidium protae from common wheat (Triticum aestivum), which inhibited the mycelial growth of Fusarium graminearum and Fusarium culmorum, causal agents of Fusarium head blight disease. Our previous study indicated that three endophytic fungal isolates, E089 (Daldinia childiae), E282 (Nectria balsamea), and E409 (Colletotrichum acutatum), showed antifungal activities against D. quercus-mongolicae, an ascomycetous fungus that is reported to be associated with oak mortality in South Korea. The objectives of this study were to optimize and evaluate antifungal efficiency for these endophytic fungi against D. quercus-mongolicae, and this was achieved using culture filtrate retrieved from the three above-mentioned endophytes and fractions isolated from the culture filtrate. Of those, the culture filtrate from E282 showed higher mycelial growth and sporulation inhibitions on PDA medium where D. quercus-mongolicae was grown. In addition, three fractions, including hexane, CHCl3, Et2O, and H2O, were tested for antifungal activities against D. quercus-mongolicae. The results revealed that the Et2O fraction showed higher mycelial growth and sporulation inhibition rates. Taking these results together, the endophytic fungus, N. balsamea, which exhibited high antifungal efficiency, can be effectively used as a biocontrol agent for the management of oak wilt disease in the country. Full article
(This article belongs to the Special Issue Management of Forest Pests and Diseases—2nd Edition)
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Figure 1
<p>Mycelial growth of <span class="html-italic">D. quercus-mongolicae</span> on PDA medium containing culture filtrates of E089, E282, and E409 isolates during the cultured time (in the dark at 25 °C for 6 days and at room temperature for 6 days).</p>
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<p>Mycelial growth inhibition rates of E089, E282, and E409 isolates against <span class="html-italic">D. quercus-mongolicae</span> after incubating in the dark at 25 °C for 6 days. Different letters indicate a significant difference (<span class="html-italic">p</span> &lt; 0.05) among treatments by Tukey’s HSD test.</p>
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<p>Mycelial growth (<b>above</b>) and spore germination (<b>below</b>) of <span class="html-italic">D. quercus-mongolicae</span> on PDA medium containing culture filtrates of E089, E282, and E409 isolates (<b>a</b>): 2-week culture filtrates; (<b>b</b>): 3-week culture filtrates after incubating in the dark at 25 °C for 6 days and 5 days, respectively.</p>
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<p>Sporulation inhibition rates of E089, E282, and E409 isolates with different cultured periods against <span class="html-italic">D. quercus-mongolicae</span> at 12 days after inoculation (in the dark at 25 °C for 6 days and at room temperature for 6 days). Different letters indicate a significant difference (<span class="html-italic">p</span> &lt; 0.05) among treatments by Tukey’s HSD test.</p>
Full article ">Figure 5
<p>Spore germination inhibition rates of E089, E282, and E409 isolates with different cultured periods against <span class="html-italic">D. quercus-mongolicae</span> in the dark at 25 °C for 5 days after inoculation. Different letters indicate a significant difference (<span class="html-italic">p</span> &lt; 0.05) among treatments by Tukey’s HSD test.</p>
Full article ">Figure 6
<p>Mycelial growth inhibition rates of fractions against <span class="html-italic">D. quercus-mongolicae</span> on PDA medium containing 40 µL of fractions after incubating in the dark at 25 °C for 5 days. Different letters indicate a significant difference (<span class="html-italic">p</span> &lt; 0.05) among treatments by Tukey’s HSD test.</p>
Full article ">Figure 7
<p>Mycelial growth (<b>above</b>) and spore germination (<b>below</b>) of <span class="html-italic">D. quercus-mongolicae</span> on PDA medium containing 40 µL of fractions after incubating in the dark at 25 °C for 5 days.</p>
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<p>Sporulation inhibition rates of fractions against <span class="html-italic">D. quercus-mongolicae</span> at 10 days after inoculation (in the dark at 25 °C for 5 days and at room temperature for 5 days). Different letters indicate a significant difference (<span class="html-italic">p</span> &lt; 0.05) among treatments by Tukey’s HSD test.</p>
Full article ">Figure 9
<p>Spore germination inhibition rates of fractions against <span class="html-italic">D. quercus-mongolicae</span> on PDA medium containing 40 µL of fractions after incubating in the dark at 25 °C for 5 days. Different letters indicate a significant difference (<span class="html-italic">p</span> &lt; 0.05) among treatments by Tukey’s HSD test.</p>
Full article ">
11 pages, 6020 KiB  
Article
Antagonistic Activity and Potential Mechanisms of Endophytic Bacillus subtilis YL13 in Biocontrol of Camellia oleifera Anthracnose
by Yandong Xia, Junang Liu, Zhikai Wang, Yuan He, Qian Tan, Zhuang Du, Anqi Niu, Manman Liu, Zhong Li, Mengke Sang and Guoying Zhou
Forests 2023, 14(5), 886; https://doi.org/10.3390/f14050886 - 26 Apr 2023
Cited by 10 | Viewed by 2380
Abstract
Anthracnose, caused by the fungus Collectotrichum fructicola (C. fructicola), is a major disease affecting the quality and yield of Camellia oleifera (C. oleifera); it reduces C. oleifera yield by 40%–80%. Bacillus subtilis (B. subtilis) YL13 is an [...] Read more.
Anthracnose, caused by the fungus Collectotrichum fructicola (C. fructicola), is a major disease affecting the quality and yield of Camellia oleifera (C. oleifera); it reduces C. oleifera yield by 40%–80%. Bacillus subtilis (B. subtilis) YL13 is an antagonistic endophytic bacteria strain isolated from healthy C. oleifera leaves. This study was aimed at investigating the potential of YL13 for the biocontrol of C. oleifera anthracnose and the possible mechanisms involved. In in vitro assays, YL13 demonstrated remarkable antagonistic activity of C. fructicola. Its cell-free filtrates displayed antagonistic activity, which suggested that the metabolites of YL13 might play important roles. In vivo tests showed that the disease index of YL13-treated plants was obviously reduced under greenhouse conditions. YL13 secretes a variety of bioactive metabolites, including protease, cellulase, and siderophore, which might participate in the resistance to C. fructicola. In addition, C. oleifera treated with the fermentation broth of YL13 demonstrated different defense responses, e.g., accumulation of hydrogen peroxide (H2O2) and activation of the defense-related enzyme peroxidase (POD), which might contribute directly or indirectly to overcome external stresses. The significant biocontrol effect and host defense-induction activity of YL13 suggested that this B. subtilis strain as well as its metabolites have the potential to be exploited as microbial control agents for the efficient management of C. oleifera anthracnose. Full article
(This article belongs to the Special Issue Management of Forest Pests and Diseases—2nd Edition)
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Figure 1
<p>The antagonistic effect of YL13 on <span class="html-italic">C. fructicola</span> in vitro. (<b>A</b>) The antagonistic activity on <span class="html-italic">C. fructicola</span> by YL13 fermentation broth; (<b>B</b>) The antagonistic activity on <span class="html-italic">C. fructicola</span> by YL13 cell-free filtrate; (<b>C</b>) SEM observation of <span class="html-italic">C. fructicola</span> hyphal structures. CK, control, not exposed to YL13; YL13, exposed to YL13; h, hours; bars: 50 μm, 10 μm; red box indicates the hyphae were broken, wrinkled, and irregularly twined into clumps.</p>
Full article ">Figure 2
<p>The ability of YL13 to produce protease (<b>A</b>), cellulase (<b>B</b>), and siderophore (<b>C</b>).</p>
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<p>YL13-induced H<sub>2</sub>O<sub>2</sub> accumulation in <span class="html-italic">C. oleifera</span> leaves. CK, control, spraying with LB medium; YL13, spraying with YL13 fermentation broth (1.0 × 10<sup>8</sup> CFU mL<sup>−1</sup>). Bars represent the standard errors of three replicates. * <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001.</p>
Full article ">Figure 4
<p>Peroxidase (POD) activity in YL13-inoculated <span class="html-italic">C. oleifera</span> leaves. CK, control, spraying with LB medium; YL13, spraying with YL13 fermentation broth (1.0 × 10<sup>8</sup> CFU mL<sup>−1</sup>). Bars represent the standard errors of three replicates. * <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001.</p>
Full article ">
20 pages, 6289 KiB  
Article
Lattice Structure and Spatial Network Models Incorporating into Simulating Human-Mediated Dispersal of the Western Conifer Seed Bug Populations in South Korea
by Xiaodong Zhang, Dae-Seong Lee, Young-Seuk Park, Muyoung Heo, Il-Kyu Eom, Yang-Seop Bae, Tak-Gi Lee and Tae-Soo Chon
Forests 2023, 14(3), 552; https://doi.org/10.3390/f14030552 - 10 Mar 2023
Cited by 2 | Viewed by 1463
Abstract
The western conifer seed bug (WCSB), Leptoglossus occidentalis, has expanded rapidly in the southern peninsula of Korea since it was first reported in southeastern Korea in 2010. Two types of human-mediated passive movements were devised for modeling the rapid advancement of the [...] Read more.
The western conifer seed bug (WCSB), Leptoglossus occidentalis, has expanded rapidly in the southern peninsula of Korea since it was first reported in southeastern Korea in 2010. Two types of human-mediated passive movements were devised for modeling the rapid advancement of the pest population in this study: traffic effects and forest-product transportation. A lattice structure model (LSM) was developed to accommodate the traffic effects pertaining to the local area along with the natural population dynamics of the pest. Separately, a spatial network model (SNM) was constructed to present the passive movement of the WCSB because of forest-product transportation between all local areas in Korea. The gravity rule was applied to obtain the parameters for forest-product transportation between the local areas. LSM and SNM were linked to the two present types of passive movements in the model. The model simulated fast, linear advancement in a short period, compared with slow, circular advancement because of the conventional natural diffusion process of populations. Simulation results were comparable to field data observed in the southern peninsula of Korea, matching the rapid advancement of about 400 km to the north area (Seoul) from the south area (Changwon) within six years and expanding across the nation in 10 years. Possible saturation of populations was predicted in the 2020s if survival conditions for the WCSB were favorable and no control efforts were given in field conditions. Dispersal because of SNM notably surpassed the dispersal simulated by LSM when the WCSB population rapidly dispersed over a wide area. The Allee-effect and contribution ratio of SNM were the factors governing the rapid expansion of pest populations. The possibility of using the combined model was further discussed to address different types of human-mediated passive movements associated with population dynamics in forest pest dispersal. Full article
(This article belongs to the Special Issue Management of Forest Pests and Diseases—2nd Edition)
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Figure 1
<p>Dispersal of the WCSB populations in Korea between 2010–2021 [<a href="#B3-forests-14-00552" class="html-bibr">3</a>,<a href="#B6-forests-14-00552" class="html-bibr">6</a>,<a href="#B11-forests-14-00552" class="html-bibr">11</a>,<a href="#B22-forests-14-00552" class="html-bibr">22</a>] (data for 2019~2021 obtained from the field) (Orientation in all subfigures is the same shown in year 2010).</p>
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<p>Position of capitals in municipal cities and counties within provinces in Korea (red dots) (<b>a</b>), frequency of edges (forest-product transportation between local areas) (<b>b</b>), edges over the threshold (7.0 in common log.) on the map (No. of nodes; 233, Threshold value; 7.0 (Log. of tons per year), and No. of edges; 8402) (green dots presenting local area capitols) (<b>c</b>), highway network in the southern peninsula of Korea (thick red line indicated by an arrow to present the Gyeongbu Highway from Busan to Seoul) (<b>d</b>), frequencies of distances from all spatial units to the nearest point of highway (<b>e</b>), and sampling points for traffic load (no. of cars per day) in Korea in the highway network (<b>f</b>) with kriging data (<b>g</b>).</p>
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<p>Distribution of sapling farms in Korea (blue circles presenting the number of sapling farms in local areas) (<b>a</b>), heat map (Radius = 20 km; stronger blue tones indicating higher densities) (<b>b</b>), map of land-cover types (<b>c</b>), habitat preference score for the WCSB (<b>d</b>), and spatial distribution of habitat preference on the map (<b>e</b>).</p>
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<p>Incorporating lattice-structured model (LSM) and spatial network model (SNM) into simulating population dispersal of the WCSB: flow chart (<b>a</b>), and linkage graph of two models (green dots presenting imaginary positions of local areas, and blue and green arrows indicating data transfer from LSM to SNM and vice versa, respectively) (<b>b</b>).</p>
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<p>Two stages in passive movements in highway networks (The distance for the symbol <span class="html-italic">d</span><sub>2</sub> is drawn intentionally short for simplicity of visualization). (<b>a</b>), probability of arriving at the road for Stage I according to distance to the road (<b>b</b>) and traffic load (<b>c</b>), and probability for dispersal distance for Stage II of passive movement according to traffic density (After the distance was determined by Equation (3), probability of dispersal in the model was generated according to the Poisson distribution) (<b>d</b>).</p>
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<p>Determining probability of movement distance of the WCSB in the model according to field data (<b>a</b>), weight for movement direction based on habitat preference difference compared with the neighbor units (<b>b</b>), and probabilistic selection of spatial units according to habitat preference differences (dotted lines indicating probabilistic movement to new spatial units) (<b>c</b>).</p>
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<p>Simulating advancement patterns of WCSB populations between 2011–2030 in the southern Korean peninsula starting from 2010 according to LSM and SNM (Allee threshold; 1000 individuals/km<sup>2</sup>, Gamma; 0.25) for the years of 2011 (<b>a</b>), 2015 (<b>b</b>), 2016 (<b>c</b>), 2020 (<b>d</b>), 2022 (<b>e</b>), and 2030 (<b>f</b>). In each subfigure top panel indicates spatial map and bottom panel presents increase in the total number of individuals (log.) during the simulation period. Horizontal and vertical units in two-dimensional maps in the top panel are expressed in km for convenience of illustration. Arrows in the bottom panel indicating the points where the population size obtained by SNM surpasses the population size obtained by LSM.</p>
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<p>Simulating advancement patterns of WCSB populations with different Allee-effect thresholds (<span class="html-italic">A</span>) in the southern Korean peninsula in 2011–2030, with <span class="html-italic">A</span> = 125 individuals per spatial unit in 2020 (<b>a</b>) and 2030 (<b>b</b>), and with <span class="html-italic">A</span> = 2000 individuals per spatial unit in 2020 (<b>c</b>) and 2030 (<b>d</b>). (Horizontal and vertical units in two-dimensional maps are expressed in km for convenience of illustration.) Changes in population size (log.) of the WCSB with different <span class="html-italic">A</span> (γ = 0.25) with 125, 1000, and 2000 individuals per spatial unit in the southern Korean peninsula between 2010 and 2030 according to LSM (e) and SNM (f). Arrows in (e,f) indicating the number of individuals matching different levels of <span class="html-italic">A</span> in the sixth year.</p>
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<p>Simulating advancement patterns of WCSB populations with γ = 0.15 in 2020 (<b>a</b>) and 2030 (<b>b</b>), and with γ = 0.35 in 2020 (<b>c</b>) and 2030 (<b>d</b>) in the southern Korean peninsula starting from 2010 (Allee threshold; 1000 individuals per spatial unit). (Horizontal and vertical units in two-dimensional maps are expressed in km for convenience of illustration.) Changes in population size (log.) of WCSB with different conditions of γ (0.15 and 0.35) in the southern Korean peninsula between 2011–2030, starting from 2010 according to LSM (<b>e</b>) and SNM (<b>f</b>).</p>
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<p>Simulation results for WCSB dispersal according to LSM plus SNM in 2016 (dotted ellipse indicating global, linear dispersal and solid ellipses presenting local, circular dispersal) (<b>a</b>), compared with field data (dotted ellipse indicating global, linear dispersal) (<b>b</b>), dispersal of Pine needle gall midge [<a href="#B15-forests-14-00552" class="html-bibr">15</a>] (<b>c</b>), and dispersal of Pine wilt disease [<a href="#B15-forests-14-00552" class="html-bibr">15</a>] (<b>d</b>). (The symbols resembling ‘4’ in (<b>c</b>,<b>d</b>) present orientation with the top indicating north.)</p>
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13 pages, 2408 KiB  
Article
Breeding of Highly Virulent Beauveria bassiana Strains for Biological Control of the Leaf-Eating Pests of Dalbergia odorifera
by Xianpeng Ni, Hongjun Li, Yandong Xia, Yan Lin, Chuanting Wang, Cong Li, Junang Liu and Guoying Zhou
Forests 2023, 14(2), 316; https://doi.org/10.3390/f14020316 - 6 Feb 2023
Cited by 1 | Viewed by 1709
Abstract
Dalbergia odorifera (D. odorifera), commonly named the fragrant rosewood, is one of the second-level protected wild plants in China, and one of 34 species of rosewood in five genera and eight categories in the National Standard of China. As a kind [...] Read more.
Dalbergia odorifera (D. odorifera), commonly named the fragrant rosewood, is one of the second-level protected wild plants in China, and one of 34 species of rosewood in five genera and eight categories in the National Standard of China. As a kind of traditional Chinese medicine (TCM), it plays an important role in the pharmaceutical industry, including the treatment of cardiovascular diseases, rheumatic pain, etc. With the continuous expansion of the planting area of D. odorifera, the diseases and pests of D. odorifera become more and more serious, among which leaf-eating pests are the most serious. In this study, ultraviolet rays and microwaves were used to mutagenize Beauveria bassiana (B. bassiana) strain HNCMBJ-P-01, and excellent mutant strains with high spore yield and high virulence were screened out, and then they were prepared into a wettable powder for forest control experiments to study their biocontrol effects. The virulence screening test showed that the virulence of strain HBWB-44 was the strongest, and the 10 day corrected mortality rate was 80.00%, and the lethal time was 5.622 days. The results of biological control test showed that the control effect of B. bassiana wettable powder 100 times solution reached 60.89%, second only to the botanical fungicide matrine. Generically, The B. bassiana that we screened and mutated showed a good killing effect on Plecoptera bilinealis (P. bilinealis), and the wettable powder produced by it showed a good control effect on the leaf-eating pests of D. odorifera. The application of fungal insecticides in plantations has a good prospect for controlling the occurrence of leaf-eating pests of D. odorifera. Full article
(This article belongs to the Special Issue Management of Forest Pests and Diseases—2nd Edition)
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<p>The mortality and positive mutation rate of strain HNCMBJ-P-01 by UV mutagenesis. Bars represent standard errors of three replicates.</p>
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<p>The mortality and positive mutation rate of strain HBUV-22 by microwave mutagenesis. Bars represent standard errors of three replicates.</p>
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<p>Mortality trend of <span class="html-italic">P. bilinealis</span> larvae with different treatment solutions. Bars represent standard errors of three replicates.</p>
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<p>Effects of different treatment agents on the population decline rate of <span class="html-italic">P. bilinealis</span> larvae. Bars represent standard errors of three replicates.</p>
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<p>Forest control effect of spraying different treatment agents on <span class="html-italic">P. bilinealis</span> larvae. Bars represent standard errors of three replicates.</p>
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14 pages, 3650 KiB  
Article
Occurrence Prediction of Western Conifer Seed Bug (Leptoglossus occidentalis: Coreidae) and Evaluation of the Effects of Climate Change on Its Distribution in South Korea Using Machine Learning Methods
by Dae-Seong Lee, Tak-Gi Lee, Yang-Seop Bae and Young-Seuk Park
Forests 2023, 14(1), 117; https://doi.org/10.3390/f14010117 - 8 Jan 2023
Cited by 5 | Viewed by 3537
Abstract
The western conifer seed bug (WCSB; Leptoglossus occidentalis) causes huge ecological and economic problems as an alien invasive species in forests. In this study, a species distribution model (SDM) was developed to evaluate the potential occurrence of the WCSBs and the effects [...] Read more.
The western conifer seed bug (WCSB; Leptoglossus occidentalis) causes huge ecological and economic problems as an alien invasive species in forests. In this study, a species distribution model (SDM) was developed to evaluate the potential occurrence of the WCSBs and the effects of climate on WCSB distribution in South Korea. Based on WCSB occurrence and environmental data, including geographical and meteorological variables, SDMs were developed with maximum entropy (MaxEnt) and random forest (RF) algorithms, which are machine learning methods, and they showed good performance in predicting WCSB occurrence. On the potential distribution map of WCSBs developed by the model ensemble with integrated MaxEnt and RF models, the WCSB occurrence areas were mostly located at low altitudes, near roads, and in urban areas. Additionally, environmental factors associated with anthropogenic activities, such as roads and night lights, strongly influenced the occurrence and dispersal of WCSBs. Metropolitan cities and their vicinities in South Korea showed a high probability of WCSB occurrence. Furthermore, the occurrence of WCSBs in South Korea is predicted to intensify in the future owing to climate change. Full article
(This article belongs to the Special Issue Management of Forest Pests and Diseases—2nd Edition)
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<p>Distribution of WCSB occurrence (red points) in South Korea. These are the points after performing spatial filtering.</p>
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<p>Comparison of environmental conditions between the presence (P) and absence (A) sites of WCSBs. The z-score (z) and <span class="html-italic">p</span>-value (<span class="html-italic">p</span>) were calculated based on test statistics (U) of the Mann–Whitney U test. The bars and error bars represent the mean and standard error of each variable. (<b>a</b>) Maximum temperature of the warmest month, (<b>b</b>) minimum temperature of the coldest month, (<b>c</b>) annual precipitation, (<b>d</b>) precipitation of driest month, (<b>e</b>) elevation, (<b>f</b>) slope, (<b>g</b>) night light, (<b>h</b>) distance to the road.</p>
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<p>The relationship between the environments in the occurrence sites of WCSBs. Spearman’s correlation analysis was used. The numbers in the figure mean correlation coefficient (<span class="html-italic">r</span>). Gray letters indicate statistically insignificant relationships (<span class="html-italic">p</span> ≥ 0.05). Bio5: maximum temperature of the warmest month; Bio6: minimum temperature of the coldest month; Bio12: annual precipitation; Bio14: precipitation of driest month; Ele: elevation; Light: night light; Road: distance to the road.</p>
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<p>Variable importance in the RF model (<b>a</b>) and the MaxEnt model (<b>b</b>) and importance ranks (<b>c</b>) to predict the occurrence of WCSBs. The bars and error bars represent the mean and standard error of each variable. The abbreviation of environmental variables is the same as in <a href="#forests-14-00117-f003" class="html-fig">Figure 3</a>.</p>
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<p>Partial dependence plots of both the SDMs for WCSBs. Solid lines are regression curves using LOESS, and gray areas display the 95% confidence interval. (<b>a</b>) Maximum temperature of the warmest month, (<b>b</b>) minimum temperature of the coldest month, (<b>c</b>) annual precipitation, (<b>d</b>) precipitation of driest month, (<b>e</b>) elevation, (<b>f</b>) slope, (<b>g</b>) night light, (<b>h</b>) distance to the road.</p>
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<p>Prediction of the potential distribution areas of WCSB in historical (<b>a</b>) and future climate conditions (<b>b</b>–<b>e</b>). Two shared socioeconomic pathway (SSP) scenarios were used for future climate data: (near future for 2021–2040) SSP1-2.6 data (<b>b</b>) and SSP5-8.5 (<b>c</b>), (far future for 2061–2080) SSP1-2.6 data (<b>d</b>) and SSP5-8.5 data (<b>e</b>). The maps are the ensemble result of the random forest model and maximum entropy model. All maps have the same color legends.</p>
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<p>The effects of climate change on the occurrence of WCSBs in South Korea. All values in the figure are interval values. Change in the occurrence risk of WCSBs according to (<b>a</b>) elevation and (<b>b</b>) latitude (NF: near future (2021–2040); FF: Far future (2061-2080)). (<b>c</b>) Impacts of intensified climate change in the future. (<b>d</b>) Change in the occurrence risk of WCSBs between climate change scenarios in the far future. The degree of change in the near future and the far future (<b>c</b>,<b>d</b>) was obtained by subtracting probability under SSP5-8.5 from probability under SSP1-2.6. Grids with gray color mean no data.</p>
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12 pages, 2289 KiB  
Article
Effect of Chilling Temperature on Survival and Post-Diapause Development of Korean Population of Lymantria dispar asiatica (Lepidoptera: Erebidae) Eggs
by Min-Jung Kim, Keonhee E. Kim, Cha Young Lee, Yonghwan Park, Jong-Kook Jung and Youngwoo Nam
Forests 2022, 13(12), 2117; https://doi.org/10.3390/f13122117 - 10 Dec 2022
Cited by 4 | Viewed by 1608
Abstract
One of the subspecies of the Eurasian spongy moth, Lymantria dispar asiatica, is a destructive forest pest in native regions and also an important quarantine pest in non-native regions. Its polyphagous nature, together with occasional outbreaks, may seriously threaten ecosystems and result [...] Read more.
One of the subspecies of the Eurasian spongy moth, Lymantria dispar asiatica, is a destructive forest pest in native regions and also an important quarantine pest in non-native regions. Its polyphagous nature, together with occasional outbreaks, may seriously threaten ecosystems and result in costly management programs. In this study, we examined the effect of chilling temperatures (−12, −6, 0, 6, and 12 °C) during the diapause phase on the survival and post-diapause development of L. d. asiatica eggs, collected before winter, in order to characterize their thermal response. The eggs were exposed to treatment temperatures for 100 days, followed by 25 °C incubation to determine their survival and development time. The eggs hatched in all the treatments, indicating that all the examined conditions could partly or sufficiently satisfy the thermal requirement for eggs to enter post-diapause development. However, exposure to chilling temperatures significantly affected both the survival and development times of overwintering eggs in a given temperature range. The survival rates declined at −12 °C, and the development rates accelerated as the chilling temperature increased. This information could offer clues for the assessment of the outbreak potential in native regions and the possibility of range expansion in non-native regions through the consideration of winter conditions that favor L. d. asiatica egg hatching and their subsequent development. Full article
(This article belongs to the Special Issue Management of Forest Pests and Diseases—2nd Edition)
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<p>Sampled location for <span class="html-italic">L. d. asiatica</span> eggs in this study on the distribution map of mean temperature of coldest quarter (<a href="https://www.worldclim.org/" target="_blank">https://www.worldclim.org/</a>, accessed on 31 October 2022). Abbreviations of locations are given in <a href="#forests-13-02117-t001" class="html-table">Table 1</a>.</p>
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<p>Schematic diagram of temporal pattern of temperature experienced by eggs of HC population in this study. Daily mean temperatures before the date of egg collection were obtained from KMA website (<a href="http://web.kma.go.kr/" target="_blank">http://web.kma.go.kr/</a>, accessed on 31 October 2022). The eggs were exposed to one of the five chilling temperatures (−12, −6, 0, 6, and 12 °C) for 100 days, followed by post-chill temperature of 25 °C.</p>
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<p>(<b>A</b>) survival rate and (<b>B</b>) development time of <span class="html-italic">Lymantria dispar asiatica</span> eggs of eight experimental populations for each treatment. Different letters above the bars indicate significant differences according to mixed effect models (<span class="html-italic">p</span> &lt; 0.001).</p>
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<p>Coefficient variation (CV) of (<b>A</b>) survival rate and (<b>B</b>) median development time of <span class="html-italic">Lymantria dispar asiatica</span> eggs of sampled sites (<span class="html-italic">n</span> = 8) for each treatment.</p>
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<p>Cumulative distribution models for the development completion of <span class="html-italic">Lymantria dispar asiatica</span> eggs depending on different chilling treatments.</p>
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