Full length articleWithin-tree distribution of Ricania shantungensis (Hemiptera: Ricaniidae) eggs on chestnuts
Graphical abstract
Introduction
An invasive species, Ricania shantungensis Chou & Lu (Hemiptera: Ricaniidae), which became an important pest in Korea since its occurrence in 2010, is suspected to originate from China (Rahman et al., 2012). In China, R. shantungensis is an important economic pest of various fruit plants and roadside trees in Zhejiang province (Chou et al., 1985). In Korea, host plants of R. shantungensis are known to be 138 species belonging to 62 families, including chestnut, peach, persimmon, apple, black locust, Japanese angelica tree, snowbell, pussy willow, paper mulberry, silk tree, tree of heaven, and Japanese cornlian cherry (Kim et al., 2015). Broad host range and absence of native natural enemies might allow R. shantungensis to spread out quickly since its invasion. Especially, the occurrence of R. shantungensis at agricultural areas in 2017 was increased by 109.6% compared to those in 2016 (Baek et al., 2019a, Baek et al., 2019b). Thus, most studies for R. shantungensis has been focused on developing insecticides (Jo, 2014, Jeon et al., 2016, Choi et al., 2018, Lee et al., 2018).
For integrated pest management (IPM) of R. shantungensis, sampling of R. shantungensis within a tree (i.e., count of R. shantungensis on sample unit) is necessary to estimate its population density and distribution, and determine control options. For density estimation, selected sampling units not only determine the nature of a population but also affect the components of sampling plans such as sampling techniques, sampling number, spatial pattern of samples, and timing of sampling (Pedigo and Buntin, 1994). In general, sample units are selected based on multiple criteria including stability and possibility of delineation in the field, consistency, the balance between cost (e.g., labor and time) and variation (e.g., precision), and suitable size (Morris, 1955).
Sampling of R. shantungensis for determination of its population size is targeting to eggs because its nymphs and adults are very active (Kang et al., 2013, Choi et al., 2016). Currently, there is no sample unit suggested for eggs of R. shantungensis. The vertical distribution of R. shantungensis eggs on blueberry trees was reported (Kim et al., 2016) as 56.6–60.2%, 23.8–28.1%, 11.7–19.7% in the upper, middle, lower crowns, respectively. No report was made for within-distribution of R. shantungensis eggs on chestnuts. Information of within-distribution of R. shantungensis eggs could be used not only to determine sample unit for R. shantungensis, but also to evaluate the efficiency of aerial application of insecticides. In Korea, chestnut fields are generally located in forests and most chestnut growers are aged. Thus, for control of R. shantungensis in chestnut fields, aerial application of insecticides by government agencies is commonly requested by farmers. If R. shantungensis eggs occur on the upper crowns in chestnuts like blueberries, the efficiency of aerial application would be higher.
Therefore, this study was conducted (1) to characterize within-tree distribution of R. shantungensis eggs, (2) to determine an optimal sample unit of R. shantungensis eggs, and (3) to find out the relationship of numbers of R. shantungensis eggs between a sample unit and a whole branch.
Section snippets
Study sites and sampling
Studies were conducted in two chestnut fields in Jangam-Myeon, Buyeo-Gun (N 36.203759, W 126.856220) and Sinpyung-Myeon, Gongju-Si (N 36.485042, W 126.986180), Chungcheongnam-Do, Korea in 2019. The chestnut field in Buyeo was an actively managing commercial field. In this field, R. shantungensis was first reported in 2012 (Baek et al., 2019a, Baek et al., 2019b), and insecticides for its control were applied twice a year (i.e., June and August) since 2013. Old branches of chestnuts were
Within-tree distribution of R. shantungensis
Number of R. shantungensis egg masses was not significantly different (P > 0.05) horizontally and vertically within a tree in both sites (Table 1): horizontal directions (F = 0.3574; df = 3, 116; P = 0.7839) and vertical positions (F = 1.4874; df = 2, 87; P = 0.2316) in the Buyeo field, and horizontal directions (F = 0.7082; df = 3, 116; P = 0.5490) and vertical positions (F = 1.6330; df = 2, 69; P = 0.2028) in the Gongju field.
Optimal sample unit and required sample number
CV values became lower as sample unit decreased (Table 2). However,
Discussion
There was no significant (P > 0.05) ovipositional preference of R. shantungensis for vertical and cardinal directions within a chestnut tree. This result indicates that any living branches within a tree would be suitable for sampling of R. shantungensis eggs in chestnut fields. Thus, aerial spray of pesticides would not be the best option for pesticide application for control of R. shantungensis. Pesticides for R. shantungensis should be applied thoroughly within a chestnut tree because this
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
This work was carried out with the support of “National Institute of Agricultural Science (Project No. PJ015090052020)” funded by Rural Development of Administration and “Research Program for Forest Science & Technology Development (Project No. FP0802-2017-02)” funded by National Institute of Forest Science, Republic of Korea. This work was also partially supported by BK 21 PLUS.
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