Potential Westward Spread of Emerald Ash Borer, Agrilus planipennis Fairmaire, 1888 (Coleoptera: Buprestidae) from Eastern Ukraine

Author:

Meshkova Valentyna12ORCID,Borysenko Oleksandr34ORCID,Kucheryavenko Tetiana5,Skrylnyk Yuriy2,Davydenko Kateryna26ORCID,Holusa Jaroslav1ORCID

Affiliation:

1. Faculty of Forestry and Wood Sciences, Czech University of Life Sciences Prague, Kamýcká 1283, 16500 Prague-Suchdol, Czech Republic

2. Department of Entomology, Phytopathology, and Physiology, Ukrainian Research Institute of Forestry & Forest Melioration, Pushkinska 86, UA-61024 Kharkiv, Ukraine

3. Department of Geoinformation Technologies and Space Monitoring of the Earth, National Aerospace University «Kharkiv Aviation Institute», Chkalov Street 17, UA-61070 Kharkiv, Ukraine

4. Department of Remote Sensing, Tartu Observatory, University of Tartu, EE-61602 Toravere, Estonia

5. State Specialized Forest Protection Enterprise “Kharkivlisozahyst”, Kharkiv District, Pokotylivka, Str. Nezalezhnosti, 127, UA-62458 Kharkiv, Ukraine

6. Department of Forest Mycology and Plant Pathology, Swedish University of Agricultural Sciences, P.O. Box 7026, SE-75007 Uppsala, Sweden

Abstract

Emerald ash borer (EAB), Agrilus planipennis, is a phloem-boring beetle, native to East Asia that has become a serious invasive pest of ash (Fraxinus spp.) trees in North America and European Russia since the early 2000s. In 2019, EAB was detected in Ukraine. It had spread over 300 km from the entry point over two years and killed hundreds of Fraxinus excelsior and F. pennsylvanica trees. EAB poses a threat to the ash forests of neighboring European countries, which have already been damaged by the invasive fungus Hymenoscyphus fraxineus. The purpose of this research was (i) to reveal the traits of EAB and the climatic variables that affect its survival; (ii) to predict the EAB expansion range in Ukraine and westward; and (iii) to compare the most significant bioclimatic variables in the native, invasive ranges of EAB, as well as outside these ranges. The results demonstrated the following: (i) in all ranges, EAB has adapted to the seasonal temperature variations; (ii) the MaxEnt model predicted the potential distribution of EAB with high accuracy (AUC = 0.988); the predicted area of EAB invasion covered 87%, 48%, and 32% in Luhansk, Kharkiv, and Donetsk regions, respectively; and (iii) the ranges of climatic variables in EAB-inhabited regions demonstrated the high ecological plasticity of this pest. However, the predictions could be improved by considering forest structure, as well as the localization of roads.

Funder

Czech University of Life Sciences Prague

Swedish Foundation for Strategic Research

Knut and Alice Wallenberg’s foundation project

Publisher

MDPI AG

Subject

Forestry

Reference97 articles.

1. All European ash species are susceptible to emerald ash borer Agrilus planipennis Fairmaire (Coleoptera: Buprestidae)—A Far Eastern invader;Baranchikov;Sib. For. J.,2014

2. Van Driesche, R.G., and Reardon, R.C. (2015). Biology and Control of Emerald Ash Borer, FHTET-2014-09 Department of Agriculture, Forest Service, Forest Health Technology Enterprise Team. Chapter 1.

3. The biology and ecology of the emerald ash borer, Agrilus planipennis, in China;Wang;J. Insect Sci.,2010

4. Emerald ash borer invasion of North America: History, biology, ecology, impacts, and management;Herms;Annu. Rev. Entomol.,2014

5. The emerald ash borer: A new exotic pest in North America;Haack;Newsl. Mich. Entomol. Soc.,2002

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