Abstract

Simple SummaryChestnut cultivation makes it possible to invigorate the economy of many rural areas in Europe. The chestnut gall wasp Dryocosmus kuriphilus is a serious invasive pest that causes severe damage to chestnut cultivation worldwide. Its rapid spread across Europe endangers the continuity of the entire chestnut industry. Despite this growing concern, scarce attention has been paid to the status of D. kuriphilus in its southernmost distributional range in continental Europe and limited knowledge on the factors modelling their populations is available. In this study, we assessed spatio-temporal patterns in the population dynamics, phenology and tree damage in southern Spain, and further evaluated the relationship between these variables and thermal trends. Strong variation in the population dynamics and flight phenology was found both among localities and over time, which was influenced by differences in thermal regimes. Similarly, tree damage evolved differently over time in each locality, thus suggesting that local conditions may determine significant differences in damage evolution. Our work contributes to a better understanding of this pest in countries throughout the Mediterranean basin and can be useful for further improvement of control and management strategies.The invasive chestnut gall wasp (CGW), Dryocosmus kuriphilus, the worst pest of chestnut cultivation, has spread worryingly throughout Europe in less than 20 years. Despite the great concern around this pest, little is known about the status in its southernmost distribution in continental Europe. We assessed spatio-temporal patterns in the population dynamics, phenology and tree damage caused by CGW in southern Spain. Likewise, the relationship between these variables and thermal trends was evaluated. We found strong variation in the population dynamics and flight phenology among localities and over time, which were highly influenced by changes in thermal regimes. Specifically, warmer localities and vegetative periods promoted higher population densities, a partial increase in the survival of immature stages, and advanced flight activity. Moreover, tree damage evolved differently over time in each locality, which suggests that local conditions may determine differences in damage evolution. Our findings evidence that great spatio-temporal variability in the CGW populations takes place across invaded areas in its southernmost European distributional range. Although control mechanisms have been introduced, implementation of further control and management measures are critical to cope with this main threat for the chestnut industry and to prevent its spread to nearing chestnut-producing areas.

Highlights

  • Biological invasions determine multiple pervasive effects on ecosystem processes and functions [1,2]

  • It is worth noting that sweet chestnut woods (Mediterranean Castanea sativa-dominated forests and old-established plantations with semi-natural undergrowth) are listed in Annex I of the EU Habitats Directive, so this species-rich ecosystem entails high conservation priority [49]

  • The first detections of chestnut gall wasp (CGW) in Andalusian chestnut orchards occurred in Málaga in 2014, in the municipality of Ojén, from where it spread to the rest of the studied localities in only one year

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Summary

Introduction

Biological invasions determine multiple pervasive effects on ecosystem processes and functions [1,2]. They cause huge economic impacts, such as direct production losses in agricultural/forestry systems and related management costs [3,4]. Such impacts may substantially differ between invasive species and contexts [5,6,7]. Invasive phytophagous species associated with woody plants usually show higher spread rates and potential for invasiveness than those associated with herbaceous plants [8]. Studies assessing invasion spread patterns and underlying processes are essential to understanding, predicting and managing invasions

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