Abstract

BackgroundBlack alder (Alnus glutinosa) forests are in severe decline across their area of distribution due to a disease caused by the soil-borne pathogenic Phytophthora alni species complex (class Oomycetes), “alder Phytopththora”. Mapping of the different types of damages caused by the disease is challenging in high density ecosystems in which spectral variability is high due to canopy heterogeneity. Data obtained by unmanned aerial vehicles (UAVs) may be particularly useful for such tasks due to the high resolution, flexibility of acquisition and cost efficiency of this type of data. In this study, A. glutinosa decline was assessed by considering four categories of tree health status in the field: asymptomatic, dead and defoliation above and below a 50% threshold. A combination of multispectral Parrot Sequoia and UAV unmanned aerial vehicles -red green blue (RGB) data were analysed using classical random forest (RF) and a simple and robust three-step logistic modelling approaches to identify the most important forest health indicators while adhering to the principle of parsimony. A total of 34 remote sensing variables were considered, including a set of vegetation indices, texture features from the normalized difference vegetation index (NDVI) and a digital surface model (DSM), topographic and digital aerial photogrammetry-derived structural data from the DSM at crown level.ResultsThe four categories identified by the RF yielded an overall accuracy of 67%, while aggregation of the legend to three classes (asymptomatic, defoliated, dead) and to two classes (alive, dead) improved the overall accuracy to 72% and 91% respectively. On the other hand, the confusion matrix, computed from the three logistic models by using the leave-out cross-validation method yielded overall accuracies of 75%, 80% and 94% for four-, three- and two-level classifications, respectively.DiscussionThe study findings provide forest managers with an alternative robust classification method for the rapid, effective assessment of areas affected and non-affected by the disease, thus enabling them to identify hotspots for conservation and plan control and restoration measures aimed at preserving black alder forests.

Highlights

  • Degradation of forests due to the rapid spread of damaging pests and pathogens, is already threatening forest functioning and services provision, challenging the Sustainable Development Goals (SDG) and urgently demanding innovative and cost-effective tools for their long term monitoring and for upscaling restoration efforts (European Commission 2020)

  • The results suggest that the red band is more valuable for detecting defoliation induced by the Phytophthora alni species complex

  • Our findings showed that the combination of red-edge and NIR region (RENDVI) was less capable than normalized difference vegetation index (NDVI) of detecting defoliation classes induced by alder Phytophthora

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Summary

Introduction

Degradation of forests due to the rapid spread of damaging pests and pathogens, is already threatening forest functioning and services provision, challenging the Sustainable Development Goals (SDG) and urgently demanding innovative and cost-effective tools for their long term monitoring and for upscaling restoration efforts (European Commission 2020). Alders are unusual among European trees in that they fix nitrogen (Huss-Danell 1997) supporting the riparian ecosystem and contributing to biodiversity Despite their high ecological value, alder-dominated forests are threatened due to the combination of long-lasting human impact on fluvial systems and emerging abiotic (i.e. climatic) and biotic (i.e. pests and diseases) global changes. Phytophthora-induced alder decline was first reported in the 1990s in the UK, but spread across Europe to become one of the most devastating epidemics of common trees in several countries (Jung and Blaschke 2004). It has more recently been reported in Spain (Solla et al 2010) and Portugal (Kanoun-Boulé et al 2016). A total of 34 remote sensing variables were considered, including a set of vegetation indices, texture features from the normalized difference vegetation index (NDVI) and a digital surface model (DSM), topographic and digital aerial photogrammetry-derived structural data from the DSM at crown level

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