Abstract

Over the last decades, climate change has triggered an increase in the frequency of spruce bark beetle (Ips typographus L.) in Central Europe. More than 50% of forests in the Czech Republic are seriously threatened by this pest, leading to high ecological and economic losses. The exponential increase of bark beetle infestation hinders the implementation of costly field campaigns to prevent and mitigate its effects. Remote sensing may help to overcome such limitations as it provides frequent and spatially continuous data on vegetation condition. Using Sentinel-2 images as main input, two models have been developed to test the ability of this data source to map bark beetle damage and severity. All models were based on a change detection approach, and required the generation of previous forest mask and dominant species maps. The first damage mapping model was developed for 2019 and 2020, and it was based on bi-temporal regressions in spruce areas to estimate forest vitality and bark beetle damage. A second model was developed for 2020 considering all forest area, but excluding clear-cuts and completely dead areas, in order to map only changes in stands dominated by alive trees. The three products were validated with in situ data. All the maps showed high accuracies (acc > 0.80). Accuracy was higher than 0.95 and F1-score was higher than 0.88 for areas with high severity, with omission errors under 0.09 in all cases. This confirmed the ability of all the models to detect bark beetle attack at the last phases. Areas with no damage or low severity showed more complex results. The no damage category yielded greater commission errors and relative bias (CEs = 0.30–0.42, relB = 0.42–0.51). The similar results obtained for 2020 leaving out clear-cuts and dead trees proved that the proposed methods could be used to help forest managers fight bark beetle pests. These biotic damage products based on Sentinel-2 can be set up for any location to derive regular forest vitality maps and inform of early damage.

Highlights

  • In the last three centuries, the forests in the Czech Republic have changed dramatically

  • Three different layers were developed (Table 2, Figure 7 Step 4): (1) the biotic damage A (BDA) layer using 2019 imagery (BDA19), (2) the BDA layer using 2020 imagery (BDA20), and (3) the biotic damage B (BDB) layer using 2020 imagery (BDB20) to map only changes in stands dominated by alive trees

  • Each product had two outputs: (1) a continuous map representing changes in forest vitality (Figure 8, left panel) and (2) a categorical map showing the areas of biotic damage (Figure 8, right panel), excluding cut areas for the BDB layer using imagery (BDB20) map

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Summary

Introduction

In the last three centuries, the forests in the Czech Republic have changed dramatically. The spruce currently accounts for 49.2% of stands and pine does for 15.9% [1]. These stands are less stable and more threatened by abiotic factors (e.g., drought, wind, snow, glazed frost) and, more recently, by anthropogenic influences (e.g., air pollution) as well [2]. Decrease of forest vitality, growth under stress, and greater susceptibility to spruce bark beetle (Ips typographus L.) infestation are being caused by global climate change, especially long-term droughts with extremely high temperatures in the vegetative period [2]. The common harvested volume per year in the Czech Republic is about 15 million m3 in total and around 1 million m3 of this amount is infested by insects. For 2020, the estimate is ranking between 40 and 60 million m3 of WII [4]

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