Sanitary felling of Norway spruce due to spruce bark beetles in Slovenia: A model and projections for various climate change scenarios
Introduction
Some species of spruce bark beetles (e.g., Ips typographus L. and Pityogenes chalcographus L.) can break out under favourable ecological and trophic conditions. The outbreaks of spruce bark beetles can have devastating consequences on forests. This has been confirmed by data regarding the sanitary felling of conifers in Slovenia during the period from 1995 to 2006. In 2005, for example, around 747,000 m3 of wood were felled due to bark beetles, which is 22.9% of the total felled wood, or 9.9% of the total yield in Slovenia (ZGS, 2006). Such episodes allow us to define spruce bark beetles according to the classification of disturbance described by Anko (1993), as a complex, natural, and chronic disturbance (sometimes even as an acute disturbance). A natural disturbance of the forest ecosystem means a swing between succession and dynamic equilibrium (Anko, 1993). In light of climate change, spruce bark beetles can be treated as a disturbance that affects the dynamics of the forest ecosystem, and also as a factor that is affected by such climate changes (Berryman, 1986, Malström and Raffa, 2000).
Studies have shown that the behaviour of spruce bark beetles will likely change due to climate change. For example, researchers are expecting a drastic increase in damages caused by Ips typographus in Scandinavia over the next decade, because higher temperatures will allow this species to produce two complete generations per year instead of the single generation they currently produce (Lange et al., 2006). In Slovenia, I. typographus reproduction is developing towards two complete and one sister generation per year (Jurc, 2008). In Scandinavia, the border for survival of I. typographus may move 600 km north (Lange et al., 2006). Apart from these changes in the speed of bark beetle development, changes in the resistance of Norway spruce (Picea abies (L.) Karst.), and consequently in the physiological interaction between the Norway spruce and this pest, are also expected (e.g., Berryman, 1986, Rolland and Lempérière, 2004, Wermelinger, 2004). Another likely consequence of climate change is a probable shift in the geographical distribution of the Norway spruce and its pests (e.g., Williams and Liebhold, 2002, Lange et al., 2006). Consequently, there will also be a change in the intensity of damages caused by such pests.
The dynamics of spruce bark beetles is a complex phenomenon. Risk evaluation at the individual tree level due to I. typographus is usually connected to exposure, age, trophic capacity, and water. The dynamics of I. typographus outbreaks are generally dependent on population density, tree susceptibility, weather conditions, and human activities. Outbreaks are difficult to predict due to the complexity of their dynamics (Wermelinger, 2004). A model for short-term forecasting of the numbers of spruce bark beetles was created for the Dinaric Mountains region in Slovenia (Jurc et al., 2006). The model was developed using linear regression and model tree induction. The model calculates the number of spruce bark beetles for next month or week based on the known exposition, age of pheromones in traps, number of days since the bark beetles in traps were last counted, average monthly temperature, monthly rainfall, month of the year, and previous number of bark beetles in the trap. A similar model was developed for the Alps in Italy (Faccoli and Stergulc, 2006). This model can forecast short-term trends in the I. typographus population density for the next year and, consequently, can evaluate the risk of an outbreak. The model relies on the rules determined using data obtained from bark beetles caught in pheromone traps during the period from 1996 to 2004. A comparison of the models for Slovenia and Italy shows that both models use number of bark beetles caught in traps as the input for the model; however, there are several differences in methods and time scale of the models predictions. The model for Slovenia was developed using induction of decision trees and the model for Italy is based on two different indexes. The model for Slovenia predicts the abundance of I. typographus and P. chalcographus for next week or month which depends on frequency of beetle counting caught in traps. But the model for Italy can predict the abundance of I. typographus for the following year.
Long-term predictions of damage due to spruce bark beetles and the influence of climate change in Slovenia have not yet been carried out. Due to the complex population dynamics of bark beetles, even short-term predictions are difficult. Therefore, we justifiably expect lower reliability of long-term, compared to short-term, forecasts.
In the present paper, we present a model designed to predict potential sanitary felling of Norway spruce due to bark beetles attack in Slovenia under various climate change scenarios. This model can be defined within the class of correlation models (Malström and Raffa, 2000). The correlation model attempts to determine the causes and consequences of bark beetle outbreaks over a large area, with the help of research on the relationships between variables describing the environment and the intensity of damage caused by bark beetles. An example correlation model is found in Williams and Liebhold (2002). Their model examines potential shifts in outbreaks of the southern pine beetle (Dendroctonus frontalis Zimm. and D. ponderosae Hopk.) in North America due to climate change. They used a discriminant function model, which includes climate variables, forest type groups, and damage due to southern pine beetles. When making predictions using the climate change model, they considered changes in the range of the forest and changes in climatic variables. This procedure can yield important results, but such results are still based on the assumption that the relationships between variables do not change under the new conditions which are conditioned by climate change. This assumption, and the limitations it imposes, also applies to the model described in this paper.
Section snippets
Purpose of the model and definition of the system
The purpose of the model was to predict the potential sanitary felling of Norway spruce due to bark beetles under various climate change scenarios in Slovenia. The spatial framework was the entire territory of Slovenia, with a resolution of 1 km2. There were 20,376 model cells, and the time resolution was 1 year. The model was developed using a M5′ model tree. The M5′ algorithm builds tree-based models with top-down induction of decision trees where the leaf is represented by multivariate linear
Model
The model is a regression-type decision tree (Fig. 5) that has 8 levels. The most decisive variable is located at the bottom of the model tree, i.e., at the first level. Therefore, the proportion of Norway spruce in the wood stock, which appears in the first and several other levels of the model tree, is the most decisive variable in the model. The high importance of the SPRUCE variable can be expected from the results of ReliefF (Table 2), for which it exhibited the second highest positive
Discussion
We developed a model that predicts sanitary felling of Norway spruce due to bark beetles for the entire territory of Slovenia at a resolution of 1 km2, in order to evaluate the potential damage to Norway spruce due to future climate change and spruce bark beetles. It is critical to understand the degree of reliability and accuracy afforded by the model predictions. The model possesses a correlation coefficient of 51.9% and an MAE of 15.7 m3 km−2 year−1, demonstrating a medium level of accuracy.
The
Acknowledgements
The authors are thankful to the Slovenian Research Agency for their financial support. We thank the Slovenian Forestry Service for preparing the main databases for the model. In addition, Prof. Dr. Sašo Džeroski helped improve the model. The climate change scenarios were kindly prepared by Dr. Klemen Bergant.
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2019, Forest Ecology and ManagementCitation Excerpt :Host density was also positively correlated with sanitary felling because of bark beetles (Yildiz et al., 2007, see results). This association was also observed in other species of bark beetles (de Groot et al., 2019; Fettig et al., 2007; Ogris and Jurc, 2010). However, in the case of other bark beetle species such as Ips typographus and western balsam bark beetle (Dryocoetes confuses Swaine), host trees are often found in large monocultures, which greatly increases the probability of attack.