How can a forest-based bioeconomy support biodiversity and climate neutrality?
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- EN: How can a forest-based bioeconomy support biodiversity and climate neutrality?
- DE: Wie kann eine waldbasierte Bioökonomie die biologische Vielfalt und die Klimaneutralität unterstützen?
- ES: ¿Cómo puede una bioeconomía forestal apoyar la biodiversidad y la neutralidad climática?
- FR: Comment une bioéconomie forestière peut-elle favoriser la biodiversité et la neutralité climatique?
- IT: In che modo una bioeconomia basata sulle foreste è in grado di supportare la biodiversità e la neutralità climatica?
The Paris Agreement requires major societal and economic reforms to ensure that the global average temperature remains below 2˚C pre-industrial levels. Achieving this target requires a significant reduction in gross anthropogenic carbon dioxide (CO2) emissions and an increase in human and biosphere carbon sinks. Forests are natural systems that remove carbon dioxide from the atmosphere via photosynthesis, and store carbon in biomass. Part of this carbon is transferred into soils through litterfall and tree mortality. In managed forests, part of the carbon (mainly in tree stems and major branches) may be extracted from the forest during harvest for material or energy use. If the wood is used for energy purposes, the carbon stored will be released when the wood is burned. If the wood is used for material use, the carbon is stored in wood products. In addition to carbon storage in forest ecosystems and in wood products, using wood can provide climate benefits by reducing fossil GHG emissions if they replace more greenhouse gas (GHG) intensive materials and fossil fuels.
Forests and forestry therefore play a key role in climate change mitigation; reducing deforestation and forest degradation lowers greenhouse emissions, forest management and afforestation can maintain or enhance forest carbon stocks and sinks; wood products can store carbon over the long-term; and wood products can substitute for emissions-intensive materials. Whereas it is difficult to exactly estimate the role of forests and forestry in achieving climate neutrality, the potential is generally considered to be significant (Roe et al., 2019).
For climate change mitigation and climate neutrality objectives, forest-based bioeconomy can bring climate substitution benefits (e.g. Leskinen et al., 2018), in addition to forest carbon sinks, and carbon stored in harvested wood products such as wooden buildings. For example, when using wood instead of concrete and steel as construction material, emission reductions can be achieved by less energy intensive construction processes and materials. For example, according to Leskinen et al. (2018), using 1 ton of wood for structural construction instead of concrete and steel, it is, on average, possible to avoid 2.4 tons of CO2 emissions. However, it is also important to analyze holistically the overall climate impacts of forest-based bioeconomy and take all components of mitigation into account simultaneously. In the future, it is also important to pay attention to the development of product portfolios and aim to use forest biomass for the most climate-beneficial product categories.
The scientific literature contains contrasting findings about the climate effects of forest bioenergy, mainly due to a wide variety of different production systems and their associated production environment, but also due to different assessment methods (Cowie et al. 2020). Bioenergy is commonly said to be “carbon neutral”, but this depends on the context how it is produced (Berndes et al. 2016). Within the biospheric carbon cycle, bioenergy can be carbon neutral because the carbon that is released during combustion has previously been sequestered from the atmosphere and will be sequestered again as the plants regrow, if the biomass used for energy is sustainably produced. Biomass energy is carbon neutral if growing the biomass removes as much CO2 as is emitted into the atmosphere from its combustion. Biomass energy is carbon neutral only if the net life-cycle emissions are zero. Therefore, the full supply chain must be considered, and all emissions associated with production, processing, transport and use of bioenergy need to be included. Particularly harvesting, transport and processing generally involves fossil energy use. Nevertheless, analysis shows that the fossil energy used in the supply chain is generally only a small fraction of the energy content of the bioenergy product, even for woody biomass transported over long distances, for instance, wood pellets produced in North America and transported to Europe (Dwivedi et al. 2014).
Other key issues in terms of climate impacts relate to how the forest carbon cycle is affected by management changes to provide biomass for bioenergy in addition to other forest products (Cowie et al. 2020). There are concerns that bioenergy demand could lead to increased harvest of forests for bioenergy only. However, mature forests are generally not harvested for bioenergy alone. Instead, biomass is usually a by-product of sawlog and pulpwood production which is used for material production (Spinelli et al. 2019). Logs are used to produce high-value products such as sawnwood and other wood products, which can substitute carbon intensive materials. Harvest residues (tops, branches, small-diameter trees) and wood processing residues (sawdust, bark, black liquor) are used for bioenergy. Using residues as biomass for energy production offers a good possibility for reducing greenhouse gas emissions when replacing fossil fuels and enhances the climate change mitigation value of forests managed for wood production (Gustavsson et al. 2015, Schulze et al. 2020).
The best substitution effect is reached when carbon is stored in wood products for as long as possible. That is why construction materials (replacing cement and steel) and other durable wood products have a better substitution effect compared to bioenergy (replacing fossil fuel). In long-lasting wood products, carbon is stored for decades, even up to centuries, while in bioenergy is it released to the atmosphere almost immediately. A shift towards wood products with a longer service life and substitution benefits would enhance climate mitigation benefits (Leturcq 2020, Grassi et al. 2021).
The impact of the bioeconomy on biodiversity depends to a large extent on the way we manage our forests. With quite high confidence we can say that a more intense use of forests will have negative consequences for biodiversity. However, bioeconomy development also spans many different sectors and there are also opportunities for the bioeconomy to be developed in such a way that it supports biodiversity. After all, there won’t be a bioeconomy without biodiversity.
One key issue in forest-based bioeconomy development is the prevention of deforestation. The reforestation of abandoned agricultural landscapes and degraded landscapes also plays an important role in bioeconomy development. The restoration of traditional and establishment of new silvopastoral systems (cultural landscapes such as traditional wood pastures and grazed forest) are also part of bioeconomy development. Increasing forest cover and the creation of diverse landscapes, with structural diversity (diverse natural elements and a mosaic of semi-open and closed canopy forest) will have a positive impact on biodiversity. More ecological forest management practices such as continuous forest cover management, leaving dead and living retention trees (Gustafsson et al. 2012), and an increase in course woody debris (Stokland et al. 2012) will benefit many forest species as well.
Many generalist forest species thrive quite well in managed forest. But there are also rarer and specialized forest dwellers that would need old-growth forest conditions or large undisturbed forest areas, e.g. the three-toed woodpecker, white-backed woodpecker, flying squirrel, capercaillie, Ural owl etc. For these species, large protected forest areas or relatively undisturbed wilderness areas would be beneficial. However, the area of protected forest areas in Europe is rather small (12% are protected with the main objective of conserving biodiversity, 1.5% are strictly protected with no management interventions (Bauhus et al., 2017)) and even though it is obvious that there is a need to expand protected areas this takes time and has to be balanced with other forest functions and users. Because protected areas alone are not enough to safeguard biodiversity, it is important that managed forests also focus on conservation by adapting ecological forest management principles and mimicking more close-to-nature forest conditions.
Using forest biomass for wood-based products as well as utilizing forests for non-wood forest products brings a long-term economic interest to forest owners and other stakeholders for sustainable forest management, in order to maintain and develop the capacity of natural resources in long run. In addition, different market mechanisms developed for supporting various ecosystem services can serve the same purpose. Economic interest can therefore create the motivation and financial possibilities for acting against forest disturbances, and maintaining biodiversity and ecosystem services. The development of the forest bioeconomy and related technologies may also diversify the need for different tree species for various purposes, which, in turn, encourages the diversification of forests. In addition, ensuring the continuation of forest management can help biodiversity by avoiding large-scale closed forest canopies, and lead to an underrepresentation of early development stages and open patches that also contribute in particular ways to biodiversity.
To combine objectives related to biodiversity and climate, e.g. Verkerk et al. (2020) argue for the concept of Climate Smart Forestry (CSF). According to Verkerk et al. (2020), CSF is a missing component in national strategies for implementing actions under the Paris Agreement and is needed to (a) increase the total forest area and avoid deforestation, (b) connect mitigation with adaption measures to enhance the resilience of global forest resources, and (c) use wood for products that store carbon and substitute emission-intensive fossil and non-renewable products and materials. It is critical to find the right balance between short and long-term goals, as well as between the need for wood production, the protection of biodiversity and the provision of other important ecosystem services (Verkerk et al., 2020).
Berndes, G., Abt, B., Asikainen, A., Cowie, A., Dale, V., Egnell, G., Lindner, M., Marelli, L., Paré, D., Pingoud, K., & Yeh, S. (2016). Forest biomass, carbon neutrality and climate change mitigation. European Forest Institute. From Science to Policy, 3, 3–27. https://doi.org/10.36333/fs03
Bauhus, J., Kouki, J., Paillet, Y., Asbeck, T., Marchetti, M. (2017). How does the forest-based bioeconomy impact forest biodiversity? In: Winkel, G. (ed.). Towards a Sustainable European Forest-Based Bioeconomy – Assessment and the Way Forward. What Science Can Tell Us 8, European Forest Institute, Joensuu, Finland
Cowie, A.L., Berndes, G., Bentsen, N.S., Brandão, M., Cherubini, F., Egnell, G., George, B., Gustavsson, L., Hanewinkel, M., Harris, Z.M., Johnsson, F., Junginger, M., Kline, K.L., Koponen, K., Koppejan, J., Kraxner, F., Lamers, P., Majer, S., Marland, E., Nabuurs, G.-J., Pelkmans, L., Sathre, R., Schaub, M., Smith Jr., C.T., Soimakallio, S., Van Der Hilst, F., Woods, J., Ximenes, F.A., 2021. Applying a science-based systems perspective to dispel misconceptions about climate effects of forest bioenergy. GCB Bioenergy 13, 1210–1231. https://doi.org/10.1111/gcbb.12844
Dwivedi, P., Khanna, M., Bailis, R., & Ghilardi, A. (2014). Potential greenhouse gas benefits of transatlantic wood pellet trade. Environmental Research Letters, 9, 024007.
Grassi, G., Fiorese, G., Pilli, R., Jonsson, K., Blujdea, V., Korosuo, A. and Vizzarri, M., Brief on the role of the forest-based bioeconomy in mitigating climate change through carbon storage and material substitution, Sanchez Lopez, J., Jasinevičius, G. and Avraamides, M. editor(s), European Commission, 2021, JRC124374.
Gustafsson, L., Baker, S.C., Bauhus, J., et al. (2012). Retention Forestry to Maintain Multifunctional Forests: a World Perspective. Bioscience 62: 633–645. doi:10.1525/bio.2012.62.7.6.
Gustavsson, L., Haus, S., Ortiz, C. A., Sathre, R., & Le Truong, N. (2015). Climate effects of bioenergy from forest residues in comparison to fossil energy. Applied Energy, 138, 36–50. https://doi.org/10.1016/j.apenergy.2014.10.013
Leskinen, P., Cardellini, G., González-García, S., Hurmekoski, E., Sathre, R., Seppälä, J., Smyth, C., Stern, T., Verkerk, P.J. (2018). Substitution effects of wood-based products in climate change mitigation. From Science to Policy 7, European Forest Institute. 28 p. https://doi.org/10.36333/fs07
Leturcq, P., 2020. GHG displacement factors of harvested wood products: the myth of substitution. Sci Rep 10, 20752. https://doi.org/10.1038/s41598-020-77527-8
Roe, S. et al. (2019). Contribution of the land sector to a 1.5°C world. Nature Climate Change 9(11).
Schulze, E. D., Sierra, C. A., Egenolf, V., Woerdehoff, R., Irslinger, R., Baldamus, C., Stupak, I., & Spellmann, H. (2020). The climate change mitigation effect of bioenergy from sustainably managed forests in Central Europe. Global Change Biology Bioenergy, 12(3), 186–197. https://doi.org/10.1111/gcbb.12672
Spinelli, R., Visser, R., Björheden, R., & Röser, D. (2019). Recovering energy biomass in conventional forest operations: A review of integrated harvesting systems. Current Forestry Reports, 5(2), 90–100. https://doi.org/10.1007/s40725-019-00089-0
Stokland, J. N., J. Siitonen, B. G. Jonsson. (2012). Biodiversity in dead wood. Cambridge University Press, Cambridge.
Verkerk, P.J., Costanza, R., Hetemäki, L., Kubiszewski, I., Leskinen, P., Nabuurs, G.J., Potočnik, J., Palahí, M. (2020). Climate-Smart Forestry: the missing link. Forest Policy and Economics 115.