Abstract
Trees emit a species-specific mixture of biogenic volatile organic compounds (BVOCs) like isoprene, monoterpenes and sesquiterpenes. These highly reactive BVOCs are quickly degraded by OH- NO3- and O3 radicals and hence, alter the atmospheric composition. Under high NOx conditions their chemical degradation causes the formation of ground-level ozone. Furthermore, due to progressing chemical reactions BVOCs become less volatile and form secondary organic aerosol (SOA), which is one of the main components of PM2.5. In this way, BVOCs can have negative effects on air quality and thus on human health and the ecosystem through their influence on NOx, O3 and PM2.5 concentrations. However, since BVOC emission is trees species-specific, this influence depends on the composition of the tree population. Air quality may even improve due to a selection of specific tree species. Studies with different land use datasets are performed with the model system COSMO-MUSCAT for Germany and May 2014. The consideration of isoprene, sesquiterpene, HOMs and the reaction of monoterpene with NO3 results in a doubling of organic matter (OM) concentration compared to the original SORGAM mechanism at higher temperatures.
Access this chapter
Tax calculation will be finalised at checkout
Purchases are for personal use only
References
Banzhaf, E., & Kollai, H. (2018). Land use/Land cover for Leipzig, Germany, for 2012 by an object-based image analysis (OBIA). PANGAEA.
Bastin, J. F., et al. (2019). The global tree restoration potential. Science, 365(6448), 76–79.
Berndt, T., et al. (2016a). Highly Oxidized Second-Generation Products from the Gas-Phase Reaction of OH Radicals with Isoprene. The Journal of Physical Chemistry A, 120(51), 10150–10159.
Berndt, T., et al. (2016b). Hydroxyl radical-induced formation of highly oxidized organic compounds. Nature Communications, 7, 13677.
Griffin, R. J., et al. (1999). Organic aerosol formation from the oxidation of biogenic hydrocarbons. Journal of Geophysical Research: Atmospheres, 104(3), 3555–3567.
Hoffmann, T., et al. (1997). Formation of Organic Aerosols from the Oxidation of Biogenic Hydrocarbons. Journal of Atmospheric Chemistry, 26(2), 189–222.
Jokinen, T., et al. (2015). Production of extremely low volatile organic compounds from biogenic emissions: Measured yields and atmospheric implications. Proceedings of the National Academy of Sciences of the United States of America, 112(23), 7123–7128.
Karl, M., et al. (2006). Product study of the reaction of OH radicals with isoprene in the atmosphere simulation chamber SAPHIR. Journal of Atmospheric Chemistry, 55(2), 167–187.
Karl, M., et al. (2009). Formation of secondary organic aerosol from isoprene oxidation over Europe. Atmospheric Chemistry and Physics, 9(18), 7003–7030.
Köble, R., & Seufert, G. (2001). Novel maps for forest tree species in Europe. Proceedings of the 8th European Symposium on the Physico-Chemical Behaviour of Air Pollutants: “A Changing Atmosphere!”, Torino, Italy, 17–20 September 2001.
Kroll, J. H., & Seinfeld, J. H. (2008). Formation and evolution of low-volatility organics in the atmosphere. Atmospheric Environment, 42(16), 3593–3624.
Ng, N. L., et al. (2008). Secondary organic aerosol (SOA) formation from reaction of isoprene with nitrate radicals (NO3). Atmospheric Chemistry and Physics, 8(14), 4117–4140.
Popkin, G. (2019). The forest question. Nature, 565, 280–282.
Richters, S., et al. (2016). Highly Oxidized RO2 Radicals and Consecutive Products from the Ozonolysis of Three Sesquiterpenes. Environmental Science and Technology, 50(5), 2354–2362.
Schell, B., et al. (2001). Modeling the formation of secondary organic aerosol within a comprehensive air quality model system. Journal of Geophysical Research: Atmospheres, 106(22), 28275–28293.
Schubert, S., & Grossmann-Clarke, S. (2013). The influence of green urban areas and roof albedos on air temperatures during Extreme Heat Events in Berlin, Germany. Meteorologische Zeitschrift, 22(2), 131–143.
Steinbrecher, R., et al. (2009). Intra- and inter-annual variability of VOC emissions from natural and semi-natural vegetation in Europe and neighboring countries. Atmospheric Environment, 43(7), 1380–1391.
Stockwell, W. R., et al. (1997). A new mechanism for regional atmospheric chemistry modeling. Journal of Geophysical Research: Atmospheres, 102(22), 25847–25879.
Von Schneidemesser, E., et al. (2015). Chemistry and the Linkages between Air Quality and Climate Change. Chemical Reviews, 115(10), 3856–3897.
Wolke, R., et al. (2012). Influence of grid resolution and meteorological forcing on simulated European air quality: A sensitivity study with the model system COSMO-MUSCAT. Atmospheric Environment, 53, 110–130.
Acknowledgements
M.L.L. wants to thank the Ph.D. scholarship program of the German Federal Environment Foundation (Deutsche Bundesstiftung Umwelt, DBU) for its funding (AZ 20016/452).
Author information
Authors and Affiliations
Corresponding author
Editor information
Editors and Affiliations
Questions and Answers
Questions and Answers
Questioner: Pius Lee
Question: Your study was focused on scenarios in May 2014 when the trees are in blooming stages. Your conclusions on SOA production and ozone concentrations were interesting but not quite the peak production for summers (July/August) where air quality is often worse than May. Do you have summer scenarios and/or campaigns?
Answer: The periode May 2014 was chosen for evaluation purposes as for this time periode there are AMS, ACSM and filter measurements available for the Melpitz field site. The results already show a great improvement with the extended SORGAM module especially for warmer temperatures. It is planned to further extend the simulations for the entire summer 2014 and to compare the simulations with another campaigne, the F-BEACH campaign at Waldstein in July 2014. However, this will require further changes in the chemistry and SOA mechanisms, which are currently under development. The new mechanisms will than be used for the urban setup of Leipzig and the rather hot and dry summer of 2018 and 2019 will be modeled and analyzed.
Questioner: Joachim Fallmann
Question: What efforts are planned to answer the question of what would be the best/right tree in terms of urban air quality (Resolution, urban scheme, model configuration …)?
Answer: As first step a new chemistry mechanism is beeing developed for better treatment of anthropogenic and biogenic VOCs, and associated therewith the SOA module. Therin the tree species specific monoterpene split will be addressed more detailed in terms of reaction constants. Simulations of test sceniarios are planed with diffent tree species under diverse environmental conditions (NOx emissions, temperature, radiation, wind, …). For the urban setup of Leipzig a resolution of up to 200 m and a double-canyon effect parametrization has already been realized. For more details see “High-resolution air-quality modeling in urban areas—A case study for the City of Leipzig” from Bernd Heinold. The city of Leipzig provided data for forests (in percent of area), street and park trees (exact location but no area information) on tree species basis. In 2018, a Land use/Land cover dataset was published for Leipzig by object-based image analysis for 2012 which contains area information for artificial surfaces, agriculture, grass, trees (>5 m diameter) and young trees/shrubs (Banzhaf & Kollai, 2018). With these information a tree species based map for Leipzig will be generated and urban simulations will be performed. For air quality mitigation potential of the different tree species the findings of the test scenarios will be used for future air quality assessment, where the actual existing tree species distribution is used and additional trees will be added. The influence of the additional trees will then be further analyzed for different future scenarios (NOx emissions, meteorological parameters).
Rights and permissions
Copyright information
© 2021 The Author(s), under exclusive license to Springer-Verlag GmbH, DE, part of Springer Nature
About this paper
Cite this paper
Luttkus, M.L., Wolke, R., Heinold, B., Tilgner, A., Poulain, L., Herrmann, H. (2021). Biogenic Emissions and Urban Air Quality. In: Mensink, C., Matthias, V. (eds) Air Pollution Modeling and its Application XXVII. ITM 2019. Springer Proceedings in Complexity. Springer, Berlin, Heidelberg. https://doi.org/10.1007/978-3-662-63760-9_2
Download citation
DOI: https://doi.org/10.1007/978-3-662-63760-9_2
Published:
Publisher Name: Springer, Berlin, Heidelberg
Print ISBN: 978-3-662-63759-3
Online ISBN: 978-3-662-63760-9
eBook Packages: Physics and AstronomyPhysics and Astronomy (R0)