JEP  Vol.3 No.9 A , September 2012
Biogenic Isoprene and Its Impact on Human Health in Dependence on Meteorological Conditions
Abstract: Urban green areas have an important implication on the local climate. A cross-linkage of many small green spaces could result in decreasing the effect of the urban heat island, but also increase people’s thermal comfort. By the way, urban green areas could also induce a positive effect on the local urban air quality. But attention has to be paid to the assortment of the tree species. More or less all tree species are emitting biogenic volatile organic compounds in different concentration. These serve as precursors for the formation of ozone near the ground. So near surface ozone has the ability to react with different particulate matters and could become toxic, due to oxidation or nitrification. This causes inflammations and inspired allergens may increase the risk of a respiratory disease. Therefore, an analysis and assessment of the urban green area air quality could help to make a statement about the recreational effect of these areas in dependence of the leading vegetation and for that matter for the exposure to ozone. By the help of these the results can be used as a guidance of urban planning taking into account the influence of biogenic emission as a function of actual weather conditions.
Cite this paper: S. Henninger, "Biogenic Isoprene and Its Impact on Human Health in Dependence on Meteorological Conditions," Journal of Environmental Protection, Vol. 3 No. 9, 2012, pp. 1206-1212. doi: 10.4236/jep.2012.329138.

[1]   C. Ren, E. Ng and L. Katschner, “Urban Climatic Map Studies: A Review,” International Journal of Climatology, Vol. 31, No. 15, 2011, pp. 2213-2233. doi:10.1002/joc.2237

[2]   T. Sharkey, A. Wiberley and A. Donhoue, “Isoprene Emission from Plants. Why and How,” Annals of Botany, Vol. 101, No. 1, 2008, pp. 5-18. doi:10.1093/aob/mcm240

[3]   F. Pacifico, S. P. Harrison, C. D. Jones and S. Sitch, “Isoprene Emission and Climate,” Atmospheric Environ- ment, Vol. 43, No. 39, 2009, pp. 6121-6136. doi:10.1016/j.atmosenv.2009.09.002

[4]   M. Shiraiwa, Y. Sosedova, A. Rouviere, H. Yang, Y. Zhang, J. P. D. Abbat, M. Ackermann and U. P?schl, “The Role of Long-Lived Reactive Oxygen Intermediates in the Reaction of Ozone with Aerosol Particles,” Nature Chemistry, Vol. 3, 2011, pp. 291-295. doi:10.1038/nchem.988

[5]   S. Henninger, “Urban Green Areas: Lots of Benefits, but some Drawbacks,” Proceedings REAL CORP: Change for stability: Lifecycles of Cities and Regions, Essen, 2011, pp. 1069-1077.

[6]   S. Henninger, “Urban Green and near Surface Ozone,” Proceedings Regional Geography: Climatology—Instituto Geografico Militar, 2011, pp. 78-87.

[7]   W. P. L. Carter, “Development of Ozone Reactivity Scales for Volatile Organic Compounds,” Journal of the Air and Waste Management Association, Vol. 44, 1994, pp. 881-899.

[8]   A. B. Guenther, R. L. Monson and R. Fall, “Isoprene and Monoterpene Emission Rate Variability: Observation with Eucalyptus and Emission Rage Algorithm Development,” Journal of Geophysical Research, Vol. 96, No. D6, 1991, pp. 10799-10808. doi:10.1029/91JD00960

[9]   W. Kuttler, “Climate Change in Urban Areas. Part 2, Measures,” Environmental Science Europe, Vol. 23, 2011, p. 21. doi:10.1186/2190-4715-23-21

[10]   P. J. Young, A. Arneth, G. Schurgers, G. Zeng and J. A. Pyle, “The CO2 Inhibition of Terrestrial Isoprene Emission Significantly Affects Future Ozone Projections,” Atmospheric Chemistry and Physics, Vol. 9, No. 8, 2009, pp. 2793-2803. doi:10.5194/acp-9-2793-2009

[11]   M. T. Benjamin and A. M. Winer, “Estimating the Ozone-Formating Potential of Urban Trees and Shrubs,” Atmospheric Environment, Vol. 32, No. 1, 1998, pp. 53- 68. doi:10.1016/S1352-2310(97)00176-3

[12]   H. Taha, “Modeling Impacts of Increased Urban Vegetation on Ozone Air Quality in the South Coast Air Basin,” Atmospheric Environment, Vol. 30, No. 20, 1996, pp. 3423-3430. doi:10.1016/1352-2310(96)00035-0

[13]   P. Venkatarchi and P. K. Hopke, “Development and Evaluation of a Particle-Bound Reactive Oxygen Species Generator,” Journal of Aerosol Science, Vol. 39, No. 2, 2008, pp. 168-174. doi:10.1016/j.jaerosci.2007.11.003

[14]   K. Apel and H. Hirt, “Reactive Oxygen Species: Metabolism, Oxidative Stress, and Signal Transduction,” Annual Review of Plant Biology, Vol. 55, 2004, pp. 373-399. doi:10.1146/annurev.arplant.55.031903.141701

[15]   I. J. George and J. P. D. Abbat, “Heterogeneous Oxida- tion of Atmospheric Aerosol Particles by Gas-Phase Radicals,” Nature Chemistry, Vol. 2, 2010, pp. 713-722. doi:10.1038/nchem.806

[16]   T. Franze, M. G. Weller, R. Niessner and U. P?schl, “Protein Nitration by Polluted Air,” Environmental Sci- ence Technology, Vol. 39, No. 6, 2005, pp. 1673-1678. doi:10.1021/es0488737

[17]   J. Fr?hlich-Nowoisky, D. A. Pickersgill, V. R. Despres and U. P?schl, “High Diversity of Fungi in Air Particulate Matter,” Proceedings of the National Academy of Science of the United States of America, Vol. 106, No. 31, 2009, pp. 12814-12819. doi:10.1073/pnas.0811003106

[18]   H. Sukopp and R. Wittig, “Stadt?kologie“, Gustav Fis- cher Press, Stuttgart, 1998.

[19]   S. Henninger, “A Mobile Measuring Methodology to Determine near Surface Carbon Dioxide within Urban Areas,” Air Quality—Models and Applications, 2011, pp. 173-194.

[20]   N. J. Brüggemann and J. P. Schnitzler, “Comparison of Isoprene Emission, Intercellular Isoprene Concentration and Photosynthetic Performance in Water-Limited Oak (Quercus pubescence Willd. and Quercus robur L.) Samplings,” Plant Biology, Vol. 4, 2008, pp. 456-463.

[21]   A. Strassburger, “Analyse Atmosph?rischer Spurengase zur Bestimmung des Lufthygienischen Erholungswertes Eines Urbanen Parks,” Ph.D. Thesis, University of Duis- burg-Essen, 2004.

[22]   A. Borbon, H. Fontaione, M. Veillerot, N. Locoge, J. C. Galloo and R. Guillermo, “An Investigation into the Traffic Related Fraction of Isoprene at an Urban Location,” Atmospheric Environment, Vol. 35, 2001, pp. 3749-3760.