Assessment on Health and Ecosystem Impacts and Costs of Ozone Formation from Passenger Transport in Bangkok Metropolitan Region

Main Article Content

Atiporn Hathairat
Sirima Panyametheekul
Trakarn Prapaspongsa
Ekbordin Winijkul
Achariya Suriyawong
Heekwan Lee
Maywalin Jumsai Na Ayudhya
Vitoon Chotanapund

Abstract

Using life cycle assessment framework, this research aimed to estimate and compare the emission inventories, health and ecosystem impacts, and costs of ozone formation from passenger road, rail, and water transport in the Bangkok Metropolitan Region (BMR) in 2022 and in 2027. The study considered passenger cars, public buses, and motorcycles in the road transport; electric trains and rail cars in the public rail transport; and cross river ferries, Chao Phraya boats and Saen Saep canal boats in the public water transport. The ReCiPe 2016 method and Thai Spatially Differentiated Life Cycle Impact Assessment (ThaiSD) method were applied in the impact assessment taking into account health and ecosystem impacts from two ozone precursors - NOx and NMVOCs. Thai-specific factors were applied for assessing impacts from exhaust emissions in Thailand, while global average factors were applied for assessing impacts from the energy production. In 2022, total NOx emissions, NMVOCs emissions, health impacts, ecosystem impacts and costs from the passenger transport in BMR were 5.05E+04 tonnes, 2.61E+04 tonnes, 1.21E+03 DALY, 4.95E+00 species·yr and 1.94E+03 million Baht, respectively. In 2027, total NOx emissions, NMVOCs emissions, health impacts, ecosystem impacts and costs from the passenger transport in BMR will be 5.37E+04 tonnes, 2.91E+04 tonnes, 1.40E+03 DALY, 5.42E+00 species·yr and 2.32E+03 million Baht, respectively. The scenario analysis on the modal shifts from the business-as-usual situations of BMR in 2022 and 2027 to the public transport systems (buses, electric trains and water transport) was performed. Although the modal shifts to the public buses increased NOx emission, they could reduce NMVOCs emissions, health impacts, ecosystem impacts and costs. The modal shifts to the electric trains helped reduce NOx emissions, NMVOCs emissions, health impacts, ecosystem impacts and costs. The modal shifts to the water transport resulted in increasing the emissions, impacts and costs. This study suggests the promotion of public buses and electric trains and addresses the need to improve public water transport with low emission technologies in the future. 

Article Details

Section
Research Articles

References

Global Challenge Network on Tropospheric Ozone. 2020. Ecosystem effects of ozone. www.ozone-net.org.

Wittig, V. E., Ainsworth, E. A. and Long, S. P. 2007. To what extent do current and projected increases in surface ozone affect photosynthesis and stomatal conductance of trees? A meta-analytic review of the last 3 decades of experiments. Plant, Cell & Environment. 30(9): 1150-1162.

Health Effects Institute. 2020. State of Global Air 2020. Special Report. Boston. MA: Health Effects Institute.

Pollution Control Department. 2021. The state of air and noise pollution in Thailand 2021.

United State Environmental Protection Agency. 2022. Sources of Hydrocarbon and NOx Emissions in New England. Available at https://www3.epa.gov/region1/airquality/piechart.html.

Winijkul, E. and Punpukdee, P. 2022. Final Project Report "Improving Calculation in the Emission Inventory Management Platform".

Ministry of Transport. 2019. The 20-year strategy for the development of Thailand's transportation system (2018-2037).

Hauschild, M. and Huijbregts, M. 2015. Introducing Life Cycle Impact Assessment. In: Hauschild, M., Huijbregts, M. (eds) Life Cycle Impact Assessment. LCA Compendium – The Complete World of Life Cycle Assessment. Springer, Dordrecht.

Chavanaves, S., Fantke, P., Limpaseni, W., Attavanich, W., Panyametheekul, S., Gheewala, S. and Prapaspongsa, T. 2021. Health impacts and costs of fine particulate matter formation from road transport in Bangkok Metropolitan Region. Atmospheric Pollution Research. 12(10): 101191.

Sakpheng, P., Chavanaves, S., Mankhong, C., Saengdao, S., Limpaseni, W., Panyametheekul, S., Winijkul, E., Fantke, P., Gheewala, S. H. and Prapaspongsa, T. 2021. PM2.5 Footprint: a Tool for Enhancing Sustainable Passenger Transport. 8th International Conference on Green and Sustainable Innovation, Krabi, Thailand.

Office of Transport and Traffic Policy and Planning. 2018. Travel demand survey (final report).

European Environment Agency. 2019. EMEP/EEA air pollutant emission inventory guidebook 2019: technical guidance to prepare national emission inventories.

Winijkul, E. 2020. Development of Emissions Inventory for Inland Water Transport in Bangkok, Thailand (Final Report).

Huijbregts, M., Steinmann, Z., Elshout, P., Stam, G., Verones, F., Vieira, M., Zijp, M., Hollander, A. and Zelm, R. 2016. ReCiPe2016: a harmonised life cycle impact assessment method at midpoint and endpoint level. The International Journal of Life Cycle Assessment. 22: 138-147.

Huijbregts, M., Zelm, R. v., Steinmann, Z., Stam, G., Elshout, P., Vieira, M., Zijp, M. and Hollander, A. 2020. ReCiPe2016 country factors v1.1 20171221. Available at https://www.rivm.nl/documenten/recipe2016country-factorsv1120171221.

Prapaspongsa, T., Gheewala, S. H., Mankong, P., Rotthong, M., Sakpheng, P., Chavanaves, S., Balasuriya, T., Deuja, A. and Oo, P. Z. 2021. ThaiSD v1.0: Thai Spatially Differentiated Life Cycle Impact Assessment Method version 1.0 – Background Report.

Moreno Ruiz E., FitzGerald D., Symeonidis A., Ioannidou D., Müller J., Valsasina L., Vadenbo C., Minas N., Sonderegger T., and Dellenbach D. 2021. Documentation of changes implemented in the ecoinvent database v3.8.

Kaenchan, P. and Gheewala, S. H. 2017. Budget constraint and the valuation of environmental impacts in Thailand. The International Journal of Life Cycle Assessment. 22(11): 1678-1691.

Prapaspongsa, T., Jumsai Na Ayudhya, M., Sukuman, T. and Chavanaves, S. 2022. White Paper “PM2.5 and Health Impact Reduction Options for Road Transport in Bangkok Metropolitan Region”. Mahidol University.

Charernporn, P. 2014. NOx Emissions mitigation in a fluidized bed combustor firing biomass fuel. Silpakorn University.

Pollution Control Department. 2003. Adjustment and maintenance of large diesel engines to reduce pollution and save energy.

Semakula, M. and Inambao, F. 2018. The Formation, Effects and Control of Oxides of Nitrogen in Diesel Engines. International Journal of Applied Engineering Research. 13: 3200-3209.

Century Fuel Products. 2023. Fuel characteristics. Available at https://centuryfuelproducts.com/media/schematics/Fuel_Characteristics.pdf.

Suranaree University of Technology. 2016. Combustion Science. Available at http://eng.sut.ac.th/ae/ae2016/src/file/SubjectDocument/file/%E0%B8%9A%E0%B8%97%E0%B8%97%E0%B8%B5%E0%B9%88%202_1_1492766706.pdf.

Kulprasut, P. 2008. Gasoline engine theory. Chulalongkorn University Press.

Kulprasut, P. 2010. Diesel engine theory. Chulalongkorn University Press.

Berryman Products. 2023. What’s The Difference Between 2-Stroke & 4-Stroke Engines? Available at https://www.berrymanproducts.com/two-stroke-vs-four-stroke-engines/.

Edgar School District. 2023. Two-Cycle and Four-Cycle Engines. Available at https://www.edgar.k12.wi.us/faculty/mreinders/Chapter%205%20%202%20and% 204%20cycle%20engines.pdf.

Pollution Control Department. 2022a. 5-year action plan (2023-2027) of the Pollution Control Department. Available at https://www.pcd.go.th/wp-content/plugins/wonderplugin-pdf-embed/pdfjs/web/images/texture.png.

Office of Transport and Traffic Policy and Planning. 2022. Transport action plan in 2022 of Ministry of Transport. Available at https://www.otp.go.th/post/view/6124.

Pollution Control Department. 2022b. Annual Pollution Control Department action plan in 2022. Available at https://www.pcd.go.th/wp-content/plugins/wonderplugin-pdf-embed/pdfjs/web/images/texture.png.

Department of Land Transport. 2023. Number of new registered cars classified by fuel type. Available at https://web.dlt.go.th/statistics.