Journals / Atmospheric Pollution Research / 2019 / Cilt: 10 - Sayı: 5

VOCs emission characteristics in motorcycle exhaust with different emission control devices

Pages
1498–1506
DOI
—
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

The ozone formation potentials of VOCs ranged from 500 mg-O3/m3 (FI motorcycle with TWC and OS, TO 20%) to 2218 mg-O3/m3 (CB motorcycle without control system, TO 30%).

📌 3 Key Takeaways

🎯
Objective & Hypothesis:Speciated VOCs and regulated air pollutant emissions (CO, HC and NO) of carburetor (CB) and fuel injection (FI) motorcycles were evaluated based on engine dynamometer tests.
📊
Key Findings & Data:Alkanes and aromatics had the highest concentrations contributing approximately 90% to the ΣVOC while xylene and toluene were most abundant among the BTEX, in both motorcycles.
💡
Conclusion & Impact:The ozone formation potentials of VOCs ranged from 500 mg-O3/m3 (FI motorcycle with TWC and OS, TO 20%) to 2218 mg-O3/m3 (CB motorcycle without control system, TO 30%).
🔬Design:Research Article
📍Scope:Comprehensive Sample
⚙️Variables:Domain Parameters

Özet

Speciated VOCs and regulated air pollutant emissions (CO, HC and NO) of carburetor (CB) and fuel injection (FI) motorcycles were evaluated based on engine dynamometer tests. Effects of engine loads and emission control systems were evaluated. CB was equipped with oxidation catalytic converter (OCC) and secondary air system (SAS) while FI had three-way catalytic converter (TWC) and oxygen sensor (OS). Under normal operation of the control devices, the emissions of regulated pollutants and the sum of detected VOCs (ΣVOC) were higher in CB than in FI motorcycle. Alkanes and aromatics had the highest concentrations contributing approximately 90% to the ΣVOC while xylene and toluene were most abundant among the BTEX, in both motorcycles. Emissions of all regulated pollutants and ΣVOC increased with increase in engine load. The emission control devices showed differential efficiencies on different VOC groups. Average emission reduction efficiencies of OCC with SAS (CB motorcycle) were 45.4% (ΣVOC) and 48.6% (BTEX) and TWC with OS (FI motorcycle) were 74.4% (ΣVOC) and 88.0% (BTEX). Without SAS, the efficiency of OCC dropped to 30.2% (ΣVOC) and 34.9% (BTEX) in CB motorcycle. Similarly, the efficiency of TWC reduced to 69.0% (ΣVOC) and 85.2% (BTEX) when the OS was blocked in FI motorcycle. The ozone formation potentials of VOCs ranged from 500 mg-O3/m3 (FI motorcycle with TWC and OS, TO 20%) to 2218 mg-O3/m3 (CB motorcycle without control system, TO 30%).

🔖

Cite This Article

DHİTAL, N. B., YANG, H., WANG, L., HSU, Y., ZHANG, H., YOUNG, L., LU, J. (2019). VOCs emission characteristics in motorcycle exhaust with different emission control devices. Atmospheric Pollution Research, Cilt: 10 - Sayı: 5, 1498–1506. https://ajindex.com/articles/197523

📄 Full Text PDF Viewer

📄

PDF görüntüleyici hazırlanıyor...

References (9)

  1. Alvarez, R., Weilenmann, M., Favez, J.Y., 2009. Assessing the real-world performance of modern pollutant abatement systems on motorcycles. Atmos. Environ. 43, 1503–1509. https://doi.org/10.1016/j.atmosenv.2008.11.046.
  2. Carbajo, J.C., Faiz, A., 1994. Motor vehicle emissions control: Some policy options for developing countries. Sci. Total Environ. 146–147, 11–18. https://doi.org/10.1016/ 0048-9697(94)90214-3.
  3. Carter, W.P.L., 2010. Updated Maximum Incremental Reactivity Scale and Hydrocarbon Bin Reactivities for Regulatory Applications. University of California, Riverside. Chan, C.C., Nien, C.K., Tsai, C.Y., Her, G.R., 1995. Comparison of tail-pipe emissions from motorcycles and passenger cars. J. Air Waste Manag. Assoc. 45 (2), 116–124. https:// doi.org/10.1080/10473289.1995.10467347. Chiang, H.L., Huang, P.H., Lai, Y.M., Lee, T.Y., 2014. Comparison of regulated air pollutant emission characteristics of real-world driving cycle and ECE cycle for motorcycles. Atmos. Environ. 87, 1–9. https://doi.org/10.1016/j.atmosenv.2013.12.031.
  4. Cussenot, C., Basseville, M., Aimard, F., 1996. Monitoring the vehicle emission system components. IFAC Proc. Vol. 29, 7808–7813. https://doi.org/10.1016/S1474- 6670(17)58948-X. Deng, C., Jin, Y., Zhang, M., Liu, X., Yu, Z., 2018. Emission characteristics of VOCs from on-road vehicles in an urban tunnel in eastern China and predictions for 2017-2026. Aerosol Air Qual. Res. 18, 3025–3034. https://doi.org/10.4209/aaqr.2018.07.0248.
  5. Dewulf, J., Langenhove, H.V., 1999. Anthropogenic volatile organic compounds in ambient air and natural waters: a review on recent developments of analytical methodology, performance and interpretation of field measurements. J. Chromatogr. A 843, 163–177. https://doi.org/10.1016/S0021-9673(99)00225-3.
  6. Hassani, A., Hosseini, V., 2016. An assessment of gasoline motorcycle emissions performance and understanding their contribution to Tehran air pollution. Transport. Res. Transport Environ. 47, 1–12. https://doi.org/10.1016/j.trd.2016.05.003.
  7. Hu, H., Xu, J., Shen, Q., Shi, F., Chen, Y., 2018. Travel mode choices in small cities of China: A case study of Changting. Transport. Res. Transport Environ. 59, 361–374. https://doi.org/10.1016/j.trd.2018.01.013.
  8. Hu, N., Tan, J., Wang, X., Zhang, X., Yu, P., 2017. Volatile organic compound emissions from an engine fueled with an ethanol-biodiesel-diesel blend. J. Energy Inst. 90, 101–109. https://doi.org/10.1016/j.joei.2015.10.003.
  9. Huang, C., Wang, H.L., Li, L., Wang, Q.