Influence of Traffic Flow Patterns on Air Quality inside the Longest Tunnel in Asia

The long tunnel is a fixed, semi-closed environment where excessive concentrations of air pollutants are easily accumulated. This can potentially have a serious affect on drivers' health, especially when operating vehicles in the long tunnel for a lengthy period of time. Therefore, studies on pollutant emission characteristics and influential factors of emission in the tunnel are important. In this study, several sampling sites were arranged in the 12.9 km long Hsueh-shan Tunnel, to help understand the piston effect of pollutant emission characteristics and spatial concentration distribution. In order to understand the influential factor of air quality in the long tunnel, several tests were run during a closed period, an open period, a non-rush hour period, and a rush hour period. The results showed that during the closed period, the CO, SO2, NOx, and PM10 concentrations in the Hsueh-shan Tunnel were in the range of: 0.58–0.64 ppm, 0.94–1.08 ppb, 6.33–7.11 ppb, and 45.4–54.3 μg/m 3 , respectively. In contrast, during the open period, the CO, SO2, NOx, and PM10 concentrations reached 12–39 ppm, 20–48 ppb, 1.2–3.1 ppm, and 75–177 μg/m 3 , respectively. In the Hsueh-shan Tunnel, the number of vehicles at rush hour was about 1400 per hour, three times higher than during non-rush hour. The piston effect is very obvious since pollutant concentrations are elevated with increasing distance from the inlet. This study found that the pollutant concentration near the outlet can be three times higher than that near the inlet.

[1]  Shuenn-Chin Chang,et al.  On-road emission factors from light-duty vehicles measured in Hsuehshan Tunnel (12.9 km), the longest tunnel in Asia , 2009, Environmental monitoring and assessment.

[2]  Wan Ki Chow,et al.  Field measurement on transient carbon monoxide levels in vehicular tunnels , 2003 .

[3]  F. D. Sutterfield,et al.  HYDROCARBON COMPOSITION OF URBAN AIR POLLUTION , 1974 .

[4]  D. Peden Pollutants and asthma: role of air toxics. , 2002, Environmental health perspectives.

[5]  J L Mauderly Toxicological and epidemiological evidence for health risks from inhaled engine emissions. , 1994, Environmental health perspectives.

[6]  Peter F. Nelson,et al.  NON-METHANE EXHAUST COMPOSITION IN THE SYDNEY HARBOUR TUNNEL: A FOCUS ON BENZENE AND 1,3-BUTADIENE , 1996 .

[7]  Ute Pott,et al.  Use of Tracer Gas for Direct Calibration of Emission-Factor Measurements in a Traffic Tunnel. , 1998, Journal of the Air & Waste Management Association.

[8]  W. T. Davis,et al.  Air Pollution: Its Origin and Control , 1976 .

[9]  Xiao-Feng Huang,et al.  Fine particle emissions from on-road vehicles in the Zhujiang Tunnel, China. , 2008, Environmental science & technology.

[10]  R. Seila,et al.  Non-methane organic composition in the Lincoln Tunnel. , 1986, Environmental science & technology.

[11]  Martin Weilenmann,et al.  NO2/NO emissions of gasoline passenger cars and light-duty trucks with Euro-2 emission standard , 2003 .

[12]  Michael R Cayo,et al.  Childhood asthma hospitalization and residential exposure to state route traffic. , 2002, Environmental research.

[13]  T. Y. Chen,et al.  Investigations of piston-effect and jet fan-effect in model vehicle tunnels , 1998 .

[14]  Barbara Zielinska,et al.  Real-world automotive emissions—Summary of studies in the Fort McHenry and Tuscarora mountain tunnels , 1995 .

[15]  Jan Beyea,et al.  Airborne Emissions from 1961 to 2004 of Benzo[a]pyrene from U.S. Vehicles per km of Travel Based on Tunnel Studies , 2008, Environmental science & technology.

[16]  Lo-Yin Chan,et al.  Carbon monoxide levels measured in major commuting corridors covering different landuse and roadway microenvironments in Hong Kong , 2002 .

[17]  On-road measurements of ultrafine particle concentration profiles and their size distributions inside the longest highway tunnel in Southeast Asia , 2010 .