Experimental Investigation on the Discharge of Pollutants from Tunnel Fires

Many pollutants are generated during tunnel fires, such as smoke and toxic gases. How to control the smoke generated by tunnel fires was focused on in this paper. A series of experiments were carried out in a 1:10 model tunnel with dimensions of 6.0 m × 1.0 m × 0.7 m. The purpose was to investigate...

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Main Authors: Lihua Zhai, Zhongxing Nong, Guanhong He, Baochao Xie, Zhisheng Xu, Jiaming Zhao
Format: Article
Language:English
Published: MDPI AG 2020-02-01
Series:Sustainability
Subjects:
Online Access:https://www.mdpi.com/2071-1050/12/5/1817
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spelling doaj-22bb94071a33409db6ad15dea7433fea2020-11-25T02:15:06ZengMDPI AGSustainability2071-10502020-02-01125181710.3390/su12051817su12051817Experimental Investigation on the Discharge of Pollutants from Tunnel FiresLihua Zhai0Zhongxing Nong1Guanhong He2Baochao Xie3Zhisheng Xu4Jiaming Zhao5Guangzhou Metro Design and Research Institute Co., Ltd., Guangzhou 510000, ChinaGuangzhou Metro Design and Research Institute Co., Ltd., Guangzhou 510000, ChinaGuangzhou Metro Design and Research Institute Co., Ltd., Guangzhou 510000, ChinaInstitute of Disaster Prevention Science and Safety Technology, Central South University, Changsha 410075, ChinaInstitute of Disaster Prevention Science and Safety Technology, Central South University, Changsha 410075, ChinaInstitute of Disaster Prevention Science and Safety Technology, Central South University, Changsha 410075, ChinaMany pollutants are generated during tunnel fires, such as smoke and toxic gases. How to control the smoke generated by tunnel fires was focused on in this paper. A series of experiments were carried out in a 1:10 model tunnel with dimensions of 6.0 m × 1.0 m × 0.7 m. The purpose was to investigate the smoke layer thickness and the heat exhaust coefficient of the tunnel mechanical smoke exhaust mode under longitudinal wind. Ethanol was employed as fuel, and the heat release rates were set to be 10.6 kW, 18.6 kW, and 31.9 kW. The exhaust velocity was 0.32–3.16 m/s, and the longitudinal velocity was 0–0.47 m/s. The temperature profile in the tunnel was measured, and the buoyant flow stratification regime was visualized by a laser sheet. The results showed that the longitudinal ventilation leads to a secondary stratification of the smoke flow. In the ceiling extract tunnel under longitudinal ventilation, considering the research results of the smoke layer height and the heat exhaust coefficient, a better scheme for fire-producing pollutants was that an exhaust velocity of 1.26–2.21 m/s (corresponding to the actual velocity of 4.0–7.0 m/s) should be used. The longitudinal velocity should be 0.16–0.32 m/s (corresponding to the actual velocity of 0.5–1.0 m/s).https://www.mdpi.com/2071-1050/12/5/1817tunnel firepollutant controlsmoke layer heightheat exhaust coefficient
collection DOAJ
language English
format Article
sources DOAJ
author Lihua Zhai
Zhongxing Nong
Guanhong He
Baochao Xie
Zhisheng Xu
Jiaming Zhao
spellingShingle Lihua Zhai
Zhongxing Nong
Guanhong He
Baochao Xie
Zhisheng Xu
Jiaming Zhao
Experimental Investigation on the Discharge of Pollutants from Tunnel Fires
Sustainability
tunnel fire
pollutant control
smoke layer height
heat exhaust coefficient
author_facet Lihua Zhai
Zhongxing Nong
Guanhong He
Baochao Xie
Zhisheng Xu
Jiaming Zhao
author_sort Lihua Zhai
title Experimental Investigation on the Discharge of Pollutants from Tunnel Fires
title_short Experimental Investigation on the Discharge of Pollutants from Tunnel Fires
title_full Experimental Investigation on the Discharge of Pollutants from Tunnel Fires
title_fullStr Experimental Investigation on the Discharge of Pollutants from Tunnel Fires
title_full_unstemmed Experimental Investigation on the Discharge of Pollutants from Tunnel Fires
title_sort experimental investigation on the discharge of pollutants from tunnel fires
publisher MDPI AG
series Sustainability
issn 2071-1050
publishDate 2020-02-01
description Many pollutants are generated during tunnel fires, such as smoke and toxic gases. How to control the smoke generated by tunnel fires was focused on in this paper. A series of experiments were carried out in a 1:10 model tunnel with dimensions of 6.0 m × 1.0 m × 0.7 m. The purpose was to investigate the smoke layer thickness and the heat exhaust coefficient of the tunnel mechanical smoke exhaust mode under longitudinal wind. Ethanol was employed as fuel, and the heat release rates were set to be 10.6 kW, 18.6 kW, and 31.9 kW. The exhaust velocity was 0.32–3.16 m/s, and the longitudinal velocity was 0–0.47 m/s. The temperature profile in the tunnel was measured, and the buoyant flow stratification regime was visualized by a laser sheet. The results showed that the longitudinal ventilation leads to a secondary stratification of the smoke flow. In the ceiling extract tunnel under longitudinal ventilation, considering the research results of the smoke layer height and the heat exhaust coefficient, a better scheme for fire-producing pollutants was that an exhaust velocity of 1.26–2.21 m/s (corresponding to the actual velocity of 4.0–7.0 m/s) should be used. The longitudinal velocity should be 0.16–0.32 m/s (corresponding to the actual velocity of 0.5–1.0 m/s).
topic tunnel fire
pollutant control
smoke layer height
heat exhaust coefficient
url https://www.mdpi.com/2071-1050/12/5/1817
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