Domestic and international urban rail transit noise evaluation standards and regulations were investigated to develop a noise evaluation method with indexes and thresholds for urban rail transit underground station platforms in China. This comparison evaluates the similarities and differences in the evaluation methods, evaluation indexes and thresholds. The platform noise and vibrations at a typical underground station are measured during operating hours to identify the noise and vibration distributions at different locations on the platform. The results show that the noise levels are significantly greater at both ends of the platform than in the middle and that current noise evaluation methods do not accurately reflect the feelings of passengers at both ends of the platform. Thus, the noise levels at both ends should be considered when evaluating platform noise levels. The maximum A-weighted sound pressure at both ends of the platform is 88.4-90.4 dB(A) which annoys the passengers when superimposed on the platform vibrations. Thus, the maximum A-weighted sound pressure is recommended to serve as an auxiliary evaluation index. Field tests show that the equivalent continuous A-weighted sound pressure for 1 hour is 75.3-79.4 dB(A), which is higher than the environmental noise threshold along the railway line used in the current norms. This will impact passengers staying on the platform for a long time or staff working on the platform.
General Administration of Quality Supervision, Inspection and Quarantine, Standardization Administration of China. Acoustical requirement and measurement on station platform of urban rail transit: GB 14227-2006[S]. Beijing: Standards Press of China, 2006. (in Chinese)
9
ROSINGER G , NIXON C W , VON GIERKE H E . Quantification of the noisiness of "approaching" and "receding" sounds[J]. The Journal of the Acoustical Society of America, 1970. 48 (4A): 843- 853.
doi: 10.1121/1.1912212
11
?HRSTR?M E , SK?NBERG A B . A field survey on effects of exposure to noise and vibration from railway traffic, Part Ⅰ:Annoyance and activity disturbance effects[J]. Journal of Sound and Vibration, 1996. 193 (1): 39- 47.
doi: 10.1006/jsvi.1996.0244
State Bureau of Technical Supervision. Hygienic standard for waiting room of publictransit means: GB 9672-1996[S]. Beijing: Standards Press of China, 1996. (in Chinese)
Ministry of Environmental Protection. Environmental quality standards for noise: GB 3096-2008[S]. Beijing: China Environmental Science Press, 2008. (in Chinese)
National Environmental Protection Agency. Emission standards and measurement methods of railway noise on the boundary alongside railway line: GB 12525-1990[S]. Beijing: China Environmental Science Press, 1990. (in Chinese)
15
SEGAWA T, FUJIMOTO M, SAITO T, et al. Assessment of environmental noise immission in Japan[C]//The 2005 Congress and Exposition on Noise Control Engineering. Rio de Janeiro, Brazil: Institute of Noise Control Engineering, 2005.
16
HANSON C E, ROSS J C, TOWERS D A. High-speed ground transportation noise and vibration impact assessment[R]. Washington DC, USA: Department of Transportation, Federal Railroad Administration, 2005.
17
LAMBERT J , CHAMPELOVIER P , VERNET I . Annoyance from high speed train noise:A social survey[J]. Journal of Sound and Vibration, 1996. 193 (1): 21- 28.
doi: 10.1006/jsvi.1996.0241
18
KALIVODA M , DANNESKIOLD-SAMS?E U , KRüGER F , et al. EURailNoise:A study of European priorities and strategies for railway noise abatement[J]. Journal of Sound and Vibration, 2003. 267 (3): 387- 396.
doi: 10.1016/S0022-460X(03)00701-6
General Administration of Quality Supervision, Inspection and Quarantine, Standardization Administration of China. Acoustics: Assessment of noise annoyance by means of social and socio-acoustics surveys: GB/Z 21233-2007[S]. Beijing: Standards Press of China, 2008. (in Chinese)