DURATION OF ELEMENTARY EVENTS IN THE STRUCTURE OF NOISE OF ROAD MOTION OF THE GREAT CITY
Abstract
To characterize the duration of the elementary events of noise increase or decrease due to the car passes by the noise meter, the autocorrelation functions were calculated on the serial samples of the street noise level registrations.
It was shown that the duration of mentioned transport flow events can be significantly larger than standard periods of 2-3 or 5-6 seconds prescribed for the registration of the street noise levels generated by the city transport.
Under these conditions the standard deviation of equivalent noise level assessments cannot be estimated by the use of the usual statistics.
Keywords: noise, noise pollution, auto-correlation function, road traffic.
References
Література
Schultz, T. (1978) Synthesis of social surveys on noise annoyance. J. Acoust. Soc., 64. 377–405.
Fidell, S., Barber, D., Schultz, T. (1991) Updating a dosage-effect relationship for the prevalence of annoyance due togeneral transportation noise. J. Acous.t Soc. Am., 89, 221–233.
Fields, J. (1999) An Updated Catalog of 360 Social Surveys of Residents Reactions to Envronmental Noise (1943–1993). Atlanta, GA: Georgia Institute of Technology.
Babisch, W., Ising, H., Elwood, P., Sharp, D.,& Bainton, D. (1993) Traffic noise and cardiovas cular risk: The Caerphilly and Speedwell studies, second phase. Risk estimation, prevalence and incidence of ischemic heart disease. Arch. Environ. Health,48, 406–413.
Miedema, H., Vos, H. (1998) Exposure-response relationships for transportation noise. J. Acoust. Soc. Am., 104(6), 3432–3445.
Directive 2002/49/EC of the European Parliament and of the Council of 25.06.2002 Relating to the Assessment and Management of Environmental Noise (2002) Official Journal of the European Communities, 189, 12–25.
Guidance Note for Noise (2016): Licence Applications, Surveys and Assessments in Relation to Scheduled Activities (NG4). Environmental Protection Agency, Office of Environmental Enforcement (OEE), 80.
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References
Schultz, T. (1978) Synthesis of social surveys on noise annoyance. J. Acoust. Soc., 64. 377–405.
Fidell, S., Barber, D., Schultz, T. (1991) Updating a dosage-effect relationship for the prevalence of annoyance due togeneral transportation noise. J. Acous.t Soc. Am., 89, 221–233.
Fields, J. (1999) An Updated Catalog of 360 Social Surveys of Residents Reactions to Envronmental Noise (1943–1993). Atlanta, GA: Georgia Institute of Technology.
Babisch, W., Ising, H., Elwood, P., Sharp, D.,& Bainton, D. (1993) Traffic noise and cardiovas cular risk: The Caerphilly and Speedwell studies, second phase. Risk estimation, prevalence and incidence of ischemic heart disease. Arch. Environ. Health,48, 406–413.
Miedema, H., Vos, H. (1998) Exposure-response relationships for transportation noise. J. Acoust. Soc. Am., 104(6), 3432–3445.
Directive 2002/49/EC of the European Parliament and of the Council of 25.06.2002 Relating to the Assessment and Management of Environmental Noise (2002) Official Journal of the European Communities, 189, 12–25.
Guidance Note for Noise (2016): Licence Applications, Surveys and Assessments in Relation to Scheduled Activities (NG4). Environmental Protection Agency, Office of Environmental Enforcement (OEE), 80.
Standard 20444-85 Noise. Transport flows. Methods for measuring noise performance (1985), 37.
Standard 23337-78. Noise. Methods of measuring noise in the residential area and in the premises of residential and public buildings (1984), 21.
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