Monitoring of Sound Pressure Level
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Definition and Measurement of Sound Energy Level of a Transient Sound Source
J. Acoust. Soc. Jpn. (E) 8, 6 (1987) Definition and measurement of sound energy level of a transient sound source Hideki Tachibana,* Hiroo Yano,* and Koichi Yoshihisa** *Institute of Industrial Science , University of Tokyo, 7-22-1, Roppongi, Minato-ku, Tokyo, 106 Japan **Faculty of Science and Technology, Meijo University, 1-501, Shiogamaguti, Tenpaku-ku, Nagoya, 468 Japan (Received 1 May 1987) Concerning stationary sound sources, sound power level which describes the sound power radiated by a sound source is clearly defined. For its measuring methods, the sound pressure methods using free field, hemi-free field and diffuse field have been established, and they have been standardized in the international and national stan- dards. Further, the method of sound power measurement using the sound intensity technique has become popular. On the other hand, concerning transient sound sources such as impulsive and intermittent sound sources, the way of describing and measuring their acoustic outputs has not been established. In this paper, therefore, "sound energy level" which represents the total sound energy radiated by a single event of a transient sound source is first defined as contrasted with the sound power level. Subsequently, its measuring methods by two kinds of sound pressure method and sound intensity method are investigated theoretically and experimentally on referring to the methods of sound power level measurement. PACS number : 43. 50. Cb, 43. 50. Pn, 43. 50. Yw sources, the way of describing and measuring their 1. INTRODUCTION acoustic outputs has not been established. In noise control problems, it is essential to obtain In this paper, "sound energy level" which repre- the information regarding the noise sources. -
The Psychophysiological Implications of Soundscape: a Systematic Review of Empirical Literature and a Research Agenda
International Journal of Environmental Research and Public Health Review The Psychophysiological Implications of Soundscape: A Systematic Review of Empirical Literature and a Research Agenda Mercede Erfanian * , Andrew J. Mitchell , Jian Kang * and Francesco Aletta UCL Institute for Environmental Design and Engineering, The Bartlett, University College London (UCL), Central House, 14 Upper Woburn Place, London WC1H 0NN, UK; [email protected] (A.J.M.); [email protected] (F.A.) * Correspondence: [email protected] (M.E.); [email protected] (J.K.); Tel.: +44-(0)20-3108-7338 (J.K.) Received: 16 September 2019; Accepted: 19 September 2019; Published: 21 September 2019 Abstract: The soundscape is defined by the International Standard Organization (ISO) 12913-1 as the human’s perception of the acoustic environment, in context, accompanying physiological and psychological responses. Previous research is synthesized with studies designed to investigate soundscape at the ‘unconscious’ level in an effort to more specifically conceptualize biomarkers of the soundscape. This review aims firstly, to investigate the consistency of methodologies applied for the investigation of physiological aspects of soundscape; secondly, to underline the feasibility of physiological markers as biomarkers of soundscape; and finally, to explore the association between the physiological responses and the well-founded psychological components of the soundscape which are continually advancing. For this review, Web of Science, PubMed, Scopus, and -
Noise Exposure Limit for Children in Recreational Settings: Review of Available Evidence
Noise exposure limit for children in recreational Make Listening Safe settings: review of WHO available evidence This document presents a review of existing evidence on risk of noise induced hearing loss due to exposure to sounds in recreational settings, with respect to children. The evidence was used to stimulate discussion for determination of exposure limits (in children) to be applied to standards for personal audio devices. The review has been undertaken by February 2018 Dr Benjamin Roberts under the supervision of Dr Richard Neitzel, in collaboration with WHO. The document has been reviewed by members of WHO expert group on exposure limits for NIHL in recreational settings. Noise exposure limit for children in recreational settings: review of available evidence Authors: Dr Benjamin Roberts Dr Richard Neitzel Reviewed by: Dr Brian Fligor Dr Ian Wiggins Dr Peter Thorne 1 Contents List of Tables 1 List of Figures 1 Definitions and Acronyms ............................................................................................................................. 2 Executive Summary ....................................................................................................................................... 3 Background and Significance ........................................................................................................................ 4 How Noises is Assessed............................................................................................................................. 5 Overview of the Health -
Soundscape Mapping in Environmental Noise Management and Urban Planning
This is a repository copy of Soundscape mapping in environmental noise management and urban planning. White Rose Research Online URL for this paper: http://eprints.whiterose.ac.uk/128385/ Version: Published Version Article: Margaritis, E. and Kang, J. orcid.org/0000-0001-8995-5636 (2017) Soundscape mapping in environmental noise management and urban planning. Noise Mapping (4). 1. pp. 87-103. ISSN 2084-879X https://doi.org/10.1515/noise-2017-0007 Reuse This article is distributed under the terms of the Creative Commons Attribution-NonCommercial-NoDerivs (CC BY-NC-ND) licence. This licence only allows you to download this work and share it with others as long as you credit the authors, but you can’t change the article in any way or use it commercially. More information and the full terms of the licence here: https://creativecommons.org/licenses/ Takedown If you consider content in White Rose Research Online to be in breach of UK law, please notify us by emailing [email protected] including the URL of the record and the reason for the withdrawal request. [email protected] https://eprints.whiterose.ac.uk/ Noise Mapp. 2017; 4:87ś103 Research Article Efstathios Margaritis* and Jian Kang Soundscape mapping in environmental noise management and urban planning: case studies in two UK cities https://doi.org/10.1515/noise-2017-0007 tentional design process comparable to landscape and to Received Dec 22, 2017; accepted Dec 28, 2017 introduce the theories of soundscape into the design pro- cess of urban public spaces”. Lately, suggestions of ap- plied soundscape practises were introduced in the Master plan level thanks to the initiative of the local authorities. -
5. Noise Pollution
5. Noise pollution 1. Please describe the present situation and development over the last five to ten years in relation to (max. 1,000 words): Within the scope of implementing “Directive 2002/49/EC of the European Parliament and the Council of 25 June 2002, relating to the assessment and management of environmental noise”, the proportion of Hamburg’s population subjected to noise emanations from road, railway and air traffic sources as well as industrial, commercial and port facilities has been determined in terms of the noise indicators L den, for noise levels during the day, evening and night, and L night, for noise levels at night. The assessment was calculated on the basis of national provisional computation methods; namely, the “Provisional computation method for environmental noise on roads – VBUS”, the “Provisional computation method for environmental noise on railways – VBUSch”, the “Provisional computation method for environmental noise at airports – VBUF”, the “Provisional computation method for environmental noise from industry and commercial facilities – VBUI”, and the “Provisional computation method for determining the number of individuals exposed to environmental noise – VBEB”. In terms of the industrial, commercial and port sector, in addition to plants located in the port area, only those industrial or commercial zones with one or more plants as per Appendix 1 of the “European Council Directive 96/61/EC of 24 September 1996 concerning integrated pollution prevention and control” are afforded consideration. The period of reference is 2006. Accordingly, the number of individuals affected is as follows: Affected by L den > Affected by L night > 55 dB(A) 45 dB(A) Road traffic 363600 420900 Rail traffic 56200 38900 (L night > 50 dB(A)) Air traffic 43700 5000 (L night > 50 dB(A)) Industry/commercial 4200 10200 /port facilities In line with the requirements of the EU directive, the analyses are updated at least every 5 years, from which commensurate developments regarding issues of concern can be ascertained. -
Measurement of Total Sound Energy Density in Enclosures at Low Frequencies Abstract of Paper
View metadata,Downloaded citation and from similar orbit.dtu.dk papers on:at core.ac.uk Dec 17, 2017 brought to you by CORE provided by Online Research Database In Technology Measurement of total sound energy density in enclosures at low frequencies Abstract of paper Jacobsen, Finn Published in: Acoustical Society of America. Journal Link to article, DOI: 10.1121/1.2934233 Publication date: 2008 Document Version Publisher's PDF, also known as Version of record Link back to DTU Orbit Citation (APA): Jacobsen, F. (2008). Measurement of total sound energy density in enclosures at low frequencies: Abstract of paper. Acoustical Society of America. Journal, 123(5), 3439. DOI: 10.1121/1.2934233 General rights Copyright and moral rights for the publications made accessible in the public portal are retained by the authors and/or other copyright owners and it is a condition of accessing publications that users recognise and abide by the legal requirements associated with these rights. • Users may download and print one copy of any publication from the public portal for the purpose of private study or research. • You may not further distribute the material or use it for any profit-making activity or commercial gain • You may freely distribute the URL identifying the publication in the public portal If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim. WEDNESDAY MORNING, 2 JULY 2008 ROOM 242B, 8:00 A.M. TO 12:40 P.M. Session 3aAAa Architectural Acoustics: Case Studies and Design Approaches I Bryon Harrison, Cochair 124 South Boulevard, Oak Park, IL, 60302 Witew Jugo, Cochair Institut für Technische Akustik, RWTH Aachen University, Neustrasse 50, 52066 Aachen, Germany Contributed Papers 8:00 The detailed objective acoustic parameters are presented for measurements 3aAAa1. -
What to Do About Environmental Noise?
What To Do About Environmental Noise? Enda Murphy The evidence linking environmental noise to negative human health out- Postal: comes is increasing. As a pollution problem, is it taken seriously? School of Architecture, Planning and Environmental Policy Environmental noise is a difficult concept to define. This is due to noise being Planning Building, Richview somewhat subjective to humans depending on their perceptions of specific sounds. University College Dublin We know, for example, that trains, automobiles, and aircraft producing sounds at Dublin 4 the same decibel level are all perceived differently when self-reported scores are Ireland utilized to assess annoyance for each mode (Lam et al., 2009). There is also evi- dence that noise from trains is less annoying than noise from aircraft or automo- Email: biles. So although definitions can be slippery, they are important nevertheless for [email protected] placing boundaries around individual concepts, particularly if scholars, acousti- cians, and policymakers are to understand the nature of environmental noise and its impact on human beings. At a very basic level, definitions determine how noise is assessed, regulated, and mitigated as an environmental problem. Moreover, defi- nitions are crucial if governments, national, and supranational organizations are to work together in a holistic manner to reduce environmental noise in the future. Environmental noise is any unwanted sound created by human activities that is considered harmful or detrimental to human health and quality of life (Murphy et al., 2009); it results from human interaction with the natural environment. It refers only to noise affecting humans and is typically (but not exclusively) asso- ciated with outdoor sound produced by transport, industry, and/or recreational activities. -
Mobile Applications for Environmental Noise and Soundscape Evaluation
Mobile applications for environmental noise and soundscape evaluation Radicchi, Antonella1 Institute of City and Regional Planning, Technical University of Berlin Hardenbergstraße 40 a Sekr. B 4 – 10623 Berlin ABSTRACT In the past ten years, in parallel to the development of low-cost digital technology, we witnessed the increasing development of mobile applications deployed as environmental noise and soundscape evaluation tools. Firstly, this paper presents the results of a survey conducted through literature and market review covering the past 10 years, spanning from the release of the first app, Noise Tube, to the more recent ones, such as Hush City. Secondly, it discusses the benefits and challenges of using mobile apps for environmental noise and soundscape projects. In conclusion, considering the release of ISO norms on soundscape, it discusses the possibility to standardize the design and implementation of mobile apps for soundscape research. Keywords: Soundscape, Mobile Apps, Citizen Science I-INCE Classification of Subject Number: 66, 70, 81 _______________________________ 1 [email protected] 1. INTRODUCTION The interest for the acoustic environment of cities, its impact on human health, well-being and quality of life and its implication on design and policy planning has a rather long history that can be traced back to the anti-noise movements of the late XIX centuries and more recently to the so-called soundscape studies stemming from the research conducted by Michael Southworth in the US and by Murray Schafer in Canada in the late Sixties of the XX century1. In order to study and evaluate the characteristics of the acoustic environment different indicators, tools and methods have been developed in the course of the decades (e.g. -
Appendix A1 Discussion of Noise and Its Effects on the Environment
NAS Whidbey Island Complex Growler FEIS, Volume 2 September 2018 Appendix A1 Discussion of Noise and Its Effects on the Environment A1‐1 Appendix A1 NAS Whidbey Island Complex Growler FEIS, Volume 2 September 2018 This page intentionally left blank. A1-2 Appendix A1 NAS Whidbey Island Complex Growler FEIS, Volume 2 September 2018 Acknowledgements This review of noise and its effects on the environment was prepared by Wyle Laboratories, Inc., with contributions from Blue Ridge Research and Consulting LLC and Ecology and Environment, Inc. A1-3 Appendix A1 NAS Whidbey Island Complex Growler FEIS, Volume 2 September 2018 This page intentionally left blank. A1-4 Appendix A1 NAS Whidbey Island Complex Growler FEIS, Volume 2 September 2018 TABLE OF CONTENTS A1 DISCUSSION OF NOISE AND ITS EFFECTS ON THE ENVIRONMENT ....................................... A1-11 A1.1 Basics of Sound ............................................................................................................... A1-11 A1.1.1 Sound Waves and Decibels .................................................................................. A1-11 A1.1.2 Sound Levels and Types of Sounds ...................................................................... A1-14 A1.1.3 Low-Frequency Noise .......................................................................................... A1-15 A1.2 Noise Metrics .................................................................................................................. A1-16 A1.2.1 Single Events ....................................................................................................... -
Environmental Noise
Environmental Noise Issue 29 November 2011 Editorial Contents Page Traffic noise causes loss of over one million Steps to reduce noise pollution: for a healthy life years 4 healthier environment Up to 1.6 million healthy life years could be lost annually as a result of the impact of traffic noise in western Europe, says a recent report. Noise pollution is among the most common complaints regarding environmental issues in Europe, especially in densely populated and Cognitive impairment caused by aircraft residential areas near major roads, railways and airports. But noise noise: school versus home 5 - unwanted sound - is more than a mere annoyance, even at levels Children’s exposure to aircraft noise during the day has more impact than sleep-disruption caused below ear damaging volumes. It disturbs sleep, affects cognitive by exposure to aircraft noise during the night. functions in children, causes physiological stress reactions and can lead to cardiovascular health problems, including artery disease Noise maps suggest too many people (atherosclerosis), high blood pressure and heart disease, for those exposed to damaging noise levels 6 exposed to it on a repeated, long-term basis. Researchers explain how they have assessed population exposure to noise and calculated the impacts of several noise reduction measures. The EU’s Environmental Noise Directive (END) has initiated action plans in Member States to reduce environmental noise exposure Is the public really becoming more annoyed and its effects. This Thematic Issue reports on recent research to by aircraft noise? 7 help guide effective noise action plans throughout Europe. Increasing complaints about aircraft noise could partly be caused by changes in survey methods and participants, says a recent study. -
Environmental Noise Monitoring Top 10 Things You Need to Know for Your Measurements
ENVIRONMENTAL NOISE MONITORING TOP 10 THINGS YOU NEED TO KNOW FOR YOUR MEASUREMENTS larsondavis.com | +1 716.926.8243 1. FAST VS SLOW 2. FREQUENCY TIME WEIGHTINGS WEIGHTINGS The time weighting selected determines the response speed of Frequency weightings are common, special frequency filters that the sound level meter when reacting to changes in noise level. adjusts the amplitude of all parts of the frequency spectrum of the This dates back to the days of analog sound level meters, which sound or vibration had a needle moving back and forth to give a reading. The needle ■ A-Weighting: A weighting filter that most closely matches would be in constant motion as sound pressure levels quickly how humans perceive sound, especially low to moderate changed. Early sound level meters damped the movement of the levels. This weighting is most often used for evaluation of needle to make the meter easier to read. Different meters could environmental sounds. Notated by the “A” in measurement display different results depending on the properties of the needle. parameters including dBA, L , L , L , etc. Eventually, the standards of slow, fast, and impulse time weightings Aeq AF AS were developed to help standardize readings. ■ C-Weighting: Commonly used filter that adjusts the levels of a frequency spectrum in the same way the human Although the current IEC 61672-1 standard includes Fast and Slow ear does when exposed to high or impulsive levels of time weightings, modern digital meters include the three described sound. This weighting is most often used for evaluation of here so modern measurements can be compared with tests done in equipment sounds. -
Aircraft Noise (Excerpt from the Oakland International Airport Master Plan Update – 2006)
Aircraft Noise (Excerpt from the Oakland International Airport Master Plan Update – 2006) Background This report presents background information on the characteristics of noise. Noise analyses involve the use of technical terms that are used to describe aviation noise. This section provides an overview of the metrics and methodologies used to assess the effects of noise. Characteristics of Sound Sound Level and Frequency — Sound can be technically described in terms of the sound pressure (amplitude) and frequency (similar to pitch). Sound pressure is a direct measure of the magnitude of a sound without consideration for other factors that may influence its perception. The range of sound pressures that occur in the environment is so large that it is convenient to express these pressures as sound pressure levels on a logarithmic scale that compresses the wide range of sound pressures to a more usable range of numbers. The standard unit of measurement of sound is the Decibel (dB) that describes the pressure of a sound relative to a reference pressure. The frequency (pitch) of a sound is expressed as Hertz (Hz) or cycles per second. The normal audible frequency for young adults is 20 Hz to 20,000 Hz. Community noise, including aircraft and motor vehicles, typically ranges between 50 Hz and 5,000 Hz. The human ear is not equally sensitive to all frequencies, with some frequencies judged to be louder for a given signal than others. See Figure 6.2. As a result of this, various methods of frequency weighting have been developed. The most common weighting is the A-weighted noise curve (dBA).