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   Abstract
  Introduction
  Background
  Results
  Discussion
  Conclusion
  Acknowledgments
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ARTICLE  
Year : 2012  |  Volume : 14  |  Issue : 57  |  Page : 86-90
Occupational noise exposure and regulatory adherence in music venues in the United Kingdom

School of Technology, Maritime and Technology Faculty, Southampton Solent University, East Park Terrace, Southampton-United Kingdom, SO14 0RD, United Kingdom

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Date of Web Publication18-Apr-2012
 
  Abstract 

Noise in most working environments is an unwanted by-product of the process. In most countries, noise exposure for workers has been controlled by legislation for many years. In the music industry the "noise" is actually the "desired" product, and for a long time the UK entertainment industry was exempt from these regulations. From April 2008, however, it became regulated under the Noise at Work Regulations 2005, meaning that employers from orchestras to nightclubs are legally required to adhere to the same requirements (based on ISO 9612:2009) for controlling noise exposure for their staff that have been applied to other industries for many years. A key question is to what degree, 2 years after implementation, these employers are complying with their legal responsibilities to protect the staff from noise? This study assessed four public music venues where live and/or recorded music is regularly played. Thirty staff members in different roles in the venues were monitored using noise dosimetry to determine noise exposure. Questionnaires were used to determine work patterns, attitudes to noise and hearing loss, and levels of training about noise risk. Results showed that the majority of staff (70%) in all venues exceeded the daily noise exposure limit value in their working shift. Use of hearing protection was rare (<30%) and not enforced by most venues. The understanding of the hazard posed by noise was low, and implementation of the noise regulations was haphazard, with staff regularly exceeding regulatory limits. The implication is that the industry is failing to meet regulatory requirements.

Keywords: Music, NIHL, noise exposure, occupational noise, regulations, venues

How to cite this article:
Barlow C, Castilla-Sanchez F. Occupational noise exposure and regulatory adherence in music venues in the United Kingdom. Noise Health 2012;14:86-90

How to cite this URL:
Barlow C, Castilla-Sanchez F. Occupational noise exposure and regulatory adherence in music venues in the United Kingdom. Noise Health [serial online] 2012 [cited 2019 Jul 21];14:86-90. Available from: http://www.noiseandhealth.org/text.asp?2012/14/57/86/95137

  Introduction Top


The relationship between noise and hearing loss is well known and documented, [1],[2] and legislation has been in place in most countries for many years to control the exposure of workers to noise in the workplace. Regular personal noise exposure that gives an equivalent noise dose in excess of 80 dBA for an 8-hour period is likely to cause some hearing loss in a small proportion of listeners, [3] while daily noise exposure above 85 dBA (LEX 8H) is likely to cause some hearing loss in a large proportion of people. [4]

In the United Kingdom, the current regulations are the Control of Noise at Work Regulations 2005 (NaWR), which are aligned with Directive 2003/10/EC of the European parliament [5] and based on the recommendations of ISO 9612:2009. [6]

In the music industry, noise is the desired product rather than a by-product, and for a long time, the entertainment industry in Europe was exempt from the regulations, meaning that staff working in entertainment venues (such as music venues, cinemas, and outdoor festivals) were unprotected by legislation.

When NaWR was put in place the music industry was included in the provision. They were given a 2-year window to respond to the requirements of the legislation, and from April 2008 the music and entertainment industries became regulated under the control of NaWR 2005. [7] The regulations require employers in all area of the entertainment industry to adhere to the same action levels for controlling noise exposure that previously were applied to other industries such as construction. This includes a wide variety of staff and employment situations, from concert promoters, bar and security staff, and maintenance staff in the venue, to those involved in creating the music such as musicians and sound engineers. Freelance workers are also generally covered under the terms of the regulations (ibid).

High levels of sound have traditionally been an integral part of both the live music industry [8] and the nightclub industry, [9] as this is considered an integral part of the experience. Press publications regularly give positive publicity to particularly high sound levels - for example a review of a live festival in a music trade magazine includes comments such as "elevated the show to the next level and secured it as one of the UK's loudest outdoor dance festivals" . [10] Noise levels in live popular music and rock concerts have been shown by a number of authors to be around 105-110 dBA LA EQ over the duration of a concert, [11] with some large events and festivals reaching average levels of over 115 dBA. As many of the musicians, and more importantly the paying customers view high levels of sound in a positive manner, there is a low incentive to engage with the regulations. The key issue is whether over 2 years after the application of the noise regulations to the industry, the regulations are being applied, and if so to what degree.


  Background Top


In Europe, noise exposure for any given time uses the long-term average measure LA EQ (sometimes expressed as dBA Leq), which is used to calculate a "personal daily noise exposure" or L EX 8H which normalizes the exposure to an 8-hour working day, [12] Under the 3 dB "exchange rule" defined by the ISO, with each doubling of sound energy (an increase of 3 dB), the time taken to reach the maximum daily dose reduces by half. [6] Where noise exposure is highly variable, the measure may be normalized over a working week (five 8-hour days).

If an employee works in an environment in which he or she is exposed to an L EX 8H exceeding the "lower exposure action level" of 80 dBA the employer is obliged to provide a number of regulatory requirements. [12] These include the provision of optional noise protection, a range of monitoring programs including audiometry, and training in noise risk for employees. If the average sound level exceeds the "upper exposure action level" of 85 dBA, it is mandatory for the employer both to provide protection and to ensure that protection is worn, (ibid) as well as to use other controls to minimize exposure - for instance using engineering solutions and administrative options such as variation in working patterns. The mandatory upper limit for noise exposure of an employee (the exposure limit value or ELV) is 87 dBA L EX 8H . This must take into account the effects of any controls such as use of hearing protection. Monitoring must be undertaken if the workplace is likely to exceed the lower action level. In Europe, there are also controls on the levels of exposure to impulsive "peak" noise, with the lower exposure action level being 135 dBC, the upper exposure action level being 137 dBC, and the ELV being 140 dBC.

These regulations are common across many countries as the majority of noise regulations are based on ISO 9612:2009. However, these regulations are different from those in the USA, where both the measures and action levels vary, though the employer requirements are largely similar. The USA calculates a time-weighted average (TWA) [13] rather than L EX 8H . Use of TWA in itself has minimal effect on average exposure values; however, the exchange rule used under US legislation is 5 dB rather than 3 dB; this will give a lower value for an 8-hour TWA compared to L EX 8H for identical durations of exposure in excess of 85 dBA. In addition, the first action level is set at 85 dBA (8-hour TWA) (ibid) rather than 80 dBA.

The permitted exposure level in the USA is the equivalent to the upper exposure action level in Europe. This is currently set at 90 dBA (8-hour TWA). [13] As the exchange rules also differ, durations of exposure considered hazardous by the regulatory bodies of the European countries and the United States are considerably different, particularly as sound levels increase. For example, in an environment where noise levels reach 115 dBA, in Europe an unprotected employee would be considered to have reached maximum noise dose in 30 seconds, whereas the maximum duration of exposure at this level would be 15 minutes in the USA. Canadian legislation varies between jurisdictions, but the majority of jurisdictions use the 85 dBA TWA and the 3 dB exchange rule (with the exception of Quebec, which uses the 90 dBA TWA and 5 dB exchange rule). [14]

In the USA, the National Institute for Occupational Safety and Health (NIOSH) uses the 3 dB energy exchange rule and 8-hour 85 dBA permitted exposure level recommendation. Although this is based on a TWA, it is essentially the same as the ISO standards applied in Europe. [3] Their calculations of acceptable limits are therefore very close to the UK/EU regulations. It recommends that "levels at or above this level (85 dBA) are considered hazardous" [3:1].

Criteria

This study measured noise exposure levels across a number of small-to-medium size (capacity ~300-500) music venues where live and recorded music is played on a daily basis, to analyze the current occupational noise exposure on different employee roles in typical venues. In conjunction with the noise exposure measurements, the study used questionnaires also investigated levels of understanding and compliance by staff and employers with the Noise at work regulations in music venues and particularly focused on the following research questions:

  • The actual level of noise exposure of employees in the venues under investigation.
  • The level of understanding of the noise regulations among staff and management.
  • The degree to which employers and employees in these venues adhered to the regulations.
Noise dosimetry was used to measure personal noise exposure of a number of 30 different staff in separate roles working at eight events over a 6-month period. Each member of the staff was fitted with a Cirrus Research® Dosebadge TM model CR:110A for the duration of their shift. This was placed on the shoulder approximately 10 cm from the ear. Each meter had up to date manufacturer calibration, and was also calibrated immediately before use using the supplied calibration system built into the RC:110A reader unit (which complies with IEC 60942:2003 Class 2). Results were analyzed using the Cirrus Research dBLink3 software which provides time history reporting [Figure 1] and statistical analysis of results.
Figure 1: A typical time history plot of noise levels from dBlink3 software

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The understanding of the regulations by staff and the application of the regulatory requirements in the venues were assessed using an 11 point structured questionnaire, and also by semistructured interviews with staff.

Analysis

For the purpose of analysis, staff were subdivided by job role. These were broken down into the categories of group 1: bar and catering staff, group 2: technical staff, and group 3: promotional/security staff. As shift lengths varied, for each member of the staff, the noise exposure was normalized to an 8-hour personal noise dose (L EX 8H ), in line with ISO 9612:2009. In addition, exposure to peak impulse noise in dBC was also recorded.

Questionnaire responses were broken down by job category and venue. Responses were entered into a spreadsheet for statistical analysis. The sample of subjects consisted of 42% bar and catering staff, 38% technical staff, and the remaining 20% door and promotional staff. The general demographic was young, with 70% of the questionnaire respondents between the ages of 18 and 24, and only one respondent over the age of 50. A total of 73% of respondents were male and 27% female.


  Results Top


Personal noise doses (L EX 8H ) from a single work shift are presented for all employees in [Table 1]. Subjects are subdivided by venue and job category.
Table 1: Noise exposure for staff shifts sorted by occupation and venue

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  Discussion Top


Results showed that in total, 70% of the staff in all venues exceeded the daily noise exposure limit value for LA EQ in their working shift. Of the bar and catering staff, more than half exceeded the exposure limit value and only 15% (2 from 13) were under the lower action level of 80 dB LA EX [Figure 2], [Table 1]. None of the bar/catering staff at any venue wore any form of hearing protection at any time during the events being monitored. Despite the high levels of exposure, when questioned in semistructured interviews on site no member of the bar or catering staff in any of the venues could recall ever having used hearing protection at work.
Figure 2: Proportion of bar/catering staff within exposure

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Of the technical staff, all of those listed as sound engineers (84% of the group) were exposed to sounds in excess of the ELV during their working shift [Figure 3]. Despite the high levels only one sound engineer was observed used hearing protection, although the lighting engineer and stage engineer both used in-ear hearing protection (ER-20 TM type). Users of earplugs are marked by asterisk in [Table 1]. According to their specifications these attenuate sound by an average of 16 dB in higher frequencies (>2000 Hz) and 11 dB in lower frequencies. [15] However, research suggests that due to poor user fitting, attenuation from most earplugs will be at least 5 dB less than stated values, [16],[17] with some users gaining negligible benefit. For this reason NIOSH recommend derating earplugs by 50% (6 dB) from the manufacturer's specifications. [3] This indicates an attenuation of around 5-9 dB for these earplugs. Due to their high exposure, the stage engineer in venue 1 (100 dB LA EX exposure) and sound engineer in venue 3 (98.9 dB LAEX) are therefore not considered to be below ELV despite wearing earplugs.
Figure 3: Proportion of technical staff within exposure levels

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There were fewer door and promotional staff in the sample; however, of these, 3 out of 5 were in a position exposed to noise above the upper action level, and only one was wearing hearing protection.

Results from the questionnaires indicated that 75% of the staff had worked in the venue for more than a year, with the same proportion working part time (3 or fewer days per week). Mean part time hours were 16 hours per week, with a standard deviation of 7.4 hours. The full time staff worked between 30 and 49 hours per week.

Over 85% of subjects questioned had experienced symptoms identified as tinnitus (for instance "ringing" or "noises in the ears"') and 50% had experienced threshold shift (reported as "reduction in hearing level" or "muffled" hearing) at some point, with more than 75% of these reporting that this had occurred during or after a work shift.

A total of 61.5% of staff reported having been taught about the effects and levels of noise exposure at work. Despite this, 55% of staff (82% of the bar and catering staff, 60% of the door and promotional staff and 20% of the technical staff) did not think that hearing protection was available in the venue, while 70% of staff reported never using hearing protection, with 15% using it occasionally, and 15% regularly.

When the results are considered by venue, of the four venues, three venues had the majority of their staff exposed to levels over the ELV. In one venue, all bar and door staff were under the second action level, although the technical staff exceeded ELV. From the questionnaire analysis, it would appear that this result was not due to an effective implementation of the regulations for the bar and door staff, but was due to the construction of the venue in which the bar was separated from the main performance space. Of the other three venues, in two venues, all staff exceeded the upper action level - with most also exceeding ELV, while in the third only one member of the staff was below the upper action level.


  Conclusion Top


It is understandable that music venues feel the need to create high sound levels to satisfy audience requirements. However, employees working in these venues should not be put at a health risk. The Noise at work regulations had been in force for the music industry for over 2 years at the point of this study, yet these results show that in most cases the daily personal noise exposure level of these employees are well over the regulatory limits.

Potentially more importantly, the understanding of the regulations by staff and employers appears to be poor. Despite 61% of the staff reporting having had training, few employees were aware of the provision of hearing protection in their workplace, and there was no apparent attempt by employers or managers in the events monitored in this study to encourage or enforce the use of hearing protection in noisy areas. Despite the very high proportion of the staff reporting tinnitus and threshold shift after work shifts, only one venue appeared to be protecting nontechnical staff, and this was primarily due to the construction of the venue in which the bar was segregated from the live show. The technical staff in this venue were still exceeding regulatory limits without hearing protection. In the other three venues virtually all the staff exceeded ELV during their shift, with only the lighting/stage engineers making use of hearing protection.

There was also an apparent resistance to the wearing of hearing protection. When interviewed, some bar staff and sound engineers reported inability of carrying out the job as long as they wear hearing protection, due to communication difficulties and difficulty hearing or balancing the mix. Very few of the staff had been introduced to "musician's ear plugs" which reduce levels while keeping the tonal balance intact. [18]

In summary, from the events and venues monitored, elements of the music industry currently appear to be largely ignoring their legal responsibility to protect staff from high noise levels, despite high profile campaigns to inform and educate the industry. [7] In particular, the fact that the industry press gives positive publicity to particularly loud levels indicates a lack of concern for the potential health effects.

Given the large and expanding size of the live music industry, and the young average age of people working in this sector, this suggests a very high number of staff across this industry who are at risk of noise induced hearing loss in later life. These results indicate that a much more strenuous effort needs to be made to both educate workers and employers, and also to enforce the regulations where they are applicable, as implementation of the current regulation does not appear to be generally occurring.


  Acknowledgments Top


The authors gratefully acknowledge the participation of the subjects who took part in the survey, as well as the music venues which agreed to noise level measurements during public performances.

This study was conducted in accordance with the Research Ethics policy of Southampton Solent University, and was approved by the University Ethics Committee.

 
  References Top

1.Peters C, Thom J, Mcintyre E, McIntyre E, Winters M, Teschke K, et al. Noise and hearing loss in musicians. Vancouver, Canada: Safety and health in arts production and entertainment publications (SHAPE); 2005.  Back to cited text no. 1
    
2.RNID. Noise Exposure-The Facts. London, UK: Royal National institute for deaf people; 2009. Available from: http://www.rnid.org.uk/VirtualContent/101700/Noise_exposure_August_2009.pdf. [Last accessed on 2011 Oct 5].  Back to cited text no. 2
    
3.NIOSH. Criteria for a recommended standard: Occupational noise exposure, revised criteria 1998. Atlanta: National Institute for occupational safety and health, centers for disease control and prevention; 1998. Available from: http://www.cdc.gov/niosh/docs/98-126/. [Last accessed on 2010 Nov 16].  Back to cited text no. 3
    
4.SCENHIR. Potential health risks of exposure to noise from personal music players and mobile phones including a music playing function. Brussels: Scientific committee on emerging and newly identified health risks. European commission directorate general for health and consumers; 2008;23. Available from: http://ec.europa.eu/health/ph_risk/committees/04_scenihr/docs/scenihr_o_018.pdf. [[Last accessed on 2011 Oct 5].   Back to cited text no. 4
    
5.European Commission. Directive 2003/10/EC of the European parliament and of the council of 6 February 2003 on the minimum health and safety requirements regarding exposure of workers to the risks arising from physical agents (noise). Official Journal of the European Union, 15 Feb 2003. Available from: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri = OJ: L:2003:042:0038:0044: EN: PDF. [Last accessed on 2010 Nov 18].  Back to cited text no. 5
    
6.ISO. International organisation for standardization. Acoustics: Determination of occupational noise exposure-engineering method (ISO 9612:2009). Geneva: ISO Technical Committee; 2009.  Back to cited text no. 6
    
7.Health and Safety Executive. Sound advice-Control of noise at work in music and entertainment. Norwich, UK: HMSO Publications; 2008.  Back to cited text no. 7
    
8.Butterfield D. Measurement of noise levels that staff are exposed to at live music events. Norwich, UK: Health and Safety Executive/HMSO Publications; 2005.  Back to cited text no. 8
    
9.Smeatham D. Noise levels and noise exposure of workers in pubs and clubs-a review of the literature. Norwich, UK: Health and Safety Executive/HMSO publications; 2002.  Back to cited text no. 9
    
10.Low A. A phat dance party with a heart. London: Audio Pro International; 2009. p. 21-2.  Back to cited text no. 10
    
11.Barlow C. Potential hazard of hearing damage to students in undergraduate popular music courses. Med Probl Perform Art 2010;25:175-83.  Back to cited text no. 11
[PUBMED]    
12.Health and Safety Executive. The control of noise at work regulations 2005: guidance on regulations. Norwich UK: HMSO Publications; 2005.  Back to cited text no. 12
    
13.OSHA occupational safety and health standards: 29 cfr 1910.95 Occupational noise exposure. Washington, DC: department of labor, occupational safety and health administration; 2011. Available from: http://www.osha.gov/pls/oshaweb/owadisp.show_document?p_table = standardsandp_id = 973. [Last accessed on 2011 Apr 8].  Back to cited text no. 13
    
14.CCOHS. Occupational Exposure Limits in Canada. Hamilton, ON: Canadian Centre for Occupational Health and Safety: Noise. 2009. Available from: http://www.ccohs.ca/oshanswers/phys_agents/exposure_can.html. [Last accessed on 2010 Nov 16].  Back to cited text no. 14
    
15.ACS Ltd. Elacin ER-20s Specification sheet. Available from: http://www.hearingprotection.co.uk/images/specsheets/specsheeter20.jpg. [Last accessed on 2012 Jan 17].  Back to cited text no. 15
    
16.Witt BK. In-ear Dosimetry as a leading indicator of workplace hearing loss. In: Baines D, editor. Proceedings of Springnoise, 2011. Edmonton: Alberta Acoustical Association; 2011.  Back to cited text no. 16
    
17.Brueck L. Real World use and performance of hearing protection. Norwich, UK: The Health and Safety Executive/HMSO; 2009.  Back to cited text no. 17
    
18.Patel J. Musician's Hearing Protection-A Review. Norwich, UK: The health and safety executive/HMSO; 2008.  Back to cited text no. 18
    

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Correspondence Address:
Christopher Barlow
School of Technology, Southampton Solent University, East Park Terrace, Southampton, SO14 0RD
United Kingdom
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Source of Support: None, Conflict of Interest: None


DOI: 10.4103/1463-1741.95137

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