This is the full thesis, written for an undergraduate physics audience. A PDF version is available HERE (right click and select "Save As").





 

SENIOR THESIS

 

Noise exposure associated with marching and pep bands:
 measurements, assessment of risks, and possible solutions

 

 

 

 

 

Joseph Keefe

Dr. Dewey Lawson, faculty advisor

Duke University Department of Physics


 




ABSTRACT

            High school and college marching bands routinely rehearse and perform in a number of locations, including band rooms, auditoriums, practice fields, and football stadiums. Each of these common locations, as well as others unique to specific ensembles, provides varying risk of hearing loss.

A Larson Davis System 824 Precision Sound Level Meter and Real Time Analyzer was used to record A-weighted sound pressure levels while bands rehearsed and performed. At all times during measurements the researcher wore ER-25 flat response musician’s earplugs. The microphone of the System 824 was either placed on a tripod or affixed to an extension, depending on whether the measurement was inside or outside, moving or stationary; the goal in all cases was to place the microphone as close to the subjects' ears as possible without interfering with their duties as band members. The researcher marched extensively with the bands to gather data in a realistic environment.

Using NIOSH recommendations for safe occupational exposure, data are presented according to whether they present no risk for the duration of the measurement or the estimated exposure time, risk for the estimated exposure time but not the duration of the measurement, or risk for both the duration of the measurement and the estimated exposure time. Specific locations in the bands as well as different situations (indoor and outdoor rehearsals and performances, drums only, rehearsals without the drumline, etc.) are analyzed. In addition, an acoustical analysis of a rehearsal hall demonstrates that acoustical modifications to the room would be unsuccessful in reducing exposure levels.

Resulting data indicate a significant risk of short- and long-term hearing loss as a result of rehearsing and performing with marching bands. Exposures that would be considered illegal in the workplace are accepted as commonplace in educational environments. Students and band directors must take steps to recognize the risk posed by various instruments and various locations on the field, and must implement hearing conservation efforts.

 

 

An Introduction to Marching Bands

The contemporary marching band originates from battlefield drums and bugles used in eighteenth and nineteenth century military conflicts. Previously intended to communicate information (march, retreat, go to sleep, etc.), marching bands now exist solely for the purpose of musical entertainment. A modern marching band consists of woodwinds (flute, clarinet, saxophone), brass (trumpet, trombone, mellophone, baritone, tuba; low brass includes all brass except for the trumpet), marching percussion (snare drum, tenors, bass drum, cymbals), and pit percussion (xylophone, vibraphone, suspended cymbals, bongos, tambourine etc.; i.e. anything that cannot be marched on a field).

Marching bands also act as pep bands at football and basketball games, remaining stationary and playing music to excite the crowd. Sometimes a drumset is played in a pep band in place of marching percussion instruments.

Today marching bands are easily recognizable from their performances at the Macy’s Thanksgiving Day Parade, their appearances on ESPN commercials (i.e. Ohio State and Michigan), feature films such as Drumline, and infamous incidents such as the 1982 California–Stanford game where the Stanford band was caught on the field during the final play and a particularly unfortunate trombone player was run over by a California ball carrier. Beyond the high-profile appearances for a select few, thousands of high school and college bands rehearse and perform throughout the football season on a daily or weekly basis.

A marching band typically performs during halftime at football games, with each member marching to a set of precise locations, called drill spots, on the football field. One set of simultaneous spots on the field for each band member is called a drill set, and a full-length halftime show (usually seven to ten minutes in duration) contains anywhere from fifteen to forty-five sets (also called pages of drill, because drill for a halftime show is distributed in a packet of full-page drill diagrams).

Below is a typical page of drill; it is drawn with the home sideline at the bottom of the page. The yard lines found on a football fields are clearly labeled, as are the home and visitor hash marks (each 17.5 yards from the sidelines in high school football); the end zones are excluded. Each grid box on the drill chart represents 2.5 yards, or 4 standardized marching band steps; a standardized step is 22.5”, and is called an “8-to-5” step because 8 steps of the correct size will move a band member 5 yards. Individual band members are labeled with specific letter/number combinations, and to learn their drill they learn the position of their numbers as fixed distances from yard lines, sidelines, and hash marks, and as positions relative to other band members. Other information found on a page of drill includes the page number in that set of drill (the chart below is the 12th page in a set), measure numbers, counts for moves and halts, and other specific instructions.

A typical drill chart.1  

 

ACOUSTICAL TERMINOLOGY

Sound Pressure Level

Humans judge the relative loudness of two sounds by the ratio of their intensities. As a result, and because audible sound intensities range from approximately 10-12 W/m2 to 10 W/m2, it is appropriate to use a logarithmic scale to express these quantities. The most commonly used scale is called the decibel scale. Decibels (dB) are expressed in reference to a specified value. For sounds transmitted through air, this reference intensity is 10-12 W/m2, the approximate intensity of a 1000 Hz tone that is barely audible to someone with completely unimpaired hearing2 (i.e. an adolescent female).  Sound pressure level (SPL) “is a measure of the amplitude of the pressure change that produces the sound. This amplitude is perceived by the listener as loudness" 3. For sound waves with an effective pressure amplitude P and reference quantity Pref, the sound pressure level is

 

                        SPL = 10 log10 (P/ Pref) 2

 

and is expressed as “dB re Pref " 4. When the standard reference pressure corresponding to an intensity of 10-12 W/m2 is used, the statement of reference value is unnecessary, and is usually omitted by convention. Below are some typical SPLs of easily recognized sound sources.

 

SPL (dB)

Typical Sound

120

Jet aircraft takeoff at 60m

110

Construction site

100

Shout at 1.5m

90

Heavy Truck at 15m

80

Urban street

70

Automobile interior

60

Normal conversation at 1m

50

Office / classroom

40

Living room

30

Bedroom at night

20

Broadcast studio

10

Rustling leaves

Table 1: Sound pressure levels of typical sounds. 5

 

Pain and audibility thresholds for the human ear are shown below.

Approximate range of frequency and sound level of music compared to the total range of hearing.6

 

                        Decibel Scales

            Human hearing has a frequency range from 20 Hz to 20,000 Hz and is most sensitive at 2700 Hz (the lowest natural resonance of the ear canal)7and least sensitive at low frequencies. To adjust the response of a sound level meter, frequency-weighting scales are used. The most often used weighting scale (and the scale used in almost all noise standards) is the A scale, expressed as dBA or dB(A); it approximates the response of the human ear to moderate level sounds and includes a large low-frequency drop-off. The C scale approximates the response to high level sounds, and incorporates small drop-offs at both low and high frequencies. Despite the fact that this study deals with high level sounds, A weighting is used throughout for comparison with noise exposure standards.

 

Octave-center Frequency (Hz)

 

Weighted Response (dB)

 

A scale

C scale

 

 

 

 

31.5

 

-39.4

-3.0

63

 

-26.2

-0.8

125

 

-16.1

-0.2

250

 

-8.6

0

500

 

-3.2

0

1000

 

0

0

2000

 

1.2

-0.2

4000

 

1.0

-0.8

8000

 

-1.1

-3.0

16000

 

-6.6

-8.5

Table 2: Sound level meter weighting responses. 8

 

                         Equal Energy Hypothesis

            Many in the hearing loss community subscribe to the equal energy hypothesis, although there is some evidence to support other hypotheses. The premise behind the equal energy hypothesis is that “equal amounts of sound energy will produce equal amounts of hearing impairment regardless of how the sound energy is distributed in time”.9 Therefore, one must determine the exchange rate, or doubling rate, of sound energy10. The energy is proportional to sound intensity and to the square of sound pressure. From the description of SPL above and assuming an exchange rate R,

 

SPL = 10 log10(P/Pref) 2

10 log10(P/Pref)2 + R = 10 log10(√2P/Pref) 2

R = 10 log10(√2P/Pref) 2 - 10 log10(P/Pref) 2

R = 10 log10(√2) 2

R = 10 log10(2)

R = 3.01 ≈ 3

 

The result is that SPL increases by 3 dB whenever the sound energy doubles. As of May 2004, a 5 dB exchange rate is enforced in workplace regulations. This higher rate is less protective than the 3 dB rule and attempts to account for the interruptions in noise exposure that occur throughout a typical workday (breaks, meals, trips to the restroom, etc.). The National Institute of Occupational Safety and Health (NIOSH) recommends the 3 dB exchange after reviewing more recent data than was used to establish the 5 dB guidelines. The 3 dB exchange rate is appropriate to the scope of this research discussion because music is a mix between impulsive and continuous noise, and periods of reduced noise levels during band rehearsals only last for brief periods of time (typically less than one minute). In this study, comparisons will be made to the recommended NIOSH values using a 3 dB exchange rate.

 

            Time-Weighted Averages

A time-weighted average (TWA) is an average of different exposure levels over a period of exposure. Repeated studies have shown that there is low risk of hearing loss for exposures at or below 85 dBA. Therefore, the NIOSH recommendations are based on a safe 8-hour exposure to 85 dBA, called an 8-hour 85 dBA TWA. From this starting point, safe exposure lengths of time T in minutes for any 24-hour period can be calculated for any sound pressure level L in dBA11:

 

T = 480 / 2(L-85)/3

 

Below are the combinations of exposure and duration that are considered safe.

 

 

Exposure (dBA)

Duration

Exposure (dBA)

Duration

Hours

Minutes

Seconds

Hours

Minutes

Seconds

80

25

24

--

106

--

3

45

81

20

10

--

107

--

2

59

82

16

--

--

108

--

2

22

83

12

42

--

109

--

1

53

84

10

5

--

110

--

1

29

85

8

--

--

111

--

1

11

86

6

21

--

112

--

--

56

87

5

2

--

113

--

--

45

88

4

--

--

114

--

--

35

89

3

10

--

115

--

--

28

90

2

31

--

116

--

--

22

91

2

--

--

117

--

--

18

92

1

35

--

118

--

--

14

93

1

16

--

119

--

--

11

94

1

--

--

120

--

--

9

95

--

47

37

121

--

--

7

96

--

37

48

122

--

--

6

97

--

30

--

123

--

--

4

98

--

23

49

124

--

--

3

99

--

18

59

125

--

--

3

100

--

15

--

126

--

--

2

101

--

11

54

127

--

--

1

102

--

9

27

128

--

--

1

103

--

7

30

129

--

--

1

104

--

5

57

130-140

--

--

<1

105

--

4

43

--

--

--

--

Table 3: NIOSH combinations of noise exposure levels and durations that no worker exposure shall equal or exceed.12

 

 

THE HISTORY OF NOISE REGULATION13

            In 1970, Congress passed Public Law 95-164, the Occupational Safety and Health Act. This law established the Occupational Safety and Health Administration (OSHA) within the Department of Labor. According to the Act, OSHA is responsible for protecting the safety and health of much of the workforce of the United States. The Act also established the National Institute for Occupational Safety and Health (NIOSH) within what is now the Department of Health and Human Services. NIOSH’s purpose is to develop criteria for safe occupational workplace noise exposure.

            In compliance with the Act, NIOSH published Criteria for a Recommended Standard: Occupational Exposure to Noise in 1972. This document recommended an exposure limit of 85 dBA as an 8-hour TWA using a 5 dB exchange rate, and discussed measuring, calculating, and preventing noise exposure. However, OSHA’s initial guidelines were based on an exposure limit of 90 dBA as an 8-hour TWA, with a 5 dB exchange rate. Despite revisions of the OSHA guidelines throughout the 1980s, permissible exposure limits continued to be based on 90 dBA for an 8 hour exposure, although current regulations require hearing conservation program implementation when the 8-hour TWA exceeds 85 dBA.

            In 1998 NIOSH published Criteria for a Recommended Standard: Occupational Noise Exposure – Revised Criteria 1998. The revised document offers several major changes to the information presented in 1972; most notably, NIOSH now recommends a 3 dB exchange rate, for reasons previously discussed. The revision reaffirms the 85 dBA 8-hour TWA.

 

HEARING AND HEARING LOSS

When exposed to noise, the eardrum vibrates. The eardrum changes the pressure variations of sound in air into mechanical vibrations, which are transmitted to the cochlea through three small bones called ossicles. The cochlea contains two membranes, Reissner’s membrane and the basilar membrane, and resting on the basilar membrane is the organ of Corti, which contains thousands of hair cells. When the basilar membrane vibrates, the hair cells are excited and stimulate the auditory nerve; signals sent through the auditory nerve to the brain are interpreted as sound.14

            Hearing loss occurs when the above process does not function normally. In most cases, including a musician’s temporary or permanent hearing loss, this is because of damage to the hair cells.15

From extensive examinations of animal ears, and occasional post-mortem examinations of noise-damaged human ears, it has been fairly well established that excessive exposure to noise destroys the delicate hair cells in the organ of Corti and eventually the organ itself … The mechanism by which the hair cells are destroyed is not completely clear … One theory suggests that constant overexposure to sound forces the cells to work at too high a metabolic rate for too long a time, leading to the death of the cells. These delicate receptor cells do not regenerate, and if they die of overwork, they are lost for life.16


Figure 3: Drawings of the human organ of Corti that illustrate increasing degrees of noise-induced permanent damage.17

            Hair cell damage can either be temporary, which results in a temporary threshold shift (TTS), or permanent, which results in a noise-induced permanent threshold shift (NIPTS). The following facts are presented for the reader to gain a general understanding of the effects of noise on TTS and NIPTS: