THE EFFECTS OF INDUSTRIAL NOISE ON HEARING

by

Joseph Heggins II

 

Audition plays many important roles in our daily lives. From sound, we can identify and locate an object. Also, spoken language and its auditory reception have become an extremely important means of communication. A deficit in the ability to hear have tremendous effects on a person physically and mentally. Hearing loss caused by occupational noise is one of our biggest industrial diseases. It is a disease that has been recognized since the Industrial Revolution. According to Sataloff and Sataloff (1987) about 35 million Americans suffer from hearing loss, and of those, eight million suffer from occupational hearing loss. Because of the sheer number of people and our neglect of the subject, almost every American may be affected directly or indirectly.

It has certainly been technologically possible for many years to eradicate the problem of occupational hearing loss, but a delay has been caused by legislative, economic, and political resistance. Also, because hearing loss does not impede your earning power as much as vision loss would, it has taken the back burner as far as industrial perceptual diseases are concerned. Because of the new laws on worker's compensation an estimated 20 billion dollars might have to be paid out to those inflicted, which would make it the number one environmental and medical-legal problem in the United States (Harris, 1979).

Exposure to excessive noise for a sufficiently long period of time can result in the destruction and eventual loss of the organ of Corti. Harris (1979) has divided the effects of industrial noise on hearing into three categories. The first is acoustic trauma, the immediate organic damage to the ear from excessive sound energy, it is restricted to the effects of a simple exposure at very high sound levels. Such intense noise reaching the inner ear may exceed the physiological limit of those structures, producing a complete breakdown of the organ of Corti. The second is a noise-induced temporary threshold shift that results in an elevation of heighten levels following noise exposure. The loss is usually reversible. The third effect is a noise-induced permanent threshold shift, which is not reversible. It may come from acoustic trauma or be produced by the cumulative effect of repeated noise exposures over many periods of years.

The structures most susceptible to noise damage are the sensory receptor cells, the hair cells, located in the cochlea. Damage from repeated noise is a physiochemical problem where the metabolic stress exerts pressure on the maximally stimulated cells. Depending on the amount of cellular damage, it could be permanent or temporary damage. In fact, cochlear damage is the number-one characteristic of occupational hearing loss. Sataloff and Sataloff (1987) namea few others. For one,the patient must have a history of long-term exposure to intense noise levels sufficient to cause the degree and pattern of hearing loss evident in audiologic finding. The hearing loss must have developed gradually over a period of years. The hearing loss must have developed during the first eight to ten years of exposure. The hearing loss must initially have started in the higher frequencies (generally 3000-6000 Hz) and be almost equal in both ears. Speech discrimination scores, even with substantial high frequency losses, are generally good. Finally, the hearing loss should stabilize if the patient is removed from noise exposure. Another characteristic of occupational hearing loss is that specific noisy jobs produce a maximum degree of hearing loss. This is known as asymptotic hearing loss. For example, employees using jackhammers develop severe high-frequency, but minimal low-frequency hearing losses. A diagnosis of occupational hearing loss must be based on specific criteria. The potential medical, legal, and economic consequences are likely to be very serious.

Because industrial noise does affect you hearing, it leaves many residual effects, mainly psychological. Dublins National Board for Science and Technology (1980) looked into the psychological effects. First, difficulties in hearing interfere with speech communication. When people are in environments where background noise is at 75 dB, normal conversation becomes unsatisfactory. After 80dB, just raising ones voice is not enough. Workers become hoarse by the end of the day. When people have problems hearing and communicating, it leads to misunderstandings which result in waste and inefficiency, and in the worse situations, accidents. Industrial noise, and its unpleasantness, is associated with a lower level of job satisfaction. According to Dublins National Board for Science and Technology (1980), some characteristics of noise lead to increased annoyance: noise which is highly variable, where there is a considerable difference between background and peak intensities, noise in the middle frequencies where the ear is most sensitive, noise with a large component of pure tones or narrow wave-bands, and noise that is increasing rather than decreasing.

Because noise affects ones hearing, it indirectly affects your performance. Dublins National Board for Science and Technology (1980) looked at specific experiments. One experiment they spoke of dealt with the film-processing industry, in which one room they reduced the noise from 99 to 89 dB. Comparing this quieter room to another room at the regular noise level, the workers in the quieter room had a significant reduction of film breakage. Another study found that the number of sorting errors made by the postal sorters increased systematically with noise level.

In general, if people have a hard time communicating to one another, attempts to interact will become less frequent, leading to an increased sense of isolation. This in turn can lead to depression. Also, in many cases, people who obtain hearing loss have problems commuicating outside of the work place with communicating, causing people to have problems in their marriages and friendships.

Fortunately, there are things that can be done to protect the hearing of employees from the effects on industrial noise. First, if possible a company can reduce the noise coming from the source. This is the best way but cannot always be accomplished, so covering surrounding surfaces with sound absorbent materials, using noise barriers, or just moving the person or the source of noise to different location can help. When none of the above mentioned ways work, however, personal protective devices must be used. According to Sataloff and Sataloff (1987) sound energy may reach the inner ears of persons wearing protection by four ways. The first way is by passing through bone and tissue around the protector. Another way is by causing vibration of the protector, which in turn generates sound into the external ear canal; or by passing through leaks in the protector; or through leaks around the protector. They then goes on to explain the rules that should be followed in order to minimize losses due to the leaks. Hearing protectors should be made of imperforate materials. The protector should be designed to conform readily to the head or ear canal configuration. It should have a support means or a seal compliance that will minimize protector vibration. Finally, muff-type protectors should not be worn over long hair, poorly fitted eyeglass, or other obstacles.

A big fallacy about the use of hearing protective devices is that it will be even harder to communicate. Wearing hearing protectors in high-level noise environments can improve communication for normal ears because speech-to-noise ratios are kept nearly constant and the protected ear does not distort from overdriving caused by the high speech and noise levels. The two basic types of protectors are the insert-type and the muff type, and there are advantages and disadvantages to both. For the insert type the advantages are that they are small, easy to carry, and cost efficient. The disadvantages are that they can get dirty when removed and inserted with dirty hands, and that they take time to get familiar. Muff-type protectors are technically better for reducing noise levels. Unfortunately, that they are more expensive that opts the employer to get the plugs.

According to Harris (1979) the federal government showed its first real concern about industrial noise by including a noise standard in the Occupational Safety and Health Act of 1972. The standard makes it mandatory for industries to reduce noise by every feasible means where employees are exposed to 90dB or more for an eight-hour workday. If the noise cannot be reduced adequately, a hearing conservation program has to be established. Before 1948, gradual partial hearing loss caused by industrial noise was not included in state workers compensation laws. Little or no mention was made of partial hearing loss caused by long exposure to occupational noise. Law makers were unaware of the consequences of hearing loss because it did not seem to cause loss of wage or earning power. The original basic objective of workmens compensation was to provide payment for loss of earning and for medical costs of injury related to employment. Now under the system of laws in the United States, a person who suffers hearing loss from occupational noise exposure or traumatic injury may be entitled to an award for damages. In most states, noise-induced hearing impairment is treated as an occupational disease with scheduled awards based on degree of hearing loss.

Research in the area of industrial noise and its effects on hearing has been abundant. Sataloff and Sataloff (1987) have done a review of some of the basic research done in the past. In 1952 James H. Sterner, M.D. conducted an opinion poll among a large number of individuals working with noise and hearing as to the maximum intensity level of industrial noise they considered safe to hearing. The wide range of estimates demonstrated clearly the lack of agreement. Some studies were based on a very small number of subjects exposed to continuous steady state noise, particularly in the 82-92 dBA range. Workers were included who change position from time to time using noisy hand tools that hardly constitute a continuous or steady state. Around 1970, individuals from industry, labor, government, and scientific organizations got together for the purpose of gathering data on the effects of steady-state noise in the range of 82-92dB. The basic purpose was for scientific rather than regulatory reasons. They found that difference in noise intensity had observable effects on hearing levels. Age was a more important factor than duration on the job. Levels in the noise-exposed group significantly exceeded those in the control group at 3000, 4000, and 6000Hz by approximately six to nine dB. At 8000Hz, differences again became not significant. There was no real evidence of a difference between noise exposed workers and their controls with respect to the changes in hearing level during the course of their follow-up one and two years after initial audiograms.

The following is some current research done on the effects of hearing. Investigators from the National Institute for Occupational Safety and Health analyzed data collected during the 1971 and 1977 National Health Interview surveys. Self-reported hearing loss was higher among adults working in industries with potential exposures to industrial noise than among those working in industries without such potential exposures. They found that self-reported hearing loss increases with age, and that, within age groups, it is consistently greater for noisy industries. Industries in the manufacturing sector had the highest prevalence of noise exposure. Bauer, Kopert, Raber, and Schwetz (1991) looked at the risk factors for hearing loss at different frequencies. They examined how audiometric frequency was affected by sex, noise emission level, ear disease, tinnitus, and wearing protector usage. The age factor is at any observed frequency the most important predictor for the wearing threshold. Persons who did not use hearing protectors had better hearing. They suggested that workers with a beginning hearing malfunction tend to use the protection. Dryter (1991) found that industrial noise is deduced to cause about half as much overall increase in male population hearing levels as that caused by exposure to gun noise.

In a study done by Hetu and Getty (1993), they found that employees who have developed occupation hearing loss will many times not advance in their careers because of the stigma attached to hearing loss. Employees with this infliction tend to avoid areas where frequent communication is held. Also, they looked at engineering problems, such as making regulatory emergency sirens more stimulating to those that are hearing impaired. Research in the medico-legal areas is starting to rise; and because this is a very expensive disorder in terms of worker's compensation, much more research in this area is needed. Some research done by Simpson, Stewart, and Blakley (1995) reflects this need. They looked to see how reliable audiometric retesting is in identifying false-positive referral flags. They found that when second audiograms were used to confirm initial findings they had lower referral rates, which could save a lot of money in the long run. Finally, since there has been an increase in the knowledge of industrial noise and its effects on hearing, much attention has been given the hearing aid. Dolan and Maurer (1990) found that hearing aids use can do more damage the ear if worn around sufficient levels of industrial noise.

In conclusion, future research is necessary in the area of occupational hearing loss. This disease afflicts millions of people and costs society a good deal of money. For a short term solution to the problem, more research needs to be done in the areas of hearing protection devices, but for a long term solution a great deal more research needs to be done in the area of making the machines more quiet.

BIBLIOGRAPHY

 

Bauer, P., Korpert, K., Neuberger, M., Raber, A., & Schwetz, F. (1991). Risk factors for hearing loss at different frequencies in a population of 47 3888 noise-exposed workers. Journal of Acoustical Society of America, 90(6), 3086-3097.

Dolan, T. & Maurer, J. (1996). Noise exposure associated with hearing aid use in industry. Journal of Speech and Hearing Research, 48, 251-260.

Harris, C.M. (Ed.). (1979). Handbook of Noise Control (2nd ed.). New York: McGraw-Hill.

Hetu, R. & Getty, L. (1993). Overcoming difficulties experienced in the work place by employees with occupational hearing loss. The Volta Review, 95, 391-402.

Kryter, K. (1991). Effects of nosocusis, and industrial and gun noise on hearing of U.S. adults. Journal of Acoustical Society of America, 90(6), 3196-3201.

National Board for Science and Technology, Dublin (Ireland). (1980). Noise and the environment. U.S. Department of Commerce Springfield, VA. (NTIS No. PB84-108638)

National Institute for Occupational Safety and Health. (1988). Self-reported hearing loss among workers potentially exposed to industrial noise- United States. Journal of America Medical Association, 259(15), 2213-2217.

Sataloff, R. T., & Sataloff, J. (1987). Occupational Hearing Loss. New York: Marcel Dekker, INC.

Simpson, T., Stewart, M., & Blakley, B. (1995). Audiometric referral criteria for industrial hearing conservation programs. Arch Otolaryngol Head Neck Surgery, 121, 407-411.


Return to Service Learning 1998 Frontpage.