by Federico Miyara (fmiyara@unrctu.edu.ar)
August 1997
Prof. Miyara teaches
Linear Electronics, Acoustics and Psychoacoustics, Noise Control, and
Sound Systems at the National University of Rosario (Argentina).
One
of the first questions people ask when told that noise can be harmful
is: how much noise is actually necessary before human beings are
adversely affected?
The answer isn't simple,
because the effects of noise involve multiple aspects of people's health
and welfare.
From a philosophical point
of view, since noise may be defined as any unwanted acoustical stimulus
which interferes with human activity or rest, any amount of noise
affects people (otherwise it wouldn't be noise). Often, however, noise
is better tolerated if it is judged to be unavoidable. The noise of
rain, for instance, is much more acceptable than that coming from the
isolated but steadily repetitive drops from a leaking tap. Generally
speaking, periodical noises are more annoying than random ones.
But when objectively
measurable effects are considered, research has shown that there exists
a strong correlation between the physical intensity of the stimulus and
the extent of the effect. That is particularly true as regards hearing
loss. Extensive research has been done for decades on different groups
of industry workers, and several criteria have been developed in order
to assess specific situations.
One of those criteria,
namely that contained in the ISO 1999 Standard, starts by defining
"hearing loss" as a permanent increase of the auditory threshold (the
minimum audible sound level) affecting the intelligibility of speech.
This amounts to some 25 dB for middle-frequency tones. Then a double
entry table is used to assess the percentage risk of "acquiring" hearing
loss if exposed in the workplace to a certain average sound level for 8
hours per day, 6 days a week for a given number of years:
| |
dBA |
Years of exposure |
5 |
10 |
15 |
20 |
25 |
30 |
35 |
40 |
45 |
80 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
85 |
1 |
3 |
5 |
6 |
7 |
8 |
9 |
10 |
7 |
90 |
4 |
10 |
14 |
16 |
16 |
18 |
20 |
21 |
15 |
95 |
7 |
17 |
24 |
28 |
29 |
31 |
32 |
29 |
33 |
100 |
12 |
29 |
37 |
42 |
43 |
44 |
44 |
41 |
35 |
105 |
18 |
42 |
53 |
58 |
60 |
62 |
61 |
54 |
41 |
110 |
26 |
55 |
71 |
78 |
78 |
77 |
72 |
62 |
45 |
115 |
36 |
71 |
83 |
87 |
84 |
81 |
75 |
64 |
47 |
|
|
|
Whenever working hours are
halved, the criterion is applied subtracting 3 dBA from the actual sound
level.
Let's take, for example,
the case of a disc jockey working at a night-club 3 nights a week
exposed to an average sound level of 106 dBA during a 4-hour shift. We
have half the days and half the time per day, so 3 dBA must be
subtracted twice, yielding 100 dBA. Suppose, further, that the disc
jockey starts at the age of 15 and stays in this trade till 30 -- that
is, a 15-year exposure. The table reveals a 37 percent risk of suffering
speech intelligibility handicap. That is, almost 4 out of 10 such
persons will experience difficulties in understanding normal speech --
at the age of 30.
Labor regulations usually
allow exposure to levels of 85 dBA or even 90 dBA, but also compel
employers to carry out hearing conservation programs, which typically
include periodic hearing tests to screen out highly susceptible workers
from hazardous noise environments.
A closer look at the table
reveals that at 80 dBA the risk is 0% for any extension of working life.
Does this mean that 80 dB is the safe ceiling? Not at all. This is
because in the definition of "risk" there is another element which for
simplicity was not mentioned earlier. As this table is intended to
predict the risk of workplace exposure, the percentage of people
suffering from hypoacusis just by aging (i.e. presbycusis) has already
been subtracted.
There are several studies
that reveal that what was formerly considered to be presbycusis is
actually "sociocusis" -- that is, hearing loss due to exposure to social
or community noise.
In the seventies the U.S.
Environmental Protection Agency (EPA) was committed to providing
"information on levels of environmental noise requisite to protect
public health and welfare with an adequate margin of safety." The task
was not easy, because though a large amount of information on workplace
exposure to noise was readily available, very little information
regarding non-workplace exposure had been published. The approach was
thus to extrapolate the available data under a number of reasonable
asumptions. The results were published in a famous paper known as "The
Levels Documents."
The EPA criterion
regarding hearing conservation states that in order to protect virtually
all the population against hearing loss, the average sound level should
not be greater than 70 dBA during a 24-hour day. Equivalently, it should
not be greater than 75 dBA for an 8-hour working day, provided that for
the rest of the day the level is kept considerably below that figure.
This criterion differs
substantially from the ISO's in that it considers that hearing loss has
occurred when the auditory threshold rises only 5 dB instead of 25 dB.
It is thus a far stricter criterion.
It should be noted that
the EPA limit is an average, meaning that much larger levels can usually
be tolerated for brief periods of time. Indeed, each time the duration
of the exposure is halved, the safe level increases by 3 dBA, so it
would be safe to be exposed to 78 dBA for 4 hours, 81 dBA for 2 hours,
84 dBA for 1 hour, and so on. However, exposure to levels above 100 dBA
even for very short periods is not recommended, since some susceptible
persons may suffer immediate and irreversible hearing impairment.
As seen above,
occupational limits tend to be rather permissive as compared to
environmental ones, the reason being that they take into account other
factors appart from safety and welfare, such as the technical or
economical feasibility of decreasing noise levels at the workplace.
Finally, the EPA document
addresses not only the hearing impairment issue but also issues of
annoyance and interference with activities. In this case, it states that
the average outdoor noise level should be no greater than 55 dBA in the
daytime and 45 dBA at night. Indoors, the recommended limits are 45 dBA
and 35 dBA respectively. period of time.
Actual environmental noise
laws and regulations tend to be somewhat more permissive, usually
allowing for corrections under given circumstances. For instance, when
the noise source affects the surroundings of an industrial area, a
correction of as much as 25 dB is often applied to the basic EPA
criterion. Noise from motor vehicles is generally treated in a different
way: since each vehicle passes by a given location only for a short
period of time, much higher limits are imposed for individual vehicles,
and little attention is paid to the cumulative noise level arising from
continuous traffic flow.
|