noise pollution
noise pollution,
human-created noise harmful to health or welfare. Transportation
vehicles are the worst offenders, with aircraft, railroad stock,
trucks, buses, automobiles, and motorcycles all producing
excessive noise. Construction equipment, e.g., jackhammers and
bulldozers, also produce substantial noise pollution.
Noise intensity is measured in
decibel units. The decibel scale is logarithmic; each
10-decibel increase represents a tenfold increase in noise
intensity. Human perception of loudness also conforms to a
logarithmic scale; a 10-decibel increase is perceived as roughly
a doubling of loudness. Thus, 30 decibels is 10 times more
intense than 20 decibels and sounds twice as loud; 40 decibels
is 100 times more intense than 20 and sounds 4 times as loud; 80
decibels is 1 million times more intense than 20 and sounds 64
times as loud. Distance diminishes the effective decibel level
reaching the ear. Thus, moderate auto traffic at a distance of
100 ft (30 m) rates about 50 decibels. To a driver with a car
window open or a pedestrian on the sidewalk, the same traffic
rates about 70 decibels; that is, it sounds 4 times louder. At a
distance of 2,000 ft (600 m), the noise of a jet takeoff reaches
about 110 decibels—approximately the same as an automobile horn
only 3 ft (1 m) away.
Subjected to 45 decibels of noise, the average
person cannot sleep. At 120 decibels the ear registers pain, but
hearing damage begins at a much lower level, about 85 decibels.
The duration of the exposure is also important. There is
evidence that among young Americans hearing sensitivity is
decreasing year by year because of exposure to noise, including
excessively amplified music. Apart from hearing loss, such noise
can cause lack of sleep, irritability, heartburn, indigestion,
ulcers, high blood pressure, and possibly heart disease. One
burst of noise, as from a passing truck, is known to alter
endocrine, neurological, and cardiovascular functions in many
individuals; prolonged or frequent exposure to such noise tends
to make the physiological disturbances chronic. In addition,
noise-induced stress creates severe tension in daily living and
contributes to mental illness.
Noise is recognized as a controllable pollutant
that can yield to abatement technology. In the United States the
Noise Control Act of 1972 empowered the Environmental Protection
Agency to determine the limits of noise required to protect
public health and welfare; to set noise emission standards for
major sources of noise in the environment, including
transportation equipment and facilities, construction equipment,
and electrical machinery; and to recommend regulations for
controlling aircraft noise and sonic booms. Also in the 1970s,
the Occupational Safety and Health Administration began to try
to reduce workplace noise. Funding for these efforts and similar
local efforts was severely cut in the early 1980s, and
enforcement became negligible.
Noise
pollution (or environmental noise
in technical venues) is displeasing human or machine created
sound that disrupts the
environment. The dominant form of noise pollution is from
transportation sources, principally
motor vehicles[1]
. The word "noise"
comes from the Latin word
nausea meaning "seasickness",
or from a derivative (perhaps Latin noxia) of Latin
noceō = "I do harm", referring originally to nuisance noise.[2]
The overarching
source of most noise worldwide is generated by transportation
systems, principally motor vehicle noise, but also including
aircraft noise and rail noise.[3][4].
Hybrid vehicles are the first innovation within the last 100
years to achieve significant widespread noise source reduction.[citation
needed] Poor
urban planning may also give rise to noise pollution, since
juxtaposition of industrial to residential land uses, for
example, often results in adverse consequences for the
residential acoustic environment.
Besides
transportation noise, other prominent sources are office
equipment, factory machinery, appliances, power tools,
lighting hum and audio entertainment systems. Furthermore,
with the popularity of
digital audio player devices, individuals in a noisy area
might increase the volume in order to drown out ambient sounds.
Construction equipment also produces noise pollution.
Noise from
recreational vehicles has become a serious problem in rural
areas.
ATVs, also known as quads, have increased in popularity and
are joining the traditional two wheeled dirt motorcycles for
off-road riding.
The noise from
ATV machines is quite different from of the traditional dirt
bike. Some ATVs have large bore, four stroke engines that
produce a loud throaty growl that will carry further due to the
lower frequencies involved. The traditional
two stroke engines on dirt bikes have gotten larger and,
while they have higher frequencies, they still can propagate the
sound for a mile or more. The noise produced by these vehicles
is particularly disturbing due to the wide variations in
frequency and volume.
Recreational
vehicles are generally not required to be registered and control
of the noise they emit is absent in most communities. However,
there is a growing awareness that operation of these machines
can seriously degrade the quality of life of those within
earshot of the noise and some communities have enacted
regulations, either by imposing limits on the sound or through
land use laws. Rider organizations are also beginning to
recognize the problem and are enlightening members as to future
restrictions on riding if noise is not curtailed. because of
human beings
Human health
Principal
noise health effects are both
health and
behavioral in nature. The following discussion refers to
sound levels that are present within 30 to 150 meters from a
moderately busy
highway. Sound is a particular auditory impression perceived
by the sense of hearing. The presence of unwanted sound is a
called noise pollution. This unwanted sound can seriously damage
and effect physiological and psychological health. For instance,
noise pollution can cause annoyance and aggression,
hypertension, high stress levels, tinnitus, hearing loss, and
other harmful effects depending on the level of sound, or how
loud it is.[5][6]
Furthermore, stress and hypertension are the leading causes to
health problems, whereas tinnitus can lead to forgetfulness,
severe depression and at times panic attacks.[7][8]
Hearing
The mechanism for
chronic exposure to noise leading to
hearing loss is well established. The elevated sound levels
cause
trauma to the
cochlear structure in the
inner ear, which gives rise to irreversible
hearing loss.[5]
The
outer ear (visible portion of the human
ear) combined with the
middle ear amplifies
sound levels by a factor of 20 when sound reaches the
inner ear.[9]
In Rosen's seminal
work on serious
health effects regarding
hearing loss and
coronary artery disease, one of his findings derived from
tracking
Maaban
tribesmen, who were insignificantly exposed to
transportation or industrial noise. This population was
systematically compared by
cohort group to a typical U.S. population. The findings
proved that aging is an almost insignificant cause of
hearing loss, which instead is associated with chronic
exposure to moderately high levels of
environmental noise.[5]
Cardiovascular health
High noise levels can
contribute to
cardiovascular effects and exposure to moderately high (e.g.
above 70
dBA) levels during a single eight hour period causes a
statistical rise in
blood pressure of five to ten
mmHg; a clear and measurable increase in
stress
[10]; and
vasoconstriction leading to the
increased blood pressure noted above as well as to increased
incidence of
coronary artery disease.
Annoyance
Though it pales in
comparison to the health effects noted above, noise pollution
constitutes a significant factor of annoyance and distraction in
modern artificial environments:
1.
The meaning listeners attribute to the sound
influences annoyance, so that, if listeners dislike the noise
content, they are annoyed. What is music to one is noise to
another.
2.
If the sound causes activity interference, noise
is more likely to annoy (for example,
sleep disturbance)
3.
If listeners feel they can control the noise source,
the less likely the noise will be annoying.
4.
If listeners believe that the noise is subject to
third-party control, including police, but control has
failed, they are more annoyed.
5.
The inherent unpleasantness of the sound causes
annoyance.
6.
Contextual sound.
If the sound is appropriate for the activity it is in context.
If one is at a race track the noise is in context and the
psychological effects are absent. If one is at an outdoor picnic
the race track noise will produce adverse psychological and
physical effects.
A 2005 study by
Spanish researchers found that in urban areas households are
willing to pay approximately four
Euros per decibel per year for noise reduction[11].
Environment
Noise pollution can
also be harmful to wildlife . High noise levels may interfere
with the
natural cycles of animals, including feeding behavior,
breeding rituals and
migration paths.[citation
needed] The most significant impact of noise to
animal life is the systematic reduction of usable habitat, which
in the case of endangered species may be an important part of
the path to
extinction. Perhaps the most sensational damage caused by
noise pollution is the death of certain species of beached
whales, brought on by the extremely loud (up to 200
decibels) sound of military
sonar.[citation
needed]
Mitigation and control
of noise


The
sound tube in
Melbourne,
Australia, designed to reduce
roadway noise without detracting from the area's aesthetics.
There is also
technology that has been applied with the aim of mitigating or
containing noise as much as possible, provided that it has a
sufficiently localized source.
·
Roadway noise, is the most widespread environmental
component of noise pollution worldwide. There are a variety of
effective strategies for mitigating adverse sound levels
including: use of
noise barriers, limitation of vehicle speeds, alteration of
roadway surface texture, limitation of
heavy duty vehicles, use
of traffic controls that smooth vehicle flow to reduce braking
and acceleration, innovative tire design and other methods.
Thousands of case studies in the U.S. alone have been documented
starting in 1970, indicating substantial improvement in roadway
planning and design. The most important factor in applying these
strategies is a
computer model for
roadway noise, that is capable of addressing local
topography,
meteorology, traffic operations and hypothetical mitigation.
Costs of building in mitigation is often quite modest, provided
these solutions are sought in the planning stage of a roadway
project.
·
Aircraft noise can be reduced to some extent by design of
quieter
jet engines, which was pursued vigorously in the 1970s and
1980s. This strategy has brought limited but noticeable
reduction of urban sound levels. Reconsideration of operations,
such as altering
flight paths and time of day runway use, have demonstrated
significant benefits for residential populations near airports.
FAA sponsored residential retrofit (insulation) programs
initiated in the 1970s has also enjoyed widespread success in
reducing interior
residential noise in thousands of affected residences across
the United States.
·
Exposure
of
Industrial noise on workers has the longest history of
scientific study, having been addressed since the 1930s. This
scientific studies have emphasized redesign of industrial
equipment, shock mounting assemblies and physical barriers in
the workplace. Innovations have had considerable success;
however, the costs of retrofitting existing systems is often
rather high.
Legal status
Governments up until
the 1970s viewed noise as a "nuisance" rather than an
environmental problem. In the
United States there are federal standards for highway and
aircraft noise; states and local governments typically have very
specific statutes on
building codes,
urban planning and roadway development. In
Canada and the
EU there are few national, provincial, or state laws that
protect against noise. As a result in Canada and the EU, most
regulation has been left up to municipal authorities.
Noise laws and
ordinances vary widely among municipalities and indeed do not
even exist in some cities. An ordinance may contain a general
prohibition against making noise that is a nuisance, or it may
set out specific guidelines for the level of noise allowable at
certain times of the day and for certain activities. Exceptions
are generally made for activities considered essential public
services such as refuse collection and emergency vehicles.
Most city
ordinances prohibit sound above a threshold intensity from
trespassing over property line at night, typically between 10
p.m. and 6 a.m., and during the day restricts it to a higher
decibel level; however, enforcement is uneven. Many
municipalities do not follow up on complaints. Even where a
municipality has an enforcement office, it may only be willing
to issue warnings, since taking offenders to court is expensive.
For persistent nuisances, individuals may have to seek damages
through the
civil courts. Many jurisdictions, such as
New York City and
Chicago authorize police to impound cars with loud stereos
and to hold the cars as evidence until the citation has been
adjudicated.
Many conflicts over
noise pollution are handled by negotiation between the emitter
and the receiver. Escalation procedures vary by country, and may
include action in conjunction with local authorities, in
particular the
police. Clear
documentation, repetitive complaints, getting neighbors
involved, and forming a
Neighborhood Watch can be effective at obtaining
enforcement. Noise pollution often persists because only five to
ten percent of people affected by noise will lodge a formal
complaint[citation
needed]. Many people are not aware of their legal
right to quiet and do not know how to register a complaint.
Furthermore, mobile noise sources are transitory such that they
may be difficult to pursue unless a noise measurement device is
in place, so effectiveness tends to depend on whether a city has
instituted proactive enforcement policies (e.g. muffler
inspections).
What is
Noise Pollution?
Noise pollution is not easily defined
because it is different from other forms of pollution. One
measure of pollution is the danger it poses to health. Noise
causes stress, which is a leading cause of illness and suicide.
Therefore, any form of noise can be considered pollution if it
causes annoyance, sleeplessness, fright, or any other stress
reaction.
- Noise is transient; once the pollution
stops, the environment is free of it. This is not the case
for chemicals, sewage, and other pollutants introduced into
the air, soil, or water.
- Other forms of pollution can be
measured, and scientists can estimate how much material can
be introduced into the environment before harm is done. We
can measure individual sounds that may damage human hearing,
but it is difficult to monitor cumulative exposure to noise
or to determine just how much is too much.
- The definition of noise itself is
highly subjective. To some people the roar of an engine is
satisfying or thrilling; to others it is an annoyance. Loud
music may be enjoyable or a torment, depending on the
listener and the circumstances.
Broadly speaking,
any form of unwelcome sound is noise pollution, whether it is
the roar of a jet plane overhead or the sound of a barking dog a
block away. The actual loudness of a sound is only one component
of the effect it has on human beings. Other factors to consider
are the time and place, the duration, the source of the sound,
and whether the listener has any control over it. Most people
would not be bothered by the sound of a 21-gun salute on a
special occasion. On the other hand, the thump-thump of
a neighbour's music at 2 a.m., even if barely audible, could be
a major source of stress.
Measuring Sound by Decibel
(dB)
The decibel (dB) is a measure of sound
intensity; that is, the magnitude of the fluctuations in air
pressure caused by sound waves. The decibel scale is
logarithmic, not arithmetic. This means that a doubling of sound
intensity is not represented as a doubling of the decibel level.
In fact, an increase of just 3 dB means twice as much sound, and
an increase of 10 dB means ten times as much sound.
A sound pressure level of 0 dB represents the threshold of
hearing in the most sensitive frequency range of a young,
healthy ear, while the thresholds of tickling or painful
sensations in the ear occur at about 120 to 130 dB.
Decibels are usually measured with a filter that emphasizes
sounds in certain frequencies. The "A" filter (dBA) is the one
most frequently used. The "C" filter (dBC) puts more weight on
low-frequency sounds such as the bass in amplified music.
The perception of loudness by the human ear is not directly
proportional to the decibel level. For example, a sound 10 dB
greater than another is not perceived as being ten times as loud
but only about three times as loud.
The intensity of noise diminishes with distance. Outdoors, and
in absence of any close reflecting surface, the effective
decibel level diminishes at a rate of 6 dB for each factor of
two increase in distance. For example, a sound measuring 100 dB
at 10 metres would be 94 dB at 20 metres, 88 dB at 40 metres,
and so on.
How loud does noise have to be
before it's dangerous?
Because permanent hearing loss is usually
a long-term process, it is impossible to know at exactly what
point noise becomes loud enough to cause damage to the ears.
The U.S. Environmental Protection Agency has established 70 dBA
as a safe average for a 24-hour day. (This figure is based only
on the risk to hearing, and does not take into account other
health factors such as loss of sleep.)
Since sound intensity doubles with every increase of 3 dB, the
time of safe exposure would be cut in half with each such
increase. Thus a worker should wear ear protection if exposed to
a steady 75 dBA for eight hours, 78 dBA for four hours, and so
on. Brief exposure to noises of up to 100 dBA is not considered
risky, provided the average remains within the prescribed
levels.
Actual limits for labour tend to be more permissive. In most
jurisdictions, workers are permitted to be exposed to up to 85
or even 90 dBA for eight hours. Using the higher of these
figures, the sound level in a typical nightclub, 110 dBA, could
pose a risk of permanent hearing damage after as little as four
minutes of exposure.
Of course, noise is dangerous in other ways too. It can be a
cause of stress, illness, suicide, aggression, and violence. As
stated above, the volume of noise is only one component of its
effect.
For a more technical explanation, click here.
Does the law protect me against noise?
In Canada and the United States there are
no national, provincial, or state laws that give blanket
protection against noise, though there are some specific
regulations governing manufacturing standards, air traffic,
vehicle mufflers, and so on. Criminal laws may also cover things
like noisy parties.
Governments have traditionally viewed noise as a nuisance rather
than an environmental problem. As a result, most regulation has
been left up to municipal authorities.
Noise bylaws and ordinances vary widely from one municipality to
another and do not even exist in some towns and cities. Where
they exist, they may contain a general prohibition against
making noise that is a nuisance to other people, or they may set
out specific guidelines for the level of noise allowable at
certain times of the day and for certain activities. Exceptions
are generally made for activities considered legitimate or
necessary, such as lawn mowing or garbage collection.
Regardless of how lax or stringent a local law may be,
enforcement is difficult. Many municipalities do not have
adequate resources to follow-up on complaints. Even where a
municipality has an enforcement office, it may be unwilling to
do more than issue warnings, since taking offenders to court is
expensive. The police may also act on certain kinds of noise
complaints, but generally do not assign them a high priority.
For persistent nuisances, the individual may have to seek
damages through the civil courts. This can be a long, costly
procedure with no certainty of success.
In short, legal protection against noise is very patchy and
often inadequate.
Is there evidence
that noise can make us sick?
Yes, though much of it is buried in
scholarly journals. We know of only one book in print: Noise
& Health, edited by Thomas H. Fay, published by The New
York Academy of Medicine (1991). This book presents a critical
and comprehensive review of available world literature on the
effects of noise on all of the body's systems. It defines noise
and its sources, documents the specific health hazards of noise
on the body, and indicates needs for further research.
Cick here to visit Resources for more information
Cause and Effects of Noise
Pollution
by Daniel G. Nunez
Abstract
No one on earth can escape the sounds of
noise- an unwanted, disturbing sound that causes a nuisance
in the eye of the beholder. Noise is a disturbance to the
human environment that is escalating at such a high rate
that it will become a major threat to the quality of human
lives. In the past thirty years, noise in all areas,
especially in urban areas, have been increasing rapidly.
There are numerous effects on the human environment due to
the increase in noise pollution. In the following paper, the
cause and effects of noise pollution will be presented in
some detail. Slowly, insensibly, we seem to accept noise and
the physiological and psychological deterioration that
accompanies it as an inevitable part of our lives. Although
we attempt to set standards for some of the most major
sources of noise, we often are unable to monitor them. Major
sources of noise can be airplanes at takeoff and landing,
and a truck just off the assembly line, yet we seem accept
and enjoy countless other sounds, from hard rock music to
loud Harley Davidson motor cycles. The following areas will
be investigated in some detail; adolescent education,
neural-effects, sleep, hearing damage, occupational
environment, transportation, and physiological effects.
Introduction
Almost everyone has had one experience of being
temporarily "deafened" by a loud noise. This "deafness" in not
permanent, although it is often accompanied by a ringing in the
ears, and one can hear another person if he raises his voice.
Likewise, normal hearing comes back within a few hours at most.
This sort of partial hearing loss is called Temporary Threshold
Shift (TTS) (Bugliarello, et al., 1976). A TTS may be
experienced after firing a gun or after a long drive in the car
with the windows open. It may not be considered that if exposure
to this type of loud noise at a rate of eight hours a day, five
days a week can is a threat to develop permanent hearing loss.
This type of exposure to noise does not have to be as loud as a
gun being fired; it can be as simple as a person shouting across
the room. The type of hearing loss is any degree from partial to
complete hearing loss. This loss, usually, is permanent and is
not satisfactorily corrected by any devices such as, hearing
aids. The loss is caused by the destruction of the delicate hair
cells and their auditory nerve connections in the Organ of
Corti, which is contained in the cochlea (Bugliarello, et al.,
1976). Every exposure to loud noise destroys some cells, but
prolonged exposure damages a larger amount of cells, and
ultimately collapses the Organ of Corti, which causes deafness.
Most of society is now aware that noise can damage
hearing. However, short of a threat that disaster would overtake
the human race if nothing is done about noise, it is unlikely
that many people today would become strongly motivated to do
something about the problem. Yet, the evidence about the ill
effects of noise does not allow for complacency or neglect. For
instance, researchers working with children with hearing
disorders are constantly reminded of the crucial importance of
hearing to children. In the early years the child cannot learn
to speak without special training if he has enough hearing loss
to interfere effectively with the hearing of words in context
(Bugliarello, et al., 1976). In this respect, there is a clear
need for parents to protect their children?s hearing as they try
to protect their eyesight. If no steps are taken to lessen the
effects of noise, we may expect a significant percentage of
future generations to have hearing damage. It would be difficult
to predict the total outcome if total population would suffer
hearing loss. Conceivably, the loss could even be detrimental to
our survival if it were ever necessary for us to be able to hear
high frequencies. Colavita has consistently been unable to find
among university students in his classes any who could hear 20
kHz, although the classical results of Fletcher and Munson show
20 kHz as an audible frequency (Fletcher, 1953).
There are two types of hearing loss: conductive and
sensorineural (see fig.1 for anatomy of the ear). In conductive
deafness sound-pressure waves never reach the cochlea, most
often as a consequence of a ruptured eardrum or a defect in the
ossicles of the middle ear (Bugliarello, et al., 1976).
The three bones form a system of levers linked together,
hammer pushing anvil, anvil-pushing stirrup. Working together,
the bones amplify the force of sound vibrations. Taken together,
the bones double, often treble the force of the vibrations
reaching the eardrum (Bugliarello, et al., 1976).
Mitigation of potentially harmful amplification occurs via
muscles of the middle ear. These muscles act as safety device
protection the ear against excessive vibrations from very loud
noises, very much like an automatic damper or volume control.
When jarring sounds with their rapid vibrations strike the
eardrum; the muscles twist the bones slightly, allowing the
stirrup to rotate in a different direction. With this
directional shift, less force is transmitted to the inner ear:
less, not all (Bugliarello, et al., 1976).
The human ear is a delicate and fragile anatomical
structure on the other hand it?s a fairly powerful physical
force. These muscles act quickly but not always as in examples
of when the ear catches the sound of gun being shot
unexpectedly. The muscles of the ear were relaxed and were
unprepared for such a blast, because of this damage was done.
Conductive hearing loss can be minimized, even overcome by
use of the familiar hearing aids. The most common is worn over
the mastoid bond behind the pinna. It picks up sound waves and
transmits them through the skull to the cochlea.
Sensorineural hearing loss, the most common form in the
United States, occurs as a result of advancing age as well as
exposure to loud noises. In both instances there is a disruption
of the organ of Corti. The organ serves two functions:
converting mechanical energy to electrical and dispatching to
the brain a coded version of the original sound with information
bout frequency, intensity, and timbre. The hair cells of the
organ of Corti send their electrochemical signals into the
central nervous system, where the signals are picked up by
thousands of auditory nerve fibers and transmitted to the brain.
It is the decoding of all the information that enables a person
to distinguish the unique ant separate sounds of a violin,
trumpet, and clarinet, even all three are playing the same note.
The organ of corti, a gelatinous mass, is on
of the best protected parts of the body, encased as it is within
the cochlea which in turn is deeply embedded in the temporal
bone, perhaps the hardest of the 206 bones (Bugliarello, et al.,
1976). None the less, loud noise can damage the hair cells and
the auditory nerve, producing at times, depending on the type of
noise, sudden and often total deafness.
Sustained noise over a period of time can
also engender sensorineural deafness in the form of gradual
losses in hearing. This is the most common loss in teenagers
today listening to loud rock music (Bugliarello, et al., 1976).
Until a few years ago, sensorineural deafness
could not be helped by hearing aids. However, with advances in
electronic wizardry and miniaturization, devices for insertion
into the auditory canal are available.
Figure 1. Anatomy of the Ear
(von Bekesy, 1957)
The question is now; how much noise
communities will tolerate or at what point the citizenry will
have reached its threshold has never had greater currency. The
number of towns enacting strict and enforceable ordinances to
reduce and control noise levels, both day and night suggests the
point have been reached.
Barking dogs, lawn mowers, leaf blowers,
power saws, snow blowers, church bells, jackhammers,
motorcycles, airplanes, car stereo systems, and traffic
generally have combined to such a degree that noise induced
irritation, annoyance, discomfort, and hearing impairment have
become a significant public health issue, certainly enough of
one to motivate a political response.
Tables 1 and 2 indicate the magnitude of the
U.S. population exposed to noise, and the percentage expressing
annoyance with specific sources of noise. Considering that 60-dB
is akin to the sound of an air conditioner at a distance of
20ft, it is evident that with a population in excess of 280
million approximately 7%, or 17+ million people are exposed to
noise levels, from traffic alone, of from 70 to over 80 dB (U.S.
EPA).
Table 1U.S.
Population Exposed to Noise, by Level and Source, (1980)
(Million People exposed)
|
Decibels |
Traffic |
Aircraft |
Construction |
Rail
|
Industrial |
| More
than 80 |
0.1
|
0.1
|
------------ |
------
|
-------- |
| More than 75
|
1.1 |
0.3 |
0.1 |
-------
|
--------
|
| More than 70
|
5.7 |
01.3 |
0.6 |
0.8 |
---------
|
| More than 65
|
19.3 |
4.7 |
2.1 |
2.5 |
0.3 |
| More than 60
|
46.6 |
11.5 |
7.7 |
3.5 |
1.9 |
| More than 55
|
96.8 |
24.3 |
27.5 |
6.0 |
6.9 |
US Environmental Protection Agency, 1980
Table 2
Population Reporting "Highly Annoying" Noise Sources
Population per square mile
More than 20,000 3,000-20,000
Less than 3,000
| Source
|
Rank
|
% of Respondents
Highly Annoyed by Source |
Rank
|
Percentage of
Respondents Highly Annoyed by Source
|
Rank
|
Percentage of
Respondents Highly Annoyed by Source |
| Motorcycles
|
1 |
12.7 |
1 |
13.2 |
1 |
9.4 |
| Automobiles
|
2 |
9.4 |
3 |
7.4 |
3 |
4.2 |
| Large trucks
|
3 |
7.3 |
2 |
10.0 |
7 |
2.6 |
| Construction
|
4 |
6.5 |
4 |
7.2 |
4 |
3.7 |
| Sport cars
|
5 |
5.9 |
5 |
7.0 |
6 |
3.1 |
| Constant traffic
|
6 |
4.7 |
6 |
5.5 |
10 |
1.5 |
| Buses |
7 |
4.7 |
8 |
3.5 |
11 |
1.1 |
| Small trucks
|
8 |
4.1 |
7 |
4.1 |
9 |
1.5 |
| Helicopters
|
9 |
3.9 |
10 |
3.1 |
2 |
5.3 |
| Airplanes
|
10 |
3.6 |
9 |
3.4 |
5 |
3.2 |
| Power
garden tools |
11
|
1.2
|
11
|
2.1
|
8
|
1.8
|
| Total
|
|
66.0 |
|
62.2 |
|
55.9 |
Council on
Environmental Quality, 1980
Results and Discussion
Hearing loss can be entrapping in onset.
Years of traumatic exposure to high levels can occur before
symptoms become manifest. The popularity for portable sound
equipment such as Walkman-type radios and tape players has
already has already produced a sharp increase in clinically
verified hearing loss, especially among rock music addicts who
prefer their music very loud (Benarde, 1989).
Obviously, the Walkman-radio industry
believes it is not their products that are the problem; rather
it is improper use. If, they say, the volume is kept down, there
would be no problem, which is equivalent to saying that if we
all drove cautiously there would be no accidents.
Considering that earphone listening has been
around for some 20 years, why has the problem only recently
surfaced? Apparently the pattern of listening has changed.
Currently, earphones are used while walking or running on noisy
easy streets rather than in the privacy of the home or other
relatively quiet area where the listener did not wish to disturb
others. Now the volume must be turned up to overcome the noise
of city traffic. The listener wants the Walkman to blot out the
"noises of the city." Doing those courts hearing disaster. A
similar result occurs to users in noisy factory or industrial
environments.
Since to these people, louder is better, the
makings for an epidemic of hearing loss are at hand.
The Occupational Safety and Health Agency
(OSHA) has set the danger level at 95 decibels (dB) and above
for 4 or more hours per day as likely to induce permanent
hearing impairment (Benarde, 1989).
Related to the Walkman study, a recent study
conducted in New York City by Jane Mandell. Her data showed that
much of the ambulatory music is played at levels well beyond the
95-dB?upward of 100 and 125- close to the sound level of
jackhammers it may be that OSHA?s 95-dB is far to lenient and
the damage occurs below 90-dB.
Another example was during the spring and
summer of 1983; Sweden?s security was sorely tried. Russian
submarines tried to penetrate restricted naval installations in
the Hors Bay area along Sweden?s northeast coast. According to
initial reports by officials of the Naval Ministry, underwater
sound-detecting gear functioned poorly making it difficult to
pinpoint the location of the subs.
It was later determined that the problem lay
elsewhere. The young Swedish sailors manning the monitors had in
fact developed hearing losses as a consequence of excessive
exposure to rock music. On learning this, other governments
moved quickly to ascertain the hearing acuity of detectors.
Consequently, the problem of exposure to sound levels
detrimental to hearing takes on new and more serious dimensions
(Benarde, 1989).
Yet it has been argued that because noise
produces no dramatic ill effects, the public has been largely
uninterested in its suppression. It may be more to the point to
say that the degree of annoyance and discomfort that people will
endure is astonishing.
Although noise is an integral part of
civilization, it would appear that unless some definite steps
are taken to reduce the present inordinate levels in both
industry and community generally, more people will become
auditory cripples.
Fortunately, in the past few years? large
portions of the population have expressed an increasing
determination to revolt against noise. A measure of this is seen
in the number of communities moving forcefully to reduce noise
levels in their home areas.
Vexation and anger with increasing noisy
communities is not a uniquely American problem. Between May and
July 1984, over 70% of the adult population of Yamato, Japan,
signed petitions demanding cessation of the U.S. Navy?s flight
activities over their city, Yamato, with a population of
175,000, is a bedroom community for Tokyo, some 20 miles to the
northeast. U.S. Navy fighter aircraft, F-4, A-6, and E-2 jets,
100 of them on station aboard the aircraft carrier U.S.S.
Midway, fly over Yamato as they come in for landings at nearby
Atsugi Air Base. As the jets sweep low they rattle houses and
residents. The evenings are the worst with more takeoffs and
landings at full power and thus maximum noise, at a time, of
curse when the people are trying to sleep (Benarde, 1989).
Kenichi Ohsakas, a Yamato City official who
keeps track of noise levels, has been reported as saying, "it?s
just like living inside a subway car." Yamato holds regular
weekly takeoff and landing exercises to keep its pilot?s skills
honed, and night sessions are particularly important. Be that as
it may, the residents are unimpressed, cannot sleep, and prefer
the training sessions to be moved elsewhere. But where else? No
one wants them and there wretched noise.
Airplane noise can be a much greater
disturbance to sleep than other noises. Research indicates that
near a major airport-London (Heathrow) Airport- the number of
people awakened by airplanes is about 50% greater than the
number awakened by other noises (Holland-Wegman, 1967). If we
don?t isolate the problem it is going to overtake the country.
Aircraft noise began to be a major problem
with the great surge in air transportation that followed World
War II. The introduction of jet airplanes, which came into
widespread use by the end of the 1950?(Bugliarello, et al.,
1976) led to a second revolution in aviation, as well as to an
escalation of the noise level from aircraft?s. Since then,
annoyance to people living near airports caused by the noise of
jet takeoffs and landings has become a psychophysiological and
economic problem of enormous magnitude and complexity. Still a
third escalation in aircraft noise will occur when supersonic
transports come into commercial operation, and if general
aviation and, above all, vertical take off and landing.
As a result of the diffusion of air traffic,
airports tend to occupy very large land areas with multiple
runways, and large airspace?s involved in landing and takeoff
procedures. At the same time, under the pressure of population,
communities tend to expand toward airports and thus to enter
into zones of higher noise. For instance, in the area around
London (Heathrow) Airport, the population has increased by 30%
since 1963 (Wilson, 1983). Also, an increasing number of people
are working in airports and in other areas of the aviation
industry. There are signs that people?s tolerance to airport
noise is decreasing, particularly as socio-economic status
improves.
In the United States airport noise has been
hit the hardest, than any other developed country due to the
large geographic area. In 1966, in the United States there were
500 commercial air passengers per 1000 inhabitants, versus 106
for the United Kingdom, 85 for West Germany, and 36 for France
(Alexandre, 1970). By the end 1971, U.S. scheduled airlines
carried nearly 80% of all U.S. inter-city passengers traffic
traveling by common carrier (NIPCC, 1970); the major portion of
the fleet of passenger and cargo planes was powered by jet
engines, and accounted for the near totality of the capacity
flown.
Studies of both traffic noise and noise in
communities hard by major airports have concluded that elevated
blood pressure, heart disease, and psychological trauma are
direct consequences of noise exposure. Although these
associations have been reported, others contradict or do not
bear them out. Hypertension, heart disease and psychological
trauma, as well as irritation and annoyance can be engendered by
a variety of risk factors or by several operating
simultaneously. Accordingly, establishing direct causal
relationships can be exceedingly difficult. If research studies
are methodologically deficient, complications arise to further
confound relationships between the independent variable noise,
and such dependent variables as elevated blood pressure, reading
impairing, annoyance, anxiety, accidents, and heart disease.
Obviously, with the number and variety of factors known to
contribute to these events, there is good reason for
contradictory results.
One example of psychological trauma is the
research of Jenkins and his group at the London Institute of
Psychiatry (Jenkins et al., 1979). It was reviewed the findings
of two studies conducted in the area of London is Heathrow
Airport. These studies had compared rates of admission at
Springfield Psychiatric Hospital among residents living near
Heathrow. Findings suggested that areas closest to the airport,
with presumably higher levels of noise, also had the highest
rates of hospital admission.
Aircraft noise is not simply a problem for
those trying to sleep. Well- designed, well-controlled studies
have demonstrated that exposure to high levels of aircraft and
environmental noise can adversely affect reading ability in
school-age children. One example is Maser and coworkers (Maser,
et al 1978) reported that children who attended school beneath
the Seattle-Tacoma airport lnflight paths showed a deficit on
standardized tests of scholastic achievement compared to
students in quiet schools.
The problem of aircraft noise is complicated
by the great economic significance that the aviation industry
holds to the economies of developed countries. For instance, at
the end of 1971 the U.S. scheduled airlines alone had revenues
of close to $10 billion, and employed almost 300,000 employees.
Without airlines, a number of economic activities of great
importance to notional economies from business and tourism, to
the transportation of mail, would be severely affected.
Sleep disturbances are probably the most
widespread source of annoyance caused by noise, if anecdotal
responses are any criteria. Recently, French investigators
(Vallet, 1979) studied the problem under real-life conditions in
bedrooms of people living close to freeways and airports. Using
miniaturized electronic units; they recorded EEG, eye movements,
muscular activity, and heart rhythm with remote-reading
equipment. Noise inside the rooms was recorded continuously.
With the noise from the highways, subjects took longer to fall
asleep and had less deep sleep so that the young to middle-aged
group became more like the 50-60-year old group in their depth
of sleep. Rapid eye movement (REM) sleep was also reduced. If
both deep and REM sleep are physiologically and psychologically
important, this type of alteration may well be damaging. But
this remains to be substantiated by further study.
According to the investigations of Cohen and
colleagues (Cohen, et al., 1981), reading and math scores of
third grade students in noise abated classrooms were higher than
those in classrooms were without that quality were.
More recently, Green and co-workers (Green et
al., 1982) of New York University?s Institute of Environmental
Medicine found that for all elementary schools in get boroughs
of Brooklyn and Queens "an additional 3.6% of the student in the
noisiest schools read at least one year below grade level". They
went on to remark that "the dose response relationship indicated
that the percent reading below grade level increased as noise
level increased."
Other researchers have found the same kind of
relationship. For example Cohen and colleagues (Cohen et al.,
1973) determined that elementary school students living for at
least 4 years in the lower floors of an apartment complex near
heavy traffic show greater impairment of reading ability than
children living on higher floors away from the traffic. In the
studies, indoors sound levels varied form 66-dB on the lower
floors of an apartment to 55-dB on the higher floors. In a
recent U.S. EPA classification, "noisy residential areas"
averaged 58-dB and were rated low socioeconomic, while "quiet
residential" averaged 38-dB and were rated affluent
neighborhoods. These, of course, were outdoors sound levels.
With indoor levels of 55-66-dB, concentration, the ability to
pay attention, may well be difficult to nonexistent. If that is
true, it may be pertinent to ask why far more children are not
reading impaired.
Recently Peterson and co-workers (Peterson et
al., 1981) of the Department of Otolaryngology, University of
Miami School of Medicine, appeared to demonstrate in rhesus
monkeys that moderate levels of realistic noise can produce
sustained elevations in blood pressure without significant
alterations in the auditory mechanism. The unique aspect of this
investigation was the finding that changes in auditory
sensitivity did not necessarily follow changes in such
physiological paramentes as blood pressure.
Given the concern over noise, one wonders
just how desirable a quiet town would be. Darlington, near
Newcastle, England, was almost such a place. Between 1976-1978,
Darlington was designated a "quiet town experiment" (Gloag,
1980). Noise abatement zones and better traffic management was
instituted, as were vehicle noise testing and stricter
enforcement of noise regulations.
Sudden and unexpected noise has been observed
to produce marked changes in the body, such as increased blood
pressure, increased heart rate, and muscular contractions.
Moreover, digestion, stomach contractions, and the flow of
saliva and gastric juices all stop. Because the changes are so
marked, repeated exposure to unexpected noise should obviously
be kept to a minimum. These changes fortunately wear off as a
person becomes accustomed to the noise (Broadbent, 1957).
However, even when a person is accustomed to an environment
where the noise level is high, physiological changes occur.
Noise has psychological effects is undoubted.
The question is how these effects can be assessed and whether
they lead to damage. No clear case has been made thus far for
psychological damage caused by moderately high levels of noise,
the levels that would cause hearing damage to only a small
fraction of the people exposed. Indeed, fears have been
expressed that ". . . over emphasis on damage may backfire when
people come to realize that the truth of the matter seems to be
simply that people can express violently their dislike about
being disturbed by noises. This is recounted vividly by Connell
(1972):
. . . A middle-aged woman living in Soho became affected by
the incessant noise from a newly open discotheque. She
complained to the management, the Police, the Local
Authority but nothing was done to reduce the noise. Her
action took the form of suicide. In Italy a 44 year old man
took an overdose of drugs because his eleven children made
too much noise while he was watching the Olympic Games on
television. . . In a quiet part of Middlesex with an ambient
noise level of 30 to 40 decibels lived Fred, a lusty,
healthy builders laborer. The M4 Motorway was built within a
few feet of his cottage home. The resultant traffic caused
the noise level to rise to 80 and 90 decibels so this poor
man suffered an increase of 100,000 times in the noise
level. He took it for some weeks. Discovered there was
nothing he could do about it and his action was also
directed against the self. He left a note which read "The
noise; the Noise; I just couldn?t stand the Noise". . .
These are clearly extreme cases of reaction to
the intrusion of noise into one?s life. But without question the
ubiquitousness of the intrusion, even if less severe or less
fatally resented, leads to demands for acoustic privacy which
are psychologically no less important than those for visual
privacy (Cohen, 1969; EPA, 1971a).
Future Aspects
In this paper, it has been discussed of the
important aspects of a complex socio-technological problem,
noise pollution. It now remains to elaborate upon some of the
deeper issues that we have broached. There is no doubt that the
problem of noise is serious. Large segments of the population
and industrialized society are exposed to high levels of noise,
not only at their place of work, but also in their residences
and in their leisure activities. In the United Kingdom, for
example, more than 10 percent of the population is disturbed the
noise at a single airport, London Heathrow (Wilson, 1983).
Even with the relatively ambitious steps
currently being taken or envisioned to control noise in most
countries, sound levels and exposure to noise will remain high,
and possibly increase. At the same time rising living standards
will bring about demands for better environmental quality and
probably lead to more vigorous and more organized protests
against noise. These protest may even be triggered by lower
noise levels than in the past, for it is highly likely that as
the public acquires more amenities it will want to be exposed to
"comfortable" rather than merely tolerable levels of sound
(Bauer, 1970).
According to a WHO report to the UN
Conference on Environment. Of all environmental problems, noise
is the easiest to control". But the question of control will
arise only after these in awareness among the people of the need
for control and for the government to find some solution for it.
- The first approach has been to reduce
noise at source. Design and fabrication of silencing devices
and their use in aircraft engines, trucks, cars,
motorcycles, industrial machines and home appliances would
be an effective measure. Protection to workers can be
provided through wearing devices such as earplugs and
earmuffs.
- Making a change in design and operation
of machines, vibration control, sound proof cabins and
sound-absorbing materials can reduce it.
- It can get reduced by prescribing noise
limits for vehicular traffic, ban on honking of horns in
certain areas and planning main traffic arteries, industrial
establishments, amusement areas, residential colonies,
creation of silent zones near schools and hospitals and
resigning of building to make them noise proof. Other
measures can involve reduction of traffic density in
residential areas giving preferences to mass public
transport system.
- Control of Indoor Noise. Where
outdoor noise levels have been high, the following methods
can be applied for reducing their effect.
- Locate in the building as far as
possible from noise source. The noise level
drops about 6dB each time the distance is
doubled.
- Trees and shrubs may be planted in front
of building to provide some
absorption for the sound.
- Locate non-critical areas such as
corridors kitchens, bathrooms, elevators
and service spaces in the noisy side and
critical areas each as bedrooms and
living spaces on the quiet side.
- Back to back bathrooms or toilets should
be avoided unless they are effectively sound isolated.
Bathrooms, kitchen and laundry rooms should not be adjacent
to the floor.
- Bathroom walls, floor and ceiling should
be sound insulated using construction of high sound
insulation glasses.
- Noisy toilets, is bettered by quiet
siphon jet type flush toilets should be installed to reduce
the noise from the source. Commode seats with double siphon
system are now available and may be adopted wherever
possible.
- Road Noise. Vegetation buffer
zones must be created in different parts of the city.
Efforts should be made for roadside plantations.
- An Urgent Need for Legislation to
Control Noise Pollution. We have seen that in India, in
absences of a specific legislation for control and
prevention of the noise pollution, one has to seek
provisions in various branches of law and regulations. There
has been no doubt that the available provisions in various
branches of law and regulations. There has been no doubt
that the available provisions in various branches of law are
adequate, unscientific and crude. In most of the developed
countries specific legislations have been made and
scientific methods for investigation of noise pollution have
been invented. The science of audiometer and other branched
related to sound have been developed and it becomes
comfortable to device various legal provisions to control
and prevent noise pollution.
As present, there is no specific and
detailed legislation to control the noise
pollution. However, there is an urgent
need that the Central Government of India should manage to
get a legislation passed for the control of noise pollution.
Some legislation regarding water and air pollution have been
made in India.
Government should pass the ?Noise
Pollution control Act? to meet special India condition.
Apart from such kind of Central legislation, there should be
a city noise control code for all major cities in India.
Creation of unnecessary noise has to be prohibited and
should be punishable under law.
- Education. People can be educated
through radio, TV, newsreels in cinema halls about noise
pollution. In the family, elders can teach children to keep
the radio volume low, low voice talking not to horn
unnecessarily on the roads, avoid quarreling amongst each
other and so on. There should be complete ban of
loudspeakers form 8 p.m. to 7 a.m.
- Public Awakening and the Control.
It is also important that public awakening is also very
essential for the control and prevention of the noise
pollution. In India, most of the persons lack any idea about
the ways in which noise pollution could be controlled. Very
few scientist are aware of the problem and its control.
Masses are still ignorant of the grave effects of the noise
pollution. In this regard television, radio, internet, and
newspapers should give a campaign for wide publicity.
It is also true that in the present set up
of industrialization one should be able to face the noise
pollution to a certain extent. If somehow form a machinery
noise producing gadget has been taken out completely, in
such cases noiseless machinery may become more dangerous,
then with noise creating gadget. Take the example of a
locomotive engine. Noise of a locomotive engine especially
the noise of its whistle has been very useful in keeping
humans and animals away form the tracks. In such cases a
limit of noise in terms of decibels may be recommended.
The most important body of people who are
or should be involved in noise control are the manufactories
of noise-producing devices, since in their hands lies the
most effective way of controlling noise at the source.
However, we live in a society where even the most
enlightened manufacturers need an incentive to invest in the
extensive research, development, design and tooling that
might be required to reduce noise emissions form their
products. Such incentives are provided, in essence, by
legislation enforced either centrally or locally. To
appreciate the number of people and organizations involved
in legislation for noise control and with ways in which they
influence this legislation require a look at the history of
governments concern with problem of noise.
These standards or "ideas" may be easily
controlled of all environmental problems, but just as every
other problem, do we want to change for the sake of noise
pollution? If the question is answered with integrity and
honesty, it is sure that not many would want to change over
some small portion of noise pollution. With the exceptions
of the throwing the blame at someone else makes it so much
easy to control noise, since its not the life of yourself
being at stake to change.
Literature Cited
Alexandre, A., 1970. Pervison de la gene due
au bruit autour des aeroports et perspectives sur les moyens d?y
reedier. Laboratoire d?Anthropologie Appliquee, Faculte de
Medecine, Paris,
Bauer, R. A. Predicting the Future.
Transportation noise---a symposium on acceptability criteria,
Washington, D.C., 1970
Broadbent, D. E. 1967. Personal communication
Broadbent, D. 1957. Noise in Relation to
Annoyance, Performance and Mental Health. J. Acoust. Soc. Am.
Vol. 68(1): 15-17
Bugliarello, G. The Impact of Noise
Pollution, New York, 1976
Cohen, A. 1969. Effects of noise on
psychological state. In W. Ward and J. Fricke, Noise as a public
health hazard. Washington: American Speech Hearing Association
Cohen S.; Glass, D. C.; and Singer 1973.
Apartment Noise, Auditory Discrimination and Reading Ability in
Children. J. Exp. Soc. Psycho. Vol. 9: 407-422.
Connell, J. 1972. The biological effects of
noise. Paper given at the Annual Meeting of the British
Association for the Advancement of Science.
Fletcher, H. 1972. Speech and Hearing in
Communication. Princeton, NJ: Van Nostrand, 1953. Noise Control
Center, Wymondkam, Leicestershire, U.K. Personal communication.
Gloag, D. 1980. Noise and Health: Public and
Private Responsibility. Br. Med. J. Vol. 281: 1404-1406
Green; Pasternack; and Shore. 1982. Effects
of Aircraft Noise on Reading Ability of School aged Children.
Arch. Environ. Health Vol. 37: (1) 24-31.
Holland-Wegman Productions. 1967. Inc. Public
Relatins for Buffalo Airport. Personal communication,
Jenkins, L. M.; Tarnapolsky, A.; Hand, D. J.;
and Baker, S. M. 1979. Comparison of Three Studies of Aircraft
Noise and Psychiatric Hospital Admissions Conducted in the Same
Area. Psychol. Med Vol. 9: 681-693.
Maser, A.; Sorensen,; and Krypter, K. 1978.
Effects of Intrusive Sound on Classroom Behavior: Data from a
Successful Lawsuit. San Francisco.
Peterson, W. H. and Northwood, T. D. 1981.
Noise raised blood pressure without impairing auditory
sensitivity. Science Vol. 211: 1450-1452.
United States National Industrial Pollution
Control Council (NIPCC), 1970
Vallet, M. Psychophysiological 1979. Effects
of Exposure to Aircraft or to Traffic Noise. Proc. Inst.
Acoustics Vol. 3: 1-4.
Von Bekesy, George. 1957. The Ear, Scientific
American, 197: 61-67
Council on Environmental Quality. 1979. US
Government Printing Office, Washington D.C.
US Environmental Protection Agency. 1980. The
Extent of the Noise Problem.
WHO Report. 1990. UN Conference.
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pumps and gas vents. Since its inception ArtUSA has tackled silencing
problems covering the entire spectrum of industries and applications. Our
acoustical and mechanical engineers can design complete air inlet silencing
systems, including filter houses of various configurations.
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