|
The
Effects of Sound Barrier Design on Highway Noise Attenuation |
Researched
by Steven P.
1999-2000
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PURPOSE
The purpose of this experiment
was to determine if a sound barrier does reduce noise, and which
type of barrier is the most effective in reducing highway traffic
noise.
I became interested in
this idea because many people are concerned about noise pollution,
and there is a great need to reduce this noise. I wanted
to find out which sound barrier is the most effective in reducing
highway noise.
The information gained
from this experiment will help society because engineers will
know what type of sound barrier is the most effective in reducing
highway traffic noise.
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HYPOTHESIS
My hypothesis is that
a sound barrier will reduce noise and that a concrete or wooden
barrier will more effectively reduce highway noise when compared
to an earth berm or vegetation.
I base my hypothesis
on information about sound barriers and the characteristics of
sound available from the Washington State Department of Transportation
and from the book, Understanding Sound by Beulah Tannenbaum and
Myra Stillman.
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EXPERIMENT
DESIGN
The constants in this
study were:
a. The calibrated decibel
meters used.
b. The distance from
both sides of the sound barrier where the readings were taken.
c. The intervals
of time between each measurement.
The manipulated variable
was the type of sound barrier used to reduce traffic.
The responding variable
was the level of recorded traffic noise behind the sound barrier.
To measure the responding
variable I used hand-held decibel meters.
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MATERIALS
| Quantity |
Item Description |
| 3 |
Decibel Meters (digital) |
| 3 |
Decibel Meter Calibrators |
| 1 |
Hard Hat |
| 1 |
Safety Vest |
| 3 |
Clipboards |
| 1 |
30m Tape Measure
(Fiberglass Reinforced) |
| 1 |
5m Tape Measure (Metal) |
| 3 |
Watches |
| 1 |
Camera |
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PROCEDURES
Phase I: Determine
if a sound barrier is effective in reducing highway noise.
This phase
of the experiment will be conducted along a highway with a concrete
barrier adjacent to an open field. This will allow for
direct comparison of decibel readings with and without a sound
barrier.
1. After arriving at
the site, calibrate all three decibel meters using the calibrator
made for each meter.
2. Set up one decibel
meter in the open field near the road for the road side reading.
3. Take a reading
every 30 seconds for 10 minutes and record the readings on a
data sheet.
4. Record the Leq
(average sound level) and the Max (highest reading) level for
this period of testing.
5. Place a decibel
meter 3 meters back from the decibel meter location in step 2.
6. Place the next
decibel meter 17 meters farther back, and the last decibel meter
another 17 meters from the second one.
7. Station a person
at each meter to record the decibel readings every 30 seconds
for 10 minutes. Use a watch to keep track of time.
8. Have a fourth
person take a traffic count during this 10 minute period.
Count the number of light, medium, and heavy vehicles passing
by the location. Counting traffic helps determine what
is creating the noise during the experiment.
9. At the end of
this 10 minute period, record the Leq and the Max levels from
each of the decibel meters on the data recording sheet.
10. Move the three
decibel meters down the length of the sound barrier, far enough
so sound coming around the end of the barrier doesnít
affect the readings.
11. Place each meter
at the distances described in steps 5 and 6.
12. Repeat testing
procedures 7 and 9 to collect decibel readings behind the sound
barrier.
13. Retest the calibration
of each decibel meter to make sure they were accurate throughout
the test. If they are out of calibration by more than one
decibel, redo the test.
Phase II: Compare
different types of sound barriers to see which is the most effective
in reducing highway noise.
1. After arriving at
the chosen sound barrier, calibrate the decibel meter.
2. Measure out 2
meters from the barrier on the road side for the placement of
the decibel meter.
3. Start recording
decibel readings every 30 seconds for 10 minutes.
4. At the end of
the 10 minute period, record the Leq and the Max level.
5. During the same
10 minute period have another person count and record traffic
as done in Phase I.
6. Move to the other
side of the barrier and measure out 3 meters behind the barrier
to position the decibel meter.
7. Record decibel
readings every 30 seconds for 10 minutes at this new decibel
meter position.
8. Measure off 20
more meters (for a total of 23 meters behind the barrier) for
the next decibel meter position, and repeat steps 3 and 4.
9. Measure off another
20 meters (for a new total of 43 meters behind the barrier) for
the final decibel meter position, and repeat steps 3 and 4.
10. At the end of
the testing, check the calibration to see if the decibel meter
was accurate throughout the test. If it is out of calibration
by more than one decibel, redo the test.
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RESULTS
The original purpose
of this experiment was to determine if a sound barrier does reduce
highway noise, and which type of sound barrier most effectively
reduces highway noise.
A - weighted decibel
readings were used to compare noise readings in front of and
behind the barrier. This scale most closely represents
human hearing. Decibel readings were averaged (Leq) to
obtain average noise levels for easy comparison. Lower
decibel readings indicated lower noise levels. A larger
difference in readings from the road side of the barrier to behind
the barrier meant a greater reduction in noise.
Results for both phases
of the experiment are shown on tables and graphs on the following
pages.
Phase I Results:
See
Graph (long download)
The purpose of Phase
I was to determine if a sound barrier did reduce highway noise.
At three meters behind
the wall, highway noise was reduced by 9 decibels when compared
to the open field, which was the greatest noise reduction at
comparable monitoring positions. At 20 meters behind the
barrier, there was a one decibel reduction compared to the open
field readings. There was a 5 decibel reduction difference between
open field and barrier readings 37 meters behind the barrier.
At 37 meters behind the
barrier, highway noise was reduced 15 decibels from in front
of the barrier. At 37 meters back in the open field noise
was 10 decibels lower than the road side reading.
At all meter positions
behind the wall, decibel readings were lower than in open field.
Phase II Results:
See
Graph (long download)
The purpose of Phase
II was to determine which barrier effective at reducing highway
noise.
Concrete Wall: Noise
was reduced 17 decibels 3 meters behind the concrete wall, and
20 decibels at 43 meters behind the wall.
Earth Berm: 3 meters
behind the earth berm noise was reduced by 20 decibels, and by
21 decibels at 43 meters behind the berm.
Wood Fence: The wood
fence reduced noise by 10 decibels 3 meters behind the wall,
and by 16 decibels at 43 meters behind the wall.
Vegetation: Noise was
only reduced by three decibels 3 meters behind the trees, and
by 5 decibels at 43 meters behind the trees.
The earth berm had the
greatest noise reduction at all decibel meter positions, and
the concrete wall had the second highest noise reduction at all
of the decibel meter positions. However, the difference
in noise reduction between the earth berm and the concrete wall
was 3 decibels immediately behind the barrier and only 1 decibel
at the farther positions. The vegetation did the worst job at
reducing noise at all three of the decibel meter positions.
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CONCLUSIONS
My hypothesis was that
a sound barrier would reduce noise, and that a concrete or wooden
wall would reduce highway noise better than an earth berm or
vegetation.
The results indicate
that my hypothesis should be partially accepted. Data showed
the sound barrier did reduce highway noise, so the first part
of my hypothesis was correct. However, the earth berm reduced
highway noise better than a concrete barrier by a few decibels,
which was different than the second part of my hypothesis.
Because of the results
of this experiment, I wonder if a more detailed analysis would
show more clearly the shadow zone, since noise may pass over
the barrier. I also wonder what consideration engineers
give to cost, aesthetics, and space limitations in the design
and building of a sound barrier. Even though the earth
berm was the most effective in reducing highway noise, it took
up a lot of space.
My findings should be
useful to engineers because they will know that an earth berm
is effective in reducing highway noise, and so is a concrete
wall.
If I were to conduct
this project again, I would try to get four of the same decibel
meters for use at the same time. This could improve data
collection and reduce time. I would also conduct the experiment
during a time of year when there isnít as great a chance
of adverse weather conditions. Weather conditions affected the
locations and choice of barriers to study. I might also
include a section for the analyzing of the barriers to see if
they were reasonable and feasible to construct.
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RESEARCH
REPORT
Introduction
Information that is important
to sound barriers includes sound and sound barrier design.
In the first part of this report, I am going to talk about sound,
the characteristics of sound, decibels, acoustics, and noise.
In the second part I will explain the types of sound barriers,
how they work, and the design and construction of sound barriers.
SOUND
What is Sound?
Sound comes from the
vibrations in molecules, and is always traveling through a substance,
whether it is a solid, liquid, or gas. Sound cannot travel
through a vacuum because there are no molecules for the sound
to travel through.
When sound waves reach
our ears, they vibrate the eardrum. The vibrations are
sent through the three bones in the middle ear. These impulses
are then sent to the brain. Our ears are never free from
sound. There is always sound, and some of it is pleasant,
and some of it isnít. If your eyes were as sensitive
as your ears, you could see a 100-watt light bulb 3218 kilometers
(2000 miles) away. It is hard to find silence, except
in soundproof rooms, which arenít always totally soundproof.
There is constant background sound, which we usually donít
notice, and an occasional sudden sound. The background
sound can be very helpful to tell us where we are and what time
it is. Sound can also provide other information, and can
serve as a warning system.
If a sound is made, and
nobody is around to hear it, it is called unheard sound.
If a sound is made and if there is someone around to hear it,
it is called heard sound.
Characteristics of Sound
Sound waves are a series
of compressions and rarefactions. Compression occurs when
the molecules are compressed. Rarefaction happens when the molecules
are thinned out. Between the compression and rarefaction
zones, there is a neutral zone where the density of the molecules
is equal to or almost equal to the density before the sound was
made. These three zones of high pressure, low pressure,
and neutral pressure form a sphere of waves with the source of
the sound at the center.
The wavelength
of a sound is the distance from a compression or rarefaction
zone to the next similar area. The amplitude is
the pressure difference between compression or rarefaction zone
and the neutral zone. The term amplitude, intensity, and volume
are the same, and can be used to describe loud and quiet sounds.
Frequency is how many
sound waves pass by per second (cycles per second). The
number of cycles per second (or cps) is called hertz. A
higher frequency equals a shorter wavelength, and a lower frequency
equals a longer wavelength. Examples of higher frequency
sounds are someone whistling, a flute, and a high voice.
Some low frequency sounds include a foghorn, low voice and the
rumble of an earthquake. Everything has a natural frequency.
Humans can hear between 15 Hz and 20,000 Hz. If a sound is above
20,000Hz, it is called an ultrasonic sound.
Sound travels at different
speeds, depending on the substance it is traveling though.
The following chart shows some examples:
SUBSTANCE |
SPEED |
Dry Air/ 0 Degrees C |
330 mps |
Dry Air/ 1000 Degrees C |
700 mps |
| Hydrogen |
1315 mps |
| Carbon Dioxide |
182 mps |
| Water |
1400 mps |
| Copper |
3560 mps |
| Aluminum |
5100 mps |
| Brass |
3505 mps |
| Granite |
3947 mps |
Steel |
5090 mps |
mps
= meters per second
An echo is the reflection
of sound off of an object. Sonar uses echoes to determine
depth, and other distances. A megaphone also uses reflection
to direct beam of sound out of its cone.
Free vibration is vibration
that dies out in time such as when a tuning fork is struck. Maintained
vibration is making the vibration last. A trumpet holding
a note is an example of maintained vibration. Forced vibration
is making something vibrate at an unnatural frequency.
The eardrum has a natural frequency, too, but is made to vibrate
at the frequency of sounds it receives. The stick and slip
vibration method is when something is pulled or pushed until
it slips such as with a violin. The strings of the violin
are pulled by the bow until they slip, creating a vibration.
Resonance is sound waves making a separate object vibrate.
Decibels
Sound is measured in
decibels (dB). This is a unit measuring the relative intensity
of sounds. The decibel is named after inventor Alexander
Graham Bell. Most people speak in a range between 45 and
75 decibels. A decibel, which is a tenth of a bell, is
the smallest change in sound that a human can hear. The
scale starts at 0, which is the quietest sound that can be heard
by a human. The test results taken during my experiment
are measured in an A-weighted scale.
This is a scale that
is designed to approximate human hearing.
Because sound is measured
on a logarithmic scale, an increase of 10 dBA sounds twice as
loud. For example, 30 dBA sounds twice as loud as 20 dBA.
A double in the source of a sound equals a 3 dBA increase.
For example, one car may have a 70 dBA sound level. Two
cars at the same speed, distance, and point would then have a
73 dBA sound level, and 4 cars at the same speed, distance, and
point would have a 76 dBA sound level.
The amplitude of a sound
increases as you get closer to the source of a sound, and decreases
as you move away. The change in intensity is related
to the square of the ratio of the distances. For example,
the intensity of a sound 100 meters away from the source is one-fourth
as intense as it is 50 meters away from the source.
The mathematical formula in this example would be (50/100) 2
= _. Another example, the intensity of a sound 20
meters from the source is 9 times the intensity of a sound 60
meters from the source, or (60/20) 2 = 9.
Acoustics
The word acoustic comes
from the Greek language and means "to hear".
Acoustics is sometimes referred to as the science of sound.
More often it is referred to as
architectural acoustics,
which is the design of a building's acoustical environment. Recently,
this has become a greater area of study.
Marcus Pollio, a Roman
architect who lived in the first century BC made important observations
on acoustics, and formed hypotheses on reverberation and interference.
The scientific study of acoustics was not done until 1856 by
the American physicist Joseph Henry. Wallace Sibine, another
American physicist, later studied acoustics in more detail in
1900.
Sound reflects off any
surface the waves encounter. Rooms can be designed and
built for the best natural reflection with no undesired distortion.
Architects use materials that help enhance reflection and absorption
of sound. Cork and felt are good acoustical dampers while
metal and stone reflect sound. A roomís acoustics
are usually good if there is a balance between reflection and
absorption materials.
The science of acoustics
is of great concern when designing sound barriers, not only for
roads and highways, but in all necessary locations.
Noise
Noise has been defined
in many ways. The Council on Environmental Quality defines
noise as "sound without value." The World Book Encyclopedia
Dictionary entry states that noise is "a sound that is not
musical or pleasant". The American Standards Association
calls noise "an undesired sound". Encartaís
article on noise says, "Noise is a complex sound, a mixture
of many different frequencies or notes not harmonically related."
AASHTO, the American Association of State Highway and Transportation
Officials calls noise "unwanted sound."
Noise can cause physical
harm. If you are exposed to a sound of 120 decibels it
is painful. If you are exposed to a sound of 170 decibels,
even for a moment, it will knock you unconscious, and destroy
your hearing.
People thought that noise
just went along with progress, and that you had to put up with
it. We now know that noise can be reduced with out slowing
down progress. Some people donít mind some noise,
while others donít like it at all. We use sound
barriers along highways and other locations to reduce noise to
a tolerable level.
There are three major
ways of reducing highway noise. The first way is to improve
cars so that the engines and other parts run quieter, which will
reduce the noise by 5 to 10 decibels. The next way to reduce
noise is to leave open spaces between highways and houses when
either is being designed and built. You could also put
less noise-sensitive buildings or facilities next to the roads.
The last way is to use sound barriers or other noise reducing
measures if the noise level is above standards.
Sometimes insulation
can be used in buildings to reduce noise. This is usually
not a very good idea because the road contractors donít
have the authority to insulate buildings, and if buildings are
insulated, then you would have to spend more money on air conditioning
since there is no way for air to easily flow in and out.
There are several other
ways to solve the noise problem when building new roads.
You can build away from noise-sensitive areas and through non
noise-sensitive areas or through undeveloped land. Constructing
partially underground, so walls on side deflect noise from residents
is also an easy possibility. Making the road level the
best that is possible so car engines donít work as much
on hills can also reduce sound.
SOUND BARRIERS
Sound barriers are being
used more and more as the demand for reduced noise along highways
becomes greater and greater. Sound barriers are built on
new as well as existing roads. The U.S. Congress passed
legislation in 1976, which required states to reduce noise along
highways beside impacted areas. The federal government
pays for most of the barrier construction, and the state pays
for the rest. Noise barriers reduce the decibel level by
10 to 15 decibels, which is cutting the sound in half.
Usually you get a one decibel reduction for every two vertical
feet of barrier added, though the effectiveness and costs evens
out at about 13 feet in height.
Types
There are two main types
of noise barriers: earth berm and noise walls (concrete, masonry,
wood, etc.). Construction can include each type separately
or in combination. You use the noise readings to help decide
the type, location, length, and height of a noise barrier.
The visual look also is a factor that decides which type to build
at the given site. Vegetation is sometimes used for noise
reduction.
Noise walls can be constructed
out of concrete, stucco, masonry, wood, and metal. There
are a variety of designs and styles used depending on what is
needed at the location. They are designed to blend into
their surrounding but still be effective.
You should use an earth
berm for visual looks, but only if the materials and room allows.
An earth berm blends in with its surroundings very well, and
can have plants added to it to virtually cover it up. An
earth berm usually should not have a slope steeper than
about a 22º.
Vegetation can be used
if it is tall enough and it is dense enough (you canít
see though it). Vegetation at least 200 ft thick can give
a 10 decibel reduction. It is usually impractical to put
in vegetation, because of cost and because there is usually not
enough room.
Design and Construction
The engineer designing
a sound barrier must consider the most effective way to reduce
noise with its location and design. A sound barrier will
only work if the residents behind it canít see the road
(meaning that they are in the shadow zone). The barrier
wonít work for residents above wall, such as on a hillside,
and homes that are too far apart make it very hard to build a
barrier for a reasonable cost. Sections that are taken out (not
put in) of sound barriers for roads or other purposes reduces
the effectiveness of the barrier, since the sound is able to
travel through the opening.
The following are some
of the considerations for the construction and design of a sound
barrier:
- The desired noise reduction
- The right of way needs
and maintenance
- Cost and constructability
- Maintenance
- Wind
- Soil type
- Earthquakes
- Vehicle impacts
- Vehicle access( to and
through it)
- Pedestrian access
- Matches other structures
around it (design, looks)
- Drainage
- Water/Electricity
- The moving of objects
or buildings to put in the barrier.
There are several other
prospects for an engineer to consider when designing sound barriers.
Here are some factors that help calculate the sound produced
by traffic:
- 2000 cars per hour is
twice as loud as 200 cars per hour.
- Vehicles traveling at
65 miles per hour sound twice as loud as vehicles traveling at
30 miles per hour.
- 1 truck traveling at
55 miles per hour is the same as 28 cars traveling at 55 miles
per hour.
Defective mufflers, other
faulty engine parts, hills (making the engine work harder), the
engine itself, aerodynamics, and the tires on the road can all
contribute to traffic noise. Traffic noise has a
frequency of about 550 hertz, so engineers also have to know
how to design a sound barrier with these frequencies.
Engineers will
only design a sound barrier for an area if it is an impacted
location. An impacted location is an area used by humans
where traffic noise (during the design year) equals or exceeds
66 dB. The level is set at 66 dB because 2 people canít
have a normal conversation from 1 meter apart.
|
Design Year Traffic
Noise Decibel Level |
Allowed Cost Per
Household* |
Equivalent Wall
Surface Area Per Household (square meter)
|
| 66 dBA |
$15,000 |
65 sq. m |
| 67 dBA |
$17,000 |
71.5
sq. m |
| 68 dBA |
$18,500 |
77.7
sq. m |
| 69 dBA |
$20,000 |
84 sq. m |
| 70 dBA |
$21,500 |
90.5
sq. m |
| 71 dBA |
$23,000 |
96.7
sq. m |
| 72 dBA |
$24,500 |
103
sq. m |
| 73 dBA |
$26,000 |
109.2
sq. m |
| 74 dBA |
$27,500 |
115.5
sq. m |
*Reevaluated
in January of each year. Based on $22.10
per square
foot constructed cost. WSDOT
Sound decreases 3 to
4.5 dBA as the distance from the source is doubled because of
objects that deflect the sound, and because sound also gets weaker
as the distance from the source becomes greater. Generally,
a distance farther than 500 ft from heavy traffic on a freeway
is not a major concern. On lightly traveled roads distances
of 100 to 200 feet from traffic is not a major concern either.
Another consideration
is wind. You need a taller sound barrier for wind that
is traveling with sound just as in the concepts in "Characteristics
of Sound." If you have a wind travelling against the
sound, the barrier doesnít need to be as tall.
Summary
I hope you enjoyed my
report and learned about sound, its characteristics, and sound
barriers. You can continue reading my journal to see how
sound barriers reduced highway traffic noise.
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BIBLIOGRAPHY
"Acoustics,"
Microsoft Encarta, 1998.
American Association
of State Highway and Transportation Officials, A Policy on Geometric
Design of Highways and Streets, Washington. D.C., 1990.
Cohn, Louis F. Ph.D &
Harris, Roswell A. Ph.D. P.E., Special Noise Barrier Applications
Phase II, [Online] Available http://www.wsdot.wa.gov/ppsc/research/onepages/WA-RD3781/htm/,
November 2, 1999.
Grey, Jerry, Noise, Noise,
Noise!, Philadelphia, PA, Westminster Press, 1975.
Knauss, Harold P., "Sound,"
The New Book of Popular Science, Grolier, 1994.
Rubel, David, Kidís
Science, New York, Scholastic Inc., 1995.
"Sound," Microsoft
Encarta, 1998.
Tannenbaum, Beulah &
Stillman, Myra, Understanding Sound, New York, McGraw Hill Book
Company, 1973.
United States Department
of Transportation, Acoustics and Your Environment, Cambridge,
MA, February 1999.
Washington State Department
of Transportation, Design Manual (M 22-01), Olympia WA, December
1998.
Washington State Department
of Transportation, "Frequently Asked Questions," Air
Quality and Noise Studies, [Online] Available http://www.wsdot.wa.gov/regions/northwest/noise/faq.htm/,
November 2, 1999.
Washington State Department
of Transportation, Highway Traffic Noise, [Online] Available
http://www.wsdot.wa.gov/regions/northwest/noise/1.html,
November 7, 1999.
Washington State Department
of Transportation, "Noise Policies," Air Quality and
Noise Studies, [Online] Available http://www.wsdot.wa.gov/regions/northwest/noise/policies.html/,
November 8, 1999.
"Wave Motion,"
Microsoft Encarta, 1998.
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