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Alum-A-Frame
Enclosures |

Flexible Noise
Barriers |

Modular Acoustic
Panel Enclosure |
|
 
Art-Acousti-Lagging |
 
Flexible-Art-Acousti-Wrap |
 |
| Features: |
|
|
|
- High and low temperature
applications
|
|
- Quilted fiberglass decoupler
available
|
- Good corrosion resistance
|
- Meets Class A flammability rating per ASTM
E-84
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|
| Acoustical Data: |
| Sound Transmission Loss (dB) Octave Center Frequencies (Hz) |
| Products |
Sound Transmission Loss (dB)
Frequency (HZ) |
STC |
| 125 |
250 |
500 |
1000 |
2000 |
4000 |
| B-10 LAG |
15 |
16 |
21 |
26 |
33 |
38 |
26 |
| B-10 LAG / QFA-3 |
18 |
18 |
23 |
30 |
39 |
46 |
29 |
| B-10 LAG / QFA-9 |
19 |
20 |
23 |
33 |
44 |
53 |
30 |
| Per ASTM: E 90 |
|
| |
Sound Absorbtion
Data-Absorber Component Random Incident Sound
Absorbtion |
| Products |
Octave Band Center Frequencies
(HZ) |
NRC |
| 125 |
250 |
500 |
1000 |
2000 |
4000 |
| ABA Products 1" th. |
.12 |
.47 |
.85 |
.84 |
.64 |
.62 |
.70 |
| ABA Products 2" th. |
.07 |
.27 |
.96 |
1.13 |
1.08 |
.99 |
.85 |
| ABA Products 2" th. |
.19 |
.99 |
.96 |
.80 |
.57 |
.33 |
.85 |
| Per ASTM: E 90 |
|
| Physical Properties of Components: |
| Product |
Weight |
Thickness |
Service Temperature |
Tensile Strength |
Tear Strength |
Elongation |
“R”
Factor |
Barrier |
| B-10 LAG |
1 Lb. PSF |
.090” |
-10 to +180 F |
400 PSI |
72 |
40% |
- |
Decoupler / Absorber |
| QA-3 |
.2 Lb. PSF |
1“ Nom |
-20 to + 350 F |
- |
- |
- |
4.0 |
| QA-9 |
.4 Lb. PSF |
2“ Nom |
-20 to + 350 F |
- |
- |
- |
8.0 |
Sound Absorbtion
Data-Absorber Component Random Incident Sound
Absorbtion |
| Products |
Octave Band Center Frequencies
(HZ) |
NRC |
| 125 |
250 |
500 |
1000 |
2000 |
4000 |
| ABA Products 1" th. |
.12 |
.47 |
.85 |
.84 |
.64 |
.62 |
.70 |
| ABA Products 2" th. |
.07 |
.27 |
.96 |
1.13 |
1.08 |
.99 |
.85 |
| ABA Products 2" th. |
.19 |
.99 |
.96 |
.80 |
.57 |
.33 |
.85 |
| Per ASTM: E 90 |
Sound Absorbtion
Data-Absorber Component Random Incident Sound
Absorbtion |
| Products |
Octave Band Center Frequencies
(HZ) |
NRC |
| 125 |
250 |
500 |
1000 |
2000 |
4000 |
| ABA Products 1" th. |
.12 |
.47 |
.85 |
.84 |
.64 |
.62 |
.70 |
| ABA Products 2" th. |
.07 |
.27 |
.96 |
1.13 |
1.08 |
.99 |
.85 |
| ABA Products 2" th. |
.19 |
.99 |
.96 |
.80 |
.57 |
.33 |
.85 |
| Per ASTM: E 90 |
|
| |
|
Flexible Noise Barriers
by ArtUSA
More than ever
before we are experiencing disturbances in our work and personal
lives. Such noise pollution can affect not only our peace of
mind but also tension levels, communication between people, and
even safety in the workplace. Home and condo owners are becoming
aware of low EPA and EPC noise standards, allowing easy
litigation against sellers and builders for noise levels from
adjoining units. (residential is 55 db at night, 60 db during
the day) It is of course much easier to head off the problem
during construction rather than correct it (if even possible)
after. OSHA is focusing more on noise levels in the work place
than ever before. The cost effective solution, is to stop noise
problems before they happen. Today's construction techniques
leave much to be desired in these areas. The best acoustic
isolation methods (rooms within rooms) are far too costly.
Contrary to common usage, fiberglass, foam insulation, sound
board, or extra layers of drywall do little to stop noise
transmission. Even a concrete block wall is not a very good
sound barrier: Sound is very difficult to stop and solid rigid
materials actually tend to vibrate themselves, producing sound
on the other side. While others attempt various ways to stop or
absorb sound, ArtUSA has resolved the problem in a vastly
different way. The soft 1/8" thick barrier is engineered not to
stop or even absorb sound, but through a unique thermodynamic
process transforms the sound energy into trace amounts of heat.
Our barrier is made of a polymer material. As sound waves cause
the material to flex, internal friction occurs and the
acoustical energy is dissipated into a very small trace amount
of heat. The principle is isothermal for low frequencies and
adiabatic for higher frequencies. This is truly a vastly
superior method to using massive solid materials for stopping
sound transmission. Thus one 1/8" layer of barrier in a standard
wall will result in more sound reduction than 12" of poured
concrete! A concrete block wall using a metal stud and barrier
was tested by a NVLAP lab. testers commented "We have never
tested a wall assembly that achieved such a high sound
transmission loss rating... it even exceeded the testing
capabilities of most laboratories!" The barrier is not only an
incredible sound isolation product, but can be easily installed
without construction changes, special tools, or skilled labor
and is U.L. approved for use in 277 fire-rated wall and
floor/ceiling configurations. Simply cut it with a box knife,
staple or screw to studs, and ensure an airtight fit.
ArtUSA
Noise Control Products, Inc.
is leading the nation in cost effective
Noise Control, Noise Control Enclosures, Soundproofing, Sound Enclosures, Acoustical Materials, and Air Filtration Systems.
Visit our sister site
www.artusaindustries.us
Our barrier products are
http://www.artusaindustries.us/barrier_walls.html
http://www.artusaindustries.us/facings_barriers.html
http://www.artusaindustries.us/facings_barriers.html
Barrier Walls are normally used to place a sound barrier
between a noise source and a target population. Our barriers
create a zone of quiet that can be tailored to cover
almost any size area either indoors or out. When you contact
ArtUSA Noise Barriers, we work with you from beginning to end.
Our goal isn’t to sell you equipment; it’s to create a solution
for your particular problem. We’ll help design your barrier from
the ground up to protect your particular environment at the
lowest cost possible. Whether you need to protect an entire
neighborhood or just a portion of one building, ArtUSA Noise
Barriers has a solution for you. Regardless of the size of
your job, we have the right mix of one-sided or two-sided, sound
absorbing or reflecting materials, to reduce noise levels
without breaking your budget. Absorptive noise control barriers
provide maximum noise reduction with lightweight modular panels
and/or louvers. The noise barrier system is easy to install and
easy to relocate. Panels and louvers are constructed of
galvanized steel or painted finish in a weather resistant
paint or powder coating. The finish is also cleanable.
Our design services include layout, structural steel support
framework, foundation design (for ground level barriers), access
doors and certified calculations including P.E. or S.E. stamp.
Perfect for new construction or retrofit to an existing
structure.
Free-Standing or Elevated Panel Construction
- Allows for maximum flexibility of design and utility on
the ground or on the rooftop
- One– or two-sided sound absorption
- Steel Stainless or Aluminum construction
- Perfect for retrofit installation to solve existing
noise problems
- Low-weight construction ideal for roof or bridge mounted
applications
- Designed to withstand high wind loads
All-Weather Applications
- Barrier modules are designed and built to minimize water
invasion
- Panels resist “wicking” moisture through the bottom and
are self-draining
Highway Traffic Noise Barriers at a Glance
Highway traffic noise barriers:
- can reduce the loudness of traffic noise by as much as
half;
- do not completely block all traffic noise;
- can be effective, regardless of the material used;
- must be tall and long with no openings;
- are most effective within 61 meters (200 feet) of a
highway (usually the first row of homes);
- must be designed to be visually appealing;
- must be designed to preserve aesthetic values and scenic
vistas;
- do not increase noise levels perceptibly on the opposite
side of a highway; and
- substantially reduce noise levels for people living next
to highways.
Keeping the Noise Down
A sound occurs when an ear senses pressure variations or
vibrations in the air. Noise is unwanted sound. The brain
relates a subjective element to a sound, and an individual
reaction is formed. Numerous studies have indicated that the
most pervasive sources of noise in our environment today are
those associated with transportation. Highway traffic noise
tends to be a dominant noise source in our urban, as well as
rural, environment.
What are Noise Barriers?
Noise barriers are solid obstructions built
between the highway and the homes along a highway. They do not
completely block all noise they only reduce overall noise
levels. Effective noise barriers typically reduce noise levels
by 5 to 10 decibels (dB), cutting the loudness of traffic noise
by as much as one half. For example, a barrier which achieves a
10-dB reduction can reduce the sound level of a typical tractor
trailer pass-by to that of an automobile.
Barriers can be formed from earth mounds or
"berms" along the road, from high, vertical walls, or from a
combination of earth berms and walls. Earth berms have a very
natural appearance and are usually attractive. They also reduce
noise by approximately 3 dB more than vertical walls of the same
height. However, earth berms can require a lot of land to
construct, especially if they are very tall. Walls require less
space, but they are usually limited to eight meters (25 feet) in
height for structural and aesthetic reasons.

When Are Noise Barriers Required?
Noise barriers are not always required at locations where an
absolute threshold is met. There is no "number standard" which
requires the construction of a noise barrier. Federal
requirements for noise barriers may be found in Title 23 of the
U.S. Code of Federal Regulations, Part 772, "Procedures for
Abatement of Highway Traffic Noise and Construction Noise."
The Federal Highway Administration noise regulations apply
only to projects where a State transportation department has
requested Federal funding for participation in the improvements.
The State transportation department must determine if there will
be traffic noise impacts, when a project is proposed for (1) the
construction of a highway on new location or (2) the
reconstruction of an existing highway to either significantly
change the horizontal or vertical alignment or increase the
number of through-traffic lanes. If the State transportation
department identifies potential impacts, it must implement
abatement measures, possibly including the construction of noise
barriers, where reasonable and feasible.
Federal law and Federal Highway Administration regulations do
not require State transportation departments to build noise
barriers along existing highways where no other highway
improvements are planned. They may voluntarily do so, but they
are solely responsible for making this decision.
How Is a Noise Barrier Funded?
There are no special or separate Federal funds for highway
traffic noise abatement. State transportation departments
include the costs of noise barriers in their proposed
Federal-aid highway projects. The Federal share is the same as
that for the highway system on which the project is located.
Noise barriers are sometimes constructed without using Federal
funds - for example, using only State, local, or private funds.
The costs of noise barriers are sometimes shared by governmental
agencies and individual homeowners.
How Does a Noise Barrier Work?
Noise barriers reduce the sound which enters a community from
a busy highway by either absorbing the sound, transmitting it,
reflecting it back across the highway, or forcing it to take a
longer path over and around the barrier. A noise barrier must be
tall enough and long enough to block the view of a highway from
the area that is to be protected, the "receiver." Noise barriers
provide very little benefit for homes on a hillside overlooking
a highway or for buildings which rise above the barrier. A noise
barrier can achieve a 5 dB noise level reduction, when it is
tall enough to break the line-of-sight from the highway to the
home or receiver. After it breaks the line-of-sight, it can
achieve approximately 1.5dB of additional noise level reduction
for each meter of barrier height.

To effectively reduce the noise coming around its ends, a
barrier should be at least eight times as long as the distance
from the home or receiver to the barrier.

Openings in noise barriers for driveway connections or
intersecting streets destroy their effectiveness. In some areas,
homes are scattered too far apart to permit noise barriers to be
built at a reasonable cost. Noise barriers are normally most
effective in reducing noise for areas that are within
approximately 61meters (200 feet) of a highway (usually the
first row of homes).
What Type of Material Is Best for a Noise Barrier?
Noise barriers can be constructed from earth, concrete,
masonry, wood, metal, and other materials. To effectively reduce
sound transmission through the barrier, the material chosen must
be rigid and sufficiently dense (at least 20 kilograms/square
meter). All noise barrier material types are equally effective,
acoustically, if they have this density.
  
  
There are no Federal requirements specifying the
materials to be used in the construction of highway traffic
noise barriers. Individual State departments of transportation
select the materials when building these barriers. The selection
is normally made based on factors, such as aesthetics,
durability, maintenance, cost, and the desires of the public.
How Do People React to Noise Barriers?
Overall, public reaction to highway noise barriers appears to
be positive. However, specific reactions vary widely. Residents
adjacent to barriers say that conversations in households are
easier, sleeping conditions are better, the environment is more
relaxing, windows are opened more often, and yards are used more
in the summer. Residents also perceive indirect benefits, such
as increased privacy, cleaner air, improved views and a sense of
ruralness, and healthier lawns and shrubs.
Negative reactions from residents have included a restriction
of view, a feeling of confinement, a loss of air circulation, a
loss of sunlight and lighting, and poor maintenance of the
barrier. Motorists have sometimes complained of a loss of view
or scenic vistas and a feeling of being "walled in" when
traveling adjacent to barriers.
Are Residents' Views Considered?
A major consideration in the design of a noise barrier is its
visual impact on the surrounding area. A tall barrier near a
one-story, single family, detached residential area can have a
negative visual effect. One solution to addressing the size
relationship in visual quality is to provide staggered
horizontal elements to a noise barrier to reduce the visual
impact by planting landscaping in the foreground. Native
plantings are preferable.
 
The visual character of noise barriers in
relationship to their environmental setting should be carefully
considered. In general, it is desirable to locate a noise
barrier approximately four times its height from residences and
to provide landscaping near the barrier to avoid visual
dominance.
Noise barriers should reflect the character of their
surroundings as much as possible. It is always desirable to
preserve aesthetic views and scenic vistas, to the extent
possible.
Are Motorists' Views Considered?
The psychological effect of noise barriers on
the passing motorist should be a part of barrier design and
construction. Noise barriers in dense, urban settings should be
designed differently than barriers in more open suburban or
rural areas, and they should be designed to avoid monotony for
the motorist. At normal roadway speeds, motorists tend to notice
noise barriers overall form, color, and surface texture. A
primary objective of noise barrier design should be to avoid a
tunnel effect for the motorist. This can be accomplished by
varying the forms, materials, and surface treatments.
 
Graffiti on noise barriers can be a potential
problem. One solution is to use materials that can be readily
washed or repainted. Landscaping and plantings near barriers can
also be used to discourage graffiti, as well as to add visual
quality.

Does Construction of a Noise Barrier Increase
Noise Levels on the Opposite Side of the Highway?
Residents adjacent to a highway sometimes feel that their
noise levels have increased substantially, because of the
construction of a noise barrier on the opposite side of the
highway. However, field studies have shown that this is not
true. If all the noise striking a noise barrier were reflected
back to the other side of a highway, the increase would be
theoretically limited to 3 dB. In practice, not all of the
acoustical energy is reflected back to the other side. Some of
the energy goes over the barrier, some is reflected to points
other than the homes on the opposite side, some is scattered by
ground coverings (for example, grass and shrubs), and some is
blocked by the vehicles on the highway. Additionally, some of
the reflected energy is lost due to the longer path that it must
travel. Measurements made to quantify this reflective increase
have never shown an increase of greater than 1-2 dB an increase
that is not perceptible to the average human ear.
Does Construction of Noise Barriers on "Both" Sides of a
Highway Increase Noise Levels?
Multiple reflections of noise between two parallel plane
surfaces, such as noise barriers or retaining walls on both
sides of a highway, can theoretically reduce the effectiveness
of individual barriers. However, studies of this issue have
found no problems associated with this type of reflective noise.
Any measured increases in noise levels have been less than can
be perceived by normal human hearing, that is, less than 3 dB.
Studies have suggested that to avoid a reduction in the
performance of parallel reflective noise barriers, the
width-to-height ratio of the roadway section to the barriers
should be at least 10:1. The width is the distance between the
barriers, and the height is the average height of the barriers
above the roadway. This means that two parallel barriers 3
meters (10 feet) tall should be at least 30 meters (100 feet)
apart to avoid any reduction in effectiveness. These studies
have also shown that any reduction in performance can be
eliminated through the use of sound absorptive noise barriers.
Can Trees Be Planted to Act as Noise Barriers?
Vegetation, if it is high enough, wide enough, and dense
enough that it cannot be seen over or through, can decrease
highway traffic noise. A wide strip of trees with very thick
undergrowth can lower noise levels. 30 meters of dense
vegetation can reduce noise by five decibels. However, it is not
feasible to plant enough trees and other vegetation along a
highway to achieve such a reduction. Trees and other vegetation
can be planted for psychological relief but not to physically
lessen noise levels.
In Summary
Most residents near a barrier seem to feel that highway noise
barriers effectively reduce traffic noise and that the benefits
of barriers far outweigh the disadvantages of barriers. While
noise barriers do not eliminate all highway traffic noise, they
do reduce it substantially and improve the quality of life for
people who live adjacent to busy highways.
A noise
barrier is an exterior structure, designed to protect
sensitive
land uses from
noise pollution. It is commonly also called a soundwall,
sound berm, sound barrier and acoustical
barrier. Noise barriers are the most effective method of
roadway
noise mitigation, and mitigation of railway and industrial
noise sources (other than cessation of the source activity or
use of source controls). In the case of surface transportation
noise, very little can be done to further reduce the source
noise intensity (other than increase the percentage of
hybrid vehicles and
electric vehicles, a strategy that works only at low to
moderate traffic flow speeds). Extensive use of noise barriers
began in the
United States after
noise regulations that were introduced in the early 1970s.
Noise barriers have
been built intuitively, but infrequently, in the
United States since the mid twentieth century, when
vehicular traffic burgeoned; however, in the late 1960s
acoustical science technology emerged to mathematically
evaluate the efficacy of a noise barrier design adjacent to a
specific
roadway. Below, a researcher collects data to calibrate a
roadway noise model for Foothill Expressway.


Acoustical
scientist measures sound in Noise barrier design study,
Santa Clara County, Calif.
The best of these
early computer models considered the effects of roadway
geometry,
topography,
vehicle volumes, vehicle speeds, truck mix,
roadway surface type and
micrometeorology.
Several research groups within the U.S. developed variations of
the computer modelling techniques:
Caltrans Headquarters in
Sacramento, California; the
ESL inc. group in
Palo Alto, California; the
Bolt, Beranek and Newman[1]
group in
Cambridge, Massachusetts and a research team at the
University of Florida. Possibly the earliest published work
that scientifically designed a specific noise barrier was the
study for the Foothill Expressway in
Los Altos, California[2].
Rapidly following,
there ensued numerous case studies across the U.S. addressing
dozens of different existing and planned highways. These studies
were commonly commissioned by State
Highway Departments and
were mostly conducted by one of the four research groups
mentioned above. The U.S.
National Environmental Policy Act[3]
had arrived and effectively mandated the quantitative analysis
of
noise pollution from every
Federal-Aid Highway Act Project in the U.S., propelling
noise barrier model development and application. With passage of
the
Noise Control Act of 1972[4],
demand for noise barrier design soared from a host of
noise regulation spinoff.
By the late 1970s
there were over a dozen research groups in the U.S. applying
similar
computer modelling technology and addressing at least 200
different locations a year for noise barriers.
As of 2006, this technology is considered a standard in the
evaluation of
noise pollution from highways, but, remarkably, the nature
and accuracy of the
computer models used is nearly identical to the original
1970 versions of the technology.
The acoustical science
of noise barrier design is a complex task based upon treating a
roadway or railway as a
line source. Firstly, the theory is based upon blockage of
sound ray travel toward a particular
receptor; however,
diffraction of sound must be addressed. That is to say,
sound waves bend (downward) when they pass an edge, such as
the apex of a noise barrier. Further complicating matters is the
phenomenon of
refraction, the bending of sound rays in the presence of an
inhomogeneous
atmosphere.
Wind shear and
thermocline produce such inhomogeneities.
The sound sources
modelled must include
engine noise,
tire noise and
aerodynamic noise, all of which factors vary by vehicle type
and speed. One can begin to visualize the complexity of the
resulting
computer model, which is based upon dozens of physics
equations translated into thousands of lines of computer
code.


Noise barrier earth
berm along
Highway 12,
Sonoma County, California
Some noise barriers
consist of a masonry wall or earthwork, or a combination
thereof, such as a wall atop an earth
berm. Sound abatement walls are commonly constructed using
steel, concrete, masonry, wood, plastics, insulating wool, or
composites. In the most extreme cases, the entire roadway is
surrounded by a noise abatement structure, or dug into a tunnel
using the
cut-and-cover method. The noise barrier may either be
constructed on private land or on a public
right-of-way or other public land or other surface such as a
marsh, public or private. Since sound levels are measured using
a
logarithmic scale, a reduction of nine
decibels is equivalent to elimination of about 80 percent of
the unwanted sound. The bottom line is that noise barriers can
be extremely effective tools for
noise pollution abatement, although theory also calculates
that certain locations and topographies are not suitable for use
of any reasonable noise barrier. Clearly cost and
aesthetics play a role in the final choice of any noise
barrier.
There are clear
disadvantages of noise barriers, most prominently:
·
Aesthetic impacts for motorists and neighbors, particularly if
scenic vistas are blocked.
·
Considerable costs of design, construction and maintenance.
·
Necessity to design custom drainage that the barrier may
interrupt.
Normally the benefits
of noise reduction far outweigh aesthetic impacts for residents
protected from unwanted sound. These benefits include lessened
sleep disturbance, improved ability to enjoy outdoor life,
reduced
speech interference,
stress reduction, reduced risk of
hearing impairment and reduction in
blood pressure (improved
cardiovascular health).
With regard to
construction costs, a major factor is the availability of excess
soil in the immediate area which could be used for
berm construction. If the soil is present, it is often
cheaper to construct an earth berm noise barrier than to haul
away the excess dirt, provided there is sufficient land area
available for berm construction. Generally a four to one ratio
of berm cross sectional width to height is required. Thus, for
example, to build a six foot high berm, one needs an available
width of 24 feet.
Earth berm noise
barriers can be constructed solely of excess earth from
grading pads for a
residential development it will protect. Thus its entire
construction cost is negligible; arguably, it may pay into the
project, since offhaul of earth may have been needed. A further
nuance of this particular project is that the residential side
of the berm is overexcavated, which gives more privacy between
highway and homes and also enhances noise benefit. Finally, note
the
aesthetics of the earth berm which blends with scenic
elements of the natural hills of
Annadel State Park in the background. It may be a surprise
to find out this berm is over six feet in height, since the
aesthetics of earth mounding reduce the visual impact of the
structure, compared to a soundwall.
As a minor
embellishment to noise barrier design, one may note the concept
of constructing a louver or cap atop the wall that is directed
back toward the noise source. This concept follows the theory
that such a design should inhibit shadow zone diffraction
filling in sound behind the noise barrier. In actual experience
the benefits are slight compared to the benefits of a higher
barrier and the costly construction techniques necessary to
create and maintain such a device. Variation of the louver
design can be found in
Denmark, where the designs are also intended to minimize
reflected sound. Furthermore some of the Danish soundwalls are
made of transparent materials to minimize the visual impact;
such material use, however, compromises the efficacy by reducing
mass.
Typical Applications ...
Features
...
- Available with a 1" or 2" quilted decoupler
- Meets Class A flammability
- Suitable for indoor or outdoor applications
- Easy to cut and install
- ArtUSA flexible lag series combines a loaded vinyl barrier with foil
facing on one side. When a quilted fiberglass is added to the lag
barrier it acts as a decoupler to form a tight fitting
"floating" noise barrier.
Sound
Blankets
-
How Noise Barriers
Work
The "nuisance" noise is
"diffracted" over barriers increasing the distance
it must travel to the listener.
| |
Z
=A+B-C
|
Z (Metres)
|
Potential Noise
Decrease
Due to Diffraction
|
|
1
|
15dB(A)
|
|
2
|
18dB(A)
|
|
The values above are approximate
and do not represent a linear
relationship
|
|
Reflection &
Absorption
| The effectiveness
of a barrier depends on how well it
diffracts and absorbs the noise.
A high performance
barrier has negligible noise transmission
and reflection. This is controlled by two
coefficients: Absorption( )
and Sound Insulation (R). |
|
Quality Noise
Barriers
- significantly reduce
the noise levels.
- guarantee acoustic
performance.
- significantly reduce
public complaint levels.
- provide an aesthetic
visual barrier that will last.
Two Types of
Noise Barriers
|
Absorptive Barriers:
|
Reflective Barriers:
|
- Absorb the noise that
strikes them
- (Reflections are
negligible)
- For High Performance
- Sound Absorption
Coefficient > 8dB(A)
(negligible noise reflected)
- Sound Insulation
Coefficient > 25dB(A)
(negligible noise
transmitted)
|
- Redirect the noise that strikes
them.
- (They do not "reduce" the
noise)
- For High Performance
- Sound Insulation Coefficient
> 25dB(A)
(negligible noise transmitted)
- Reflections must be
accounted for.
(as shown below)
|
-
-
- Visit our new site at
http://www.artusaindustries.us
- Curtain Enclosures - Acoustical Pipe and Duct
Lagging - Sanitary Panels and Baffles - Portable
Screens - Damping Compound - Industrial Ceiling
Baffles - Class 1 Fire Rated Foams - Polyurethane
Foams - Fiber-Free - Adhesive Backed - Facings and
Barriers - SONEX - Sound Seal - Acousti Curtain -
Acousti Foam
Acoustical Baffles
& Diffusers
–
Built of absorptive or active materials these items
can be suspended from ceilings or attached to walls
to absorb or reflect noise. They are commonly
available for industrial, commercial, and or
recording, web/broadcasting applications.
Interior and
Theatrical Applications
– Acoustical panels addressing problems in theatres,
auditoriums, rehearsal studios, conference rooms,
office areas, etc. are available in all forms,
shapes and colors. Various panel types may be
covered in fabric, plastic, steel, aluminum, or
painted. Depending on where and how they are to be
used will dictate the best surface material.
While panels absorb
sound, diffusers are used to regulate sound to
optimum levels with angled surfaces. Reflector
panels can be used in ceiling systems to actually
carry sounds properly into large performing areas.
Vinyl / Barrier,
Foams & Composite Materials
–
Mass-loaded vinyl may be used for blocking sound
from leaving or entering an area. Flat foams, as
well as pyramidal foams, can be used in rooms or
machinery requiring sound absorption. Because
most noise problems require a combination of
materials, we sell them in various composites. For
instance, it is often required to have a layer of
sound barrier material, adhered to a sound absorbing
material. Instead of simply increasing the mass of a
barrier to obtain greater sound barrier properties,
a lighter construction can be achieved by separating
the barrier from the wall or panel with a de-coupler
or spacer, of light material, such as flexible foam.
Composite materials may be used in machinery
cabinets to reduce noise, around pipes for expansion
and contraction noise (pipe duct lagging), etc.
(When choosing a
barrier, some properties which should be taken into
consideration are: thickness, density, stiffness,
resistance to heat and chemicals, flammability, tear
strength, abrasion resistance, thermal insulation,
flexibility and cost.)
We offer a
tremendous variety of composite materials. Some of
these products are treated with heat resistant
coatings to withstand up to 500 degrees!
With more information about your unique problem, we
can appropriately recommend the exact material
needed to properly address your situation. We look
forward to being able to assist you!
-
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We knock out noise. Getting your work
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| The Price of Progress In recent
years, highway traffic noise - the unpleasant, unwanted
sounds generated on our nation's streets and highways -
has been of increasing concern both to the public and to
local, State, and Federal officials. At the same time,
modern acoustical technology has been providing better
ways to lessen the adverse impacts of highway traffic
noise. The purpose of this pamphlet is to explain some
of these acoustical techniques which are now being
employed by government agencies, highway planners and
designers, construction engineers, and private
developers.
Sound and Noise
As we all know, sound is created when an object
moves: the rustling of leaves as the wind blows, the air
passing through our vocal cords, and the almost
invisible movement of the speakers on a stereo. This
movement causes vibrations or waves in air molecules,
like ripples on water. When the vibrations reach our
ears, we hear sound.
Sound is quantified by a meter which measures units
called decibels (dB). For highway traffic noise, an
adjustment, or weighting, of the high- and low-pitched
sounds is made to approximate the way that an average
person hears sounds. The adjusted sounds are called "
A-weighted levels" (dBA).
The A-weighted decibel scale begins at zero. This
represents the faintest sound that can be heard by
humans with very good hearing. The loudness of sounds
(that is, how loud they seem to humans) varies from
person to person, so there is no precise definition of
loudness. However, based on many tests of large numbers
of people, a sound level of 70 is twice as loud
to the listener as a level of 60. This principle is
illustrated on the next page.

Causes of Traffic Noise
The level of highway traffic noise
depends on three things: ( 1) the volume of the traffic,
(2) the speed of the traffic, and (3) the number of
trucks in the flow oft9~traffic. Generally, the loudness
of traffic n6ise is increased by heavier traffic
volumes, higher speeds, and greater numbers of trucks. V
~hicle noise is a combination of the noises produced by
the engine, exhaust, and tires:/The loudness of traffic
noise can also be increased by defective mufflers or
other faulty equipment on vehicles. Any condition (such
as a steep incline) that causes heavy laboring of motor
vehicle engines will also increase traffic noise levels.
In addition, there are other more complicated factors
that affect the loudness of traffic noise. For example,
as a person moves away from a highway, traffic noise
levels are reduced by distance, terrain, vegetation, and
natural and manmade obstacles. Traffic noise is not
usually a serious problem for people who live more than
500 feet from heavily traveled freeways or more than 100
to 200 feet from lightly traveled roads.
How Traffic Volume Affects
Noise
2000 vehicles per hour sound twice as loud as

200 vehicles per hour
How Speed Affects Traffic
Noise
Traffic at 65 miles per hour sounds twice as loud as

traffic at 30 miles per hour
How Trucks Affect Traffic
Noise
One truck at 55 miles per hour sounds as loud as


10 cars at 55 miles per hour
Determining Noise Impact
Highway traffic noise is never constant.
The noise level is always changing with the number ,
type, and speed of the vehicles which produce the noise.
Traffic noise variations can be plotted on a graph as
shown below. However, it is usually inconvenient and
cumbersome to represent traffic noise in this manner. A
more practical method is to convert the noise data to a
single representative number. Statistical descriptors
are almost always used as a single number to describe
varying traffic noise levels. The two most common
statistical descriptors used for traffic noise are Llo
and Leq. Llo is the sound level that is exceeded 10
percent of the time.

In the above graph, the shaded areas
represent the amount of time that the Llo value is
exceeded. Adding each interval during which this
occurred shows that during the 60-minute measuring
period the Llo was exceeded 6 minutes (1/2 + 2 + 2 +
11/2 = 6) or 10 percent of the time. The calculation of
Leq is more complex. Leq is the constant, average sound
level, which over a period of time contains the same
amount of sound energy as the varying levels of the
traffic noise. Leq for typical traffic conditions is
usually about 3 dBA less than the Llo for the same
conditions. The Federal Highway Administration (FHW A)
has established noise impact criteria for different land
uses close to highways. Some of the exterior criteria
are illustrated below.
| Land Use |
L1O
|
Leq
|
| Residential |
70 dBA |
67 dBA |
| Commercial |
75 dBA |
72 dBA |
If a project causes a significant
increase in the future noise level over the existing
noise level, it is also considered to have an impact.
What Can Be Done to Reduce
Highway Noise?
Highway noise is being attacked with a
three-part strategy: motor vehicle control, land use
control, and highway planning and design. The
responsibilities for implementing these strategies must
be shared by all levels of government: Federal, State,
and local. Often, local officials can most effectively
solve specific noise problems in their areas, as
demonstrated in the U.S. Environmental Protection
Agency's (EPA) Quiet Community and Each Community Helps
Others (ECHO) programs. The following two sections
briefly describe how traffic noise impacts can be
reduced or prevented through efforts to obtain quieter
vehicles and efforts to control future development near
highways. The remainder of this pamphlet focuses mainly
on noise abatement in the Federal-aid highway program.
Motor Vehicle Control
The first part of the strategy goes
right to the source of traffic noise: the vehicles. For
example, vehicles can be designed with enclosures for
the engine, fans that turn off when not needed, and
better mufflers. Quieter vehicles would bring about a
substantial reduction in traffic noise along those roads
and streets where no other corrective measures are
possible. The EP A has issued regulations placing a
limit on the noise which new trucks can make. In
addition, many local and State governments have passed
ordinances or laws requiring existing vehicles to be
properly maintained and operated. Unfortunately, due to
limitations in technology, these EP A regulations for
new trucks and State and local regulations for
maintenance of vehicles can only partially reduce the
noise created by traffic. The best that can be expected
is a 5 to 10 dBA decrease in the noise level. Where this
is insufficient, other measures must be used. Land Use
Control The second part of the strategy calls for the
control of future development. Sometimes, complaints
about highway traffic come from occupants of new homes
built adjacent to an existing highway. Many of these
highways were originally constructed through undeveloped
lands. There are several hundred thousand miles of
existing highways in this country bordered by vacant
land which may some day be developed. Prudent land use
control can help to prevent many future traffic noise
problems in these areas. Such controls need not prohibit
development, but rather can require reasonable distances
between buildings and roads as well as "soundproofing"
or other abatement measures to lessen noise
disturbances. Many local governments are working on land
use control.

Less noise-sensitive commercial buildings can be
placed next to a highway, with residences farther away.
Highway Planning and Design
The third part of the highway noise
reduction strategy is highway planning and design. Early
in the planning stages of most highway improvements,
highway agencies do a noise study. The purpose of this
study is to determine if the project will create any
noise problems. First, the existing noise levels of a
highway are measured or computed by models. Then, the
agency predicts what the noise levels will be if the
project is constructed. If the predicted noise levels
are above Federal noise criteria, the noise study must
consider measures that can be taken to lessen these
adverse noise impacts. This information is reported at
public meetings and hearings if they occur.
Noise Reduction on Existing
Roads
Some noise reduction measures that are
possible on existing roads or on roads that are being
rebuilt include creating buffer zones, constructing
barriers, planting vegetation, installing noise
insulation in buildings, and managing traffic. Buffer
zones are undeveloped open spaces which border a
highway. Buffer zones are created when a highway agency
purchases land, or development rights, in addition to
the normal right of way, so that future dwellings cannot
be constructed close to the highway. This precludes the
possibility of constructing dwellings that would
otherwise experience an excessive noise level from
nearby highway traffic. An additional benefit of buffer
zones is that they often improve the roadside
appearance. However, because of the tremendous amount of
land that must be purchased and because in many cases
dwellings already border existing roads, creating buffer
zones is often not possible.
Open space can be left as a buffer zone between
residences and a highway.
Noise barriers are solid obstructions
built between the highway and the homes along the
highway. Effective noise barriers can reduce noise
levels by 10 to 15 decibels, cutting the loudness of
traffic noise in half. Barriers can be formed from earth
mounds along the road (usually called earth berms) or
from high, vertical walls. Earth berms have a natural
appearance and are usually attractive. However, an earth
berm can require quite a lot of land if it is very high.
Walls take less space. They are usually limited to 25
feet in height for structural and aesthetic reasons.
Noise walls can be built of wood, stucco, concrete,
masonry, metal, and other materials. Many attempts are
being made to construct noise barriers that are visually
pleasing and that blend in with their surroundings.
However, barriers do have1imitations.
For a noise barrier to work, it must be high enough and
long enough to block the view of a road. Noise barriers
do very little good for homes on a hillside overlooking
a road or for buildings which rise above the barrier.
Openings in noise walls for driveway connections or
intersecting streets destroy the effectiveness of
barriers. In some areas, homes are scattered too far
apart to permit noise barriers to be built at a
reasonable cost.

Earth Berm Noise Barrier

Wooden Noise Barrier

Concrete Noise Barrier with Woodgrain Texture

Shadow Effect of Noise Barrier
The lower house is protected by the barrier, but the
upper one is not.
Vegetation, if high enough,
wide enough, and dense enough (cannot be seen through),
can decrease highway traffic noise. A 200-foot width of
dense vegetation can reduce noise by 10 decibels, which
cuts the loudness of traffic noise in half. It is often
impractical to plant enough vegetation along a road to
achieve such reductions; however, if dense vegetation
already exists, it could be saved. If it does not exist,
roadside vegetation can be planted to create
psychological relief, if not an actual lessening of
traffic noise levels.

Loudness Cut in Half

No Noise Reduction (Psychological)
Vegetation and Noise Reduction
Insulating buildings can
greatly reduce highway traffic noise, especially when
windows are sealed and cracks and other openings are
filled. Sometimes, noise-absorbing material can be
placed in the walls of new buildings during
construction. However, insulation can be costly because
air conditioning is usually necessary once the windows
are sealed.
In many parts of the country , highway
agencies do not have: the authority to insulate
buildings. In those states, insulation cannot be
included as part of a hi.ghway project.
Managing traffic can sometimes
reduce noise problems. For example, trucks can be
prohibited from certain streets and roads, or they can
be permitted to use certain streets and roads only
during daylight hours. Traffic lights can be changed to
smooth out the flow of traffic and to eliminate the need
for frequent stops and starts. Speed limits can be
reduced; however, about a 20 mile-per-hour reduction in
speed is necessary for a noticeable decrease in noise
levels.
Pavement is sometimes mentioned
as a factor in traffic noise. While it is true that
noise levels do vary with changes in pavements and
tires, it is not clear that these variations are
significant when compared to the noise from exhausts and
engines, especially when there are a large number of
trucks on the highway. More research is needed to
determine to what extent different types of pavements
and tires contribute to traffic noise. Until this
research is completed, the use of different types of
pavement cannot be depended upon to reduce traffic
noise.
Noise Reduction on New Roads
All of the measures described above can
be employed on both existing roads and new roads. There
are, however, some additional measures which can usually
be used only on new roads.
First, a new road can be located away
from noise-sensitive areas, such as schools or
hospitals, and placed near nonsensitive areas, such as
businesses or industrial plants. New roads can also be
located in undeveloped areas.
Second, a new road can be constructed
below ground level. Much of the noise from vehicles
traveling on this type of road is deflected into the air
by embankments on the side of the road. Thus, these
embankments function in much the same way as noise
barriers.

Highway Below Ground Level
Third, a new road can be designed and
constructed as level as possible. The elimination of
steep inclines helps to reduce traffic noise because
motor vehicle engines, especially multigeared truck
engines, do not have to work as hard. Although there are
a great many noise reduction measures possible, they all
have limitations. Consequently, there are many
situations where none of these noise reduction measures
can be used. In these situations, the only option left
may be for local authorities to require adequate muffler
devices for the louder vehicles.
Federal Role
The Federal Highway Administration is
the agency responsible for administering the Federal-aid
highway program. Under this program, Federal funds are
allotted by Congress to the individual States. However,
before these monies can be used for highway projects,
the projects must be approved by FHW A, which can only
grant its approval for projects that are developed in
accordance with Federal statutes and regulations. One of
these regulations requires that a noise study be
accomplished to determine what noise impacts, if any,
will result from the proposed highway improvement and
what measures will be taken to lessen these noise
impacts. If noise impacts are expected, noise-reduction
measures that are determined by the State highway agency
and the FHW A to be practicable, reasonable, and
acceptable to the public must be incorporated into the
highway improvement. The costs of the noise-reduction
measures are included with the other costs of the
highway improvement and are eligible for Federal funding
in the same proportion as other aspects of the project.
State highway agencies may also use Federal highway
grants for noise-reduction projects on existing roads on
the Federal-aid system. The monies spent on
noise-reduction measures are deducted from funds which
would otherwise be available for highway construction.
Federal funds may be used for the construction of
noise barriers, for acquisition of land on which to
build such barriers, and for the purchase of undeveloped
land as a preemptive buffer zone. Traffic operational
measures such as truck routes and restriction of hours
of operation are often feasible noise abatement
measures, and the costs of such measures are eligible
for Federal funding. The "soundproofing" of public-use
institutional buildings may be incorporated in
Federal-aid highway projects to abate traffic noise, but
the use of Federal funds for soundproofing commercial
buildings or private dwellings is not normally
permitted. |
|