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Alum-A-Frame
Enclosures |

Flexible Noise
Barriers |

Modular Acoustic
Panel Enclosure |
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Art-Acousti-Lagging |
 
Flexible-Art-Acousti-Wrap |
http://www.noisecontrolproducts.com/barrier_walls.html
Sound Barrier Walls
Outdoor community noise problems may require an
engineered Sound Barrier Wall. Our walls offer sound reduction
by absorbing the sound at its source and blocking the noise from
transmitting to noise sensitive areas. Substations, HVAC
Chillers, Power Generators, Cooling Towers, and Compressors are
a few outdoor noise candidates for our Noise Barrier Walls.
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| Features: |
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- High and low temperature
applications
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- Quilted fiberglass decoupler
available
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- Good corrosion resistance
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- Meets Class A flammability rating per ASTM
E-84
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Acoustical Data: |
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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 |
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B-10 LAG / QFA-3 |
18 |
18 |
23 |
30 |
39 |
46 |
29 |
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B-10 LAG / QFA-9 |
19 |
20 |
23 |
33 |
44 |
53 |
30 |
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Per ASTM: E 90 |
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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 |
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Per ASTM: E 90 |
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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 |
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QA-3 |
.2 Lb. PSF |
1“ Nom |
-20 to + 350 F |
- |
- |
- |
4.0 |
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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 |
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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 |
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Per ASTM: E 90 |
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Single Applications Page
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
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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
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How Noise Barriers
Work
The "nuisance" noise is
"diffracted" over barriers increasing the distance
it must travel to the listener.
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Z
=A+B-C
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Z (Metres)
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Potential Noise
Decrease
Due to Diffraction
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1
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15dB(A)
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2
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18dB(A)
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The values above are approximate
and do not represent a linear
relationship
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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). |
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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
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Absorptive Barriers:
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Reflective Barriers:
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- 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)
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- 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)
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- 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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Home of
the Most Versatile Noise Control and
Environmental Enclosure and The Alum A Frame
Enclosure, Air Pollution Control Equipment, Noise
Control, Noise Abatement, Noise Absorbers, Noise
Attenuation, Sound Control, Machine Enclosures,
Acoustical Baffles, Acoustical Foam, Noise Barriers,
Acoustical Wall Panels, Consulting, Surveys, Noise
Control Buildings, Installation, Service, Demolition and
Construction.
Simply the best in Sound Enclosures,
Noise Abatement, Noise Control, Acoustical Materials,
Air Quality products and In-plant Offices.
Acoustical Enclosures, Weather-tight
Enclosures, Humidity Control Enclosures, Portable
Enclosures, Curtain Enclosures, Smoke Capture
Enclosures, Mist Control Enclosures, Dust Collection
......for Blowers, Clean Rooms, Chippers, CNC centers,
Compressors, Fans, Generators, Granulators, Grinders,
Molders, Planers, Pumps, Test Cells, Turbines, Work
Stations ...... any noise source.
We knock out noise. Getting your work
world down to 85dBA and below.
|
| 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. |
|
Design Guide
Basic Design Principles
This section is intended to provide a basic introduction to
design principles that can be utilized in barrier and landscape
design. It will also include discussion on how and what people see
when traveling on highways. Issues to be addressed include distance
and motion, line, form, scale, balance, rhythm and sequence and
orientation. Each of these factors must be considered and carefully
chosen in order to create a design that is compatible with its
surroundings.
Distance and motion affect what motorists see
when driving through the freeway corridor. Speed alters the
peripheral cone of vision and the distance to the motorist's point
of focus. Figure 1 illustrates the vision cone for three vehicular
speeds. In general, as speed increases, the cone of vision narrows
and the focal distance increases. Likewise, at slower speeds,
peripheral vision is expanded and the focal distance is closer to
the observer. Vision cones delineate the area within which objects
are generally in focus. Objects outside these cones become blurred.
Figure 1: Distance and Motion
Lines are created by joining two points. Lines
are fundamental to three dimensional forms. The character of forms
is expressed by lines. Smooth, flowing, horizontal lines may suggest
calm and serenity, while bold, vertical, angular lines may suggest
strength and tension. The most prominent line created by a noise
barrier is the top profile (Figure 2). Lines can be created on the
surface of the barrier wall using various materials and texture
patterns. Lines may also be implied. For example, a row of street
trees may appear to form a solid line.
Form depicts volume in three dimensions
--length, width, and depth. A barrier wall itself is a three
dimensional form. This is commonly referred to as positive form. The
horizontal wall configuration can be designed to create spaces which
are commonly referred to as negative spaces or forms (Figure 2).
Scale establishes a frame of reference. It is a
relative measurement. People commonly relate to their environment
using the human body or other elements of familiar dimension as the
reference measurement. Noise barrier walls can be 15' tall or more.
Such a wall would appear massive and overpowering located adjacent
to a back lot line since residential fences are more commonly 4 to
8' tall (Figure 2). The perceived scale of barrier walls can be
reduced through the use of landscaping and/or in the design of the
wall itself (e.g. materials, configuration, etc.).
Balance creates order and unity by attaining a
sense of equilibrium. Two basic types of balance include: symmetry
and asymmetry (Figures 3a and 3b). Symmetry results when elements
are arranged equally around a central axis, creating a mirror-image
effect. Symmetry is considered to be a formal type of balance.
Asymmetry is more informal, lacking a central axis. Elements are
juxtaposed in such a way that they counterbalance each other without
creating a mirror image.
Figure 2: Fundamental Elements of Design
Figure 3a: Symmetrical Balance
Figure 3b: Asymmetrical Balance
Rhythm and sequence establish consistent,
recognizable patterns (Figures 4 and 5). Repeated patterns create a
sense of familiarity and comfort. They also provide a sense of
progression, unless continued indefinitely. Rhythm and sequence can
be created using both the barrier wall and/or landscaping.
Figure 4: Rhythm
Figure 5: Sequence
Orientation refers to the dominant visual
direction established through design (Figure 6). Horizontal
orientation is associated with relatively flat and expansive
landforms. This type of orientation tends to direct the eye forward,
reducing the apparent height of a barrier wall by emphasizing its
relationship to the horizon. Vertical orientation is associated with
upward reaching forms such as skyscrapers. This type of orientation
tends to direct the eye upward, increasing the apparent height of a
barrier wall.
Figure 6: Visual Orientation
Barrier Design
This section is divided into subsections pertaining to design
issues specific to barrier structures, landscape treatment, and
integrating barriers and landscape.
Parts of the Barrier Wall
Walls consist of three basic parts: the cap, the body, and the
base (Figure 9). The cap provides a top edge to the wall -- giving
it a definite finished appearance. The body is the dominant part of
the wall. The base refers to where the body meets the ground. It
provides a sense of connection with the landscape.
Figure 7: Parts of a Wall
Top Profile
The profile line created by the top of the wall defines the
general character and form of the wall. The top profile can be
designed to reflect, contrast, or remain neutral to the
surroundings. Figure 8 illustrates and example of a peaked top
profile imitating a steepled skyline, and a horizontal, wavy top
profile contrasting the vertical forms of the urban downtown
skyline.
Wall Configuration
The configuration of a barrier wall can be altered by changing
its horizontal alignment. Figures 9 and 10 illustrate two common
wall configurations: serpentine and castellated. Both of these break
up the line of the wall creating a more three-dimensional form. This
results in a more visually interesting wall. In addition, the
"negative" space created by the undulations can function as planting
pockets. While these configurations potentially increase the
structural strength of the wall, they also increase the cost. How
much the cost would increase depends on specific details such as
materials and the degree and quantity of undulations.
Figure 8: Top Profile of Wall
Figure 9: Serpentine Wall Configuration
Figure 10: Castellated Wall Configuration
Materials and Textures
The most common materials for constructing noise barriers are
precast concrete, metal, and wood. Brick is also used, but only to a
limited extent because of higher cost (Figure 11). Several surface
finishes and textures are available to provide a large variety of
options for barrier wall design. Appendix B lists the common barrier
wall materials and various surface finishes and textures currently
available.
The character of the barrier wall is directly related to the
materials and textures used in the design. In general, wood appears
inherently more suburban and rural than concrete or metal, which
appear harder and more urban. However, in spite of the material
used, the character of the wall can be significantly modified by the
type of surface treatment used on the wall body.
Surface texture and patterns can be applied to lend any desired
character. How texture and patterns are perceived depends on the
speed of the observer (Figure 12a, b, c). At high speeds, textures
become blurred and patterns may not be discernable. Coarse textures
and simple, bold patterns should be used in high speed situations.
On the other hand, the residential side of noise barriers is
commonly experienced by slower moving observers. People walking or
driving at slow speeds are able to distinguish finer textures and
more intricate and complex patterns.
Figure 11: Common Barrier Wall Materials
Figure 12: Wall Texture
a. High Speed (freeway side)
b. Slow Speed (residential side)
c. Wall Texture
Variety can also be achieved through the use of contrast on the
wall surface. Smooth and rough textures can be juxtaposed and
pattern orientations may be varied to create contrast (Figure 13).
Relief on wall surfaces can create shadow patterns. A variety of
colors can be used to create contrast.
Other important considerations when selecting barrier materials
include cost and maintenance. On a cost per linear foot basis, metal
is the least expensive material (see Appendix B). Obviously,
standardized units are cheaper than custom pieces. Likewise,
unornamented panels cost less than decorative or textured panels.
The challenge to designers is to create variety within the
constraints posed by standardized units, and to use customized
panels in strategic locations to provide visual impact without being
prohibitively expensive.
Figure 13: Surface Contrast
Landscape Plant Materials
Plant materials are grouped into general categories relative to
their size and habitat (Figure 14a). These categories include:
Overstory -- tall plants (typically trees) that form overhead
canopies
Understory -- shorter plants (shrubs and small trees)
Ground cover -- plants that grow close to the ground (typically
less than 12" tall). May be used to stabilize soil or slopes.
Vines -- plants that attach themselves to other objects for
support.
Plants may also be grouped into categories based on their texture
-- fine, medium, or coarse (Figure 14b).
Fine textured plants are characterized by small leaves and twigs,
smooth bark, and slender, graceful branching habits.
Coarse textured plants are characterized by large leaves, thick
and/or corky twigs and sturdy or stiff branching habits.
Medium textured plants are those not distinctly fine or coarse.
For design purposes descriptive plant form categories have been
developed because certain forms lend themselves to specific
functions and portray particular characters or moods. Figures 15 and
16 illustrate common form descriptions for trees and shrubs.
Figure 14: Plant Categories
a. Size
b. Texture
Figure 15: Common Tree Forms
Figure 16: Common Shrub Forms
Natural Landscaping
Using plants native to a region makes aesthetic and economic
sense. Urban development, agriculture and road construction destroys
much of the original plant communities that existed prior to
settlement. Restoration of the original plant community helps blend
the roadway into the surrounding landscape and provides an
interesting and aesthetic view of the road. Wild flowers and prairie
grasses contribute a wide variety of textures and colors to the
roadside landscape. Flowers bloom at different times, from spring to
fall, offering a continuous display of changing colors. In addition,
many prairie grasses change color throughout their growing season.
The establishment of natural landscaping along a highway requires
careful selection of plants and some patience. Prairie grasses and
wild flowers will take two to three years to establish themselves
and may require a nurse crop when planted. During the first several
years the roadside will be dominated by annual weeds. These will
eventually be replaced by the perennial grasses and wild flowers of
the prairie environment. Plants should be selected to provide for a
diversity of color, height and flowering time. This will result in a
more naturalistic landscape with a variety of textures and colors
throughout the year. Prairie plants change over the season with
short growing flowers appearing early. These are gradually replaced
with taller flowers and grasses later in the season.
Prairie habitats are divided into five types: wet, wet mesic,
mesic, dry mesic and dry. Wet prairie areas have saturated soils,
typically deep clay silt loam and peat and are dominated by sedges
rather than grasses. Mesic prairie is a medium condition with medium
deep silt or sandy loam soils. Dry prairie tends to have shallow
sand or limestone soils. Each species of native grass or flowers has
a set of habitats which it prefers. Roadsides tend to have a variety
of conditions ranging from wet areas along ditches to drier zones
along embankments.
In addition to aesthetics, natural landscaping can reduce
roadside maintenance costs. Fertilization and mowing activities can
be significantly reduced. Once established, prairie grasses and wild
flowers provide an excellent means of soil stabilization. Native
plants can be especially resistant to drought and will continue to
thrive even when other types of plants dry up. Ideally prairies
should be burned once every four to five years during early spring
to reduce build-up of dead grasses and to eliminate woody plants.
This adds nutrients to the soil and accelerates growth in the
subsequent seasons. Controlled burning along a roadside may require
special efforts to maintain safety. An alternative may be to use
mowing or to forgo burning for longer time intervals.
The use of prairie plants along roadsides is becoming
increasingly popular. The Wisconsin Department of Transportation has
initiated a major project in central Wisconsin along U.S. Highway 51
to establish prairie grasses and wild flowers along the roadside. In
addition many states have active programs to plant wild flowers
along roadsides and have "adopt a roadway" programs to facilitate
maintenance and landscaping. Currently one-fourth of one percent of
federal funds for landscaping are to be used for native plantings
along highways. Appendix B lists some grasses and wild flowers
currently used by WDOT.
Uses of Landscaping for Aesthetics
Landscaping can be used in several ways to improve the aesthetics
of freeway corridors, and noise barriers in particular. Figures 17
through 21 illustrate several functions of landscaping relative to
noise barriers.
Noise barrier walls can be softened through the use of plants
that camouflage their hard edges (e.g. cap, base, and ends). Vines
cascading over the top of walls and base plantings can be used
effectively as softeners.
The scale of barrier walls can be reduced by using plants to
break up the expanse of wall surfaces and to reduce the relative
height of the wall. Mature overstory trees are tall relative to a
15' barrier wall. Planting overstory trees in front or behind a wall
can effectively reduce the apparent wall height. Shrubs and vines
can be used to break up the expanse of the wall body.
Visual direction can be added through the use of plantings that
accentuate horizontal or vertical lines. Creeping vines and low
spreading ground covers emphasize horizontally while pyramidal,
conical and columnar plants provide vertical elements, drawing the
eye upward.
Plants can be used to create points of focal interest or accent.
Plantings that provide contrast in color, form and/or size will be
visually prominent. Accent plantings can provide aesthetic
stimulation for motorists. They may also be used to subtly direct
views and provide locational cues.
Plants can be strategically placed to frame views and objects.
Figure 17: Soften
Figure 18: Reduce Scale
Figure 19: Horizontal and Vertical Emphasis
Figure 20: Create Accent
Figure 21: Framing Element
Integration of Wall, Landform, and Plants
A primary goal in designing noise barriers is to integrate them
into the landscape. Problems develop when barrier walls are placed
on the landscape with little attempt to integrate them with the
surrounding landforms or existing built elements such as bridge
abutments, endwalls, and guardrails. As a result, barrier walls can
appear as obtrusive objects in the environment. Barrier walls can be
integrated with the landscape in two basic ways. The structure
itself can be designed to appear to "grow" out of the landscape, or
the landscape (plants and earth) can become part of the barrier
structure.
Wall endings can be designed to integrate barriers with the
landscape (Figures 22a and 22b). Gradually tapering or stepping them
down to the ground level will give the appearance that the wall is
literally growing out of the ground. Earth berms and plantings may
also be used at wall ends to tie the barrier into the landscape. In
situations where existing structures such as bridges and guardrails
are present, an attempt should be made to connect the wall end with
the structure. This will provide visual continuity between highway
structures.
Figure 22: Integration of Wall, Landform, and Plants
a. Wall Endings
b. Tie Wall to Landscape and Existing Highway Structures
Plants and wall structures can be integrated in a variety of
ways. The wall itself can be designed using earth and plants as the
primary construction materials. Living barriers, which are used in
Western Europe, are such an example (Figure 23). These are
essentially vertical earth walls which function as the growth medium
for willow plants. The earth is contained in a frame constructed of
white willow posts interwoven with basket willow twigs. The twigs
sprout leaves, covering the structure and giving the appearance of a
wall-like hedge. To protect against dry periods, irrigation systems
are installed within the wall. Other maintenance is quite minimal,
consisting of trimming excessive growth every two years and
performing weed and disease control as necessary. In Germany these
walls have life expectancies of twenty to thirty years.
Living barriers provide an attractive alternative to the common
barrier constructed of hard materials, both in terms of appearance
and maintenance. However, willows are deciduous plants and therefore
lose their leaves in the fall. The attractiveness of these walls
during the winter months may be a point of concern. In addition, the
basket willow does not thrive in Southeastern Wisconsin. Until an
acceptable substitute is found, this limitation might make living
barriers difficult to implement here. As used in West Germany these
barriers are in the range of 12 feet high. It is not known if higher
barriers such as would be used in the Milwaukee area can be built
and maintained.
Figure 23: Living Barrier
A similar approach would be to design planter troughs into the
wall structure (Figure 24). Irrigation systems could be incorporated
into the troughs. The level of the planters could be varied to
produce a cascading effect. Because of the more elaborate,
multilayered design, this type of wall could be expensive. In
addition, the types of plants that can grow and survive in planters
are limited. Above ground planters are susceptible to freezing
temperatures unless they are quite large and adequately insulated.
Annuals are commonly used in planters in urban areas and would be
appropriate and very attractive in wall planters. However, they must
be planted annually and are therefore too maintenance intensive for
extensive use. They might, however, be appropriate on a limited
basis.
Figure 24: Planting Troughs Nested in the Wall
Plants can be integrated with walls by attaching them to the
surface or by providing holes through the wall which they can grow
through (Figures 25a and 25b). These approaches are especially
appropriate in situations where planting space is very limited.
Vines are the most appropriate plant type for either of these
approaches. Vines can attach themselves to the surface of concrete
and wooden wall materials. Wire supports can be used to attach
plants to metal surfaces. A system of wires and pins can be attached
to the wall surface which vines can use for growth support. Vines
planted on the residential side of the noise barrier will eventually
cascade over the top. In addition, small holes can be drilled
through the wall surface to allow the vines to grow through and
spread on the freeway side.
Figure 25: Integrate Wall and Plants
a. Attaching Plants to Walls
b. Utilize Plants on Opposite Side of Wall
Lighting
Freeway lighting is typically limited to tall overhead fixtures
required to light the roadway. Decorative lighting can be used to
provide nighttime variety and focal interest (Figure 26). Light
fixtures can be placed to cast shadows on the surface of barrier
walls. Shadows may be created by plants and/or surface relief on the
barrier itself. This may be especially desirable in the winter when
landscape color is subdued. Light fixtures can also be attached to
the wall itself to provide a "wash" of light over the surface.
Segments of barrier walls that have been specifically ornamented may
be highlighted with spot lighting.
Figure 26: Lighting to Create Shadow Patterns and
Spotlight
Maintenance
Maintenance contributes greatly to the attractiveness of noise
barriers and landscaping and is a primary economic concern in the
design of barriers and landscaping. This section will discuss the
major issues relevant to maintenance and how they can be addressed
through design and/or management and maintenance practices.
Maintenance Goals and Objectives
Maintenance begins as soon as the barrier and landscaping are
installed and continues throughout their life span. Consequently, it
constitutes a substantial ongoing cost expenditure. A major goal of
maintenance is to minimize the cost. This is best achieved by using
quality materials, appropriate to the given situation, and proper
construction techniques which will also increase the life of the
wall.
A consistent schedule of maintenance must be followed to ensure
that little problems are taken care of before they turn into large
and potentially expensive catastrophes. Therefore maintenance
capabilities must be considered during the design phase. It is
better to use simpler designs that can be adequately maintained than
to use more elaborate schemes which demand a disproportionate amount
of maintenance to remain attractive and effective.
Maintenance Issues
Material selection is an initial concern to the designer. The
chosen material must be durable enough to withstand local
environmental conditions. Of the common barrier materials, wood is
the least durable material, being more susceptible to weathering
damage. However, all materials designed for use in barrier wall
construction should be manufactured to be adequately durable. Again,
using quality materials, even if the initial cost is higher, will
pay off in the long run.
Another concern relative to material selection is vandalism.
Vandalism is a major maintenance concern regardless of the
construction material used. Vandalism can range from physical
destruction to surface defacement. The best way to deal with
vandalism is to minimize the opportunities for its occurrence. Noise
barriers present a blank canvas for "graffiti artists". Using
plants, particularly vines, to obscure the wall surface reduces the
potential canvas area. Rough surface textures can also be effective
in discouraging the defacement of barrier walls with spray paint or
other surface applied substances since the texture obscures
legibility of the graffiti. Physical destruction can be held in
check by minimizing access to the wall. Prickly plants can be used
as armor to dissuade potential vandals from getting too close to the
wall.
On the other hand, access to walls is necessary for maintenance
purposes. Likewise, access must be provided for landscape
maintenance. Typically access is gained on the side of the wall that
will receive maintenance (freeway or residential). While some
barriers are designed with maintenance doors, this is discouraged
because of the potential for persons other than maintenance
personnel to use them.
Identify Actors and Duties
Wisconsin state statutes indicate that maintenance within the
freeway corridor is the responsibility of the state (WDOT). The
state can contract with counties or municipalities to provide
maintenance activities. The Milwaukee County Department of Public
Works currently maintains all of the freeway corridors within its
jurisdiction. Specific maintenance tasks are delegated to the County
by WDOT area maintenance supervisors. Roadside maintenance generally
includes care and protection of trees and other vegetation, and
planting to prevent or minimize soil erosion.
Economic Considerations
Retrofitting urban freeway corridors with noise barriers is an
expensive endeavor. For example, costs can be over $2 million per
mile for a single side of a freeway. The state may use federal funds
to cover the cost of barrier construction. Noise barrier projects
compete for available funds with other projects such as bridge
replacement, freeway modernization, safety improvements, resurfacing
and capacity improvement projects.
Several factors affect the cost of barriers and landscaping.
Materials are probably the most fundamental cost factor. Type of
material used affects cost as does the quantity of material used.
Experience in Milwaukee County thus far has shown that metal
barriers have been the least expensive. Wood barrier use has had a
unit cost about 50% higher than metal while concrete has had a cost
65% higher than metal (Appendix A). The elaborateness of the design
has a direct bearing on the quantity of materials used. Barrier
designs with undulating configurations require more materials and
therefore will cost more. Landscaping will add cost to a barrier
system, but it is not as critical as the selection of a material. A
limited landscaping may add 5% to the cost, an average landscaping 8
to 10%, while an elaborate system could add 15 to 20% (Appendix C).
Actual costs will depend upon the extent of work, site conditions,
and maintenance considerations.
Design trade-offs are inevitable. Priorities will vary from
location to location. Decisions must be made as to how much should
be spent on the barrier versus the landscape treatment. An elaborate
landscaping scheme coupled with a lower cost barrier material may be
cheaper than using simple landscaping with more expensive material.
Such tradeoffs should be made clear to local citizens and elected
officials so they can select the option which best fits with their
community. In some contexts dense landscaping may be required to
blend the barrier with its environment. In such a situation, a
simple barrier could be used, retaining more of the funding
allotment for landscaping. In other, especially more urban
locations, the form of the wall may be the most important design
feature, with a simpler landscape scheme used to accentuate the wall
form. For more complete cost comparison information refer to
Appendix A and Appendix C.