ArtUSA -- Noise Control Products, Inc.  
Noise Control Products , Inc. --  "The Name To Know In Noise Control"  

 

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ArtUSA Noise Barriers

Noise Control and Soundproofing Inc.'s acoustical sound barrier & noise control barrier products used for noise control in Commercial Acoustic Applications, Home Theater Acoustics, Audio rooms, OEM projects, office and factory environment, Churches and several other applications where Noise Control is needed. Vinyl Barrier (often called Mass Loaded Barrier) is high density thin, weighted barrier, constructed of non reinforced high temperature fused vinyl with no lead filters. Pipe and or Duct Wrap is for wrapping noisy pipes and duct work in industrial, commercial, residential and other applications will help significantly quiet these types of mechanical items. Barrier Composites are a combination of 1 ¼" thick foam, then a 1/10" QVC vinyl, and a 1" foam faced with a protective aluminized mylar skin. Acoustic Curtain or Sound Blanket barriers are highly noise absorbent, quilted fiber glass blanket designed to absorb unwanted sound reflection in a variety of applications. Noise Control and Soundproofing Product Inc.’s Acoustical Door Cover Panels are designed to be attached to any existing door to significantly improve the sound transmission loss ability of the door and its frame.

Alum-A-Frame Enclosure Modular Enclosure Modular Enclosure


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Features:
  • STC ratings of 26-30
  • Passes FMVSS 302, UL-94
  • Easy to cut and install
  • High and low temperature applications
  • Accepts matching tape
  • Quilted fiberglass decoupler available
  • Good corrosion resistance
  • Meets Class A flammability rating per ASTM E-84

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.

 

photo:  earth berm, with trees planted on the top of the berm, and a highway with traffic (photo is intended to illustrate a typical example of an earth berm-type noise barrier)
photo:  precast concrete noise barrier, with good shrub-type landscaping in front of the barrier, and a highway with traffic (photo is intended to illustrate a typical example of a wall-type noise barrier)

photo:  precast concrete noise barrier constructed on top of an earth berm, viewed from the side of adjacent development (photo is intended to illustrate a typical example of a combination-type noise barrier)

 

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.

Figure illustrating that a noise barrier achieves 5 dB of noise reduction, when it is tall enough to break the line-of-sight from the source to the receiver, and 1.5 dB of additional attenuation for each additional 1 m of height above the line-of-sight

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.

	Figure illustrating that to effectively reduce the noise coming around its ends, a barrier should be at least eight times as long as the distance from the 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.

photo:  viewed from the top of an earth berm, showing trees planted on the berm, the backyards of homes, and a highway with traffic (photo is intended to illustrate a typical example of a well-designed and well-constructed earth berm noise barrier)photo:  precast concrete noise barrier, constructed immediately adjacent to the shoulder of a highway and protected by a concrete safety barrier (photo is intended to illustrate a typical example of a well-designed and well-constructed concrete noise barrier)photo:  brick noise barrier, constructed immediately adjacent to the shoulder of a highway, protected by a w-beam guardrail and with some vegetation beginning to grow up the face of the barrier (photo is intended to illustrate a typical example of a well-designed and well-constructed brick noise barrier)

photo:  wooden noise barrier, viewed from the highway side with vegetation in front of the barrier (photo is intended to illustrate a typical example of a well-designed and well-constructed wooden noise barrier)photo:  metal panel noise barrier, viewed from the highway side with vegetation in front of the barrier (photo is intended to illustrate a typical example of a well-designed and well-constructed metal noise barrier)photo:  noise barrier, with transparent panels set between posts on short non-transparent panels , viewed from the highway side showing yards and homes behind the barrier (photo is intended to illustrate a typical example of a well-designed and well-constructed transparent noise barrier)

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.

photo:  precast concrete noise barrier viewed from the backyard of a home, with a brick-look barrier surface and existing trees and abundant vegetation along the barrier (photo is intended to illustrate a typical example of a pleasant backyard view of a well-designed and well-constructed noise barrier)photo:  noise barrier, with transparent panels set between posts on short non-transparent panels, viewed from the residents= side of the barrier (photo is intended to illustrate a typical example of designing a noise barrier to protect residents= views of scenic vistas)

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.

photo:  metal panel noise barrier, viewed from the highway side, with a varied-color geometric design on the face of the barrier (photo is intended to illustrate a typical example of a barrier designed and constructed to enhance the motorists= view of a barrier)photo:  precast concrete noise barrier, constructed on an earth berm, with abundant shrub-type vegetation planted in front of the barrier and existing trees visible behind the barrier (photo is intended to illustrate a typical example of providing abundant vegetation with the construction of a noise barrier to help it blend into the surrounding landscape)

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.

 photo:  precast concrete noise barrier, almost covered with vine-like vegetation, viewed from the highway side of the barrier (photo is intended to illustrate a typical example of designing and constructing a noise barrier to discourage graffiti)

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.

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

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 ...

 

  • Noisy Pipes

  • Duct Work

  • Sheet Metal

  • Heat Exchangers

  • Valves

  • Custom Acoustical Jackets

    SS-105 - Acoustical Pipe & Duct Lagging

      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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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.

graph showing the A-weighted decibel scale

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

drawing of two trucks and three cars
2000 vehicles per hour sound twice as loud as

drawing of one truck and one car

200 vehicles per hour


How Speed Affects Traffic Noise

drawing of five cars moving quickly
Traffic at 65 miles per hour sounds twice as loud as

drawing of five cars moving at a normal speed

traffic at 30 miles per hour


How Trucks Affect Traffic Noise
drawing of one truck
One truck at 55 miles per hour sounds as loud as

drawing of 10 cars

drawing of 10 cars

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.

graph comparing noise level and duration of 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.

drawing showing an example of commercial buildings between a highway and a residential area.
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.

drawing showing open space between a highway and a residential area
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.


photo of an earth berm noise barrier
Earth Berm Noise Barrier

photo of a wooden noise barrier
Wooden Noise Barrier

photo of a concrete noise barrier with woodgrain texture
Concrete Noise Barrier with Woodgrain Texture


drawing comparing a house in a shadow zone and an unshileded house

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.


drawing of a house with many trees before the highway
Loudness Cut in Half

drawing showing little tree growth between a house and a highway

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.

photo showing a highway below ground level
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.

 

 

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