Chapter Six

Green Building Materials and Products

Abstract

This chapter offers a general overview of green building materials and products. It also discusses the main differences between natural versus synthetic materials, in addition to pointing out the criteria of what makes a material or product green. Low-emitting materials (including adhesives, finishes, sealants, and certain paints and coatings) and flooring green roofing systems are explained as are various building elements. Factors that can impact R-values are also discussed. LEED requirements and credits for construction waste management, material recycling, regional materials, rapidly renewable materials, and so forth are looked at. Energy-efficient office equipment and appliances are examined the advantages of the ENERGY STAR label. Finally, life-cycle cost analysis is briefly touched upon as is the LEED third-party certification program.

Keywords

Agrifiber; Biodegradable; Earthen construction; Fire-resistance; Low emitting materials; Negative impact; Prerequisites; R-value; Recyclables; U-factor

6.1. Overview

In construction terms, any material that is used for building purposes can be considered to be building material. And when designing a green building, it is vitally important to carefully consider the choice of materials to be used to achieve the desired sustainability goals. The U.S. Green Building Council (USGBC) believes that building materials choices are fundamental to achieving success in sustainable design. This is due to many factors including the extensive network of extraction, processing, and transportation steps required to process them. Additionally, the numerous activities normally required to create building materials may have a negative impact on the environment by polluting the air, water, destroying natural habitats, and depleting natural resources. Also, incorporating green products into a project should not imply sacrifice in performance or aesthetics nor does it necessarily entail higher project cost.
History shows us that for thousands of years, man has used naturally occurring materials, such as clay, sand, reed, wood, and stone, to construct his habitat. But in addition to naturally occurring materials, man has, with the passing of time, developed and supplemented these with a variety of man-made products—some more and some less synthetic. Moreover, building materials manufacture has long been an established industry in many countries around the world, from the United States to China and Iraq, and their use is typically compartmented into specific specialty trades, such as carpentry, roofing, flooring, and plumbing.
The concept of repair and reuse of a building instead of tearing it down and building new structure is a highly effective strategy for minimizing environmental impact. And refurbishment and rehabilitation of existing building components helps minimizes any potential negative impact on the environment and saves natural resources, including the raw materials, energy, and water resources required for new construction. It also helps reduce pollution that might take place as a by-product of manufacturing, extraction, and transportation of raw materials, in addition to minimizing the creation of solid waste that often ends up in landfills.
Some states, such as North Carolina, have a Building Reuse and Restoration Grants Program that provides grants for the restoration and upfitting of vacant buildings in rural communities or in economically distressed urban areas, as well as for the expansion and renovation of buildings currently occupied by certain types of businesses. Many rating systems including the USGBC’s LEED Rating System also recognize the importance of building reuse. Reusing a building can contribute to earning points under LEED “Materials Resource Credits on Building Reuse”. Of note, according to the USGBC, project teams may pursue the entire LEED v4 Materials and Resources (MR) category in place of the MR credits from LEED v2009 but all prerequisites must be met including:
• Storage and collection of recyclables (Required)
• Construction and demolition (C & D) waste management planning (Required)
• Building life-cycle impact reduction Up to 5 points
• Building product disclosure and optimization—environmental product declarations Up to 2 points
• Building product disclosure and optimization—sourcing of raw materials Up to 2 points
• Building product disclosure and optimization—material ingredients Up to 2 points
• C & D waste management Up to 2 points

6.1.1. Definition of Green Building Material and Products

Green building materials cover a vast area of themes and materials. The application and use of these materials further complicates the subject. Moreover, green building means different things to different people—it is a multifaceted concept that lends itself to numerous interpretations. Likewise, Green building materials defy easy definition; one characteristic is that they are ecofriendly and are composed of renewable, rather than nonrenewable resources. In general, building materials are called “green” because they have minimal or no negative impact on the environment (and in some cases may even have a positive impact). It should be noted that there is no perfect green material, but in practice, there is an upsurge in number of materials on the market that reduce or eliminate negative impacts on people and the environment. And especially today, with building and construction activities worldwide consuming billions of tons of raw materials each year, it has become increasingly imperative to employ green building materials and products and so help in the conservation of dwindling nonrenewable resources internationally.
Many green materials are made from recycled materials, which help the environment and puts waste to good use in addition to reducing the energy required to make them. Building materials are also considered green when they are made from renewable resources that are sustainably harvested. An example of this is flooring that is made from sustainably grown and harvested lumber or bamboo. Durability is another characteristic of a sustainable product, and some building materials are considered to be green mostly because they are very durable. A typical example of this is a durable form of siding that outlasts less durable products, resulting in substantial savings in energy and materials over the lifetime of a property. Additional benefits can be achieved when a durable product is made from environmentally friendly materials, such as recycled waste.

6.1.2. Natural Versus Synthetic Materials

Building materials generally fall into one of two classifications, natural and synthetic. Natural building materials are those materials that have not gone through any process or minimally processed by industry, such as timber or glass. Synthetic materials, on the other hand, are made in industrial settings and gone through processing after considerable human manipulations; they include plastics and petroleum-based paints. Both have their advantages and disadvantages.
Clay, mud, stone, and fibrous plants (e.g., bamboo and reeds) are among the most basic natural building materials. These materials are being used together by people all over the world to create shelters and other structures to suit their local habitat. In general, stone and/or brush are used as basic structural components in these buildings, while mud is generally used to fill in the space between, acting as a form of mortar and insulation.
In many cases, it has been clearly demonstrated that natural materials cannot cope with nor meet the required specifications of today’s industrial challenges of the construction industry. Plastic is a case in point and a good example of a typical synthetic material. The term “plastic” covers a range of synthetic or semisynthetic organic condensation or polymerization products that can be molded or extruded into objects, films, or fibers. The term is derived from the material’s malleable nature when in a semiliquid state. Plastics vary immensely in heat tolerance and are hard-wearing, highly adaptable, can be molded and cast in a variety of forms, and can mimic, and perform the task of, most other building materials. Plastics continue to be viewed as a potential replacement for other natural building materials. Combined with this adaptability, its general uniformity of composition and lightness facilitate its use in almost all industrial applications.
A material’s “greenness” is generally based on certain criteria; we mentioned its durability and also whether the material is renewable and resource efficient in its manufacture, installation, use, and disposal. Other considerations are whether the material is ecofriendly and supports the health and well-being of occupants, construction personnel, and the public; whether the material is appropriate for the application, and what the environmental and economic tradeoffs among alternatives are.
Considerable research remains to be conducted to enable persons to satisfactorily evaluate alternatives and select the best material for a project. Appropriate material selection should consider a number of factors including its impact throughout its life cycle (from raw-material extraction to use and then to reuse, recycling, or disposal). A life-cycle assessment (LCA) is a systematic set of procedures for compiling and examining the inputs and outputs of materials and energy and the associated environmental impacts directly attributable to the functioning of a product or service system throughout its life cycle. The areas of impact to consider at each stage in the life cycle of a material include:
• Energy required for extraction, manufacturing, and transport
• Natural-resource depletion; air and water pollution; hazardous- and solid-waste disposal
• Energy performance in useful life of material and its durability
• Impact of material or product on indoor air quality (IAQ); exposure of occupant, manufacturer, or installer to harmful/toxic substances; moisture and mold resistance; cleaning and maintenance methods
Properties that typical green building materials and products may share include:
• Recyclability of building material or reusable when no longer required
• Sustainably harvested from rapidly renewable resources such as genuine linoleum flooring, bamboo flooring, wool carpets, strawboard, cotton ball insulation (made from denim scrap). Using rapid renewables helps reduce the use and depletion of finite raw materials
• Durability
• Minimal toxic emissions generated by the product
• Wood or wood-based materials meet Forest Stewardship Council’s (FSC) Principles and Criteria for wood building components
• May contain postconsumer recycled content
• Can be salvaged for reuse, refurbished, remanufactured, or recycled
• Manufactured from a waste material such as straw or fly ash or a waste-reducing process
• Minimally packaged and/or wrapped with recyclable packaging
• Locally extracted and processed, which means less energy used in extraction, processing, and transport to the job site. Regional economies are helped by using materials and products manufactured regionally
• Water-efficient
• Manufactured with a water-efficient process
• Energy-efficient in use
• Minimal waste and pollution generated in the manufacturing process
• Generates renewable energy
• Financial viability

6.1.3. Storage and Collection of Recyclables

According to LEED the intent of this prerequisite is essentially to reduce the waste that is generated by building occupants and hauled to and disposed of in landfills by encouraging the storage and collection of recyclables. Thus, “Storage and Collection of Recyclables” is a MR prerequisite in most of the LEED Rating System categories. This is also why LEED stipulates that an area needs to be provided that is dedicated to recycling inside the building, so that occupants can have the option to recycle their paper, cardboard, glass, plastic, and metals. This recycling means that there is a reduction in the need for virgin materials as well as a significant reduction in the amount of waste otherwise going to landfills.
It should be noted that LEED has not set any specific standards or requirements for this area, but the USGBC guidelines (Table 6.1) state that the area should be easily accessible, serve the entire building(s), and be dedicated to the storage and collection of nonhazardous materials for recycling. The average waste per employee is estimated to be about 3 pounds per day! It is therefore important that the building occupants have the option to maintain good recycling programs throughout the lifespan of the building.

6.2. Low-Emitting Materials

The intent of low-emitting materials is to reduce concentrations of chemical contaminants that can damage air quality, human health, productivity, and the environment. This is partly why most major manufacturers and suppliers today offer a low-emitting option for any of the materials recommended for credits in the Indoor Environmental Quality section of the LEED Building Design & Construction reference guides. “Green” appears to be the latest trend, and everyone’s trying to get in and hop on the bandwagon. People are increasingly seeking out “healthy” buildings to live and work in. LEED addresses low-emitting materials within the Indoor Environmental Quality section of this book. Among the most straightforward credit to earn, of the IEQc4 credits, is IEQc4.5, particularly if you choose to meet the credit by using Greenguard Indoor Air Quality certified furniture. For the latest LEED updates, visit www.usgbc.org. Low emitting materials.

Table 6.1

Recycling storage-area guidelines based on overall building square footage

Commercial building (square footage)Minimum area (square footage)
0 to 5,00082
5,001 to 15,000125
15,001 to 50,000175
50,001 to 100,000225
100,001 to 200,000275
200,001 or greater500

Source: USGBC.

With respect to the New Construction rating system, credits MR4.1-4 relate to low-emitting materials such as adhesives and sealants, paints and coatings, flooring systems, and composite wood and agrifiber products.
Many of the environmental impacts associated with building materials have already taken place by the time the materials are installed. Pollutants are emitted during the extraction from the ground, or harvesting from forests, and during manufacture. Energy has therefore been invested throughout production. Certain materials, such as those containing ozone-depleting HCFCs and volatile organic compound (VOCs), may continue emitting pollutants during their life cycle. Some materials will also have negative environmental impacts associated with their disposal. Important considerations to bear in mind when selecting building materials and products include the following:
• Avoid materials and products that generate substantial amounts of pollution (VOCs, HCFCs, etc.) during manufacture or use.
• Specify salvaged building materials or that is produced from waste or contain postconsumer recycled content.
• Avoid materials made from toxic or hazardous constituents (benzene, arsenic, etc.).
• Specify materials with low embodied energy (the energy used in resource extraction, manufacturing, and shipping).
• The regional economy and the environment are helped by using materials and products manufactured regionally.
• Encourage environmentally responsible forestry by using wood or wood-based material that meets FSC’s Principles and Criteria for wood building components and avoid materials that unduly deplete limited natural resources, such as old-growth timber.
This credit adds new international compliance options for projects outside of North America. Moreover, project teams will now have to identify the total surface area for flooring/ceilings, walls, and insulation, and the surface area with compliant materials for each category. Of note, there are various resource-efficient products that are available at no extra charge, while others may cost more. Also, if the installation differs from standard practice, it may raise labor cost if an installer is unfamiliar with a product.

6.2.1. Adhesives, Finishes, and Sealants

The New Construction credit template for IEQc4.1, low-emitting adhesives and sealants, for example, requires the project manager or specifier to list all indoor adhesives, sealants, and sealant primer products to be used on the project and input the following information:
• Name of Product Manufacturer
• Product Name and Model
• Product VOC Content (g/L)
• Source of VOC Data
• South Coast Air Quality Management District (SCAQMD) Rule #1168 as of 2007) Allowable VOC Content (g/L), as indicated in Fig. 6.1. Aerosol adhesives not covered by Rule 1168 must meet Green Seal Standard GS-36 requirements in effect on October 19, 2000. All indoor-air contaminants that are odorous, potentially irritating, and/or harmful to the comfort and well-being of installers and occupants should be avoided or minimized.
An important characteristic of Sealants is that they can increase the resistance of materials to water or other chemical exposure, while caulks and other adhesives can assist in controlling vibration and strengthen assemblies by spreading loads beyond the immediate vicinity of fasteners. These properties enhance durability of surfaces and structures, but they do so at a cost, because very often they are shown to be hazardous in manufacture and application. Moreover, construction-adhesive formulas often contain in excess of 30% volatile petroleum-derived solvents, such as hexane, to maintain liquidity until application. This has caused workers to become exposed to toxic solvents; and, as the materials continue to outgas during curing, the occupants may be potentially exposed to emissions for extended periods.
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Figure 6.1 Adhesives, sealants, and sealant primers: South Coast Air Quality Management District (SCAQMD) Rule #1168. VOC limits are listed in the table and correspond to an effective date of July 1, 2005 and rule-amendment date of January 7, 2005. Source: USGBC.
Industry tests indicate that water-based adhesives work as well as or better than solvent-based adhesives and can pass all relevant ASTM and APA performance tests. Also, water-based adhesives can be purchased at comparable costs from numerous manufacturers, and when adhesives are purchased in bulk, larger containers can often be returned to vendors for refill.
Most stains and sealants also emit potentially toxic VOCs into indoor air. One way of managing this problem is by employing materials that do not require additional sealing, such as stone, ceramic and glass tile, and clay plasters. The toxicity and the air and water pollution generated by the manufacture of chlorinated hydrocarbons such as methylene chloride strongly reinforces the need for responsible, effective alternatives, such as plant-based, nontoxic, or low-toxicity sealant formulations.
LEED requires that all adhesives and sealants used on building interiors (defined as inside the weatherproofing system and applied on-site) need to comply with the reference standards shown in Fig. 6.1. Environmentally preferable cleaning methods and products can lessen indoor-air pollution and solid/liquid waste generation. Safe cleansers are readily available and are competitively priced and ecofriendly. The improper use and disposal of some common cleaning and maintenance products can contribute to indoor-air contamination, toxic waste, and water pollution.
The active ingredients in cleaners are surfactants, of which biodegradability is a key factor. Even low surfactant concentrations in runoff have shown to pose risks to the environment. Petroleum-derived surfactants generally break down more slowly than vegetable oil–derived fatty acids; some materials are even resistant to municipal sewage treatment. The harmful effects of toxins can be minimized by implementing the following:
• Storing hazardous materials outside the building envelope.
• Select materials with a durable finish and that do not require frequent stripping, waxing, or oiling (such as linoleum, cork, or colored concrete).
• Select products that have approved third-party or government-agency certification:
Green Seal, Scientific Certification Systems (SCS), Environmental Protection Agency (EPA) Environmentally Preferable Purchasing Program, General Services Agency, California Integrated Waste Management Board (CIWMB) Recycled Content Product Directory
• Whenever possible, select biodegradable, nontoxic cleansers.
• Avoid selecting cleansers, waxes, and oils that are labeled as toxic, poisonous, harmful, or fatal if swallowed, corrosive, flammable, explosive, volatile, requiring “adequate ventilation” or safety equipment, or causing cancer or reproductive harm.
• Place mats at all building entrances to minimize stripper use; refinish only areas where the finish surface is wearing; clean regularly, and dust-mop and/or vacuum frequently and wet mop with a liquid cleaner.

6.2.2. Paints and Coatings

Paints generally consist of a mixture of solid pigment suspended in a liquid medium and applied as a thin, (often opaque) coating to a surface for protection and/or decoration. Primers are the first coat in a paint system (i.e., basecoats), whose main function is to increase the adhesion between substrate and the total paint system (i.e., of subsequent coats of paint or varnish). Sealers are also basecoats and are applied to a surface with the main function of helping reduce the absorption of subsequent coats of paint or varnish and to prevent bleeding through the finish coat by sealing in aggressive chemicals (e.g., alkalinity). Paint was first used on a large scale thousands of years ago by the Egyptians and Babylonians in their buildings and temples.
It should be noted that the LEED Guidelines for Paints, Coatings, and Primers may vary from one LEED Program to another, although USGBC has made a determined effort to make this credit more consistent through the introduction of LEED 09. Also, LEED considers Paints and Coatings as referring only to paints and coatings used on the interior of the building, since exterior paints will not affect a building’s “indoor air quality.” Generally speaking, the USGBC requires that paints and coatings applied on-site and used on the interior of the building (defined as inside the weatherproofing system) must comply with the following referenced standards:
• Architectural paints, coatings, and primers applied to interior walls and ceilings: Do not exceed the VOC content limits established in Green Seal Standard GS-11. Of note, Green Seal redesigned GS-11 to promote the creation of safer coatings by restricting a comprehensive list of harmful chemicals, including heavy metals, certain phthalates, formaldehyde donors, carcinogens, mutagens, reproductive toxins, hazardous air pollutants, and ozone-depleting compounds.
• Anticorrosive and antirust paints applied to interior ferrous metal substrates: Do not exceed the VOC content limit of 250 g/L established in Green Seal Standard GC-03, Anti-Corrosive Paints, Second Edition, January 7, 1997.
• Clear wood finishes, floor coatings, stains, and shellacs applied to interior elements: Do not exceed the VOC content limits established in SCAQMD Rule 1113, Architectural Coatings, for January 1, 2004. Table 6.2 shows the allowable VOC levels stipulated by SCAQMD.
Santa Cruz County officials often point out that paint can have significant environmental and health implications in its manufacture, application, and disposal. Most paint, even water-based “latex,” is derived from petroleum. Its manufacture requires substantial energy and water and creates air pollution and solid/liquid waste. VOCs are typically the pollutants of greatest concern in paints. VOCs from the solvents found in most paints (including latex paints) are released into the atmosphere during manufacture and application and for weeks or months after application. VOCs emitted from paint and other building materials are associated with eye, lung, and skin irritation, headaches, nausea, respiratory problems, and liver and kidney damage. Manufacturers continue to employ the latest technology to reduce the VOCs found in these paints while maintaining costs at a reasonable level.

Table 6.2

Allowable volatile organic compound levels in paints and finishes

TypeLimit (g/L)
Paints
Flat50
Nonflat50
Primers, sealers, and undercoats100
Quick-dry enamels50
Finishes
Clear woodVarnish, 350
Lacquer, 550
Floor coatings100
SealersWaterproofing, 250
Sanding, 275
All others, 200
ShellacsClear, 730
Pigmented, 550
Stains250

image

Note: Grams/liter less water and exempt compounds, according to SCAQMD.

Although exposure to solvents emitted by finish products can be significant, renewable alternatives, such as milk paint, addresses many of these concerns. In this case, there may be a premium price to pay, and some products may not be suitable for exterior applications. Paint manufacturers have started to produce reformulated low- and zero-VOC latex paints with excellent performance in both indoor and outdoor applications and which can be purchased for the same or lower price than older high-VOC products. Paints that meet GS-11 standard meet stringent performance criteria and are low in VOCs and aromatic solvents, do not contain heavy metals, formaldehyde, or chlorinated solvents.
There are other alternative paints on the market such as silicate paints which are solvent free and may be used on concrete, stone, and stucco. Silicate paints have many advantages; they are odorless, nontoxic, vapor permeable, naturally resistant to fungi and algae, noncombustible, colorfast, light reflective, and even resist acid rain. Though silicate paints are more expensive, their extraordinary durability provides some compensation, plus the fact that these paints cannot spall or flake off and will only crack if the substrate cracks.

6.2.3. Flooring Systems

There are many kinds of flooring systems available in today’s marketplace, from nonmagnetic access flooring systems to carpet, wood block, and resinous flooring. Each system is designed to meet different requirements and to satisfy the rigorous demands of high-traffic commercial, residential, and institutional applications as well as the aesthetic requirements for high-visibility public and private facilities. “Green” flooring is nontoxic, environmentally friendly and made from sustainably harvested, recycled, or reclaimed sources.

Carpet

Carpet is a very controversial material and in most cases, it is not considered to be green. And as with any product, significant environmental impacts can occur throughout a carpet’s life cycle—i.e., its manufacture, use, and disposal. By considering a variety of life cycle attributes, from the materials used to manufacture and install carpet to recycling and disposal issues, purchasers can make informed decisions about carpet, including the potential health concerns it presents.
Various VOCs can be emitted from carpet materials, although VOC emissions from new carpet usually fall to very low levels within 48–72 h after installation if good ventilation is provided.
Most carpet products are synthetic, usually derivatives of nonrenewable petroleum products; their manufacture requires substantial energy and water and creates harmful air and solid/liquid waste. Today, however, many carpets are being manufactured with recycled content (e.g., plastic bottles), and moreover, a growing number of carpet manufacturers are refurbishing and recycling used carpets into new carpet. At the end of its useful life, most carpet tends to end up in landfills, and the EPA states that “Over four billion pounds of carpet enter the solid waste stream in the U.S. every year, accounting for more than one percent by weight and about two percent by volume of all municipal solid waste (MSW).”
Carpet remains the most popular floor covering in the United States and is installed on nearly 70% of our floors. Synthetic carpeting is the most common line of products, constructed from petroleum-based materials that have been linked to health concerns. Carpets, their backings, and adhesives used with carpets have been shown to off-gas many unhealthy VOCs, all of which pollute indoor and outdoor air. Nylon is the most popular fiber used as the face fiber in commercial carpet. Polypropylene (olefin), PET, and recycled PET are also employed in carpet face fiber. In general, carpet made from PET and polypropylene face fiber is not as durable as carpet made from nylon face fiber. Redesigned carpets, new adhesives, and natural fibers are now available that emit low or zero amounts of VOCs. For improved air quality, selected carpets and adhesives should meet a third-party standard, such as the Carpet and Rug Institute (CRI) Green Label Plus or the State of California’s Indoor Air Emission Standard 1350.
From an environmental standpoint, natural fibers are an ecofriendly and preferable carpeting option because they are renewable and biodegradable. A traditional material is wool, and in many parts of the world, sheep are still raised specifically for carpet fibers. Wool carpets are more durable than synthetics, resist dust mites, moisture, and fire and also can be more comfortable under foot. Wool carpets often use jute backing, upping the sustainable nature of these carpet products. Other natural fiber options include sisal, seagrass, abaca, coir, and wool floor coverings. One of the disadvantages of carpets is that they tend to harbor more dust, allergens, and contaminants than many other materials (Fig. 6.2). Durable flooring, such as a concrete-finish floor, linoleum, cork, or reclaimed hardwoods, is generally preferable in helping to improve IAQ.
The LEED intent of low-Emitting carpet systems is to reduce the quantity of indoor-air contaminants that are odorous and potentially irritating and or harmful to the comfort and well-being of installers and occupants. Additionally, for LEED credits, all carpet installed within a building’s interior must meet or exceed testing and product requirements of the CRI Green Label Plus program for VOC emission limits. Carpet pads installed within a building’s interior must also meet or exceed CRI’s Green Label program for VOC emission limits. Adhesives and sealants used in carpet-system installation must comply with SCAQMD Rule #1168.
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Figure 6.2 Photo of FLOR carpet squares laid in a flexible and practical “tile” format. The tiles are made from renewable and recyclable materials and are available in a range of colors, textures, and patterns. More than two million tons of carpets are landfilled in the United States each year. Courtesy: FLOR, Inc.
The EPA has developed five guiding principles to help federal government purchasers incorporate environmental considerations into purchasing decisions and which provide a framework purchasers can use to make environmentally preferable purchases. They are:
1. Include environmental factors as well as traditional considerations of price and performance as part of the normal purchasing process.
2. Emphasize pollution prevention early in the purchasing process.
3. Examine multiple environmental attributes throughout a product’s or service’s life cycle.
4. Compare relative environmental impacts when selecting products and services.
5. Collect and base purchasing decisions on accurate and meaningful information about environmental performance.
It should be noted that in LEED 2009 NC, C&S, and CI, the title of EQ 4.3 has been changed from Carpet to Flooring Systems, and this credit has been substantially expanded. From 2009 onward, LEED has stipulated that all hard-surface flooring must be certified as compliant with the FloorScore standard by an independent third party (Third-party certification means that an independent organization has reviewed the manufacturing process of a product and has independently determined that the final product complies with specific standards for safety, quality or performance). FloorScore is a program developed by the Resilient Floor Covering Institute (RFCI) together with SCS to test and certify flooring products and flooring adhesive products for compliance with IAQ emissions targets. Flooring products covered by FloorScore include vinyl, linoleum, laminate flooring, wood flooring, ceramic flooring, rubber flooring, wall base, and associated sundries. A FloorScore certification means healthier, cleaner air and therefore healthier living/working conditions.

Polyvinyl Chloride/Vinyl

PVC or Polyvinyl chloride is also referred to as “Vinyl,” is one of the most widely used synthetic materials in building and construction due to its durability, versatility, and cost. In addition to flooring, PVC is common in pipes, vinyl siding, vinyl flooring, wire insulation, conduit, window frames, packaging, wall covering, roofing, and many other products. PVC is generally transparent with a bluish tint. It is attacked by many organic solvents but has a very good resistance to oils, and it has a low permeability to gases. In its rigid form, PVC is available in sheets which can readily be welded to produce tanks, trays, and troughs. It is not recommended for use above 158°F (70°C) although it can be taken to 176°F (80°C) for short periods. PVC is important because it accounts for nearly 50% of total plastic use in construction and because it is increasingly recognized as problematic. Vinyl is common place today with about 14 billion pounds being produced annually in North America. It is inexpensive, and not all of its alternatives have yet worked out all their negative issues. Moreover, as the USGBC suggested in its long-awaited report on PVC, all materials have potential pitfalls, from IAQ to disposal. PVC is difficult to recycle for many reasons including its high chlorine content which makes recycling complicated and expensive because it cannot be mixed with other plastics.
It is said that vinyl composition tile (VCT) accounts for more square footage than any other category of resilient flooring. Today, millions of square feet of VCT have been installed around the world, in commercial buildings, retail stores supermarkets, hospitals, and schools. VCT has been extensively used because of its benefits: good strength relative to its weight, durability, water resistance, and adaptability. Vinyl tends to be inexpensive, in part because production typically requires roughly half the energy required to produce other plastics. Products made from vinyl can be resistant to biodegradation and weather and are effective insulators. The physical properties of vinyl can be tailored for a wide variety of applications. Many firms are increasingly concerned about difficulty in recycling VCT and the negative environmental impacts this creates and are therefore struggling to find appropriate alternatives.
Vinyl/PVC’s main problem is its “Toxic Lifecycle”; its life cycle begins and ends with hazards, most stemming from chlorine, its primary component. Chlorine makes PVC more fire resistant than other plastics. The production of PVC requires hazardous chemicals such as vinyl chloride (a simple chemical made of chlorine, carbon, and hydrogen), which causes cancer, and very hazardous chemicals are by-products of that same production, including dioxin and PCBs. Lead, cadmium, and other heavy metals are sometimes added to vinyl as stabilizers; and phthalate plasticizers, which give PVC its flexibility, pose potential reproductive risks. Also, some consumer products such as phthalates can over time leach out or off-gas harmful chemicals, exposing building occupants to materials linked to reproductive-system damage and cancer in laboratory animals. Manufacturing vinyl or burning it in incinerators produces toxic by-products including dioxins, which are among the most toxic chemicals known to man. Research has shown that the health effects of dioxin, even in minute quantities, include cancer and birth defects.
PVC is one of the most environmentally hazardous consumer materials being produced. It is a strong thermoplastic material that is made from vinyl chloride monomer (VCM) and ethylene dichloride, both of which are carcinogens and acutely toxic. The production of PVC causes the release of these toxic carcinogens into the environment, and there is no way to confidently quantify these hazards and upset condition impacts for an LCA or risk analysis. Clean-air regulation and liability concerns have been effective in reducing total VCM releases since 1980, while PVC use has roughly tripled. Most PVC products are believed to be basically harmless when properly used. However, some of the additives and softeners can leach out of certain vinyl products. And although PVC resin is inert in normal use, older PVC products are frequently contaminated with traces of VCM (many of the older landfills have been releasing toxic fluids for decades), which can leach into the surrounding environment and contaminate drinking water.
There are many possible substitutes on the market which may cost more or require different maintenance, but many of these alternatives can outlast plastics with proper care. Moreover, for many applications, particularly indoors where occupants can be directly exposed to off-gassing plasticizers, substitution of vinyl would clearly be prudent for maintaining health and well-being of occupants. Below are some potential examples of possible material alternatives:
• Flooring made from cork, natural linoleum, tile, finished concrete, or earth
• Stucco, lime plaster, reclaimed wood, fiber-cement, and FSC-certified wood siding
• Natural wall coverings instead of vinyl wallpaper
• Windows framed with fiberglass, FSC-certified wood, or possibly wood-based composites utilizing formaldehyde-free binders
• Substituting glass shower doors instead of vinyl curtains

Tile

Tile production is an ancient process, dating back to ancient Babylonian and Egyptian times. Tiles typically start out in the earth, where the raw materials are quarried and refined. Once the raw materials are quarried, prepared, and properly mixed, the tiles can be formed. Tiles are primarily made from fired clay (porcelain and other ceramics), glass, stone or cement; it provides a useful option for flooring, countertops, and wall applications whose principal environmental requirement is durability. Tile is very durable, even in high-traffic areas, eliminating the waste and expense of replacements. Tile production, however, is energy intensive, although tile made from recycled glass requires less energy than tile made from virgin materials. Among tiles’ positive attributes is that they do not burn, will not retain liquids, and do not absorb fumes, odors, or smoke and, when installed with low- or zero-VOC mortar, can contribute to a building’s good IAQ. But such tile performance can only be achieved if it has the appropriate surface hardness for the location. Tile hardness is measured on the Porcelain Enamel Institute (PEI) scale of 0–5, with 0 being the least hard, indicating a tile that should not be used as flooring, and five signifying a surface designed for very heavy foot traffic and abrasion. Floor tiles can easily last as long as the building they are installed in if properly maintained.
The environmental impacts of mining, producing, and delivering a unit of tile requires important considerations, although ceramic tiles production today have a lower environmental impact compared with other materials, thanks to an intense activity of technological, and production innovations conducted by the ceramics industry. Most of the tiles used in the United States today, are imported (roughly 75%). The remaining amount represents about 650 million square feet of ceramic tile produced by U.S. factories each year, together with the billions of square feet manufactured globally. This requires mining millions of tons of clay and other minerals and substantial energy to fire material into hardened tile. Once the raw materials are processed, a number of steps are put into motion to obtain the finished product. These steps include batching, mixing and grinding, spray-drying, forming, drying, glazing, and firing. In modern facilities, many of these steps are now accomplished using automated equipment. Stone, while requiring relatively little energy to process, nevertheless, requires significant energy to quarry and ship. Selecting tile produced regionally may dramatically reduce the energy use and pollution of transport and thus facilitate achieving a LEED credit.
In the United States, more than 95% of the tile industry’s product consists of glazed or unglazed floor tile and wall tile, including quarry tile and ceramic mosaic tile (Fig. 6.3). Due to the industry’s focus on decorative tiles, it has become completely dependent on the economic health of the construction and refurbishing industries. The only real difference between the production process for ceramic glazed tile and ordinary ceramic tile is that the glazed tile includes a step known as glazing. There are many ways to glaze ceramic tile; basically, it requires a liquid made from colored dyes and a glass derivative known as flirt that is applied to the tile, either using a high-pressure spray or by direct pouring. This in turn gives a glazed look to the ceramic tile. Tile in low-traffic areas, particularly roofing, may use lower-impact water-based glazes. Glazed tiles have the advantage of being practically stainproof, even though they can be more slippery. Unglazed tiles on the other hand are generally more slip resistant but may require a sealant. Also, the integral color and generally greater thickness of unglazed tiles tend to make them more durable than glazed tiles. Factory-sealed tiles can help minimize or eliminate a source of indoor VOC emissions. Glass floor tile can also offer a nonskid surface appropriate for ADA compliance. When installing stone tile, especially for countertop applications, a nontoxic sealer should be used for the grout and tile surface. Also, it is important that the final product meets certain specifications regarding physical and chemical properties. These properties are determined by standard tests established by the American Society of Testing and Materials (ASTM). The ASTM tests measure properties such as abrasion resistance, chemical resistance, mechanical strength, dimensional stability, water absorption, frost resistance, and linear coefficient of thermal expansion.
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Figure 6.3 Interior showing installation of Crystal Micro double-loading polished tile. Source: Foshan YeShengYuan Ceramics Co. Ltd.

6.2.4. Earthen Building Materials

Earthen building materials were used from Neolithic times—even before the invention of writing. But the techniques and methods for earth construction are numerous and vary with culture, climate, and resources. The primary types of earthen building materials include adobe bricks, made from clay, sand, and straw; rammed earth, compressed with fibers for stabilization; and cob, made of clay, sand; and straw that are stacked and shaped while wet, as well as wattle and daub and earth plasters and finishes. Provided they are obtained locally, earthen building materials can reduce or eliminate many of the environmental problems posed by conventional building materials since they are plentiful, nontoxic, biodegradable, and reusable. Well-built earthen buildings are known to be durable and long lasting and require little maintenance.
For thousands of years, people throughout the world have built comfortable homes and communities with earthen materials that provide excellent shelter. Though the domestic popularity of earthen materials waned during the 20th century, a revival has emerged since the 1970s. By contrast, modern “stick-frame” construction, which requires specialized skills and tools, has been a standard practice in the United States only since the end of World War II and remains today uncommon in many parts of the world. Main considerations in regard to earthen construction include:
• Earthen construction is generally labor intensive, although minimal skill is required.
• Earthen walls are thick and may comprise a high percentage of floor area on a small site, making its use inappropriate.
• Multistory and cob structures require post-and-beam designs.
It may be more difficult to obtain necessary permits in certain jurisdictions, although code recognition and structural testing are available in most states Also, unit production costs will differ in relation to local conditions including availability of soil and its suitability for stabilization, etc. If labor is done primarily by building professionals, the square-foot cost of earthen construction is comparable to conventional building methods. Advantages and benefits of earthen materials include:
• Abundance of the raw material—earth.
• They are durable and require low maintenance.
• They are ecofriendly with minimal environmental impact, provided materials come from local sources.
• High thermal insulating properties. Thermal mass helps keep indoor temperatures stable, particularly in mild to warm climates.
• High sound insulation.
• No waste generated during construction.
• They are biodegradable or reusable.
• Construction is inexpensive and simple, with high workability and flexibility. Structures are therefore easy to build, requiring few special skills or tools.
• When well designed, they provide pleasing aesthetics.
• They are highly resistant to fire.
• Not susceptible to insects or rodents.
• Inert—contains no toxic substances—therefore require no toxic treatments and do not off-gas hazardous fumes, thus are good for chemically sensitive individuals.
Earthen flooring, also called adobe floor, varies in its construction but is generally durable, inexpensive, an ecologically sustainable solution, and uniquely aesthetic complement to a home or office. Since “dirt” is abundantly plentiful and indigenous, earthen flooring can save money and virtually eliminates the waste, pollution, and energy necessary to manufacture a floor. The use of earth floors in the United States are still most often confined to outbuildings and sheds, but, if properly installed, can also be used in interior spaces (Fig. 6.4). For interior use, earth floors must be properly insulated, moisture sealed, and protected from capillary action of water by sealing with a watertight membrane underlayment. Oftentimes, an earthen floor may be constructed of two or three layers. A typical earthen floor might include 70% sand and 30% clay, with lots of chopped straw for much needed tensile strength.
Prior to proceeding with construction, the removal of any vegetation under the floor area is needed, followed by ramming of the area. The ground must be dry before installation of the floor. After the surface is moisture proofed, a foundation of stone, gravel, or sand is installed, 8–10 inches (20–25 cm) deep. An insulating layer such as a straw-clay mixture is then installed. The key to a good earthen floor is the proper mixture of dirt, clay, and straw. Stabilizers such as starch paste, casein, glues, or Portland cement are sometimes added to obtain a harder floor. Earthen floors are first troweled to a smooth finish and then usually sealed with an oxidizing oil such as linseed or hemp oil, which hardens it. Sweep or vacuum any loose debris and dust, as well as possible light mopping or sponging. Time should be given for the moisture to dry before applying the oil.
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Figure 6.4 Illustration showing the method for installing an earth floor. Source: Brian “Ziggy” Liloia, “Building My Cob House” blog.
Considerations and attributes of earthen-floor installation include:
• Earthen material is generally inexpensive when found locally.
• Construction waste elimination; any excess earth can be reincorporated into the landscape.
• Earthen materials are easy to process and require little or no transport and therefore produce minimal to zero pollution. Even when produced by a machine, a finished earthen slab is estimated to have 90% lower embodied energy than finished concrete.
• Earthen floors are durable with proper maintenance and repairable and when properly sealed can be swept or moist mopped; stabilized earthen flooring is not dusty.
• It is labor intensive to install. Not a problem in developing countries where labor is very cheap.
• In high-traffic areas such as entries or workspaces, flagstones or other protective materials may be required.
• More durable than vinyl because it is repairable but more vulnerable to scratching and gouging than hard tile or cement.
• Few contractors in the United States are experienced in the installation of earthen flooring.

6.2.5. Windows

Windows are vital elements in construction because they provide ventilation, natural light, views, and a connection to the outside world in addition to significantly improving the health, comfort, and productivity of a building’s occupants. Drafty, inefficient, poorly insulated, or simply poorly chosen windows can present a major source of unwanted heat loss, discomfort, and condensation and thus compromise the energy efficiency of a building’s envelope. Window manufacture whether made of aluminum, plastic, steel, or wood will require energy and will likely generate air pollution. Energy efficiency is one of the main considerations in reducing the environmental impacts of a window, followed by waste generated in manufacturing and general durability. However, these negative aspects have largely been addressed by modern technology. Fig. 6.5 shows the various components of a window. According to Gregg D. Ander, FAIA, “In recent years, windows have undergone a technological revolution. High-performance, energy-efficient window and glazing systems are now available that can dramatically cut energy consumption and pollution sources: they have lower heat loss, less air leakage, and warmer window surfaces that improve comfort and minimize condensation. These high-performance windows feature double or triple glazing, specialized transparent coatings, insulating gas sandwiched between panes, and improved frames. All of these features reduce heat transfer, thereby cutting the energy lost through windows.”
Windows come in a variety of glazing options. Each option offers a different thermal resistance or R-value. R-Values are a thermal resistance measure that is used in the building industry. A high R-value indicates that the window has a greater resistance to heat flow and a higher insulating value than a window with a low R-value. It should be noted that R-values are approximate and vary with temperature, type of coating, type of glass, and distance between glazings. R-value is the inverse value of the U-factor (R = 1/U) and is expressed in units of hr-sq ft-°F/Btu. U-value gives you the rate of heat flow due to conduction, convection, and radiation through a window resulting from a temperature difference between the interior and exterior. The higher the U-factor, the more heat is transferred (lost) through the window. Below are typical examples of R-values from lowest to greatest resistance:
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Figure 6.5 Drawing of a window showing individual elements.
• Single glazing and acrylic single glazing are similar; R = 1.0.
• Single glazing with a storm window and double glazing are similar: R = 2.0.
• Double glazing with a low-E coating and triple glazing are similar: R = 3.0.
• Triple glazing with a low-E coating: R = 4.0.
It is interesting to note that for a conventional insulated stud wall R = 14.0.
Residential window frames are typically made from aluminum, wood, vinyl, or fiberglass, or combinations of wood and aluminum or vinyl (i.e., “clad”). Older, single-pane windows rarely perform as well as new windows and should preferably be reused only in unheated structures such as greenhouses or barns. Each material has a different cost, insulating ability, and durability, as shown below:
• Wood is a natural material that requires continuous maintenance (stain or paint) for durability. Likewise, the wood source should be certified by an accredited organization such as the FSC.
• Fiberglass is energy intensive to manufacture but is strong and durable and has excellent insulation value.
• Aluminum and steel are poor insulators and very energy intensive to manufacture. Also, over time, aluminum will oxidize leaving a dull pitted appearance. When using metal-framed windows, look for recycled content and frames insulated with “thermal breaks” to limit the loss of heat to the exterior.
• Vinyl is a product of the plastics industry, offers good insulation but is highly toxic in its manufacture and if burned. Vinyl windows are usually nonpaintable but do offer a lifetime free maintenance. High-efficiency windows typically utilize dual or triple panes with low-E (low emissivity) coatings and gas fill (typically argon) between panes to help control heat gain and loss. Factory-applied low-E coatings on internal glass surfaces are more durable and effective than films. High-quality, efficient windows are widely available from local retailers. To make an informed choice, consider only windows that have National Fenestration Rating Council (NFRC) ratings (see sidebar). The EPA ENERGY STAR label for windows can be a useful summary of these factors.

Factors That Can Impact the Full Frame R-Value of a Window

• Type of glazing material used (e.g., glass, transparent coatings, suspended film, treated glass, single, double or triple glazing).
• The number of air chambers created by multiple layers of suspended film or glass panes.
• Type of gas (e.g., argon), if any, is used to fill the air space(s).
• Air and water “tightness” of the window can significantly affect a window’s performance.
• The thermal resistance and attributes of the frame and spacer materials affect a window’s performance.
The NFRC is a nonprofit, public/private organization created by the window, door, and skylight industry and is composed of manufacturers, suppliers, researchers, architects and designers, code officials, utilities, and government agencies. The NFRC has developed a window energy rating system based on whole product performance and provides performance ratings in five categories. They are:
• The U-factor is a measure of a window’s ability to keep heat inside or outside a building. U-factor values generally range from 0.25 to 1.25 and are measured in Btu/h·ft2·°F. The lower the U-factor, the better the window insulates. Values of 0.4 or lower are recommended.
• The solar heat-gain coefficient (SHGC) summarizes a window’s capability to block heat caused by sunlight. SHGC is measured on a scale of 0–1; values typically range from 0.25 to 0.80. The lower the SHGC, the less solar heat the window transmits. SHGC values of less than 0.4 are preferable.
• Visible-light transmittance (VLT) measures the amount of light the window lets through a window. Desired VLT varies with taste and application. VLT is measured on a scale of 0–1; values generally range from 0.20 to 0.80. The higher the VLT, the more light you can see.
• Condensation Resistance measures how well the window resists water buildup. It is scored on a scale from 0 to 100. The higher the condensation resistance, the better. Condensation can contribute to mold growth, although new, high-quality windows (with a low U-factor) are generally better equipped to resist condensation than older windows.
• Air Leakage (AL) measures the rate at which air passes through joints in the window. AL is measured in cubic feet of air passing through one square foot of window area per minute. The lower the AL value, the less AL. Most industry standards and building codes require an AL of 0.3 cf·m/ft2.

6.2.6. Miscellaneous Building Elements

Gypsum Wall Board (Drywall)

Gypsum board is the most common indoor building material in the United States. In the United States and Canada, gypsum board is manufactured to comply with ASTM Specification C 1396 which was designed to replace several existing ASTM specifications, leaving one reference standard for all gypsum board products. This standard is to be applied whether the core consists of natural ore or synthetic gypsum.
Gypsum wall board, also known as drywall, or plasterboard is a plaster-based wall finish that is available in a variety of standard sizes; 4 ft wide by 8 ft high is the most common. Thicknesses vary in 1/8-inch increments from 1/4 to 3/4 inch. Gypsum wall board, which is also known by its proprietary names Drywall and Sheetrock, is ubiquitous in construction. Gypsum wall board is a benign substance (basically paper-covered calcium sulfate), but it has significant environmental impacts because it is used on a vast scale; domestic construction uses an estimated 30 billion square feet per year. Advantages of gypsum board include its low cost, ease of installation and finishing, fire resistance, nontoxicity, sound attenuation, and availability. Disadvantages include: difficulty in curved-surface application and low durability when subject to damage from impact or abrasion.
Gypsum board manufacturers are increasingly relying on “synthetic” gypsum as an effective alternative to natural gypsum. It is estimated that roughly 45% of the gypsum used by U.S. manufacturers in 2010 was of the synthetic variety. Synthetic gypsum and natural gypsum have similar general chemical compositions (CaSO4·2H20). The vast majority of the synthetic gypsum used by the industry is a by-product of the process used to remove pollutants from the exhaust created by the burning of fossil fuels for power generation. If synthetic gypsum was not used to manufacture gypsum panel products, it would end up in landfills.
Though synthetic gypsum-board use is growing in popularity, and reclaimed gypsum board can easily be recycled into new gypsum panels that conform to the same quality standards as natural and synthetic gypsum, doing this may not be practical because gypsum is an inexpensive material which can require significant labor to separate and prepare for recycling. Gypsum-board face paper is nearly 100% recycled from newsprint, cardboard, and other postconsumer waste streams, but most recycled gypsum in wall-board products is postindustrial, made from gypsum-board manufacture.
Ecology Action, a nonprofit environmental consultancy states that the main environmental impacts of gypsum include habitat disruption from mining, energy use and associated emissions in processing and shipment, in addition to solid waste from disposal. Some of these impacts can be significantly reduced by the use of “synthetic” or recycled gypsum board. Synthetic gypsum, which is now used in about 30% of drywall, is a by-product of coal-fired power plants. It is sometimes confused with fly ash another coal combustion product with which it has very little in common. In excess of 80% of coal fly ash sold in the United States is used in gypsum board.
New technologies have helped in the development of several new Gypsum board products that have come on the market and that are more environmentally friendly and superior in many ways to the traditional gypsum board. One such example is the new ecofriendly EcoRock Drywall which has significantly changed and improved the drywall product from its basic material elements to its production processing methods. EcoRock is a fully recyclable and highly attractive alternative. It is manufactured from 80% postindustrial recycling and exploits material from steel and cement plant waste and can be safely discarded in landfills. EcoRock is naturally cured and dried, which means that 80% less energy is required than the traditional methods use in the manufacturing process. Moreover, it contains no gypsum, thus eliminating the need for high-intense energy consumption during production and improves air quality by eliminating airborne mercury. EcoRock drywall, which creates 60% less dust, is resistant to termites and is 50% more resistant to mildew and mold.

Siding

Siding is the external covering or cladding applied to the outermost surface of an exterior wall with the main function of providing protection from adverse effects of extreme weather, moisture and excess water, the heat and ultraviolet radiation of the sun. There are many types of siding materials that one can choose from, such as plastic (vinyl) siding, fiber cement siding, wood siding, composite siding, metal siding, and masonry siding to name but a few. Selecting siding that is reclaimed, recyclable, or incorporating recycled material will reduce waste and pollution. However, the environmental impact of a siding product will vary considerably according to the material it is made from.
Siding may be formed of horizontal boards or vertical boards (also known as weatherboarding in some countries), shingles, or sheet materials. In all these cases, avoiding wind and rain infiltration through the joints is a real challenge that is met by overlapping, by covering or sealing the joint, or alternatively by creating an interlocking joint (such as a tongue-and-groove or rabbet). Creating rigid joints between the siding elements is not practical because materials will contract or expand according to the changing temperature and humidity. Moreover, siding may be attached directly to the building structure (studs in the case of wood construction) or to an intermediate layer of horizontal planks called sheathing. There are many types of siding including:
Vinyl siding is made from a PVC plastic and is very widely used. Unlike wood or cedar, it would not rot or flake. Vinyl siding has grown in popularity because it requires little maintenance and is generally less costly to purchase and install than most other siding materials. The main drawbacks of vinyl are that it cracks, fades, and grows dingy over time. It is also controversial because of environmental concerns.
Earth or lime plasters may last a long time and do not require much maintenance. Cement or lime is commonly added to improve its hardening and durability attributes, but the relatively low (or zero) overall cement content of natural plasters means that the material requires relatively small amounts of pollution and energy use to prepare and install. Deep eaves or overhangs are often needed to protect the siding from extended moisture exposure and which are critical to the extending the natural plaster’s useful life.
Fiber cement siding has proven to be extremely durable, in addition to many products being backed by 50-year or lifetime warranties. The siding is made from cement, sand, and cellulose fiber. In addition to its improved ecofriendliness, fiber cement siding also comes with a lower price tag than other materials. Moreover, it is fire resistant and pest resistant and emits no pollutants in use. However, it does possess a high embodied energy due to its cement content.
Quality cement stucco is another alternative material that can be extremely durable, which helps minimize long-term waste, but it is also energy intensive to manufacture. Cement substitutes such as fly ash or rice-hull ash can mitigate the environmental cost of stuccos.
Metal siding comes in a variety of metals, styles, and colors. It is very durable and recyclable and typically contains significant postconsumer recycled content. It is generally energy intensive to manufacture, although recycled steel and aluminum require far less energy than virgin ore. Metal siding is most often associated with modern, industrial, and retro buildings. Utilitarian buildings often use corrugated galvanized steel sheet siding or cladding, and corrugated aluminum cladding is common where a more durable finish is required.
Composite siding such as hardboard is made of newspaper or wood fiber mixed with recycled plastic or binding agents. It is highly durable and generally resists moisture and decay. It also often has significant recycled content and is not prone to warping or cracking like wood. Composites generally do not require frequent repainting, and some need not be painted at all, saving waste and valuable resources.
Wood siding is one of the oldest types of siding and is popular in old and historic homes. Wood siding’s main disadvantage is that it requires more maintenance (polishing and painting) than many of the other siding options. If it is not well maintained, wood can easily be the least durable option, generating significant waste. Wood siding is also more vulnerable to warping, splitting, and damage by insects and termites. Among its positive attributes is that it is renewable and requires relatively little energy to harvest and process. Wood siding can also be made of unpainted weather-resistant woods such as redwood.
As with most green products, selecting the most appropriate green siding is often a matter of weighing trade-offs in longevity, biodegradability, insulation, maintenance, and, sometimes, cost. Final selection will also depend largely on your objectives and requiring you to prioritize which attributes will best meet these objectives. Such considerations should include:
• Selecting the most durable siding product that is appropriate. Siding failures that allow water into the wall cavity can lead to expensive repairs, the waste of damaged components, and the environmental costs of replacement materials. Fire resistance is a feature that helps reduce the financial and environmental impact of rebuilding, particularly in high-risk areas.
• For existing buildings, consideration should be given to refinishing existing siding to minimize waste, pollution, and energy use.
• Preference should be given to selecting materials that are biodegradable, have recycled content, and/or are recyclable.
• Reclaimed or remilled wood siding should be used to reduce demand for virgin wood and waste. Painted wood should be tested for lead contamination prior to use.
• New wood siding should display an FSC-certified label.
• Although vinyl is durable, it is not considered a green building material. Attributed disadvantages include pollution generated in manufacturing, air emissions, human health hazards of manufacturing and installation, the release of dioxin and other toxic persistent organic pollutants in the event of fire, and the difficulty in recycling it.

6.2.7. Roofing

A roof system’s primary function is to protect against and manage the weather elements, particularly precipitation, thereby protecting the interior and structural components of a structure from deterioration. There are two basic types of roof construction, sloped or pitched and flat. Sloped roofs are generally covered with individual pieces of overlapped shingling material to prevent water penetration. Flat roofs are basically watertight membranes that should have just enough of a slope to allow water to run off. Flat roofs are more popular in hot arid climates, particularly in developing countries where they are used in the evenings for sleeping, etc. In the United States and Europe, however, flat or low-slope roofs are typically selected when the roof is expected to accommodate rooftop equipment.
The most critical characteristics of roofing materials are moisture/water resistance, dependability, and durability. The development of new materials and processes are needed to minimize creation of new health or environmental safety problems. The transporting and processing of the materials are coming under increasingly strict regulation to protect the health of workers involved in production and distribution. Roofing material extraction, manufacture, transport, and disposal pollute air and water, deplete resources, and damage natural habitats. Roofing materials comprise an estimated 12–15% of C & D waste.
For a roof to be environmentally sustainable, it must be durable and long lasting and ideally also contain recycled or low-impact materials. Roofs that are environmentally friendly can provide several advantages such as aesthetically pleasing design options, reduced life-cycle costs (LCCs), and environmental benefits such as reduced landfill waste, energy use, and impacts from harvesting or mining of virgin materials. It takes roughly the same materials, energy, and labor to manufacture and install a 50-year-warranted roof as a 30-year roof, yet the first option is “greener” because disposal and the roof’s lifetime cycles are extended, thereby providing a better investment. Moreover, a properly installed 50+ rated roof can reduce roofing waste by 80–90% over its lifetime, relative to a roof with a warranty of only 20 years.
Normally, mild climates are better suited for passive temperature controls that reduce winter heating and reduce or eliminate the need for mechanical cooling. The need for air conditioning is generally less in mild climates because operable windows and skylights are often employed that can easily provide ventilation and cooling, particularly in smaller buildings. But even larger commercial buildings can be cooled effectively in mild climates without the use of air conditioning providing care is taken in the initial design, and the design of the roofing structure minimizes heat gain. And although cool roofing does not renew resources, it is often a highly cost-effective way to conserve them. Likewise, electricity from solar photovoltaic panels reduces demand for fossil fuels and is therefore environmentally friendly.

Choosing Roofing Materials

Choosing the right roofing materials requires taking into consideration numerous factors, including climate and weather conditions in the project area, the roof’s lifespan expectancy, budget, aesthetic preferences, and various sustainability factors. Some primary considerations that could impact the type of roof to be chosen include:
• Roof’s ability to resist heat flow from the roof into the interior, whether through insulation, radiant barriers (highly reflective material that inhibits heat transfer by thermal radiation), or both.
• Roof’s capacity to reflect sunlight and reemit surface heat. Cool roofs can reduce cooling loads and urban heat-island effects while extending roof life.
• Roof’s ability to reduce ambient roof air temperatures through evaporation and shading, as in the case of vegetated green roofs.
• Roof’s recyclability and/or capability of being reusable at the end of its useful life to minimize waste, pollution, and resource use. Roofs with high postconsumer recycled content (up to 30%) are preferable.
• Look for nonhalogenated fire-retardant roofing membranes (i.e., materials that do not contain bromine or chlorine) that meet fire code requirements. Burning of PVC and thermoplastic olefin (TPO) produces strong acids and persistent toxic organic pollution, such as dioxin.
For local fire codes compliance, the roof may require protective ballast such as concrete tile. Existing PVC and TPO roofing membranes, as well as underlying polystyrene (PS) insulation, are increasingly being recycled as federal construction-specification requirements generate increased demand in the industry. The following are some of the roofing options for residential and commercial applications:
• Clay or cement tiles are very durable and made from abundant materials, but they are heavy and expensive. Ensure that structure can take additional weight.
• Recycled plastic, rubber, or wood composite shingles are generally durable, lightweight, and sometimes recyclable but they are not biodegradable.
• Composition shingles are very popular and typically have a lifetime of 15–30 years although some manufacturers offer up to 50-year warranties. The composition shingle has a fiberglass mat core which gives the shingle flexibility and provides some fire resistance. The exterior of the composition shingle has a weather-resistant asphalt coating embedded with crushed rock. Composition shingle roofs can be recycled but are susceptible to algae growth unless an antialgae coating is applied.
• Fiber cement is durable and fire- and insect proof but is heavy and not renewable or biodegradable but may be used as inert fill at demolition.
• Metal (e.g., aluminum, steel) is a durable, fire- and insect proof recyclable material. It typically contains recycled content, but manufacture is generally energy intensive and causes pollution and habitat destruction.
• Built-up roofs are said to have a track record exceeding 150 years, but their durability depends largely on the structure, installation, flashing, and membrane chosen. Also, most membranes are not made from renewable resources, although some may contain recycled content. Although built-up roofs are highly reliable, their market share has declined significantly over recent decades mainly due to the increasing cost of tar. Of note, high-VOC products emit air pollution during installation.
• Vegetated green roofs are most commonly installed on low-pitched roofs (at least one inch of rise for every foot of run, to facilitate drainage). Green roofs help reduce the negative aspects of conventional roofing, while adding green space to the property.
• Wood shakes have a rustic appearance and are biodegradable, but they are also flammable and not very durable. Wood shakes are not typically considered to be a “green” option for areas that are fire prone.
New technologies continue to emerge that encourage the promotion of sustainability/green building and green roofs, because green roofs offer many economic, social, and environmental benefits. Today we are witnessing increasing efforts to make usable space on existing rooftops and/or new roofs to allow additional living space (Fig. 6.6). Green or “living” roofing which involves the use of vegetation as the weathering surface has proved very successful because it helps reduce extremes in rooftop temperature that shorten the life of a roof (leading to increased C & D waste), conserves energy, and extends the useful life of the roof. An important factor in creating these spaces is the need to use lightweight and recycled materials and to help with managing storm water run-off because traditional drainage systems using pipe and stone are not plausible. Green roof systems are a natural and cost-effective way of providing additional clean air through the transference of CO2 and oxygen between the plants and vegetation and the atmosphere, thereby helping to control urban air pollution.
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Figure 6.6 Example of a 70,000-square-foot vegetated roof on the LDS Assembly Hall building, Salt Lake City, UT. Source: American Hydrotech, Inc.
The main reasons that Green roofing has proven to be effective is that the large surface area of soil and plants helps to reradiate heat; it also provides shade and insulation for the waterproof roof membrane, while the plants’ transpiration provides cooling. The net result of this is a 25- to 80-degree decrease in peak roof temperature and a much reduced cooling-energy demand (up to 75%). Cooler roof temperatures will also reduce the urban heat-island effect and thus help reduce the cooling load for surrounding buildings.
In addition to the environmental benefits, green roofs provide aesthetic and cost benefits (as well as benefiting local property values). The soil and vegetation in many common designs can retain up to 75% of a one-inch rainfall and will filter the remainder. This on-site storm-water management helps reduce demand on storm-water infrastructure, saving resources and money for the entire community. To help address this issue, New York City property owners are assessed a tax based on the volume of storm water runoff, whereas, they are offered a tax reduction if the building has a green roof. Green roofs can often facilitate urban wildlife microhabitat. Although not a replacement for wild land, a vegetated roof can accommodate birds, beneficial insects, and native plants far better than tar and gravel. Contemporary green-roof designs generally contain a mixture of hard and soft landscaping. It is very important therefore that the selected drainage/retention layer is capable of supporting any type of landscape from roadways and paths to soil and trees so as to permit excess water to drain unobstructed underneath as shown in Fig. 6.7a–c.
Green roof systems generally contain certain essential layers and components to be viable. The main layers generally consist of: vegetation; soil; filter and a waterproofing membrane; root barrier; drainage and irrigation system; roof membrane; and sometimes an insulation layer. AWD, a leader in roof garden and prefabricated drainage systems, notes that the main components, materials, and locations to take into consideration when contemplating the installation of a green or vegetated roof are:
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Figure 6.7 (a) Rendering showing commercial application of green elements. (b) Drawing showing two types of roofing systems: sand and gravel system and the Amergreen roofing system. (c) Drawing of a Quad-lock roofing system detail. (a, b) Source: American Wick Drain Corporation; (c) Source: Quad-lock Insulating Concrete Forms.
• Structural support: Roof and roof garden systems are required to have an underlying structural system in place to support additional weights resulting from use of normal building materials such as concrete, wood, etc. The structural engineer needs to consider the load of the roof-garden system in the initial design phase.
• Roofing membrane: The design engineer has a number of roofing membrane options available at his/her disposal. The final membrane choice may be decided by several factors such as loads imposed by the rooftop garden, by available membrane protection elements in the rooftop-garden system, by root penetration properties of the membrane, and by membrane drainage and aeration requirements.
• Membrane protection: The roofing membrane may require protection from installation damage, long-term water exposure, UV exposure, drainage-medium loads, chemical properties, or growing-medium loads.
• Root barrier: A root barrier filter fabric may be required between the growing medium and the lower components to allow excess water in the growing medium to drain while preventing small particles in the growing medium from moving into drain core. It may also be needed to eliminate or mitigate potential root penetration into the roofing membrane, drainage medium, or water-storage medium. The optimum location is above the membrane, drainage medium, and water-storage medium so that all three components are protected. Alternate locations may require multiple roof-guard elements to avoid long-term root penetration. While some systems have the root barrier placed under the drainage layer, AMERGREEN, for example, who specialize in green roofs, states that it designs the root barrier “at the most effective location for system performance-above the drainage layer and in direct contact with the soil medium”. Some roofs do not incorporate a specific insulation layer unless a higher insulation is required. Insulation (usually based on a rigid synthetic board foam) may be installed above the structural support, depending on the thermal design of the structure. Insulation may also be installed above or below the roofing membrane whichever proves more effective.
• Drainage medium: An appropriate drainage medium is required to ensure the proper range of water content in the growing medium. An excess of water can have an adverse effect and cause root rot. Insufficient water can result in poor vegetation growth. There are various drainage-medium options ranging from gravel to materials designed specifically for this purpose. Plastic materials usually combine the drainage function with water storage and aeration in addition to protecting the membrane from roots and potentially damaging materials in the growing medium.
• Aeration: It is a vital element to promote optimal vegetation growth. The aeration medium usually serves as both drainage and aeration medium. The open channels incorporated in the prefabricated drain core are designed to provide necessary air to the plant roots.
• Growing medium: There are a number of natural and manufactured materials that may be used as a growing medium. Soil is often mixed with other materials to reduce weight, to provide better structure for roots, as well as to provide essential nutrients, oxygen, and water.
• Water storage: While the growing medium will store a certain quantity of water, additional water storage may be required to provide more efficient growth of vegetation. Most prefabricated plastic roof-garden products have water-storage capability. The plastic cones of the prefabricated core provide positive water-storage reservoirs. Likewise, sand and gravel may hold a certain amount of water.
• Vegetation: This provides the upper and most visible layer of the roof-garden system. There is a wide variety of typical landscaping and garden plants that may be employed for a rooftop garden. An experienced landscape architect should preferably be involved in plant selection to ensure that the vegetation chosen is appropriate both for the geographic region and for a rooftop-garden environment. Moreover, careful consideration should be given to the type of vegetation chosen as this will inevitably affect the selection of other components of the roof-garden system such as root protection, water and aeration needs, and drainage requirements—all of which are affected by plant selection.

Extensive and Intensive Green Roofs

There are basically two primary categories of green roofs—extensive or intensive—although a green roof is frequently designed to contain features of both and are then referred to as a semiextensive or semiintensive green roof (sometimes spelled greenroof). The roof’s function or objective of the roof space usually determines the final design—e.g., whether it is intended as an ecological cover or whether it is intended for human recreation, vegetable gardening, etc.
Extensive green roofs (sometimes called ecoroofs or low-profile roofs) typically contain a layer of soil medium that is relatively thin (two to six inches) and lightweight (weighs 10 to 50 pounds per square foot for the entire system when fully saturated with water). They are lightweight, relatively easy to install, durable, require very low maintenance, and cost effective. Extensive green roofs are usually built when the main goal is for an ecological roof cover with limited human access. Ideal plants for this type of roof are low growing, horizontally spreading root ground covers, having a general maximum plant height of 16–24 inches. Alpine-type plants are typically successful because they have the necessary attributes for green roofs including high drought, wind, frost, and heat tolerance. Appropriate plants include sedums and other succulents, flowering herbs, and certain types of grass.
Intensive green roofs (sometimes called high profile) often look like traditional roof gardens because they are designed to accommodate trees and gardens. Soil can be as deep as needed to accommodate the desired tree or plant species, but deeper, denser soil dramatically increases dead load, requiring a stronger and more expensive structure, greater maintenance, and either terracing or a relatively flat roof. The engineered soil media for an intensive green roof usually contains about 45–50% organic material to 50—55% mineral material and when fully saturated with water, weighs between about 80 and 120 lbs/sq. ft. or more. The inclusion of architectural and decorative elements such as waterfalls, ponds, gazebos, etc. are possible, and these green roofs provide recreation spaces and encourage interaction between nature and a building’s occupants. It should be noted that there are green-roof options available for almost any building type or location. Among the many benefits attributed to green roofs include:
• They provide greater insulation and more moderate rooftop temperatures, which reduce cooling and heating requirements, saving energy and money. Research by the National Research Council of Canada found that extensive green roofs reduced the daily energy demand for air conditioning in the summer by over 75% (Liu, 2003).
• They are considered a best practice because they facilitate filtration and detention of storm water, reducing pollution and the cost of new and expanded infrastructure as paved areas increase. Green roofs can reduce the amount of storm water runoff volume to sewer systems by 50–90% and peak storm water runoff flow by 75–90% resulting in decreased stress on sewer systems at peak flow periods. By comparison, a typical roof will retain 10% of storm water runoff.
• They naturally absorb dust and filter harmful particulates and airborne pollutants. They also have superior noise attenuation, especially for low-frequency sounds. An extensive green roof, for example, can reduce sound from outside by 40 decibels, while an intensive one can reduce sound by 46–50 decibels (Peck et al., 1999).
• They are an effective fire retardant. Green roofs generally have a much lower burning heat load (the heat generated when a substance burns) than do conventional roofs.
• They reduce ambient air temperatures, lowering urban heat-island effects and helping to enhance microclimate of surrounding areas, because one of plants’ natural functions is to cool the air through the release of water through plants into the atmosphere.
• They extend the life of roof membranes, by decreasing exposure to large temperature fluctuations that can cause microtearing and protect the roof from ultraviolet radiation, extreme temperatures, and mechanical damage. Plant species, soil depth, and root-resistant layers are carefully matched to ensure that the roof membrane is not damaged by the roots themselves.
• Lightweight extensive systems can be designed with dead loads comparable to standard low-slope roofing ballast. Structural reinforcement may not be necessary, and cost can be comparable to conventional high-quality roofing options.
• Can increase a building’s marketability, resulting in higher rents and increased resale value. A recent study by UMass Boston estimates that green roofs can increase a property’s value by an average of 15%. Green roofs can also facilitate employee recruiting and decreases employee and tenant turnover.
• The can transform rooftop eyesores into attractive assets.

6.2.8. Wood

There are thousands of species of wood, which can probably best be separated into two broad categories: hardwoods and softwoods.

Wood Types

The distinction between hardwood and softwood is botanical, rather than referring to the strength or hardness of the wood. “Hardwood” is a term generally applied to trees that lose their leaves in winter, whereas “Softwood” generally describes evergreens such as pine and redwood. It should be noted that hardwoods are not necessarily hard and softwoods are not necessarily soft (e.g., balsa is a hardwood, and white cypress is very strong softwood). The different types of wood have a multitude of uses and in many cases are interchangeable.
Pressure-treated lumber such as chromated copper arsenate (CCA) pressure treated wood has been popular over the decades partially due to its resistance to rotting, insects, and microbial agents. Existing CCA-treated lumber, however, poses a challenge because arsenic is acutely toxic and carcinogenic and was shown to be leaching into surrounding soils; this prompted it being largely phased out in a cooperative effort between manufacturers and the EPA (effective December 31, 2003). CCA is a chemical wood preservative containing chromium, copper and arsenic. CCA has been classified by the EPA as a restricted use product, i.e., for use only by certified pesticide applicators.
Reuse of CCA pressure treated wood would help conserve forest resources and keep a potentially useful resource out of landfills. Still, permitting its reuse would allow CCA to continue to leach arsenic into soils. CCA-treated wood should not be composted or disposed of in green-waste or wood-waste bins. CCA-treated wood is now mandated to be disposed of in a lined landfill or as class I hazardous waste. The burning of CCA-treated wood is highly toxic. Newer alternative wood treatments which are less toxic, such as copper azole (CA) and alkaline copper quaternary (ACQ), are more corrosive than CCA. To address this, and to minimize rust and prevent staining, manufacturer-recommended fasteners should be employed. The following points should be considered when working with wood products:
• Reuse wood in good condition.
• Repair and/or refinish existing decks, railing, or fencing with nontoxic materials.
• Build with durable materials such as plastic lumber. The composition of plastic lumber varies widely, from 100% postconsumer recycled content to 100% virgin plastic resin.
• The majority of plastic lumber products currently on the market are made from polyethylene although some manufacturers are also employing PS and PVC. In addition, there are some plastic lumber products that rely on a commingled mix of different types of plastics, collected mainly from municipal recycling programs.
• If the structural elements will be in contact with soil and water, consider:
Heartwood (the dense inner part of a tree trunk), yielding the hardest timber from decay-resistant species such as redwood or cedar that has been FSC-certified as harvested from a responsibly managed forest.
When the use of pressure-treated lumber is required, the two water-resistant preservatives currently employed are CA and ACQ, which are significantly less toxic than CCA.
Remaining stocks of CCA should be avoided.
• For fencing, consider ecofriendly alternatives such as a living fence of bushes, shrubs, or live bamboo in urban settings or fencing made of a rapidly renewable material such as cut bamboo.
As wood is a renewable material, it requires less energy than the majority of other materials to process into finished products, as opposed to the significant negative environmental impacts caused by the logging, manufacture, transport, and disposal of wood products. Standard logging practices are known to cause erosion, pollute streams and waterways with sediments, damage sensitive ecosystems, reduce biodiversity, and lead to a loss of soil carbon. These impacts can be reduced by the minimization of wood use through the substitution of suitable alternatives, e.g., reusing salvaged wood, selecting wood from responsibly managed forests, controlling waste, and minimizing redundant components. Where salvaged or reclaimed wood is unavailable or not applicable (e.g., for structural applications), specify products that are certified by an approved and accredited organization such as the FSC.
Engineered lumber (also known as composite wood or man-made wood), consists of a range of derivative wood products that are manufactured by pressing or laminating together the strands, particles, fibers, or veneers of wood with a binding agent to produce a range of different types of building products such as structural framing lumber and trim material. Engineered wood is normally straighter, more stable, and structurally consistent than dimensional lumber. Its superior strength and durability allows it to displace the use of large (and increasingly unavailable), mature timber. In joist and rafter applications, the reconstituted products have proven to be particularly useful because of their ability to span long distances with less sagging than similarly sized conventional lumber. Engineered lumber is also less susceptible to humidity-induced warping than equivalent solid woods, although the majority of particle-based and fiber-based boards require treatment with an appropriate sealant or paint to prevent possible water penetration.
There are numerous applications for engineered products. Generally, they are products that are engineered to meet precise application-specific design specifications and are tested to meet national or international standards. Employing engineered lumber instead of large-dimension rafters, joists, trusses, and posts can save money and reduce total wood use by up to 35%. Engineered lumber also allows for wider spacing of members, which in turn allows for increasing the insulated portion of walls. Other advantages include its ability to form large panels from fibers taken from small-diameter trees, small pieces of wood, and wood that has defects; these panels can be used in many engineered-wood products, especially particle-based and fiber-based boards. Engineered-wood products are used in a number of ways, usually in applications similar to solid wood products, but many builders prefer engineered products because they are economical and typically longer, stronger, straighter, more durable, and lighter than comparable solid lumber.
Engineered-wood products also have several disadvantages in comparison to dimensional lumber; for example, they require more primary energy for their manufacture than solid lumber. They are also less fire resistant and have adhesives that can potentially release toxins into the environment, as well as being prone to moisture damage. An expressed concern with some resins is the release of formaldehyde in the finished product, often seen with urea-formaldehyde-bonded products. Working with engineered wood products can therefore potentially expose workers to toxic constituents that could cause harm. The applications of engineered wood products are varied and include being used as columns, beams, joists, girders, rafters, studs, and bracing. Although engineered wood is generally more expensive than dimensional lumber, the cost can be offset to some degree by labor savings and improved quality of the product.
Wood adhesives have been important in helping use timber resources efficiently. The main function of an adhesive is to bond wood components such as veneer, particles, strands, and fibers, etc. Moreover, an adhesive must provide the necessary strength immediately following manufacture as well as after long-term use. Prior to the introduction of synthetic adhesives in the 1930s, the adhesives used for bonding wood were generally made from natural polymers found in plants and animals.
Today, natural adhesives continue to being used (but to a much lesser extent) in some nonstructural products; they do not provide the necessary strength and durability required for many of today’s engineered wood products. To address the needs of contemporary engineered wood products, polymer scientists have developed various types of synthetic adhesives that are designed to perform a variety of functions in product applications. These man-made polymers resemble natural resins in physical characteristics, but they can be tailored to meet specific woodworking requirements. The choice of an adhesive is determined by several factors; these include cost, structural performance, moisture resistance, fire performance, adhesive curing needs, etc. Generally, there are two primary categories of adhesives currently employed in engineered wood; the first category is for structural products, and the second is for interior nonstructural products. This first group of resins includes:
• Phenolic (also called phenol formaldehyde or PF), which has a yellow/brown or dark reddish color and is available as liquid and powder or in film form. It is commonly used for exterior exposure products and used to produce softwood plywood for severe service conditions.
• Resorcinol, which is purple in color and waterproof/boil proof, is typically used for structural wood beams.
• Melamine-formaldehyde resin, which is white in color, heat- and water-resistant, and preferred for exposed surfaces in more costly designs. Its use is limited to a few special applications such as marine plywood where the need for a light-colored water-resistant adhesive justifies its cost.
• Methylene diphenyl diisocyanate (MDI) which is an aromatic diisocyanate, although not benign, is the least hazardous of the commonly available isocyanates. It is generally expensive, waterproof, and does not contain formaldehyde.
• Polyurethane (PU) resin, which MDI is also generally expensive, waterproof, and does not contain formaldehyde. It is used largely in the sphere of coatings and adhesives because of its high reactivity, high flexibility in formulation and application technologies, adhesion and mechanical properties, and resistance to adverse weather.
Typical examples of structural products include OSB, plywood, end-jointed lumber, glued laminated timber (glulam), I-joists, and structural composite lumber. The second group of adhesives includes adhesives formulated from materials of natural origin such as animal, vegetable, casein, and blood glues. They lack the temperature capabilities or environmental durability evidenced by structural adhesives. Nevertheless, they generally provide an instantaneous bond due to their pressure sensitive or hot melt characteristic. Nonstructural adhesives are generally used for interior applications, although many new products are also seeing exterior applications as well. Nonstructural adhesives also include adhesives such as urea formaldehyde resin (UF), which is widely used for the manufacture of interior grade plywood and also for the manufacture of particleboard. It is considered to be the most widely used thermosetting resin for wood, which although not waterproof, is, nevertheless, popular because it is inexpensive. Moreover, the low resistance to heat and moisture of these adhesives makes their use appropriate for indoor, nonstructural wood products.
Sheathing is the structural covering of plywood or oriented strand board (OSB) that is applied to studs and roof/floor joists to provide shear strength and serve as a base for finish flooring or a building’s weatherproof exterior. Sheathing is considered to be the second most wood-intensive element of wood-frame construction. Exterior Gypsum Sheathing comes in various sizes including a 1/2″ thick, 2′ wide with a tongue-and-groove edge or, 1/2″ & 5/8″ thick, 4′ wide square edge product. 5/8″ Exterior Gypsum Sheathing has a Type X core, for use in fire-rated assemblies. Engineered-wood sheathing materials do have some environmental tradeoffs because the wood fibers are typically bound with formaldehyde-based resins. Interior-grade plywood typically contains UF, which is less chemically stable than the PF found in water-resistant exterior-grade plywood and OSB. This advantage makes exterior-grade plywood preferable for indoor applications, as it emits less toxic and suspected carcinogenic compounds.
There are numerous alternatives to these wood-intensive conventional and engineered materials. For example, fiberboard products rated for structural applications (such as Homasote, a 100-percent-recycled nailable structural board) are considered alternatives to plywood and OSB. Structural-grade fiber-cement composite siding combines sheathing and cladding, providing shear strength and protection from the elements while reducing labor costs for installation. It is promoted as being ecofriendly because it requires fewer trees, would not burn, would not rot, extends the life of a paint job, and usually is warranted for 50 years.
This product is relatively new but has become increasingly popular since its introduction, in part because it can be manufactured to have the realistic appearance of wood, stucco, or masonry. Its main drawback, however, is that it is heavy to lift, and its installation requires specialized cutting tools. Water-resistant exterior-grade gypsum sheathing is one of the options that can be employed as an underlayment for various exterior siding materials such as wood, stucco, metal or vinyl siding, masonry veneer, etc., to reduce wood requirements. The panel is manufactured with a wax-treated, water-resistant core faced with water-repellent paper on the face and back surfaces as well as on the long edges. Structural insulated-panel construction provides interior and exterior sheathing as well as insulation in precut, factory-made panels. And by designing for disassembly, sheathing materials can be readily reused or recycled. Also, designs that combine bracing with nonstructural sheathing can provide necessary strength while increasing insulation and reducing wood requirements. Medium-density fiberboard (MDF) is an engineered composite wood product that is nonstructural and somewhat similar to particleboard. MDF is one of the most rapidly growing composite board products to enter the market in recent years. It typically consists of low-value wood by-products such as sawdust combined with a synthetic resin such as UF or other suitable bonding system and joined together under heat and pressure. Additives are often introduced during the manufacturing process to impart additional characteristics. MDF panels are therefore manufactured with a variety of physical properties and dimensions that allow the end product to be designed with the specific characteristics and density needed. MDF is widely employed in the manufacture of furniture, kitchen cabinets, laminate flooring, paneling, door parts, shelving, millwork, and moldings. Generally, it can provide an excellent substitute for solid wood in many applications, except when the stiffness of solid wood is needed.
MDF can be dangerous to use if the correct safety precautions are not taken. MDF contains UF, which may be released from the material through cutting, and sanding, and which may cause irritation to the eyes and lungs. It is necessary therefore to have proper ventilation when using it, and facemasks are needed when cutting or sanding MDF with machinery because the dust produced can be very dangerous. And although MDF is highly toxic to manufacture, it does not emit VOCs in use. MDF will accept a wide variety of sealers, primers, and coatings to produce a hard, durable tool surface, but it is not suitable for high-temperature applications. MDF-type panels can also be made using waste wood fiber from demolition wood and waste paper.
The properties of MDF will likely vary from country to country and region to region, based on where it is produced; thus the properties of MDF board produced in China will likely differ from MDF boards produced in Romania or Indonesia. MDF also comes in several densities depending on the intended application. The surface of MDF is generally flat, smooth, uniform, dense, and free of knots and grain patterns. The homogenous density profile of MDF allows intricate and precise machining and finishing techniques for superior finished products. Trim waste is significantly reduced when using MDF compared to other substrates. Stability and strength are important attributes of MDF, which can be machined into complex and delicate patterns that require precise tolerances. Moreover, its smooth surfaces also make MDF an excellent base for veneers and laminate applications.
Some of the current environmental pollution problems are created by burning and dumping of agricultural residues and, together with concern for the conservation of future forest resources, have generated considerable interest in finding suitable outlets to utilize the large amounts of crop residues being produced annually. And because agricultural residues are abundant and renewable annually, it became evident that they are excellent alternative sources to replace wood and wood fiber. Increasing constraints on residue burning have also been a prime motivator for their introduction. This new environmentally friendly technology for turning agricultural residues into ecofriendly boards entails compressing the agricultural residue materials with nonformaldehyde glues; the panels provide an excellent alternative to plywood sheets 3/8 inch and thicker and can be used in much the same way as MDF. They can also replace OSB and MDF for interior walls and partitions work.
Agricultural-residue (ag-res) boards are made from waste wheat straw, rice straw, jute, coconut coirs, bagasse, cotton stalks, casuarina leaves, banana stem, or even sunflower seed husks. Ag boards are aesthetically pleasing, often stronger than MDF and just as functional. Under heat and pressure, microscopic “hooks” on the straws link together, reducing or eliminating the need for binders. The use of new soy adhesives promises both improved performance and economics to the ag-composites industry. They are also expected to be safer to handle and to reduce VOC emissions.
Homasote is a brand name that has become synonymous with the product generically known as cellulose based fiber wall board. It is a panel product made of 100-percent postconsumer recycled newspaper fiber and has actually been in production longer than plywood and OSB (about 100 years). It has many potential fiberboard applications specific to sound control in floors and walls, tackable wall board, fire protection for roof decks, concrete expansion joints, low emission IAQ, and thermal insulation. Homasote is weather resistant, structural, and extremely durable, and it has two to three times the strength of typical light-density wood fiberboards. Furthermore, it is nontoxic, wax emulsified for moisture and mold resistance and integrally protected against termites and fungi, ensuring a healthy environment, conserving natural resources, and reducing solid waste in landfills.

Framing

Advanced framing, or optimum-value engineering (OVE) as it is sometimes referred to, consists of a variety of framing techniques designed to reduce the amount of lumber used and waste generated in the construction of wood-framed structures. This helps reduce material cost and use of natural resources while at the same time increasing energy efficiency by providing more space for insulation. It also helps reduce the processes of extraction and manufacture, as well as transport, and lumber disposal which deplete resources, damage natural habitats, and pollute air and water.
Another problematic issue here is that dimensional lumber supplies depend upon larger trees that need decades to mature. Although OVE framing techniques are accepted by code, for one reason or another, they have received limited market penetration and acceptance by builders, framers, and consumers (less than one percent of the residential building market), and this is despite the long-term experience and significant resources that continue to support its use. Provisions for several key OVE framing practices can be found in model U.S. building codes (ICC, 2012a,b).
Modern OVE advanced framing techniques include the spacing of studs at 24-inch on center (o.c.); 2-foot modular designs that reduce cutoff waste from standard-sized building materials (Fig. 6.8a); in-line framing that reduces the need for double top plates; building corners with two studs; and insulated headers over exterior building openings (or no headers for nonload-bearing walls). The advantage of spacing studs at 24-inch o.c. rather than 16-inch o.c. is that it reduces the amount of framing lumber required to construct a home and replaces framing members with insulation. This allows the wall to achieve a higher overall insulating value and costs less to construct than a conventionally framed wall while still meeting the structural requirements of the home.
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Figure 6.8 (a) Isometric drawing illustrating advanced framing techniques used in residential construction. (b) Isometric drawings illustrating OVE framing details used in residential construction. Source: Adapted from Building Science Corporation.
Still, to achieve maximum success, advanced framing techniques should be considered at the earliest phases of the design process. For this reason, preliminary building design and planning decisions can significantly impact the ability to effectively implement OVE practices or offset potential benefits that can be achieved by using them. Likewise, including OVE framing details on construction plans can greatly facilitate proper implementation (Fig. 6.8b). Another key aspect of appropriately selecting OVE framing techniques is the careful consideration of all factors that can impact the final result, including trade-offs that may affect detailing and installation of nonstructural components (such as flooring, trim, and siding) to ensure that the lumber savings are justifiable.
Home owners and builders alike can benefit from advanced framing techniques by providing structurally sound homes that require less material and have lower labor costs than a conventionally framed house. Moreover, additional construction cost savings can be achieved from less construction waste to be disposed of, which also helps the environment. The use of fewer studs in OVE improves energy efficiency and enhances insulation values because fewer studs help maximize the insulated wall area through replacing lumber with increased insulation material and reduction of thermal bridging (conduction of heat through framing).
Conventional framing is often found to be structurally redundant, using wood unnecessarily for convenience. The Department of Energy’s Office of Building Technology points out that with advanced framing techniques, savings in material costs of some $500 per 1200 sq. ft. can be achieved in addition to 3–5% of labor costs and a 5% saving in annual heating and cooling costs. While it is true that advanced framing is more wood efficient than conventional framing, it is also true that some alternative structural technologies such as insulated structural systems, straw bale or earthen construction, and high recycled-content steel framing with thermal breaks place fewer demands on our forest resources than OVE framing techniques.
OVE framing techniques have without a doubt been proven to be effective, yet some techniques are, nevertheless, not allowed under certain circumstances (i.e., areas prone to high winds or with seismic potential) or in some jurisdictions. Local building officials should therefore be consulted early in the design phase to verify or obtain acceptance of these techniques. According to the Partnership for Advancing Technology in Housing (PATH), “The OVE techniques that can be practical to implement (if visibly marked on the construction plans) and have noticeable material savings, thermal benefits, and contribute to the quality of the framing job include:
• Right sizing headers according to the IRC 2006
• Three-stud insulated corners
• Ladder-blocking for intersecting walls
• 24″ o.c. floor joist framing (using L/480 deflection limits). The use of 2-foot modules helps to make the best use of common sheet-goods’ sizes and reduce waste and labor.”
PATH goes on to say that, “Future design and construction guidelines for OVE framing must address OVE decision-making factors and potential trade-offs with respect to serviceability considerations, energy-efficiency impacts, installation practices, and manufacturer requirements for various assemblies, components, and finishes. In addition, OVE guidance in the area of wall bracing would fill a needed void created by increased complexity of wall bracing provisions in modern building codes. Current guides tend to stress material savings without in-depth consideration of some of the cost and performance trade-offs involved. The goal should be to optimize, not maximize, the use of OVE framing in the context of all costs and objectives associated with a building project.
Additional OVE framing practices, such as the use of single headers or band-joist headers, should be incorporated into prescriptive building codes to facilitate their use without incurring the added cost of professional engineering for each application.”
Structural insulated panels (SIPs) are high-performance building panels used in floors, walls, and roofs mainly for residential and light commercial buildings. The panels usually consist of two sheets of rigid structural facing board, such as OSB or plywood, which is applied to both sides of a core of rigid foam plastic such as expanded PS (EPS) that is 4 or more inches thick. Alternative skin material can be used for specific purposes. The result of this simple sandwich is a strong structural building system for building walls, roofs, and floors that are significantly more energy-efficient, cost-effective, and yield-improved R-values compared to traditional framing. SIPs are manufactured under factory controlled conditions and can be custom designed for each project. In addition to SIP’s excellent insulation properties, it offers airtight assembly, noise attenuation, and superior structural strength. Though SIP panels may initially cost more per square foot than conventional construction, total construction costs are often minimized due to reduced labor and faster completion.
The superior insulation afforded by utilizing the SIP system as well as cost savings due to the reduction in construction waste is especially significant when compared to conventional stick or steel stud systems. SIP panels can be delivered precut to the precise dimensions required, and each panel contains the structure, insulation, and moisture barrier of the wall system. OSB is the most common sheathing and facing material in SIP, reducing wood use by as much as 35% and reducing pressure on mature forests by allowing the use of smaller farm-grown trees for structural applications. OSB differs from traditional plywood in that it has no gaps, laps, knots, or voids. In most applications, OSB sheathing is also dimensionally stronger and stiffer than comparable dimensional plywood boards, and is a low-emitting material. However, one of an SIP panel’s adverse characteristics and for which it has been often criticized is its environmental footprint. Usually the resin adhesive that the OSB strands are bonded together with is not ecofriendly and usually contains formaldehyde which can be toxic, allergenic, and carcinogenic. Recent technological developments appear to be addressing this issue and make SIPs more environmentally friendly.
SIPs are generally chosen for their versatility, strength, cost effectiveness, and energy efficiency and are engineered and custom-manufactured to give the designer greater control over the project, which includes materials and costs. Another advantage of insulated structural systems is that they integrate a building’s structure and insulation into a single component. These characteristics also make them suitable for a wide range of residential and commercial applications. SIP wall assemblies are custom-made according to specifications and drawings and therefore tend to be well sealed, thus enhancing energy efficiency. As with any tightly sealed structure, moisture control and well-designed ventilation are critical. SIP construction systems can make a significant contribution to good IAQ; the plastic insulating foams used in their manufacture (EPS or PU/polyisocyanurate) are chemically stable.
SIP cores can be made of several materials, of which EPS is the most common. EPS requires less energy to manufacture than some of the other options and is more recyclable than PU or polyisocyanurate. Many products now offer a 1-h fire rating when installed with 5/8-inch or thicker gypsum sheathing. Another advantage of EPS foam is that it is expanded with pentane, which does not contribute to ozone depletion or global warming; additionally, it is often recaptured at the factory for reuse, thus adding to its value.
Although PU and polyisocyanurate have superior insulation properties per inch of foam than EPS and offer greater resistance to thermal breakdown, they are unlikely to be recycled. Moreover, PU and polyisocyanurate use HCFC blowing agents, which contribute to global warming and ozone depletion (although to a lesser degree than CFCs). Research is currently underway to develop more suitable ecofriendly alternatives for use in SIPs—new resins derived from soy.
The beauty of using straw-core SIPs is that they are made from waste agricultural straw, are renewable, and recyclable, and pressed-straw core does not require a binding agent. The drawback of using straw-core SIPs is that they offer less insulation per inch of thickness and are significantly heavier than other options; energy used in shipping is a significant consideration when using straw-core SIPs. Preplanning is one of the keys to successful SIP construction, and there are a number of factors to consider when building with SIPs, include:
• SIP designs should be to standardized panel dimensions. Also, to minimize waste, SIP panels should be ordered precut to meet project requirements when delivered to the job site, including window and door openings. This will save 20–30% on framing labor and approximately 30% on waste costs.
• Plumbing and electrical runs need to be predetermined so that the manufacturer can accommodate these needs.
• A tighter house means smaller HVAC systems (up to 40% savings), so when sizing the heating system, consider the thermal performance of SIPs to save money up front and energy over time. Oversized heating and cooling systems are inefficient.
• With improved IAQ, smaller or no air purification systems are required in many climates.
• Roofs using SIP systems often do not require ventilation, making them appropriate for low-slope roofs. If local jurisdiction mandates ventilated roofs, consider SIPs with integrated air channels or upgrading from composition roofing.
• Check to see whether the SIP supplier or manufacturer is willing to take back any offcuts for recycling.
Insulated concrete forms (ICFs) are forms or molds that have built-in insulation for accepting reinforced concrete and are rapidly becoming a mainstream preferred building product. The forms consist of large interlocking modular units that are dry-stacked (without mortar) and filled with concrete. The forms lock together somewhat like LEGO bricks and serve to create a form for the structural walls of a building. Concrete is pumped into the cavity every several feet to form the structural element of the walls. ICFs usually employ reinforcing steel (rebar) before concrete placement to give the resulting walls flexural strength, similar to that of bridges and concrete high-rise buildings. ICFs also employ an insulating material as permanent formwork that becomes a part of the finished wall.
After the concrete has cured or firmed up, the ICFs are left in place permanently to increase thermal and acoustic insulation and render greater fire protection. ICFs can also accommodate electrical and plumbing installations (Fig. 6.9). The end result leaves you with a high-performing wall that is structurally sound, insulated, strapped, has a vapor barrier, and is ready to accept final exterior and interior finishes. ICFs can generally be considered “green” materials because they are durable, produce little or no waste during construction, and significantly improve the thermal performance of concrete walls. Also, there are no CFCs, HCFCs, or formaldehydes, or wood to rot and mold.
There are essentially three main types of ICF systems on the market. Each type addresses significantly different construction issues and different completed results to the owner. The comparisons are typically based on a variety of different test standards, criteria, and calculations. The different features of the three types are shown below:
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Figure 6.9 (a, b) Two Photos depicting application of insulating concrete formwork Quad-Lock system. This can be considered a “green” material as it is durable, produces little or no waste during construction, and greatly improves the thermal performance of concrete walls and floors. Moreover, Quad-lock panels are molded of fire-retardant Expanded Polystyrene, which is a foamed insulation that has a zero ozone-depletion rating. Source: Quad-Lock Building Systems.
• The solid monolithic concrete forms or flat system forms consist of an even thickness of concrete throughout the walls like a conventionally poured wall.
• The waffle-grid system creates a waffle pattern where the concrete is thicker at some points than others.
• The screen grid or post-and-beam system forms consist of detached horizontal and vertical columns of concrete.
An important characteristic of standard concrete is that it is a dense material with a high heat capacity that can be utilized as thermal mass, thereby reducing the energy required to maintain comfortable interior temperatures. One of concrete’s negative attributes is that it is not a good insulator, and standard formwork is therefore waste intensive. Additionally, toxic materials are frequently required to separate the formwork from the hardened product. ICF is able to address these weaknesses by reducing solid waste, air and water pollution, and (potentially) construction cost. ICF wall systems have proven to be thermally superior, thus enhancing their usefulness for passive heating and cooling; comfort is also enhanced and energy costs are reduced. Any possible higher initial costs that are incurred can be offset or minimized by the downsizing of the heating/cooling system.
A variety of materials can be employed in the manufacturer of ICF systems including lightweight foamed-concrete panels, rigid foams such as EPS and PU, and composites that combine concrete with mineral wool, wood waste, paper pulp, or EPS beads. Likewise, there are several ICF systems currently on the market that substitute straw bales or fiber cement for PS, such as BaleBlock and Faswall. Rigid foams used in ICFs are generally less green because they do not have significant recycled content and are less likely to be recyclable at the end of their life. However, this does not preclude them from being reused in fill or other composite concrete products to meet market demands.
A distinct attribute of ICFs is that they offer the structural and fire-resistance benefits of reinforced concrete; structural failures due to fire are therefore not common place. By adding flame-retardant additives, PS ICFs tend to melt rather than burn, and interior ICF walls tend to contain fires far better than wood frame walls, improving overall fire safety. As is the case in most heated structures, a key design consideration for ICF walls is moisture control. Solid concrete walls sandwiched in PS blocks tend to be very well sealed to enhance energy efficiency, but they consequently also tend to seal water vapor within the structure. Potential mold growth and impaired IAQ are serious health concerns that require attention and need addressing. A simple approach to resolving this is by incorporating mechanical ventilation. Certain systems such as straw bale and RASTRA tend to be more vapor permeable, thereby reducing this concern. Several ICF products such as RASTRA are more ecofriendly because they are made from recycled postconsumer PS (foam) waste products.

6.2.9. Concrete

Concrete is a composite building material made up of three basic components: water, aggregate (rock, crushed stone, sand, or gravel), and a binder or paste such as cement. The cement hydrates after mixing and hardens into a stonelike durable material with which we are all familiar. Concrete has a low tensile strength and is generally strengthened by the addition of steel reinforcing bars; this is commonly referred to as reinforced concrete.
Over the centuries, concrete has proven to be a strong, durable, yet inexpensive building material and is widely used as a structural building material in the United States and throughout the world. Due to the increasing scale of concrete demand, the impacts of its manufacture, use, and demolition are widespread. Habitats are disturbed from materials extraction; significant energy is used to extract, produce, and ship cement; and toxic air and water emissions result from cement manufacturing. It is estimated that approximately one ton of carbon dioxide is released for each ton of cement produced, resulting in 7–8% of man-made CO2 emissions. And although concrete is generally only 9–13% cement, it, nevertheless, accounts for 92% of concrete’s embodied energy. Cement dust contains free silicon dioxide crystals, the trace element chromium, and lime, all of which can have negative impacts on worker health and the environment. Mixing concrete requires large amounts of water and generates alkaline waste water and runoff that can contaminate vegetation and waterways.
Admixtures are often added to a concrete mix so as to achieve certain specific goals. Below are some of the main admixtures that are used and what they are designed to achieve:
Accelerating admixture is added to concrete to reduce the concrete’s setting time and to accelerate achieving early strength. The amount of reduction in setting time will vary according to the amount of accelerator used. Although calcium chloride is a low-cost accelerator, specifications will often specify a nonchloride accelerator to prevent the corrosion of reinforcing steel.
Retarding admixtures are frequently required in hot weather conditions to facilitate delaying the setting time. They are also used to delay set in more difficult jobs or for special finishing operations such as exposing aggregate. Retarders also often act as a water reducer.
Fly Ash is a residue from coal combustion. Fly ash can replace 15–30% of the cement in the concrete mix. Its use is quite popular as a cement substitute, and its use improves concrete performance, giving greater compressive strength, decreased porosity, greater durability, improved workability, and more resistance to chemical attack, although the curing time is increased. Using fly ash also creates significant benefits for the environment.
Water reducing admixtures will reduce the amount of water needed in the concrete mix. The water–cement ratio will be lower while the concrete’s strength will be greater. Most low-range water reducers reduce the water needed in the mix by 5–10%.
Air Entraining Admixtures should be used whenever concrete is exposed to freezing, thawing, and deicing salts. Air entraining agents entrain microscopic air bubbles in the concrete, so that when the hardened concrete freezes, the frozen water inside the concrete expands into these air bubbles instead of damaging the concrete.
The incorporation of local and/or recycled aggregate (such as ground concrete from demolition) is an excellent way to reduce the impacts of solid waste, transit emissions, and habitat disturbance.
In nonstructural applications, concrete use may be reduced by trapping air in the finished product or through the use of low-density aggregates. Trapped air displaces concrete while enhancing insulation value and reduces weight and material costs without compromising its durability and fire resistance. Similar insulation and weight-reduction benefits are provided by other low-density aggregates such as vermiculite, perlite, pumice, shale, PS beads, and mineral fiber. Cast-in-place or precast concrete and concrete-masonry unit (CMU) considerations include the following:
• Recycling of demolished concrete on site for use as aggregate or fill material for new projects or recycle at local landfills.
• Whenever possible, redeploy portions of existing structures, such as slabs or walls that are in satisfactory condition.
• Employing precast systems to minimize waste of forming material and to reduce the impact of wash water on soils.
• Incorporating the maximum amount of fly ash, blast-furnace slag, silica fume, and/or rice-husk slag appropriate to the project can reduce cement use by 15–100%.
• The employment of alternative material substitutes for concrete should be considered such as ICFs to reduce waste, enhance thermal performance, and reduce construction schedules. Likewise, cellular, foamed, autoclaved-aerated, and other lightweight concretes add insulation value while reducing weight and concrete required. The use of earthen and rapidly renewable materials, such as rammed earth, cob, or straw bale, also help reduce the need for insulation and finish materials in both residential and commercial projects.
• Nontoxic form-release agents to be used when possible.
• Waste can be minimized by carefully planning concrete material quantities.
• Fabric-based form systems should be considered for footings to achieve faster installation and greater wood savings.
• Wood waste and material costs can be reduced by employing steel or aluminum concrete forms, which unlike many wood forms can be reused many times over.
• Permeable or porous/pervious surfaces allow water to percolate into the soil to filter out pollutants and recharge the water table.
Urban and suburban sites typically contain large areas of impermeable surfaces which are causing a number of problems. It is estimated that up to 75% of urban surface area is covered by impermeable/impervious pavement, which are solid surfaces that do not allow water to penetrate, which forces it to run off, and inhibits groundwater recharge, contributing to erosion and flooding, conveying pollution to local waters, and increasing the complexity and expense of storm-water treatment. Also due to the heat-absorbing quality of asphalt and other paving materials, sites with high ratios of impermeable surfaces increase ambient air temperatures and require more energy for cooling, thereby creating a heat island effect.
One of the main characteristics of permeable surfaces/paving (also known as porous or pervious surfaces), on the other hand, is that it contains voids that allow water to percolate into the soil to filter out pollutants and recharge the water table. Pervious paving may incorporate recycled aggregate and fly ash, which help reduce waste and embodied energy. Pervious paving is suitable for use in parking and access areas, as it has a compressive strength of up to 4000 psi. It also mitigates problems with tree roots; percolation areas encourage roots to grow deeper. Enhanced heat exchange with the underlying soil can decrease summer ambient-air temperature by 2–4°F.
Concrete poured-in-place applications require on-site formwork which acts as a mold to give shape to walls, slabs, and other project elements as they cure to a satisfactory strength and after which it is removed (Fig. 6.10). Plywood and milled lumber are the most common form materials, contributing to construction waste and the impacts of timber harvesting and processing. Wooden formwork can be made from salvaged wood and typically be disassembled and reused several times.
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Figure 6.10 Photo of carpenters setting concrete formwork for high-level waste facility pit walls. Source: Bechtel Corporation.
Form release agents are materials that prevent the adhesion of freshly placed concrete to the forming surface (which is usually plywood, overlaid plywood, steel, or aluminum). Such materials prevent concrete from bonding to the form, which can mar the surface when forms are dismantled. There are two principal categories of release agents available; these are barrier (nonreactive or passive) and reactive (or chemically active). Barrier release agents prevent adhesion by creating a physical film or barrier between the forming surface and the fresh concrete. Reactive or Chemically active release agents on the other hand work by the process of a chemical reaction between the release agent and the calcium (lime) that is available in fresh concrete. A soapy film is created which prevents adhesion. Also, as it is a chemically reactive process, there is generally little to no residue on the forming surface or concrete thus providing for a cleaner process.
Traditional form releasers such as diesel fuel, motor oil, and home heating oil are carcinogenic and are now prohibited by a variety of state and federal regulations, including the Clean Air Act, because it exposes construction personnel (and potentially occupants as well) to VOCs. Low- and zero-VOC water-based form-release compounds that incorporate soy or other biologically derived oils dramatically reduce health risks to construction staff and occupants and often make it easier to apply finishes or sealants when necessary. Many soy-based options are generally less expensive than their petroleum-based counterparts.
The designing of concrete formwork necessitates that all factors that will adversely affect concrete-formwork pressure be taken into consideration. These factors include the rate of placement, concrete mix, and temperature. The rate of placement should generally be lower in the winter than in the summer. It does not matter how many cubic yards are actually placed per hour or how large the project is. What does matter is the rate of placement per height and time (height of wall poured per hour). Moreover, the forms should also be of sufficient strength and stability to enable it to carry all live and dead loads that may be encountered before, during, and after placing of the concrete. Most exterior type APA panels can be used for concrete formwork because these panels are manufactured with waterproof glue.

6.3. Building and Material Reuse

The term building reuse generally means leaving the main portion of the building structure and shell in place while performing a “gut rehab,” as it is known in the trade.

6.3.1. Building Reuse

The intent of this LEED Credit is to extend the life cycle of existing building stock, reusing building materials and products, retain cultural resources, reduce waste, protect virgin resources, and reduce environmental impacts of new buildings as they relate to materials manufacturing and transport. This is particularly important for green building because repairing a building rather than tearing it down saves natural resources as well as a significant reduction of materials ending up in the landfill. The reuse of materials is also important because of the embodied energy that is within the production, manufacture, transportation, and construction of the new material. Reuse discourages the production of new products and minimizes the negative impact of embodied energy through reduction in raw material extraction. A key factor in building reuse is the durability of the original structure.
In some states, including North Carolina, grants are provided to renovate vacant buildings in rural counties or in economically distressed urban areas. Note that disaster-recovered materials such as trees uprooted by tornadoes or hurricanes are not eligible for LEED credit.

Maintaining Structural Elements: Existing Walls, Floors, and Roof

LEED requirements for New Construction are to maintain a minimum of 50, 75, or 95% (for up to three points) of the existing building structure (based on surface area), including structural floor and roof decking as well as the envelope (exterior skin and framing but excluding window assemblies and nonstructural roofing material). It is possible to achieve a credit by maintaining a minimum of 50% (by area) of interior nonstructural elements of an existing building, such as interior walls, doors, refurbished wood floors, and ceiling systems, of the new building. Hazardous materials that are remediated as a part of the project scope are to be excluded from the calculation of the percentage maintained. The credit will not apply if the project includes an addition to an existing building where the square footage of the addition is more than twice the square footage of the existing building.
Table 6.3 below shows the minimum percent of building-structure reuse required for achieving LEED credits for New Construction (always check USGBC website for latest update). However, for Core and Shell, you are required to maintain a minimum of 25, 33, 42, 50, or 75% of existing walls, floors, and roof for up to five credits. Schools must maintain 55 or 75% of existing walls, floors, and roof for up to two credits. It is strongly advised to check with LEED for the updated requirements of a particular category.

Potential Technologies and Strategies

Potential technologies and strategies: Consider the use of salvaged, refurbished, or reused materials from previously occupied buildings, including structure, envelope, and elements. Hazardous materials that pose contamination risk to building occupants and that are remediated as a part of the project scope shall be excluded from the calculation of the percentage maintained. Upgrade components that would improve energy and water efficiency, such as windows, mechanical systems, and plumbing fixtures. However, mechanical, electrical, plumbing, or specialty items and components should be excluded for this credit. Furniture may be included only if it is included in the other MR Credits.

Table 6.3

Minimum building structure reuse

Building reuse (%)Points
551
752
953

Interior Nonstructural Elements

Retain 50% of interior nonstructural elements for New Construction and Schools and 40 and 60% for Commercial Interiors. The intent here according to LEED is to extend the life cycle of existing building stock, conserve resources, retain cultural resources, reduce waste, and reduce environmental impacts of new buildings as they relate to materials’ manufacturing and transport.

LEED Requirements

Maintain at least 50% (by area) of existing interior nonshell and nonstructural elements (interior walls, doors, floor coverings, and ceiling systems) of the completed building (including additions). If the project includes an addition to an existing building, this credit is not applicable if the square footage of the addition is more than two times the square footage of the existing building.
In terms of potential technologies and strategies, LEED requires that consideration be given to the reuse of existing buildings, including structure, envelope, and interior nonstructural elements. Hazardous elements that pose contamination risk to building occupants are to be removed, and components that would improve energy and water efficiency, such as mechanical systems and plumbing fixtures, should be upgraded. For the LEED credit the extent of building reuse needs to be quantified, and the owner/developer must provide a report prepared by a qualified person outlining the extent to which major building elements from a previous building were incorporated into the existing building. The report should include preconstruction and postconstruction details highlighting and quantifying the reused elements such as foundations, structural elements, and facades. Windows, doors, and similar assemblies may be excluded.

6.3.2. Materials Reuse

Materials reuse should be 5 and 10% for New Construction, Schools, and Commercial Interiors (30% for furniture and furnishing), and 5% for Core and Shell. The intent is to reuse building materials and products to protect and reduce demand for virgin resources and to reduce waste, thereby reducing impacts associated with the extraction and processing of virgin resources.

LEED Requirements

Use salvaged, refurbished, or reused materials such that the sum of these materials constitutes at least 5, 10, or 30% (for Commercial Interiors, Furniture, and Furnishings), based on cost of the total value of materials on the project. Mechanical, electrical, and plumbing components and specialty items such as elevators and equipment are not to be included in this calculation. Include only materials permanently installed in the project. Furniture may be included, providing it is included consistently in MR Credits 3–7. Most credits in the Material and Resource category are calculated using a percentage of total building materials.

LEED Potential Technologies and Strategies

Include the identification of opportunities to incorporate salvaged materials into the building design and research potential material suppliers. Salvaged materials such as beams and posts, flooring, paneling, doors and frames, cabinetry and furniture, brick, and decorative items should be considered. The difference between Reuse and Recycling is that Reuse is essentially the salvage and reinstallation of materials in their original form, whereas Recycling is the collection and remanufacture of materials into a new material or product, typically different from the original. Biodegradable material breaks down organically and may be returned to the earth with none of the damage associated with the generation of typical waste materials.
C & D are estimated to be responsible for about 30% of the U.S. solid-waste stream. Real-world case studies by the Alameda County Waste Management Authority, for example, have concluded that more than 85% of that material, from flooring to roofing to packaging, is reusable or recyclable. For this reason, reusing materials slated for the landfill has become an extremely ecofriendly way to build, so as to avoid negative elements such as the extraction, manufacture, transport, and disposal of virgin building materials which pollute air and water, deplete resources, and damage natural habitats.
The salvaging of materials from renovation projects and specifying salvaged materials can reduce the costs of material while adding character to projects and maximizing environmental benefits, such as reduced landfill waste, reduced embodied energy, and reduced impacts from harvesting/mining of virgin materials (e.g., logging old-growth or tropical hardwood trees, mining metals, etc.). On the other hand, some materials require remediation or should not be reused at all. For example, materials contaminated by hazardous substances such as asbestos, arsenic, and lead paint must be treated and/or disposed of properly. Avoiding materials that will cause future problems is critical to long-term waste reduction as well as the health of communities and the environment.
Factors that impact the selection of reusable building materials include:
• Reusing existing building shells, when appropriate, can yield the greatest overall reduction in project impacts.
• Materials from remodeling or renovations should be reused on site.
• Products containing hazardous materials such as asbestos, lead, or arsenic should be disposed of properly or remediated prior to reuse.
• Building materials composed of one substance (e.g., steel, concrete, wood, etc.) or that are readily disassembled are generally easiest to reuse or recycle.
• For remodels and redevelopment, adequate time should be allowed in the construction schedule for deconstruction and recycling.
• Replace inefficient fixtures, components, and appliances (e.g., toilets using more than 1.6 gallons per flush, single-pane windows, and refrigerators or other appliances over 5 years old).
• Note that salvaged materials can vary in availability, quality, and uniformity. Ensure that materials are readily available to meet project needs before specifying them.
• Materials should be carefully evaluated to ensure that they offer the best choice for the application. They need to be durable and can preferably be readily disassembled for reuse, recycling, or biodegrading at the end of the useful life of the building.
• Materials composed of many ingredients, such as vinyl siding, OSB, or particleboard are generally not recyclable or biodegradable.

6.4. Construction Waste Management

The overall intent of the Construction Waste Management credit is to avoid materials going to landfills during construction by diverting the construction waste, demolition debris, and land-clearing debris from landfill disposal and incinerators; redirecting recyclable recovered resources back to the manufacturing process; and redirecting reusable materials to appropriate sites.

6.4.1. LEED Requirements

Recycle and/or salvage at least 50 or 75% of nonhazardous construction, demolition, and packaging debris (95% for extra credit). Develop and implement a construction waste–management plan that at a minimum identifies and quantifies the materials generated during construction that is to be salvaged, recycled, refurbished, or diverted from disposal and notes whether such materials will be sorted on-site or comingled. Typical items would include recycled cardboard, metal, brick, acoustical tile, concrete, plastics, clean wood, glass, gypsum board, carpet and insulation, as well as doors and windows, ductwork, clean dimensional wood, paperboard, paneling, cabinetry and plastic used in packing, etc. MEP (mechanical, electrical, plumbing) may now be included although this is not clear from the LEED reference books (Fig. 6.11). Excavated soil, rocks, vegetation, hazardous materials, and land-clearing debris do not contribute to this credit. Calculations can be done by weight or by volume but must be consistent throughout.
Documentation is required for each credit a project attempts to achieve using the LEED system to prove the activity was completed. LEED letter templates are to be used to certify that requirements are met for each prerequisite and credit. Additional documentation may also be required. The contractor will generally be responsible for completing the required LEED documentation for these two credits since the responsibility for construction waste management lies with the contractor.
The LEED Letter Template has to be signed by the architect, owner, or other responsible party, tabulating the total waste material, quantities diverted and the means by which they were diverted, and declaring that the credit requirements have been met. As a portion of the credits in each application may be audited, the contractor should be prepared with backup documentation. Most LEED projects will require a waste-management plan with regular submittals tracking progress. The plan should indicate how the required recycling rate is to be achieved, including materials to be recycled or salvaged, cost estimates comparing recycling to disposal fees, materials-handling requirements, and how the plan will be communicated to the crew and subcontractors. All subcontractors are required to adhere to the plan in their contracts. Considerations relating to construction waste reduction include:
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Figure 6.11 Truck from DRC Emergency Services unloading construction and demolition debris at Birmingham’s New Georgia Landfill, which is being used for brush, tree, construction, and demolition debris from the April 27, 2011, tornadoes. Source: Birmingham News/Joe Songer.
• The smaller the project, the less material used, reducing both solid waste and operating costs.
• Design of assemblies to match the standard dimensions of the materials to be used.
• Disassembly design should be considered so that materials can be readily reused or recycled.
• Track recycling through construction process (general contractor to keep records, i.e., receipts of recyclable and waste diversion pickups).
• Designate site in construction area for separation process.
• Employ clips and stops to support drywall or wood paneling at top plates, end walls, and corners. Clips can provide the potential for two-stud corners, reducing wood use, easing electrical and plumbing rough-in, and improving thermal performance.
• Materials attached with removable fasteners are generally quicker, cheaper, and more feasible to deconstruct than materials installed with adhesives, although adhesives distribute loads over larger areas than fasteners used alone.
• When possible, make use of existing foundations and structures in good condition, reducing waste, material requirements, and possibly labor costs.
• Design for flexibility and changing use of spaces.
• Specify materials such as SIPs, panelized wood framing, and precast concrete that can be delivered precut for rapid, almost waste-free installation.
• For wood construction, consider 24-inch on center framing with insulated headers, trusses for roofs and floors, finger-jointed studs, and engineered-wood framing and sheathing materials.
• Whenever practical, specify materials with high recycled content.
According to the United States Environmental Protection Agency (U.S. EPA), “Commercial construction typically generates between 2 and 2.5 pounds of solid waste per square foot, the majority of which can be recycled. Salvaging and recycling C&D waste reduces demand for virgin resources and the associated environmental impacts. Effective construction waste management, including appropriate handling of non-recyclables, can reduce contamination from and extend the life of existing landfills. Whenever feasible, reducing initial waste generation is environmentally preferable to reuse or recycling.”
The EPA goes on to say that, “The Construction Waste Management Plan should ideally recognize project waste as an integral part of overall materials management. The premise that waste management is a part of materials management, and the recognition that one project’s wastes are materials available for another project, facilitates efficient and effective waste management.”
It is also important for waste-management requirements be taken into account early in the design process and be a topic of discussion at both preconstruction and ongoing regular job meetings to ensure that contractors and appropriate subcontractors are fully informed of the implications of these requirements on their work prior to and throughout construction. Furthermore, the EPA states that “Plan Implementation of the waste management should be coordinated with or part of the standard quality assurance program and waste management requirements should be addressed regularly throughout the project. If possible, adherence to the plan would be facilitated by tying completion of recycling documentation to one of the payments for each trade contractor.”

6.5. Recycled Materials

Material Recycling can be defined in several ways depending largely on the different processes that recycling is involved in. It can be as simple as reusing a given product beyond its intended use such as passing old clothes on to charities, the poor, or relatives, to avoid throwing them out so that someone else can make good use of them. However, Recycling is more commonly associated with the practice of recovering old goods from the waste stream and reincorporating them into the manufacturing process, thus allowing them to be turned into new products. The Recycling process of waste materials into new products therefore helps prevent the waste of potentially useful materials and reduces the potential consumption of fresh virgin materials. Additionally, it lessens energy usage, reduces air pollution (by incineration), and reduces the need for “conventional” waste disposal. Recyclable materials is a key component of modern waste reduction and can take many forms including different kinds of plastic, paper, glass, metal, textiles, and electronics.
According to the Environmental Building News (BuildingGreen.com), “Recycled content refers to the portion of materials used in a product that have been diverted from the solid waste stream. If those materials are diverted during the manufacturing process, they are referred to as preconsumer recycled content (sometimes referred to as postindustrial). If they are diverted after consumer use, they are postconsumer.
Postconsumer content is generally viewed as offering greater environmental benefit than preconsumer content. Although preconsumer waste is much more vast, it is also more likely to be diverted from the waste stream. Postconsumer waste is more likely to fill limited space in municipal landfills and is typically mixed, making recovery more difficult.
To claim that it is using preconsumer recycled content, a company must be able to substantiate that the material it is using would have become garbage, had it not purchased it from another company’s waste stream, for example. If a manufacturer routinely collects scraps and feeds them back into its own process, that material does not qualify as recycled.”
Recycled content is the most widely cited attribute of green building products. The LEED intent for MR Credit 4.1 is to protect virgin resources by increasing demand for building products with recycled content.
The LEED requirements are: “Use materials with recycled content such that the sum of postconsumer recycled content plus one-half of the preconsumer content constitutes at least 10% (based on cost) of the total value of the materials in the project. The recycled content value of a material assembly shall be determined by weight. The recycled fraction of the assembly is then multiplied by the cost of assembly to determine the recycled content value.
Mechanical, electrical and plumbing components and specialty items such as elevators shall not be included in this calculation. Only include materials permanently installed in the project. Furniture may be included, providing it is included consistently in MR Credits 3–7.”
Recycled content is to be defined in accordance with the International Organization of Standards (ISO) document, ISO 14021—Environmental Labels and Declarations—Self-declared Environmental Claims (Type II Environmental Labeling). Companies claiming to use preconsumer recycled content must be able to substantiate that the material it is using would have been discarded, had it not been purchased from another company’s waste stream. However, if the manufacturer routinely collects scraps and feeds them back into its own process, that material according to LEED does not qualify as recycled.
Many federal, state, and local government agencies around the nation have established “buy recycled” programs aimed at increasing markets for recycled materials. Among these include, The California Department of Resources Recycling and Recovery (CalRecycle), San Mateo County, Iowa Program, Montgomery County, and others. These programs support the Department of General Services (DGS), other State agencies, as well as local governments in establishing policies and practices for purchasing recycled-content products (RCPs), in addition to supporting activities that promote waste reduction and management. Likewise, a principal goal of these programs is supporting all recycling activities to reduce solid-waste disposal, and many communities in the United States now offer regular curbside collection or drop-off sites for certain recyclable materials. Materials collection in itself, however, is insufficient toward making the recycling process work. Successful recycling also requires that manufacturers produce viable products from the recovered materials and, in turn, there is a market ready to purchase products made of recycled materials.
Recyclability is a characteristic of materials that maintain useful physical or chemical properties after serving their original purpose and which therefore allows them to be reused or remanufactured into additional products through a recognized process. In fact, many national and international companies constantly seek an environmental marketing edge by advertising the recycled content of their products, which is often undocumented or certified and often misleading. Such claims come under the jurisdiction of the Federal Trade Commission (FTC), which first published definitions for common environmental terms in its Green Guides in 1992. The LEED Rating System offers credit for recycled-content materials, referencing definitions from ISO 14021. However, these definitions leave a lot of gray areas, which many manufacturers often interpret in their own favor. Third-party certification of recycled content is useful in maintaining a high standard and offering the ability to verify any claims that are made regarding sustainability.
Waste is not a luxury we can afford, although we have to bear it. Yet, the extraction, manufacture/transport, and disposal of building materials continue to clog our landfills, pollutes our air and water, deplete our resources, and damage our natural habitats. The CIWMB notes that C & D waste comprised 22% of California’s solid-waste stream in 2004. Probably, more than 85% of that material, from flooring to roofing, and much of that material can be salvaged for reuse or recycled. In addition to C & D waste, we must also consider the material in our recycling bins, our used bottles, paper, cans, and cardboard, which can provide suitable raw materials for RCPs. But keeping a material out of the landfill is only the first step to putting “waste” back into productive use. The “waste” has to be reprocessed into a new, quality product, and that product must be cable of being sold to an entity that recognizes its benefits. The reprocessing of our “waste” as the raw material for new products, increases demand for recycling, and encourages manufacturers to employ more recycled material, continuously strengthening this cycle.
The benefits of using recycled-content materials are many and include reduced pollution, reduced solid waste, reduced energy and water use, reduced greenhouse gas emissions, and a healthier IAQ. Below is a partial list of materials that are readily recyclable and which generally may cost less to recycle than to dispose of as garbage:
• Acoustical ceiling tiles
• Asphalt
• Asphalt shingles
• Cardboard
• Carpet and carpet pad made of plastic bottles (or sometimes from used carpet); up to half of all polyester carpet made in the United States contains recycled plastic
• Concrete containing ground-up concrete as aggregate, fly ash—a cementitious waste product from coal-burning power plants—asphalt, brick, and other cementitious materials
• Countertops made with everything from recycled glass to sunflower-seed shells
• Drywall made with recycled gypsum and Homasote wall board made from recycled paper
• Fluorescent lights and ballasts
• Insulation, such as cotton made from denim, newspaper processed into cellulose, or fiberglass with some recycled-glass content
• Land-clearing debris (vegetation, stumpage, dirt)
• Metals (pipes, rebar flashing, steel, aluminum, copper, brass, and stainless steel)
• Paint (use a hazardous waste outlet)
• Plastic film (sheeting, shrink wrap, packaging)
• Plastic and wood-plastic composite lumber from plastic and wood chips, ideal for outdoor decking and railings
• Tile containing recycled glass
• Window glass
• Wood (Includes engineered products; nails are acceptable)
To achieve maximum benefit when selecting a recycled-content building material, the following points should be taken into consideration:
• Choose materials that contain the highest recycled content possible. For example, a recycled product that is 70% recycled is preferable to one that is only 10% recycled and 90% virgin material.
• Choose materials with high postconsumer recycled content. Some “recycled” content is waste from manufacturing processes. Reducing manufacturing waste is important, but recycling postconsumer material is necessary to close the loop.
• Choose materials that are appropriate for the application in hand.
• Salvaging (reusing) whole materials is preferable to recycling, and all but eliminates waste, energy, water use, and pollution.
• When possible, choose materials that are both recycled and also recyclable or biodegradable at the end of their useful life. Ideally, a material may be continuously recycled back into the same product.
Reclaimed wood has many applications, including, but not limited to, flooring, siding, furniture, and in some cases as structural members. Reusing wood from an existing building on site should be carefully considered, or where appropriate, look to salvage yards and on-site deconstruction sales for a portion of a project’s material needs. It is important to note that salvaging or reusing wood can reduce solid waste, save forest resources, and save money. Moreover, reclaimed wood is often available in dimensions, species, and old-growth quality that is no longer available today. Table 6.4 lists examples of Reusable (RU), recyclable (RC) and biodegradable (B) building materials.
Deconstruction consists of the systematic disassembly of a building, with the purpose of recovering valuable materials for reuse in construction, renovation, or manufacturing into new wood products, thereby preserving the useful value of its component materials. Deconstruction is preferable to demolishing; the combination of various tax breaks, new tools, and increasing local expertise are making it easier to keep materials out of the landfill. Deconstruction has grown by leaps and bounds in recent years, due mainly to new for-profit and nonprofit entities throughout the United States. Although deconstruction takes longer and may initially cost more than demolition, it is, nevertheless, likely to reduce the overall project cost. Waste reduction has the benefits of minimizing energy use, conserving resources, and easing pressure on landfill capacity.

Table 6.4

RU, RC, and B building materials

ReusableRecyclableBiodegradable
BricksAsphaltEarthen materials
Doors and windowsBricksGypsum wall board
Earthen materialsConcrete, ground and used as aggregateLinoleum flooring
Gypsum wall boardMetal: Steel, aluminum, iron, copperStraw bales
Lighting fixturesWood and dimensional lumber, such as beams, trusses, studs, and plywoodWood and dimensional lumber, such as beams, trusses, studs, and plywood
Metal: Steel, aluminum, iron, copperWool carpet
Plumbing
Unique and antique products that may no longer be available
Wood and dimensional lumber, such as beams, trusses, studs, and plywood

6.6. Regional Materials

Regional materials are those that are extracted, harvested, and manufactured within a 500 miles radius of the project site. The main LEED intent here is to reduce material transport by increasing demand for building materials and products that are extracted and manufactured within the region where the project is located, thereby supporting both use of indigenous resources and the regional economy as well as reducing the negative environmental impacts associated with transportation.

6.6.1. LEED Requirement

Use a minimum of 10 or 20% (based on cost) of total building materials and products that are extracted, harvested, recovered, or manufactured regionally within a radius of 500 miles of the site (Fig. 6.12). To calculate, either the default 45-percent rule or actual materials cost may be used. All mechanical, electrical, plumbing and specialty items such as elevator equipment need to be excluded. If only a fraction of the product/material is extracted, harvested, recovered, or manufactured within 500 miles of the site, then only that percentage (based on weight) may contribute to the regional value. Furniture may be included only if it is included throughout MR Credits 3 to 7. Of note, “manufacturing” alludes to the final assembly of components into the building product that is furnished and installed by the contractor. Thus, if the hardware comes from Los Angeles, California, the lumber from Vancouver, British Columbia, and the joist assembled in Fairfax, Virginia, then the location of the final assembly destination is considered to be Fairfax, Virginia. One or two points can be earned for using materials that are both harvested and manufactured within a 500-mile radius of the site. In LEED for Commercial Interiors (and in older versions of LEED for New Construction and LEED for Core & Shell), one point is given for merely manufacturing within that radius, and a second point for harvesting as well.
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Figure 6.12 Diagram of a map program that is capable of drawing any required radius for any chosen location. Source: Free Map Tools, www.freemaptools.com.
By simply tracking the materials that are typically produced and supplied within 500 miles of the project site, it is possible to achieve the 20-percent-credit threshold without impacting the cost. In some cases, however, the 20-percent threshold can only be achieved by targeting certain materials (e.g., specific types of stone or brick) or limiting the number of manufacturers whose products are to be considered in the project bids. In such instances, there is a possibility of incurring additional costs.
To verify that the extraction/harvest/recovery site is located within a 500-mile radius of the project site, project teams are required to attest to the actual mileage between the project site and the manufacturer and, likewise, attest to the distance between the project site and the extraction site for each indigenous material in the submittal template. Alternatively, a statement on the manufacturer’s letterhead indicating that the point of manufacture is within 500 miles of the LEED project site will also be accepted as part of the documentation and credit submittals. The benefit of using indigenous materials is that it reduces transportation distances and the associated environmental impacts.

6.7. Rapidly Renewable Materials

Rapidly renewable materials are those that grow back very quickly. These can be sustainably harvested at a fairly high rate, so the burden of proof is less for certification as it is for wood products. Rapidly renewable materials are numerous and include bamboo, cork, insulation, linoleum, straw-bale, wheat board, wool, etc. These are considered sustainable because they are natural, nonpetroleum-based building materials (petroleum-based materials are nonrenewable) that can be grown and harvested within 10 years. LEED states that the intent of using rapidly renewable materials is to “reduce the use and depletion of finite raw materials and long-cycle renewable materials by replacing them with rapidly renewable materials.” LEED MR Credit 6.0 states that to be eligible for credits, rapidly renewable materials must be equal to no less than 2.5% of the cost of a building project in terms of value. It has been found that the use of rapidly renewable resources can often save land as well as other resources that usually go into conventional materials. Moreover, because of their shorter harvesting cycles, rapidly renewable materials provide environmental benefits and are able to sustain a community for a longer period than more finite sources can.

6.7.1. Bamboo

Bamboo is considered to be one of many rapidly renewable resources for LEED certification under MR Credit 6. Furthermore, some bamboo lines are also made with no formaldehyde, thereby contributing to EQ 4.4—Low-Emitting Materials. Partly because of its rapid regeneration, Bamboo has emerged as an alternative resource to other types of wood commonly used in the United States and abroad. In the past, it was used as a basic material for making household objects and small structures, but continuous research and engineering efforts have enabled bamboo’s true value to be realized. That the bamboo plant meets all the criteria of being rapidly renewable is because when harvested sustainably, it will regrow from the same root stalk, maturing in just a few years, whereas trees such as oak and maple take far longer to grow and are incapable of regrowing from the same plant, in addition to the fact that they can be harvested only once.
Technically, Bamboo is not a wood; it’s a giant grass that comes in 1500 varieties that produces hard, strong, dimensionally stable wood. It can be found in many tropical regions of Asia, Africa, and South America. It has been used as both a building material and for furniture construction for thousands of years (Fig. 6.13a). In addition to being considered to be a fast-growing woody plant, it is also one of the most versatile and sustainable building materials available. Bamboo can reach maturity in months in a wide range of climates—and is exceedingly strong for its weight and can be used both structurally and as a finish material. Likewise, it can be clear-cut and will grow right back.
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Figure 6.13 (a) Bamboo plants in Kyoto, Japan. (b) Kitchen cabinets made of bamboo. (c) Photo showing use of bamboo as exterior siding. Sources: (a) Wikipedia, photo by Paul Viaar, 2004; (b and c) Bamboo Technologies.
Bamboo’s rapid regeneration, strength, and durability make it an environmentally superior alternative to conventional hardwood flooring. While some hardwood trees may require decades to reach maturity, bamboo can usually be harvested on a 4- or 5-year cycle, and the mature forest will continue to send up new shoots for decades. Pine forests are known to have the most rapid growth among tree species, but bamboo grass species used in flooring can grow much faster—more than 3 ft. per day and produce nearly twice as much harvestable fiber per year. At the same time, Bamboo can yield a product that is 13% harder than rock maple and durability comparable to red oak. Nevertheless, one has to be careful with bamboo as an inferior manufacturing process can sometimes neutralize the hardness benefits of the material itself. Indeed, a poor-quality topcoat will scratch no matter how durable the flooring. Bamboo canes have a natural beauty when exposed which is why it is often used for paneling, furnishings, and cabinetry (Fig. 6.13b and c).
Many developing countries around the world, especially those with more tropical climates, and where Bamboo often grows into larger diameter canes, have a long vernacular tradition for its use in structures. However, the general use of bamboo today in the United States is limited by a lack of architects and/or engineers trained in bamboo design, joining systems, harvesting, treatment and strength of relevant species, as well as a lack of capable carpenters with the skills to economically and efficiently build bamboo structures. One of the issues to confront the sustainability of bamboo is the amount of transportation it requires to get it to North America. The majority of bamboo currently used in hardwood flooring comes from Hunan Province in China which means it has to be shipped across the ocean to get to North America and then put on trucks or trains to get to its final destination.
When using bamboo, particular care should be given to joinery details, since its strength comes from its integral structure, and it cannot be joined with many of the traditional methods used with wood. In this respect, the ancient ways of building with bamboo can be especially informative. Also, exposing bamboo to heavy moisture can eventually destroy it by fungus, which is what happens when it is exposed to adverse weather. Even with direct exposure, it is possible to prevent this by injecting it with chemical formulae of varying levels of environmental acceptability.
Tests have shown Bamboo to be an extremely strong fiber having twice the compressive strength of concrete and roughly the same strength-to-weight ratio of steel in tension. Some bamboo fibers also have greater shear strength than structural woods and take much longer to come to ultimate failure. However, Bamboo has the ability to bend without breaking which makes it unsuitable for building floor structures due to our low tolerance for deflection and lacking a willingness to accept a floor that has a “bouncy” feel. An appropriate substitute for the standard oak is a ¾-inch-thick bamboo finished floor because it installs the same way, is harder, and expands less. Likewise, vertically laminated flooring and plywood products that consist of layers of bamboo compressed with a binder can create a durable, resilient finish material. And when well maintained, bamboo floors can last for decades. Like most interior-grade hardwood plywood, bamboo flooring is typically made with a urea-formaldehyde binder, which can emit tiny amounts of formaldehyde. To counter this and minimize indoor-air pollution caused by the use of urea-formaldehyde, it is important to choose high-quality products, particularly from manufacturers that provide independent air quality testing data.

6.7.2. Cork

Ninety nine percent of the world’s cork grows in the sunny Mediterranean. Cork is a natural, sustainable product harvested from the bark of the cork oak, Quercus suber. It can be first harvested when it is 25 years old, when the virgin bark is carefully cut from the tree. It should be noted that from the three layers of the cork bark that is harvested, only the middle layer is used to make cork products. And the harvesting of cork does not require a single tree to be cut down, and only a percentage of the bark is removed from each tree, thus allowing it to maintain its protection while regenerating. Following this, the tree can be regularly “stripped” of its cork every 9 years for roughly 200 years without any harm coming to the tree. This helps to encourage long-term management of this renewable resource. It is estimated that an 80-year-old cork tree can produce nearly 500 pounds of cork. And unlike synthetic vinyl flooring, cork provides a resilient building alternative with a 50+ year lifespan compared to the 10- to 20-year lifespan of synthetic flooring. It also has a negligible impact on energy performance at its point of use.
Cork applications are becoming increasingly popular due to its unusual characteristics—a combination of beauty, durability (can last for decades), insulation, and renewability (see Fig. 6.14). Likewise, modern cork floors are very durable, fire resistant, and provide thermal and acoustic insulation. In addition to being soft on the feet, Cork is also antimicrobial and inherently resistant to mold and mildew, has low off-gassing from natural oils, does not produce chemicals during the manufacturing process (dioxin specifically), and the material is completely biodegradable. Cork adapts well to weight and will recover from large amounts of pressure which makes it appropriate for use in kitchens and laundry rooms. They are usually covered with an acrylic finish but may alternatively be covered with PU for bathroom or kitchen applications. The extraction, manufacture, transport, and disposal of synthetic flooring materials on the other hand, pollutes air and water, depletes resources, damages natural habitats, and can have negative health impacts.
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Figure 6.14 (a) Residential interior using cork flooring. (b) Cork pattern detail. Source: Globus Cork.
Cork floors are sometimes considered as a natural alternative to carpet because it provides the majority of the benefits of carpet without its liabilities. Carpet can attract and hold indoor pollutants in its fibers, whereas cork is easier to thoroughly clean, sheds no dust or fibers, and is naturally antistatic. In addition to its hypoallergenic properties, it offers thermal and acoustic insulation. But the benefits of using cork go beyond human health; they include less landfill waste (it can be recycled back into the manufacturing process to minimize further waste), many products locally obtainable, exemplary aesthetics, and reduced ecological impacts of harvesting/mining the raw materials. However, there is significant regulation for cork harvesting (unlike bamboo), and to minimize potential damage to the trees and ecosystems, countries that harvest cork monitor the frequency at which the resource can be harvested.

6.7.3. Insulation

The majority of insulation employed in buildings is for thermal purposes, but the term also applies to acoustic insulation, fire insulation, and impact insulation (e.g., for vibrations caused by industrial applications). Insulation will therefore help to protect a building’s occupants from heat, cold, and noise, in addition to reducing pollution while conserving the energy needed to heat and cool a building. Insulation materials will often be chosen for their ability to perform several of these functions at once, and well-insulated building envelopes are primary considerations in comfort and sustainability. Environmentally preferable insulation options can offer additional benefits, such as reduced waste and pollution in manufacture and installation, as well as a more efficient resource use, better recyclability, improved R-value, and reduced or eliminated health risks for installers and occupants. The comfort and energy efficiency of a home or office depend on the R-value of the entire wall, roof, or floor (i.e., whole-wall R-value) and not just the R-value of the insulation.
Fiberglass which is usually the material of choice for insulating ceilings and walls consists of extremely fine glass fibers. Its popularity is often based on economic grounds even though its use may present potential health risks. It is advisable that all fiberglass insulation used be formaldehyde free with a minimum 50% total recycled content (minimum 25% postconsumer). Some products are manufactured with heavier, intertwined glass fibers to reduce the amount of fibers becoming airborne and also to mitigate the fraction of fibers that can enter the lungs. One of the issues with using Fiberglass fibers is that they are friable and can easily become airborne, particularly during installation. These fibers can be inhaled, and some health experts claim that this particulate matter is carcinogenic.
Fiberglass insulation is similar to other glass products in that it is made primarily from silica heated to high temperatures, requiring significant energy and releasing formaldehyde. Short-term effects that may be experienced during installation or other contact include irritation to eyes, nose, throat, lungs, and skin. Longer-term effects are controversial, but OSHA now requires fiberglass insulation to carry a cancer warning label. Binders in most fiberglass batts contain toxic formaldehyde that continues to slowly emit for months or years after installation, potentially contaminating indoor air.
There are also various environmentally preferable insulation options including the use of recycled cotton, which insulates as well as fiberglass and offers superior noise reduction. Cotton insulation typically comes in batt form and is easy to work with. It is also soft, not irritating during installation and poses no health risk to the installer (unlike fiberglass) or occupants, nor does it use a formaldehyde-based binder. To maximize its energy performance, the insulation should be fitted to completely fill the wall and ceiling cavities without being compressed by pipes or wires. Cotton insulation can retain up to 15% moisture, which may not create problems in walls assemblies that are dry or are able dry out between cycles of water loading. However, care should be taken to avoid repeated wetting and drying which could cause the borate treatment to seep out and encourage the growth of mold. Also, cotton insulation costs roughly twice as much as fiberglass batts, bearing in mind that insulation material costs are generally a very small percentage of the total cost of construction. In addition, the excellent sound and safety qualities of cotton insulation give it an edge over fiberglass.
BioBased Insulation is essentially PU spray-in-place foam that is manufactured with annually renewable soybean oil, which allows it to be classified as a rapidly renewable product. Such innovative products have excellent thermal and sound insulating properties that can help to provide a healthy, comfortable, energy-efficient, and durable residential or commercial building. Depending on the size, cost, and amount of the project insulated, BioBased Insulation can contribute a significant portion of LEED’s required 2.5% of rapidly renewable products and materials used in the project.
Likewise, cellulose (recycled newspaper) insulation can be an acceptable alternative because it generates a nontoxic, fire-retardant insulation product. It also acts as an effective protective shield to reduce the transmission of heat or sound and is suitable for insulation of Timber Frame Walls, Attics, and Lofts. It poses no health risk and offers superior R-value per inch. Both cellulose and cotton are treated with borate, which is not toxic to humans and makes both materials more resistant to fire and insects than fiberglass. Some cellulose insulation products are manufactured entirely from recycled newspaper which might otherwise end up in a landfill.
Sprayed PU foam is sometimes used in large to midscale applications and is sprayed onto concrete slabs, into wall cavities of an unfinished wall, or through holes drilled in sheathing or drywall into the wall cavity of a finished wall to provide insulation, vapor barrier, and additional shear strength. Although the cost of Sprayed PU foam can be high compared to traditional insulation, it is offset by many advantages, including increased structural stability (unlike loose-fill), and blocking airflow through expansion and sealing off leaks, gaps, and penetrations. Sprayed cementitious foams such as Air-Krete have similar properties. Air-Krete is environmentally friendly, nontoxic, nonhazardous, fireproof, nonexpansive, insect resistant, mold proof, zero VOC emission, and Insoluble in water.

6.7.4. Linoleum

Linoleum is a highly durable, environment friendly, resilient material that is used mainly for flooring. It is made from a mixture of natural materials such as solidified linseed oil (linoxyn), recycled wood flour, ground cork dust, pine rosin, and mineral pigments which are mounted onto a jute-fiber backing. Linoleum is also naturally antibacterial and biodegradable. The manufacture of Linoleum requires mixing oxidized linseed oil (or a combination of oxidized linseed oil and tall oil) and rosin with the other raw materials to form linoleum granules. The granules are then pressed onto a jute backing, creating Linoleum sheets. These sheets are then hung and allowed to cure in special drying rooms to achieve the required flexibility and resilience. Maximum waste reduction is achieved by recycling back any linoleum remnants into the production process. Linoleum manufacturing should be conducted in accordance with ISO 14001 standards. LEED credits may be given for purchasing local materials.
Although Flexible vinyl flooring (often incorrectly referred to as linoleum), largely displaced linoleum from the marketplace in the 1960s, Linoleum has made a dramatic reappearance in the marketplace as a flooring choice for those who are environmentally conscientious. In addition, being made of organic materials and purportedly nonallergenic in nature, high-quality linoleum continues to be in use in many places (especially in nonallergenic homes, hospitals, and health care facilities). The two materials are quite different. First costs of linoleum are higher, but linoleum offers certain performance advantages that are superior to vinyl, such as lasting longer, being inherently antistatic, as well as antibacterial. Moreover, all-natural, linoleum requires less energy and creates less waste in its manufacture, and it can be chipped and composted at the end of its useful life. Maintenance of linoleum is likewise less labor intensive and less expensive as it does not require sealing, waxing, or polishing as frequently as vinyl. On the other hand, flexible vinyl flooring remains a more prolific generator of solid waste because it is manufactured from toxic materials and will typically last about 10 years; it is neither biodegradable nor generally recyclable. Linoleum also emits far fewer VOCs when installed with a low-VOC adhesive than flexible vinyl and does not exude the phthalate plasticizers that are an increasing concern for human health.
Vinyl tile is still favored over many other kinds of flooring materials in various commercial and institutional applications where high traffic is anticipated because of its characteristically low cost, durability, and ease of maintenance. The durability of hard VCT may be comparable to linoleum, but recycling has until recently been impractical, which is why VCT tile usually ends up in a landfill. However, new technology has allowed VCT to contain increasingly high percentages of recycled content, reduced energy consumption, and waste generation. But vinyl products can, nevertheless, be harmful because their manufacture consumes petroleum and involves the generation of hazardous wastes and air pollution. Important Linoleum attributes include:
• It is made from all natural nontoxic materials, and these natural raw materials are available in abundance.
• It does not contain formaldehyde, asbestos, or plasticizers.
• Very durable, often lasting for 25–40 years; this helps reduce waste associated with the frequent replacement of flexible vinyl flooring.
• It is 100% biodegradable at the end of its useful life.
• It is resilient, quiet, and comfortable.
• Linoleum can be 100% recycled. As a common alternative to incineration, linoleum can be safely added to landfill refuse sites, where natural decomposition takes place.
• It is easy to clean and maintain, using gentle detergent with a minimal amounts of water. However, Linoleum floors can be kept in satisfactory condition for long periods without the need for major maintenance.
• While its resistance to temporary water exposure makes it suitable for use in kitchens, its sensitivity to standing water is a concern for use in bathrooms.
• Its natural bactericidal and antistatic properties help control the presence of dust and dirt and the subsequent growth of household mites and/or bacteria.
• It contains virtually no trace of toxic material and therefore very low VOC emissions (no off gassing) when installed with appropriate adhesives, and is thus naturally beneficial to air quality.
• Square-foot cost may be comparable to high-quality flexible vinyl flooring, although flexible vinyl is commonly replaced within 10 years (as opposed to 25–40 years for linoleum) and is toxic to manufacture; it is neither biodegradable nor recyclable.
• It is the same color all the way through, which permits gouges and scratches to be buffed out, reducing long-term costs and waste.
Linoleum is also considered to be a rapidly renewable resource, which has environmental advantages over finite raw material and long-cycle renewable resource extraction.

6.7.5. Straw-Bale Construction

Straw and reeds have been used as building materials in the Middle East for thousands of years (Fig. 6.15). Today, Straw-bale building consists of stacking a series of rows of compressed blocks (bales) of straw (often in running bond), on a raised footing or foundation, with a moisture barrier between. This can be implemented as fill for a wall cavity (nonload-bearing) or as a structural component of a wall in which the bales may actually provide the support for openings and roof (load bearing). The most common nonload-bearing approach is using a post-and-beam framework that supports the basic structure of the building, with the bales of straw being employed as infill (serving mainly as insulation and plaster substrate). This method is also the main one that is permitted in many jurisdictions, although many localities now have specific codes for straw-bale construction. Until recently, “field-bales,” bales that were created on farms with baling machines have been used, but lately higher-density “recompressed” bales have come into use that are increasing the loads that may be supported. Whereas field bales may be capable of supporting roughly 600 pounds per linear foot of wall, the high-density bales are designed to support up to 4000 pounds per linear foot. This is particularly important in northern regions, where there is a potential for snow-loading that can exceed the strength of the straw-bale walls.
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Figure 6.15 Illustration of a typical Marsh Arab Mudhif (Guest House) made of reed which is similar to that built in Mesopotamia (ancient Iraq) thousands of years ago by the Sumerians.
In wet climates, it is necessary to apply a vapor-permeable finish that precludes the use of cement-based stucco commonly used on load-bearing bale walls, since the interior and exterior sides of a bale wall is usually covered by stucco, plaster, clay, or other treatment. This type of construction can offer structural properties superior to the sum of its parts. Both load- and nonload-bearing straw-bale designs divert agricultural waste from the landfill for use as a building material with many ecofriendly qualities.
Straw-bale construction is increasing in popularity in many parts of the country, partly because it lends itself well to an owner builder project, so that today there are thousands of straw-bale homes in the United States. However, in designing load-bearing straw-bale buildings, architects and engineers must take into consideration the possible settling of the straw bales as the weight of the roof and other elements compress them. It is also important to ensure that the straw is kept dry, or it will eventually rot. For this reason, it is generally best to allow a straw-bale wall to remain breathable; any incorrectly applied moisture barrier may invite condensation to collect and potentially undermine the structure. Additionally, the skin on the straw-bale walls should be treated to resist infestation of rodents and insects.
Straw bale houses can typically save about 15% of the wood that would normally be needed in a conventionally framed house. However, it should be noted that Straw-bales do not hold nails as well as wood, and thus nailing surfaces need to be provided. Also, because of the specialized work that goes into plastering both sides of straw-bale walls (to provide thermal mass), and the extra expense needed to protect them from moisture, the cost of finishing a straw-bale house sometimes exceeds that of standard construction. Moreover, because Straw-bale walls are thick, they may constitute a high percentage of the floor area which may be problematic on a small site. Nevertheless, the final product often provides excellent value because of the superior insulation and wall depth that is achieved. Advantages of employing straw-bale construction methods include:
• Provides extemporary thermal insulation, thereby enhancing occupant comfort. It is estimated that a well-built straw bale home can save you nearly 75% on heating and cooling costs. Applying interior plaster to straw-bale houses increases the “thermal mass” of the home, which helps to stabilize interior temperature fluctuations.
• Straw-bale provides superior acoustic insulation which is particularly helpful for home owners seeking to block out exterior noise emanating from traffic or airplanes in urban environments.
• Straw-bale is environmentally friendly and does not require toxic treatment, thereby helping chemically sensitive individuals.
• Straw-bales are inexpensive (or free), and owners, builders, and volunteers are able to contribute significantly to labor.
• Straw-bale construction offers much greater fire resistance (roughly three times that of conventional construction).
• Typically, a traditional “stick frame” home of 2 × 6 construction will often have an insulating value of R-14, whereas with a properly insulated roof straw-bale can increase this to an R factor of R-35 to R-50.
• It reduces construction waste which has a positive impact on the environment. The main building material is a waste product, and any excess straw can be used on-site in compost or as soil-protecting ground cover.
• Straw-bale is biodegradable or reusable at the end of its useful life.
• Has potential for major reductions in wood and cement use, particularly in load-bearing straw-bale designs. In a load bearing assembly, the wood in the walls can be completely eliminated, except around the windows.
• Conventional foundations and roofs can be employed with straw bale-buildings.
• Highly resistant to vermin (including termites).
• Provides great potential for aesthetic flexibility from conventional linearity to organic undulation.
• Using straw as insulation means that unhealthy insulation materials cease to be required. For example, fiberglass insulation generally has formaldehyde in it, a known carcinogen will no longer be used. Bale walls also eliminate the use of plywood (which often contains unhealthy glues) in the walls.
As can be deduced from the preceding, straw-bale provides a notable alternative building material that helps to reduce or eliminate many of the environmental problems that plague the environment (Fig. 6.16).

6.7.6. Wheat Board

One of the more popular renewable materials is wheat board, which is a fiber-composite by-product of wheat-straw. This material is environmentally friendly, has no formaldehyde, and can be used to create, among other things, quality furniture and cabinets. Wheat board is a durable material that is produced in 4 foot by 8 foot sheets of various thicknesses and posses superior panel properties compared to wood-based composite panels. It can be painted or laminated with a wide variety of surface treatments, sealed, stained, or varnished. It can also be shaped in a wide variety of designs, and is used in millwork, cabinetry, and finished product applications for a renewable, nontoxic alternative to commercial MDF. It can also provide a sustainable alternative to traditional wood flooring and gypsum walls.
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Figure 6.16 An interior of a residence built of straw-bale. Source: StrawBale Innovations, LLC.
In the past, wheat board has been burned or added to landfills. Today, there are a number of manufacturers that produce wheat board in the United States, Canada, and Europe. It is a viable substitute for wood and benefits the environment by reducing deforestation and also lessening both air pollution and landfill use. In addition to its versatility, using wheat board can also help a building project earn crucial LEED credits for rapidly renewable materials (Credit 6—Rapidly Renewable Resources), recycled content (Credit 4.1/4.2—Recycled Content), and IAQ (Credit 4.1 Low-emitting adhesives and sealants).

6.8. Green Office Equipment

Today the nation is transitioning to a more service focused economy, a large portion of which are small businesses, in which the amount of energy-consuming office equipment will also increase.
This is why for some time now enlightened designers, building owners, and leading edge organizations have been searching for ways to reduce their environmental footprint by becoming greener, both at home and at the work place. Likewise, manufacturers of office equipment are responding to consumer desire for more environmentally sound products. One of the main driving forces behind this trend has been the ENERGY STAR program which was begun by the U.S. EPA in 1992.
Modern research shows that office equipment accounts for approximately 16% of an office’s energy use, and buildings generally contribute about 40% of U.S. CO2 emissions, and therefore even minor changes at the office can potentially have a significant impact. And although the energy component generally represents about 30% of operating expenses in a typical office building, thereby making it the single largest and most manageable operating expense in the provision of office space, many facility operators unlike their enlightened counterparts, nevertheless, fail to focus on the energy-consuming office equipment or appliances when they consider energy consumption. Instead they unwittingly focus on building operations such as lighting and air-conditioning and its shell components.
People often do not realize that the cost of energy to operate office equipment or an appliance over time can cost substantially more than the original cost of the equipment itself. Moreover, choosing the most energy-efficient models available can have a positive impact on the environment while at the same time saving money. Nevertheless, more often than not, building owners and tenants decide to choose the cheapest and least expensive equipment or appliance on the market, which means that the owner/tenant ends up spending the minimum amount up front on an appliance or office equipment, only to find that they are paying through the nose for years to come in recurring monthly energy costs. It is also important that all nonessential electrical equipment (TVs, copiers, computers, VCRs, etc.) be switched off at night or when not in use.
It is no secret that much of the energy and water that appliances and office equipment consume promptly translates into additional fuel being burned at power plants, which in turn contributes to air pollution, and the waste of our limited natural resources. The good news is that continuous technological advances have helped create efficient new appliances and office equipment that can use only one-half to one-third as much energy as those purchased only a decade ago. The Lawrence Berkeley Laboratory reports that the replacement of older appliances and equipment such as refrigerators, dishwashers, clothes washers, thermostats, heating equipment, and incandescent lighting with ENERGY STAR equipment, enough energy and water can be saved to provide an average after tax return on investment (ROI) of over 16%. This is a substantially better return than the stock market. Moreover, in today’s era of escalating energy costs and climate change, energy efficiency has become the most important aspect of greening a business.
In the United States, most retailers carry efficient, durable appliances and office equipment. Appliances and equipment with the ENERGY STAR label are typically preferred, although they are not necessarily always the most efficient of all available models. Nevertheless, ENERGY STAR® products do usually perform significantly better than federal minimum efficiency standards. ENERGY STAR is a label from the U.S. EPA that identifies various energy-saving products in over 60 product categories, including appliances, lighting, office equipment, and consumer electronics. According to a 2002 EPA report, ENERGY STAR–labeled office buildings generally generate utility bills that are 40% less than the average office building. In addition, there are often rebates and/or incentives for the purchase of energy- and water-saving appliances. Inefficient office equipment not only draws power but also emits heat that can contribute to higher cooling bills.
Factors that should be considered when selecting office equipment and appliances:
• Always buy appliances and equipment that use the least energy and preferably are ENERGY STAR–qualified products. The ENERGY STAR label indicates the most efficient light bulbs, computers, printers, copiers, refrigerators, televisions, windows, thermostats, ceiling fans, and other appliances and equipment.
• Install appliances and equipment that use the least water, e.g., low-flow showers, faucets, toilets, urinals, hose valves, etc. (Zero-water urinals, 1-gpf toilets, and 0.5-gmp faucets are all readily available.)
• Choose durable appliances and equipment that meet long-term needs.
• For space and water heating, select natural-gas appliances; gas is often more cost effective and can reduce overall energy, but, like other fossil fuels, it is not a renewable resource.
• Incorporate sealed combustion and direct-vent furnaces and water heaters to increase IAQ.
• Consider using occupancy sensors in offices to minimize unnecessary lighting, as well as “smart” energy-efficient power strips that combine an occupancy sensor with a surge protector; smart power strips will shut down devices (such as monitors, task lights, space heaters, and printers) that can be safely turned off when space is unoccupied. The latest versions can be found with remote control shut-offs, main shut-offs that can power down peripheral equipment, and motion-detecting shut-offs.
• Install low-cost energy monitors that can provide an accurate display of the cost and energy use of individual equipment. Research shows that this step alone can lead to energy savings of up to 40%.
By using green office equipment, there is also the potential to achieve LEED credit points. For example, for existing buildings the requirements for electronics can be found in the MR 2.1 section under “Sustainable Purchasing: Durable Goods, Electric,” which states:

One point is awarded to projects that achieve sustainable purchases of at least 40 percent of total purchases of electric-powered equipment (by cost) over the performance period. Examples of electric-powered equipment include, but are not limited to, office equipment (computers, monitors, copiers, printers, scanners, fax machines), appliances (refrigerators, dishwashers, water coolers), external power adapters, and televisions and other audiovisual equipment.

As for residential construction, ENERGY STAR offers homebuyers many of the features they desire in a new home, in addition to the energy-efficient improvements that deliver better performance, greater comfort, and lower utility bills. To earn the ENERGY STAR label, a home is required to meet strict guidelines for energy efficiency as set by the U.S. EPA. Such homes are typically 20 to 30% more efficient than conventional homes.

6.9. Forestry Certification and Certified Wood

Forest certification was launched more than a decade ago to help protect forests from destructive logging practices. It involves the green labeling of companies and wood products that meet specific standards of “sustainable” or “responsible” forestry, while at the same time providing a means for independent organizations to develop standards of good forest management and independent auditors to issue certificates to forest operations that comply with those standards. The intention is therefore to reflect a seal of approval and a means of notifying consumers that a wood or paper product comes from forests managed in accordance with strict environmental and social standards. For example, a person shopping for wall paneling or furniture would seek a certified forest product to ensure that the wood was harvested in a sustainable manner from a healthy forest and not procured from a tropical rainforest or the ancestral homelands of forest-dependent indigenous people.
The primary purpose of forest certification is that it provides market recognition for forest producers who meet a set of agreed-upon environmental and social standards. The importance, therefore, of this certification is that it verifies that the forests are well managed, as defined by a particular standard, and ensures that certain wood and paper products come from responsibly managed forests. This is particularly important today since current forestry practices have a multitude of negative effects on the environment such as soil erosion and loss of wildlife habitat.
The Intent of the LEED Certified Wood credit here is to encourage such environmentally responsible forest-management programs. The Green Globes rating system, unlike the LEED rating system, does not have an FSC-only policy. Moreover, there has been much controversy relating to certified in the LEED Rating System and LEED encountered considerable criticism.
In response to the USGBC’s recently released new rating system LEED 2012, which took effect in 2012, the American Forest Foundation (AFF) states that while recognizing the significance of the proposed changes, it believes that the story for wood remains unchanged and the increase recognition of American Tree Farm System wood remains unchanged. AFF believes that “While wood is an energy-efficient, renewable, carbon sequestering material, LEED has done very little to promote the environmental benefits of wood or to encourage builders to choose wood products—essentially blocking wood from the growing green building market.” LEED has also been at odds with the National Lumber and Building Material Dealers Association (NLBMDA) regarding certifications. Earlier rewrites of the certified wood policy in the LEED rating systems unfortunately failed to get a two-thirds majority votes from USGBC members to become a policy. Without a two-thirds majority, the policy failed to pass under LEED rules, and the certified wood credits will remain unchanged. Melissa Harden, a Public Affairs Manager at AFF, says that, “Builders and architects can collect few credits under LEED for using wood, and the credits that are related to wood products are even more restrictive. For example, under the current LEED system, the forest certification credit does not recognize the two largest forest certification standards in North America, the American Tree Farm System and the Sustainable Forestry Initiative, only wood certified by the FSC is recognized. LEED 2012 is even more restrictive in only recognizing ‘FSC Pure’ certified wood products. Very few North American wood products are certified as FSC Pure.” Harden goes on to say that “While LEED 2012 does offer some new changes with seeming potential for increased recognition of wood products, these new changes come with additional questions. For example, LEED 2012 would allow materials, like wood, to achieve recognition through performance-based Life Cycle Assessment (LCA) and Environmental Product Declarations (EPDs).” And although the LEED 2012 recognizes products that are “bio-based,” they rely on the U.S. Department of Agriculture’s (USDA) definition and database of BioPreferred products. USDA’s BioPreferred program currently does not include products with a mature market—therefore including the majority of paper and wood products.
The criteria for LEED certified wood credits continue to change, and it is best to be constantly updated by checking with the USGBC website. Previously, LEED awarded credit to projects that used wood certified to the standards of the FSC for at least half of their wood-based materials. The USGBC has now purportedly broadened the credit to recognize any forest-certification program that meets its criteria. The change is partly in response to criticism that LEED favors one forest-certification program, FSC, over others—in particular, the Sustainable Forestry Initiative (SFI), a rival to the FSC that is portrayed by some environmentalists as being less rigorous. Nevertheless, the revision brings the credit into line with a trend in LEED toward using transparent criteria to determine which third-party certification programs to recognize.
At present the FSC, remains the only certification program granted a “certified wood credit” in the LEED system, although LEED claims that it will recognize wood certification programs that are found to be compliant with the benchmark. On the other hand, wood certification programs that are not found to be in alignment with the benchmark would have a clear and transparent understanding of what modifications are needed to receive recognition under LEED. A number of other programs, including SFI and the Canadian Standards Association (CSA), may face some difficulty with parts of the LEED benchmark system to receive certification.
In recent years, many progressive companies have decided whenever possible to preferentially buy wood and paper from FSC-certified suppliers, although they still use products from other sources to meet their needs. According to the USGBC, homebuilders can currently earn up to 6.5 points out of a possible 136 for using FSC-certified wood. Specifically, they can earn a half point each for using FSC-certified wood in:
• Exterior wall framing
• Exterior wall siding
• Flooring
• Floor framing
• Interior wall framing
• Decking
• Cabinets
• Counters
• Doors
• Trim
• Window framing
• Roof framing
• Sheathing
The SCS has emerged as a global leader in certifying forest-management operations and wood-product manufacturers. It first developed its Forest Conservation Program in 1991, and in 1996 the FSC accredited it as a certification body, enabling it to evaluate forests according to the FSC Principles and Criteria for Forest Stewardship. Through a well-developed network of regional representatives and contractors, SCS provides timely and cost-effective certification services globally. Implementation requirements to achieve the LEED credit include:
• A minimum of 50% of wood-based materials and products used which are certified in accordance with an accredited certifier (e.g., FSC) meeting these principles and criteria for wood building components such as framing, flooring and subflooring, wood doors, etc.
• Based on cost of sustainable wood products as determined by the ratio of total cost of wood material purchased for the project, unlike previous credits which are based on total materials purchased.
• MEP and elevator equipment to be excluded.
• Furniture may be included in calculation.
• Contractor does not require the certification number but supplier does.
To receive the new pilot credit, LEED projects must validate that, based on value, at least 10% of nonstructural products meet any of the following requirements:
• Product environmental claims to be verified by a third party
• Products are certified to third-party multiattribute performance standards
• Product manufacturer completed a LCA report or a third-party verified Environmental Product Declaration for the product.
Many thought that the certified wood controversy had ended last December with USGBC’s decision to keep the FSC as the only wood that gets a point for being sustainably harvested. However, a new and very confusing controversial credit has recently been introduced that appears to get a foot in the door for other certification systems. It was recently noted in a press release from UL Environment, which does third-party certification. They explain that the credit is designed to promote use of certified products.
The recently released pilot credit will be used as a “testing ground” or “trial run” credit before its formal adoption into the LEED rating system. This new pilot credit is important to the sustainable building community because certified products provide a mechanism for market transformation as it awards points for improving performance, transparency, and evaluation of the environmental impact of products and materials. The President of UL Environment, Steve Wenc, echoes this, “This move toward increased performance, transparency, authenticity and third-party verification of manufacturers’ claims will help transform the market.” We have yet to see if it does.

6.10. Life-Cycle Assessment and Life-Cycle Cost Analysis of Building Materials and Products

LCC analysis (LCCA) is discussed in greater detail in Chapter 10.

6.10.1. Life-Cycle Assessment

LCA, also known as life-cycle analysis, is the analysis method most directly related to sustainability. It is a technique for assessing environmental impacts associated with all the stages of a product’s life from cradle-to-grave. “Cradle-to-grave” begins with the extraction of raw materials from the earth to create the product through materials processing, manufacture, distribution, use, repair and maintenance, and disposal or recycling, thus ending at the point when all materials are returned to the earth. LCA, therefore, is a tool that takes into account the entire life cycle of a product. It assesses the many stages of a product’s life from the point of view that they are interdependent, meaning that one operation leads to the next.
An important characteristic of LCA is that it enables the estimation of the cumulative environmental impacts emanating from all stages in the product life cycle, often including impacts not considered in more traditional analyses (e.g., raw material extraction, material transportation, ultimate product disposal, etc.). Inclusion of these impacts throughout the product’s life cycle provides for a more accurate assessment of a materials true environmental impact and allows LCA to offer a more complete view of the environmental features of the product or process and a fundamentally improved picture of the true environmental compromises in product and process selection. It also takes into account any resale or salvage value recovered during or at the end of the time period examined. This type of analysis allows for comprehensive and multidimensional product comparisons.

6.10.2. Life-Cycle Cost Analysis

According to the National Institute of Standards and Technology (NIST) LCC is defined as “the total discounted dollar cost of owning, operating, maintaining, and disposing of a building or a building system” over a period of time. LCC is therefore an economic evaluation methodology for assessing the total cost of acquiring, owning, and operating a facility over a period of time and takes into consideration relevant costs of alternative building designs, systems, components, materials, or practices in addition to the multiple impacts on the environment (both positive and negative) that building materials and certain products have. LCCA can prove especially useful when comparing project alternatives that fulfill similar performance requirements but differ with respect to initial costs and operating costs, so that one can be selected for maximum net savings. One of the advantages of LCCA is that it can be applied to both large and small buildings as well as to isolated building systems. However, LCCA is not helpful for budget allocation.
Whenever possible, anticipate and determine from the outset the potential health and safety issues that may emerge during the construction, occupation, maintenance, alteration, and disposal of the facility. Many astute building owners apply the principles of LCCA in decisions they make regarding construction or improvements to a facility. While initial cost has always been an important factor in the decision-making process, it is only one factor of several that impact the final decision.
Related to LCA, LCC measures the opportunity cost of one investment versus another alternative and provides data as to which might provide a better ROI. LCC provides a systematic evaluation of financial ramifications of a material, a design decision, or a whole building, and unlike a simple payback analysis, the LCC examines both the initial cost of a project, as well as the expected operations, maintenance, financing, useful life, and any salvage value that the project may have at the end of its life. LCC’s tools can also help calculate future factors such as payback period, cash flow, present value, internal rate of return, and other financial criteria. It can then calculate a present value of the future investment using a discount rate percentage that is specific to the investor’s requirements. This can go a long way toward comprehending how a modest up-front cost for environmentally preferable materials or design features can provide a very sound investment over the life of a building.
Lowest life-cycle cost is considered the most straightforward and easy-to-interpret system of economic evaluation. There are other commonly used measures available, such as internal rate of return, savings-to-investment ratio, net savings (or net benefits), and payback period. If the same criterion and length of study period are used, then these systems are all compatible with the lowest LCC measure of evaluation. Quantity surveyors, architects, cost engineers, and others might choose any or several of these techniques to evaluate a project. The approach to making cost-effective choices for building-related projects can be quite similar whether it is called cost estimating, value engineering, or economic analysis. Open-book accounting, when shared across the whole project team, helps everyone to see and appreciate the project’s actual costs. The LCCA should typically be performed early in the design process while there remains an opportunity to refine or modify the design in a way that would reduce LCCs.
Sieglinde Fuller of the NIST says that “The first and most challenging task of an LCCA, or any economic evaluation method for that matter, is to determine the economic effects of alternative designs of buildings and building systems and to quantify these effects and express them in dollar amounts.” Fuller also believes that when viewed over a 30-year period, initial building costs have been shown to generally account for approximately just 2% of the total, while operations and maintenance costs equal 6% and personnel costs reflect the lion’s share of 92% (Source: Sustainable Building Technical Manual/Joseph J. Romm, Lean and Clean Management, 1994).
A variety of building-related costs are associated with acquiring, operating, maintaining, and disposing of a building or building system. These costs typically fall into one of several categories (see Chapter 10) including:
• First costs: purchase, acquisition, construction costs
• Operation, maintenance, and repair costs
• Fuel costs
• Replacement costs
• Residual values: resale or salvage values or disposal costs
• Finance charges: loan interest payments
• Nonmonetary benefits or costs
It is not necessary to include costs that are minor and insignificant in amount or costs within each category that are irrelevant to making a valid investment decision. For relevancy, costs should vary from one alternative to another. Significance is achieved when the costs are large enough to make an appreciable difference in the LCC of a project alternative. For calculation purposes, costs are entered as base-year amounts in today’s dollars. The LCCA method is then applied which accelerates these amounts to their future year of occurrence and then discounts them back to the base date to convert them to current dollar values.
Of note, detailed construction cost estimates are not required for preliminary economic analyses of alternative building designs or systems. Detailed estimates are usually unavailable until the design is fairly advanced and the possible contingency for cost-reducing modifications has been missed. LCCA can be repeated throughout the different stages of the design process whenever more detailed cost information becomes available. To start with, construction costs may be estimated by referencing historical data from similar facilities, or they can be estimated using government or private-sector cost-estimating guides and databases.
Detailed cost estimates rely mainly on cost databases such as the R. S. Means Building Construction Cost Database. They are usually prepared at the submittal stages of design and are based on quantity takeoff calculations. There are also several well-known testing organizations such as ASTM International and the NIST as well as various trade organizations that have reference data available for materials and products they represent or have tested. To avoid or minimize cost overruns, the discerning owner/developer needs to have:
• A complete sustainable design that meets planning and statutory requirements and one that will not later necessitate modification
• A project brief that is comprehensive, unambiguous, and consistent
• Green goals that are appropriate and unlikely to be subject to modification during the course of the project
• A coordinated sustainable design that from the beginning takes into account factors such as maintenance, health and safety, IAQ, etc.
• An uncomplicated payment mechanism that incentivizes the parties to achieve common and agreed objectives
• Clear leadership with a qualified project team and appropriate management controls in place
• Project estimates using BIM technology or similar to provide realistic and comprehensive cost estimates
• An appropriate risk allocation and contingency that is clear and unambiguous

6.11. Third-Party Certification

The LEED third-party certification program is an internationally recognized green building certification system and benchmark for the design, construction, and operation of high-performance green buildings, and that a building or community was designed and built employing strategies and methods intended to improve performance in metrics such as energy savings, water efficiency, and improved indoor environmental quality, etc. According to Alice Soulek, Vice President of LEED development, “Third-party certification is the hallmark of the LEED program,” and “Moving the administration of LEED certification under GBCI will continue to support market transformation by delivering auditable third-party certification. Importantly, it also allows UGSBC to stick to the knitting of advancing the technical and scientific basis of LEED.”
Moving the administration of the LEED certification process to the Green Building Certification Institute (GBCI), a nonprofit organization established in 2007 with the support of USGBC, was a wise decision and is having far-reaching positive ramifications for the USGBC and its influential LEED rating systems. Working together with the selected certification bodies, GBCI is now in a better position to deliver a substantially improved, ISO-compliant certification process that will continue to grow with the green building movement.
USGBC has decided to outsource LEED certification to independent, accredited certifiers overseen by GBCI. In that respect, the USGBC’s Leadership in Energy and Environmental Design (LEED) v3 has announced the names of the certification bodies for the updated LEED Green Building Rating System. The companies are well known and respected for their role in certifying organizations, processes, and products to ISO and other standards. A list of the members can be found in Chapter 2, Section 2.3.5. This development in the certification process has been undertaken as an integrated part of a major update to the technical rating system that was put in place as LEED 2009. The update will also include a comprehensive technology upgrade to LEED Online aimed at improving the user experience and expanding its portfolio-management capabilities.
To acquire LEED credits, third-party testing and certification are required, so as to provide an independent analysis of manufacturers’ environmental performance claims, based upon established standards. This provides building owners and operators with the tools required to have an immediate and measurable impact on their buildings’ performance. Sustainable building strategies should be considered early in the development cycle. An integrated project team will include the major stakeholders of the project, such as the developer/owner, asset and property-management staff, BIM manager, architect, engineer, contractor, and landscape architect.
Making choices based on third-party analysis is often easier than LCA, but it is vitally important to determine the independence, credibility, and testing protocols of the third-party certifiers. Michelle Moore, senior vice president of policy and public affairs at USGBC, says, “We believe in third-party certification,” and “the USGBC provides independent third-party verification to ensure that a building meets these high performance standards. As part of this process, USGBC requires technically rigorous documentation that includes information such as project drawings and renderings, product manufacturer specifications, energy calculations, and actual utility bills. This process is facilitated through a comprehensive online system that guides project teams through the certification process. All certification submittals are audited by third-party reviewers.” Moore also believes that the separation of LEED from the certification process will bring LEED into alignment with norms established by the ISO for certification programs.
For healthy IAQ, green-building materials and methods should typically have zero or low emissions of toxic or irritating chemicals and be moisture, and should also be mold resistant. Green materials and products are typically manufactured with a low-pollution process from nontoxic components, have low maintenance requirements, and do not require the use of toxic cleansers. This may explain why most green materials do not emit VOCs, particularly indoors, and are free of toxic materials such as chlorine, lead, mercury, and arsenic. While individual products do not carry LEED points, they can, nevertheless, contribute to LEED points. Green-building strategies include the monitoring of indoor pollutants and poor ventilation through the use of radon and carbon monoxide detectors. The use of ozone-depleting gases such as halons and HCFCs are to be avoided.
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