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Home Energy Magazine Online January/February 1995
| Reducing the Embodied
Energy of Buildings |
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by Tracy Mumma
Tracy Mumma is research coordinator with the Center for Resourceful
Building Technology in Missoula, Montana.
Sure you know about improving a building's
energy efficiency by reducing its operating energy. But what about recognizing
or reducing the embodied energy of structures?
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One of the major
uses for energy is building construction and operation. According to the
Environmental Resource Guide, produced by the American Institute
of Architects, more than 30% of the energy consumed in the United States
goes to making and maintaining buildings. This includes both operating
energy--the energy required for space heating and cooling, lighting, refrigeration,
water heating and other building functions--and energy embodied in the
physical structure.
Most people are familiar with the concept of
improving the energy efficiency of buildings by reducing the operating
energy they use--especially if they've been reading Home Energy. It's
a common claim that energy-efficiency measures can reduce the operating
energy of an individual building by 60% or more. Comparatively little attention
has been focused, however, on recognizing or reducing the embodied energy
of structures.
Embodied energy, or "embedded energy,"
is an assessment that includes the energy required to extract raw materials
from nature, plus the energy used in primary and secondary manufacturing
activities to provide a finished product. There is embodied energy in any
processed product, from a drinking cup to a car. In embodied energy terms,
buildings represent a huge, relatively long-duration energy investment.
Every building is a complex combination of many
processed materials, each of which contributes to the building's total
embodied energy. The energy required to extract and process the raw material
for an individual component, as well the energy used to transport the finished
product to the job site and install it, all become part of the embodied
energy cost of the completed structure. Furthermore, energy involved in
maintaining an individual building component, and finally removing it and
recycling it or otherwise disposing of it at the end of its useful life,
can all be part of the embodied energy equation for a particular building
material, depending on how the embodied energy is quantified.
As the operating energy required for buildings
declines, the embodied energy they represent becomes a more significant
percentage of the total energy buildings use. In coming years more efforts
will probably be directed toward measuring and reducing the amount of embodied
energy in buildings.
An Inexact Science
The quantification
of embodied energy for any particular material is an inexact science, requiring
a "long view" look at the entire manufacturing and utilization
process, and filled with a large number of potentially significant variables.
Consequently, the complexity of embodied energy calculations is frustrating
even for scientists, and it is easy for the individual homeowner, builder,
designer or government specifier to become discouraged at the difficulty
of obtaining accurate figures. Fortunately, precise figures are not absolutely
necessary for informed decisions on which building materials to use in
order to lower the embodied energy in a structure. Builders need only recognize
the potential differences in relative embodied energy to make wise material
and system choices.
Part of the challenge of assessing and making
decisions based on embodied energy is the lack of current data. The "definitive"
U.S. study on embodied energy was produced under the auspices of the Energy
Research and Development Administration and dates from December 1976. Many
of the statistics it includes are of 1967 vintage, and most current papers
and references on embodied energy still cite data drawn from this old study.
While some of the data may still be relevant, the tremendous advances in
processing technology and recycling during the past 20 years limit the
applicability of this information. Tools, transportation, and installation
methods have changed, and most significantly, some building materials in
widespread use today didn't even exist at the time the report came out.
Fortunately, some researchers in other countries haven't let embodied energy
research lag as much as the United States has.
The Canadian Mortgage and Housing Corporation,
and SAR Engineering, have developed a computer program called "Optimize"
that is designed to estimate the embodied energy, lifecycle energy, and
environmental impact of a house. Figures from the creators of the Optimize
program provide the estimate that for a "standard house in Toronto
with a 40-year life," the total embodied energy is 2,352 Gj (One gigajoule
is equivalent to about 1 million Btu) The total operating energy over 40
years is 9,060 Gj, which results in expected operating energy of approximately
226 Gj per year. This means that a typical house will exist and operate
for ten years before the total operating energy starts to outstrip the
embodied energy contained in the building components. The embodied energy
of a house is not static, either. Very few houses go through an entire
40-year life span without undergoing remodeling projects that involve tearing
out old materials and installing new ones, further increasing the embodied
energy contained within a house.
Estimates by Ray Cole of the University of British
Columbia's School of Architecture also compare embodied energy with operating
energy. Cole's figures relate to a 3,750 ft2 ranch-style home,
constructed in either conventional or energy-efficient style.1
The energy-efficient version of this house includes R-42 ceilings, 226
walls, additional glazing on the south elevation, and added thermal mass.
As in the other Canadian study, Cole's figures reveal an embodied energy
for both versions of the house that is equal to several years' worth of
heating energy, which is the major component of home operating energy in
Canada (see Table 1). According to Cole's data,
it follows that the more operating-energy efficient the house is, the larger
percentage embodied energy will be of the structure's total energy.
Another study, conducted by Andrew Buchanan and
Brian Honey of the University of Canterbury in New Zealand (which has a
similar range of climates to California) concluded that the energy required
to manufacture a house is of a similar order of magnitude to the energy
required to heat the house over a 25-year life (see
Table 2). That study drew upon research conducted at New Zealand's
Energy Research and Development Committee in 1983, which among other things
estimated "energy coefficients" for various building materials
(see Table 3).
Table 1. Embodied Energy versus Operating
Energy
| Home type, location |
Heating Energy
MM Btu/year
(Gj/year)
|
Embodied Energy
MM Btu
(Gj)
|
Embodied Energy
in years of
heating energy
|
| Conventional, Vancouver |
101 (107)
|
948 (1,000)
|
9.4
|
| Energy-efficient, Vancouver |
57 (60)
|
1019 (1,075)
|
17.9
|
| Conventional, Toronto |
136 (143)
|
948 (1,000)
|
7.0
|
| Energy-efficient, Toronto |
78 (82)
|
1019 (1,075)
|
13.1
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Table 2. Energy Use Resulting from
Construction of Three Types of Houses in New Zealand
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|
House type
|
|
|
Maximum
impact
|
Most
common
|
Minimum
impact
|
| Floor |
Concrete
|
Concrete
|
Timber
|
| Exterior walls |
Brick
|
Concrete block
|
Weatherboard
|
| Roof |
Corrugated galvanized steel
|
Corrugated galvanized steel
|
Concrete tiles
|
| Framing |
Steel
|
Timber
|
Timber
|
| Windows |
Aluminum
|
Aluminum
|
Wood
|
| Embodied Energy (Gj) |
520
|
372
|
215
|
| Annual space heating requirements (Gj per year) |
32.5
|
5.4
|
1.9
|
| Space heating requirements over 25 years |
812
|
135
|
47
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Table 3. Energy Required to Manufacture
Some Common Building Materials
| Material |
Unit
|
Energy Coefficient
Mj per unit
|
| Timber, rough |
m3
|
848
|
| Timber, air-dry, treated |
m3
|
1,200
|
| Timber Glulam |
m3
|
4,500
|
| Timber, kiln-dry, treated |
m3
|
4,692
|
| Timber, form work |
m3
|
283
|
| Plywood |
m3
|
9,440
|
| Building paper |
m2
|
7.5
|
| Gypsum board |
m3
|
5,000
|
| Glass |
kg
|
31.5
|
| Structural steel |
kg
|
59
|
| Aluminum |
kg
|
145
|
| Fiberglass batts |
kg
|
150
|
| Asphalt, strip shingle |
m2
|
280
|
| Source: "Energy and carbon
dioxide implications of building construction," by Andrew H. Buchanan
and Brian G. Honey, Energy and Buildings, 20 1994. Elsevier Science,
Inc, 655 Avenue of the Americas, New York, NY, 10010. Tel: (212)633-3764;
Fax: (212)633-3764. |
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Comparing Apples and Oranges
Even with computer programs and sample data,
embodied energy of entire buildings--or even of individual materials--is
difficult to quantify, since production and installation of building components
is a lengthy and complex process involving many variables. No measurement
standards exist, either. In practice, each individual researcher studying
embodied energy has a different methodology for quantifying the embodied
energy of materials. Some calculations fail to take disposal costs of a
material into account, and little is known about the long-term disposal
costs for many materials, especially as landfill siting becomes more difficult
and the cost of containing leachate from existing landfills rises. Some
measurements don't include transportation, or consider only part of the
extraction energy involved in producing a material.
Some researchers differentiate between the embodied
energy of the house "as built" and "life-cycle embodied
energy" that includes the maintenance, repair, demolition and disposal
of the structure. (This life-cycle embodied energy is not the equivalent
of life-cycle analysis, which includes environmental costs such as resource
depletion and pollution as a way of internalizing the costs of present
externalities. Life-cycle embodied energy only measures energy use, not
energy costs or other environmental costs.)
Comparing the various figures provided on different
materials is akin to comparing the proverbial apples and oranges. And as
though the figures for materials weren't confusing enough, calculations
of embodied energy will be different for each job site. Factors such as
distance of the site from manufacturer, distance from railhead, and even
the distance that tradespeople must travel to and from the site during
construction, are all part of the embodied energy equation. Furthermore,
the type of fuel used in processing and transporting materials can affect
the amount of embodied energy contained in the final product. Two products
of identical appearance may have different embodied energies, depending
on where and how they were made, and where and how they will finally be
used.
Given these complexities, builders bent on reducing
energy consumption should learn as much as possible about materials options,
and consider the probable relative embodied energies of these materials.
Fortunately, a few general rules of thumb apply:
The embodied energy in recycled building materials
is generally less than that contained in new materials. Recycling provides
easily obtainable manufacturing feedstock. There is very low extraction
energy associated with recycled materials. Although manufacturing with
recycled feedstocks can involve transporting, cleaning, and sorting the
recycled materials, this often requires far less energy than manufacturing
from a virgin resource that must be extracted and refined before use (see
Table 4.
Table 4. Potential Production Energy
Savings of Recycled Materials
|
Energy required
to produce from
virgin material
(million Btu/ton)
|
Energy saved
by using
recycled materials
(percentage)
|
| Aluminum |
250
|
95
|
| Plastics |
98
|
88
|
| Newsprint |
29.8
|
34
|
| Corrugated Cardboard |
26.5
|
24
|
| Glass |
15.6
|
5
|
| Source:Roberta Forsell Stauffer
of National Technical Assistance Service (NATAS), published in Resource
Recycling, Jan/Feb 1989). |
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While these figures will vary with the quality
and quantity of recycled feedstock, as well as with the efficiency of the
processing equipment used, they show that using recycled materials as raw
material for manufacturing can result in substantial energy savings for
at least a few frequently used materials. Figures provided by Resource
Conservation Consultants in Portland, Oregon, cite energy savings of 88%-95%
for use of recycled copper, and 70% for recycled rubber, among significant
savings for other materials.
Reusing materials, or even reusing entire
buildings by retrofitting them, reduces the total amount of embodied energy
even more than using recycled materials. Although reusing materials often
requires intensive cleaning, and frequently entails repair, it represents
a means of attaining substantial embodied energy savings. Builders can
save embodied energy by incorporating as many salvaged and reused building
components as practical.
Meanwhile, the embodied energy of a manufactured
material can be lowered by reducing the energy required at any stage
of production. For instance, the energy of lumber is greatly reduced
by air drying it instead of kiln-drying it. Even if the lumber is harvested,
milled, and transported by the same means, lumber that is air-dried has
only about one-third as much embodied energy as kiln-dried lumber, measured
in millions of Btu per thousand square feet.2
Choose durable, long-lived building materials.
Durable materials, especially those with low maintenance requirements,
tend to have a lower embodied energy than disposable or short-lived materials.
Although less-durable materials may not involve as much energy in their
manufacture, the need for frequent replacement, combined with the need
to dispose of the product following removal, results in a higher total
embodied energy over the life of the structure.
Use indigenous, or local, materials.
Besides lower transportation energy costs, indigenous materials usually
involve less processing energy than conventional construction materials.
Using materials such as local stone for patios involves less embodied energy
than using concrete or treated wood for patios and decks. Some builders
build entire structures of indigenous materials, such as adobe, straw bales,
straw-clay mixes, or rammed earth (see "From
the Southwest, Unconventional Insulations," HE Mar/Apr '93
p.11).
Common Sense Decisions
After all the rules
of thumb have been applied, the best hope of reducing embodied energy in
buildings comes down to the reasoned actions of responsible individuals.
Designers, builders, homeowners, manufacturers and policy makers can act
to reduce the level of embodied energy in building materials in a number
of ways.
First, encourage improved efficiency in manufacturing,
transportation and installation. Second, look for additional and updated
research on the embodied energy of building materials. Only with more current
and standard information can materials be compared with one another to
determine the most energy-efficient alternative. Beware of comparing results
from studies that may have different parameters for measuring embodied
energy. Finally, even before final evaluations of embodied energy are available
for all materials, identify building products with relatively lower
embodied energy.
As operating energy is reduced through energy
efficiency measures, embodied energy comes to represent an increasingly
significant percentage of the total energy consumed by a structure. Only
by addressing both components of energy usage--the operating and the embodied--can
we comprehensively address the vast amount of energy consumed by buildings.
Notes
1. This information first appeared in Environmental
Building News. See "Embodied Energy--Just What is it and
Why Do We Care" by Nadav Malin in the May/June 1993 issue. Environmental
Building News R.R. 1 Box 161, Brattleboro, VT 05301. Tel: (802)257-7300;
Fax: (802)257-7304.
2. See "Assessing Sheathing Options,"
in the Sept/Oct 1992 issue of Environmental Building News.
Further Reading
Environmental Choices for Home Builders and
Renovators, published by The Canadian Home Builders' Association, Canada
Mortgage and Housing Corporation and Ontario New Home Warranty Corporation.
Ottawa, Ontario, January 1994. Contact: Canadian Homebuilders Association,
150 Laurier Ave West, Suite 200, Otowa, Ontario, Canada, K1P 5J4 Tel: (613)230-3060.
Environmental Resource Guide, The American
Institute of Architects, 1735 New York Ave NW, Washington D.C. 20006. Tel:
(202)626-7300; Fax: (202)626-7421.
"Energy and Carbon Dioxide Implications
of Building Construction," by Andrew H. Buchanan and Brian G. Honey,
Energy and Buildings, 20 1994. Elsevier Science Inc, 655 Avenue of the
Americas, New York NY, 10010. Tel: (212)633-3764; Fax:(212)633-3764.
"Environmental Impact of Energy Conservation
in Buildings--Real Case Studies," by Peter Suter, ETH Zuerich, Energy
and Environment Division, Lawrence Berkeley Laboratory, 1 Cyclotron Road,
Berkeley, CA 94720. Tel: (510)486-7438; Fax: (510)486-6996.
"The Estimation of Energy Consumption and
CO2 Emission Due to Housing Construction,"
by Michiya Suzuki, Technology Division, Shimizu Corporation, Tokyo, Japan;
Tatsuo Oka, Faculty of Engineering, Utsunomiya University, Tochigi Prefecture,
Japan; and Kiyoshi Okada, Faculty of Engineering, Utsunomiya University,
Tochigi Prefecture, Japan.
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