reliability of building embodied energy modelling: an analysis of 30 melbourne case studies
TRANSCRIPT
This article was downloaded by: [Radboud Universiteit Nijmegen]On: 03 November 2014, At: 05:27Publisher: RoutledgeInforma Ltd Registered in England and Wales Registered Number: 1072954 Registered office: Mortimer House,37-41 Mortimer Street, London W1T 3JH, UK
Construction Management and EconomicsPublication details, including instructions for authors and subscription information:http://www.tandfonline.com/loi/rcme20
Reliability of building embodied energy modelling: ananalysis of 30 Melbourne case studiesYu Lay Langston a & Craig Ashley Langston aa Faculty of Science and Technology , Deakin University , School of Architecture andBuilding , 1 Gheringhap Street, Geelong, 3217 AustraliaPublished online: 26 Feb 2008.
To cite this article: Yu Lay Langston & Craig Ashley Langston (2008) Reliability of building embodied energymodelling: an analysis of 30 Melbourne case studies, Construction Management and Economics, 26:2, 147-160, DOI:10.1080/01446190701716564
To link to this article: http://dx.doi.org/10.1080/01446190701716564
PLEASE SCROLL DOWN FOR ARTICLE
Taylor & Francis makes every effort to ensure the accuracy of all the information (the “Content”) containedin the publications on our platform. However, Taylor & Francis, our agents, and our licensors make norepresentations or warranties whatsoever as to the accuracy, completeness, or suitability for any purpose of theContent. Any opinions and views expressed in this publication are the opinions and views of the authors, andare not the views of or endorsed by Taylor & Francis. The accuracy of the Content should not be relied upon andshould be independently verified with primary sources of information. Taylor and Francis shall not be liable forany losses, actions, claims, proceedings, demands, costs, expenses, damages, and other liabilities whatsoeveror howsoever caused arising directly or indirectly in connection with, in relation to or arising out of the use ofthe Content.
This article may be used for research, teaching, and private study purposes. Any substantial or systematicreproduction, redistribution, reselling, loan, sub-licensing, systematic supply, or distribution in anyform to anyone is expressly forbidden. Terms & Conditions of access and use can be found at http://www.tandfonline.com/page/terms-and-conditions
Reliability of building embodied energy modelling: ananalysis of 30 Melbourne case studies
YU LAY LANGSTON and CRAIG ASHLEY LANGSTON*
Faculty of Science and Technology, Deakin University, School of Architecture and Building, 1 Gheringhap Street,
Geelong, 3217 Australia
Received 11 May 2007; accepted 1 October 2007
Building design decisions are commonly based on issues pertaining to construction cost, and consideration of
energy performance is made only within the context of the initial project budget. Even where energy is elevated to
more importance, operating energy is seen as the focus and embodied energy is nearly always ignored. For the first
time, a large sample of buildings has been assembled and analysed in a single study to improve the understanding of
the relationship between energy and cost performance over their full life cycle. Thirty recently completed buildings
in Melbourne, Australia have been studied to explore the accuracy of initial embodied energy prediction based on
capital cost at various levels of model detail. The embodied energy of projects, elemental groups, elements and
selected items of work are correlated against capital cost and the strength of the relationship is computed. The
relationship between initial embodied energy and capital cost generally declines as the predictive model assumes
more detail, although elemental modelling may provide the best solution on balance.
Keywords: Accuracy, capital cost, embodied energy, capital cost, modelling.
Introduction
Energy has become a significant issue worldwide.
Greenhouse gas emissions (GGE) and the perceived
threat of climate change (caused by phenomena such
as global warming and ozone depletion) are identified
by Beggs (2002, p. 10) as driving ‘more than any
other issue’ change in energy consumption attitudes.
Since the energy crisis of the mid-1970s attention
has been directed towards strategies that lower operat-
ing energy demand (Robertson, 1991), yet it has
been only recently that the impact of energy embodied
in building materials themselves has come under
scrutiny.
Australia has the highest per capita GGE in the world
(NAEEEC, 1999; Department of Natural Resources
and Environment, 2000; ASEC, 2001). Without
targeted and effective action, these emissions are
projected to grow by 28% from 1990 to 2010
(NAEEEC, 1999). Bell and Fawcett (2000) indicate
that GGE from the Australian construction industry are
substantial and rapidly rising, particularly in the
commercial sector. Buildings consume 40–50% of the
energy and 16% of the water used annually worldwide
(Lippiatt, 1999; Hoglund, 1992; Lam et al., 1992).
Buildings comprise a combination of embodied energy
and operating energy. According to Boustead and
Hancock (1979), embodied energy is defined as the
energy demanded by construction plus all the necessary
upstream processes for materials such as mining,
refining, manufacturing, transportation, erection and
the like, while operating energy is related to issues of
recurrent occupancy and building use. It is now
realized that a focus on operating energy is insufficient
to address either national or international GGE
concerns (Fossdal, 1995). Embodied energy is steadily
increasing (AGO, 1999) owing to a greater use of
energy-intensive materials (such as aluminium, stain-
less steel, coated glass and high strength concrete),
larger buildings, more frequent refurbishment cycles,
more machine utilization in construction processes,
higher transportation energy and the introduction of
new technologies such as photovoltaic cells and
building management systems. Despite this trend, the
routine analysis of embodied energy remains absent
(Treloar et al., 2002).*Author for correspondence. E-mail: [email protected]
Construction Management and Economics (February 2008) 26, 147–160
Construction Management and EconomicsISSN 0144-6193 print/ISSN 1466-433X online # 2008 Taylor & Francis
http://www.tandf.co.uk/journalsDOI: 10.1080/01446190701716564
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
Proper energy analysis during the design process can
no longer be simply overlooked. ASEC (2001, p. 100)
indicate that ‘total energy use has doubled [in
Australia] over the last 25 years […] at a faster rate
than GDP’. The rationale behind this paper firmly lies
with the perceived lack of integration of energy analysis
into current practice. Capital cost still remains the
primary criterion for building procurement decisions
(Brown and Yanuck, 1985; Langston, 1991; Bull,
1992), while other criteria are given less significance
either because of a narrow myopic focus (Ashworth,
1988) or because a suitable multi-criteria technique has
not been satisfactorily identified (van Pelt et al., 1990).
Energy analysis is costly, time consuming and, when
undertaken during the design phase, usually based on a
large number of assumptions (Verbeek and Wibberley,
1996). Even so, it is likely to produce advice that conflicts
with that generated from capital cost estimates (Arnold,
1993). This occurs because energy analysis takes a long-
term view, one that introduces multiple stakeholders and
wider social concerns, rather than merely reflecting
immediacy and profit-centred objectives. It has been
argued over many years (e.g. Stone, 1960; Kirk and
Dell’Isola, 1995; Flanagan and Norman, 1983; Langston
and Lauge-Kristensen, 2002) that costs should also be
accounted over a longer time span. Known as life cycle
costs (LCCs), these comprise both initial (capital) and
recurrent (operating) components that can be aggregated
to give a more realistic picture of the total expenditure
commitment (Fuller, 1982).
The problem essentially is how two criteria, one
measured in financial terms and the other in pure
energy terms, can ever be reconciled to provide clear
building design guidance. It is not commonly under-
stood that the lowest LCC solution will automatically
be the lowest energy solution. In fact, any comparison
of particular material choices will usually indicate that
cost and energy ratios vary widely (Irurah and Holm,
1999). Yet at the level of an entire building this
differential is expected to be less—a view that is
supported to some extent by the manner in which
embodied energy intensities are often determined (i.e.
from national input–output financial tables) and
operating energy interpreted (i.e. incurred cost).
If there is an inherent relationship between energy
and cost that can be exploited to enable better design
solutions to be identified, then it should be possible to
quantify energy directly from an LCC investigation.
The outcomes will naturally be dependent on the
chosen time horizon for the study but will simplify the
process of embodied energy calculation (in particular)
that to date has proved elusive to common practice.
The purpose of this paper is to explore the predictive
accuracy of initial embodied energy modelling based on
capital cost, using data derived from a range of building
types in Melbourne, Australia. From this information, a
better understanding of facilities performance can be
obtained, leading to further insight into the relationship
between energy and cost. The structure of this paper is to
review previous research findings, to outline the method
adopted in this research, to analyse the results, and to
make observations and draw conclusions for practice.
Background
Energy is a vital consideration for the effective design
and operation of the built environment, not only in
Australia, but globally. There is an increasing need for
society in general and the construction industry in
particular to calculate the expected energy performance
of buildings, in terms of both capital (embodied)
energy and operating (recurrent) energy. While operat-
ing energy is fairly simple to quantify, embodied energy
is time consuming, complex and highly dependent on
the chosen measurement algorithm. This problem has
hindered the uptake of energy considerations in
practice that in turn has made it difficult to make
judgments about the appropriate and sustainable
deployment of resources.
Thus if it were possible to routinely produce accurate
estimates of total embodied energy for individual
buildings, then a major impediment to the widespread
use of energy analysis would be overcome. Such a step
forward would lead to significant improvements in the
performance of the Australian construction sector and
in turn the economic and environmental performance
of the nation through the design, construction and
management of facilities that are energy optimized.
There are four types of embodied energy analysis
described in the literature. These comprise process
analysis, statistical analysis, input–output analysis and
hybrid analysis. No method is perfect. Incompleteness
in typical embodied energy analysis is estimated at
around 20% (Treloar, 1997).
The input–output-based hybrid method, as used in
this paper, is described by Crawford (2004; p. 130) as
‘the most sophisticated complete life cycle inventory
assessment method currently available for assessing
environmental impacts associated with building and
building-related products’. Energy analysis using this
method can be defined using a series of equations as
discussed below.
Total life cycle energy LEGJ~IEEGJzREEGJ
zOEGJ
ð1Þ
where:
IEEGJ 5 initial embodied energy;
148 Langston and Langston
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
REEGJ 5 recurrent embodied energy over the
chosen time horizon (t);
OEGJ 5 operating energy over the chosen time
horizon (t).
Total life cycle energy excludes other energy involved
in reusing, recycling and final disposal. Fossil fuels such
as coal, oil and natural gas are responsible for over 90%
of global purchased energy (Chukwuma, 1996) and most
of Australian purchased energy (Lawson, 1995). Primary
energy is reduced by conversion and transmission losses,
resulting in delivered energy to the end user (Crawford
et al., 2002). Total life cycle energy is measured in
primary energy terms so that the total amount of fossil
fuels used directly and indirectly in the manufacture of
the delivered energy provides a complete assessment of
resource depletion and environmental impact (Treloar,
1996; Shen, 1981; Peet and Baines, 1986). The
estimated primary energy factor (primary energy needed
to create one unit of delivered energy) in Victoria is 3.4
for electricity and 1.4 for gas (Treloar, 1997; Treloar
et al., 2001).
Initial embodied energy IEEGJ~DEGJzIEGJ
zOIEGJ
ð2Þ
where:
DEGJ 5 direct energy in construction;
IEGJ 5 indirect energy (modified pathways);
OIEGJ 5 other indirect energy (remaining path-
ways).
Treloar et al. (2001) describe direct energy as a single
pathway related to the main process of construction while
indirect energy comprises upstream multiple energy
pathways. Those multiple pathways that can be quanti-
fied are called modified pathways. Other indirect energy
represents the embodied energy of the remaining path-
ways (sometimes referred to as ‘incompleteness’).
Direct energy DEGJ~DEIGJ=$1000|PP$ ð3Þ
where:
DEIGJ/$1000 5 direct energy intensity of I-O sector
(n);
PP$ 5 project price.
Direct energy is calculated using input–output data
where process analysis data are unavailable (Crawford,
2004). The total energy intensities and direct energy
intensities of the 106 sectors of the Australian economy
are compiled by Lenzen and Lundie (2002) based on
Australian Bureau of Statistics input–output data for
the financial year 1996–97.
Indirect energy IEGJ~QTYunit|EIGJ=unit ð4Þ
where:
QTYunit 5 delivered material quantity;
EIGJ/unit 5 hybrid material energy intensity per unit.
Indirect energy is a factor of delivered quantities of
materials and their energy intensities. Material quan-
tities are converted into delivered quantities using
wastage multipliers derived from Wainwright and
Wood (1981) and Fay (1999). The database of hybrid
material energy intensities compiled by Dr Graham
Treloar is in primary energy terms and comprises
various process data and input–output data also
obtained from the Australian Bureau of Statistics for
the financial year 1996–97.
Other indirect energy OIEGJ~REIGJ=$1000|PP$ ð5Þ
where:
REIGJ 5 energy intensity of remaining paths;
PP$ 5 project price.
Other indirect energy is the energy required to fill the
gap between total multiple pathways and modified
pathways (Crawford, 2005). Treloar (1998, p. 173)
emphasizes that the most crucial task in input–output-
based hybrid analysis is ‘not the modification of direct
energy paths with process analysis data but rather the
inclusion of the remainder of unmodified direct energy
paths to make the framework more comprehensive’. A
sector’s overall total energy intensity in the input–
output model consists of all the pathways’ energy
intensities. The energy intensity of the remaining
pathways is the gap between total energy intensity
and the sum of the modified pathways’ total energy
intensity and the direct energy intensity.
Recurrent embodied energy REEGJ~REGJ
zMEGJzOIEGJ
ð6Þ
where:
REGJ 5 replacement energy over the chosen time
horizon (t);
MEGJ 5 maintenance energy over the chosen time
horizon (t);
OIEGJ 5 other indirect energy over the chosen time
horizon (t).
Recurrent embodied energy consists of the embodied
energy of building materials and systems based on their
life expectancy and maintenance requirements and can
be estimated by sources such as Langston (1994),
Dell’Isola and Kirk (1995), AIQS (2002) and Langston
(2005).
Reliability of building embodied energy modelling 149
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
Method
The selected research method is sampling via case
studies. Case study is an ideal methodology when a
holistic in-depth investigation is needed (Feagin et al.,
1991). It has been used in varied investigations,
particularly in sociological studies but increasingly in
construction. The procedures are robust, and when
followed the approach is as well developed and tested
as any in the scientific field. Whether the study is
experimental or quasi-experimental, the data collection
and analysis methods are known to hide some details.
Case studies, on the other hand, are designed to bring
out the details from the viewpoint of the participants by
using multiple sources of data (Tellis, 1997).
The data for the research are drawn from 30 actual
case studies obtained courtesy of the Melbourne office
of Davis Langdon Australia, a large national quantity
surveying practice. Case studies are located across
Greater Melbourne and are specifically intended to
reflect a broad range of functional purpose. They
represent a ‘random’ mix in that no selection decisions
were applied, including provision of office workspace,
health facilities, residential accommodation, teaching
and laboratory space, retail, hotel accommodation and
a number of specialist uses. Projects comprise both new
construction (73.3%) and redevelopment (26.7%). So-
called residential projects, comprising apartment build-
ings and aged care facilities, account for 23.3% of the
case studies, and the remainder are constructed for
various other commercial uses. One-third of the case
studies are hospitals or healthcare facilities. It should be
noted that no claims are being made that the case
studies are representative of the mix of building stock in
Melbourne (or Australia), yet the variety in the mix
adds confidence that the correlation between energy
and cost is robust and reliable.
Capital cost data and floor areas are obtained direct
from the elemental cost plans prepared by Davis
Langdon Australia. Embodied energy intensities are
estimated from the composite items of work listed in
these documents using the input–output-based hybrid
method (Treloar, 1998; Crawford, 2004). All costs are
adjusted and expressed in fourth quarter 2006 dollars
using published building price indices (BPI) also
supplied by Davis Langdon Australia.
Projects range from 1997 to 2004, and vary in floor
area from 249m2 to 18 821m2 gross floor area (GFA).
The mean floor area is 3749m2 (coefficient of variation
of 110.75%). They comprise a wide range of materials
and standards, some are air-conditioned and some not,
some have fire sprinkler systems, some have loose
furniture and special equipment, and some have
substantial external works.
This mix decreases the likelihood that projects
exhibit similarities in energy and cost performance.
Economies of scale also play a part in larger projects,
which tend to have lower unit costs than identical
designs of smaller size. The mix is therefore effectively
random, enabling a range of statistical techniques to be
applied to the sample.
Table 1 lists the case studies used in this research by
building type. Case studies are identified by a
numerical code, as the name and location of projects
needs to be kept confidential (this is a non-negotiable
agreement made between the researchers and Davis
Langdon Australia).
Data supplied by Davis Langdon Australia comprise
GFA and elemental capital costs based on abbreviated
measured quantities extracted from design cost plans.
The full project cost is presented, including prelimin-
aries, site works and external services, and special
provisions (such as allowances for loose furniture and
equipment), but excluding contingencies, professional
fees, land acquisition costs and goods and services tax.
Capital costs are converted to fourth quarter 2006
prices using a BPI provided by Davis Langdon
Australia. Otherwise no adjustment to capital costs is
undertaken and all unit rates are taken as correct and
reflective of the project given applicable market
conditions at the time. The BPI for fourth quarter
2006 is 175.0 (later indices were not used as they were
still forecasts at the time of analysis).
Embodied energy is determined using a sophisticated
spreadsheet model using an input–output-based hybrid
method that embraces both process analysis data
(where available) supplemented with the input–output
data from published government statistics (1996–97
financial year), extracted and compiled at Deakin
University by Dr Graham Treloar and Dr Robert
Crawford. The basis of this method is described earlier
and reflected in the equations provided. Examples of
the detailed calculations for embodied energy in this
study can be found in Langston (2006).
No allowance has been made for the embodied
energy of labour. This is common practice for
embodied energy analysis despite the fact that labour-
intensive activities have ‘upstream’ consequences.
Furthermore, the energy involved in reusing, recycling
and final disposal of materials is excluded from this
study. The introduction of labour potentially breaks the
close relationship between energy and GGE. This
situation can be traced to the assumption that the
traditional primary energy factors of economic produc-
tion—land, labour and capital—are independent
(Costanza, 1980). Yet a strong case can be made that
these input factors are not independent and that energy
is required for their production (Odum, 1971; Baird
and Chan, 1983). Hill (1978) concludes that human
150 Langston and Langston
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
energy is ignored because the methods for assessing it
are not satisfactorily resolved. The treatment of labour
is therefore controversial.
Results
It is hypothesized that initial embodied energy is
reliably modelled by capital cost, but this reliability
decreases proportionally with the level of detail at
which the model is expected to operate. Linear
regression has been used in this study for two reasons:
to keep the model relatively simple so it can be
understood and applied by practitioners, and to adopt
a consistent approach at all levels of the investigation.
Adjusted r2 takes into account the number of data
points on the regression line. While 30 data points is a
reliable indicator of correlation (hence the difference
between r2 and adjusted r2 is small), fewer data points
see a bigger gap between the two variables. P-values are
calculated to confirm the existence of a relationship
(based on 95% confidence levels), so where p-value is
more than 0.05 no relationship exists. Similarly, where
the value of t-critical for one-tailed relationships is
significantly greater than zero, increased estimating
confidence in the slope coefficient or gradient (m) of
the regression line is provided.
The correlation between initial embodied energy and
capital cost is very strong (r250.9542) and the
discovered regression line is y50.0071x. The result is
presented in Figure 1. Furthermore, statistical analysis
shows a very robust relationship: adjusted r250.9179,
p-value51.12224 and t-statistic535.05.
Provided costs are expressed in fourth quarter 2006
terms, the embodied energy can be derived in minimal
time using the constant (gradient) of 0.0071. This
relationship can be used to help predict embodied
energy based on initial construction cost estimates. The
reliability of this constant is now investigated further.
Table 2 summarizes key correlation outcomes for
each elemental group. It should be noted that the
reliability of alterations and renovations (AR), external
services (XK-XS) and special provisions (YY) is poor
(in fact, coefficients cannot be calculated for YY), and
Table 1 Case study base information (Davis Langdon Australia, Melbourne Office)
Building
IDYear Building type Gross floor area (m2)
1 2003 Residence (new) 1409
2 2004 Residence (new) 450
3 2004 Residence (new) 1791
4 2000 Office (new) 2543
5 2003 Health Centre (redevelopment) 528
6 2003 Hospital (new) 6761
7 2003 Residence (new) 328
8 2003 Information Centre (new) 1223
9 2004 Hospital (redevelopment) 3278
10 2003 Hospital (redevelopment) 3760
11 2004 Library (new) 249
12 2004 Civic Hall (new) 625
13 2004 Primary School (new) 2696
14 2001 Residence (new) 2790
15 2001 Hospital (redevelopment) 5677
16 2000 Hospital (new) 378
17 1999 Hotel (redevelopment) 652
18 2000 Car parking station (new) 5412
19 1998 Hospital (new) 4281
20 1998 Health Centre (new) 787
21 1998 Hospital (new) 1159
22 1999 Hotel (new) 12 930
23 1999 Residence (redevelopment) 18 821
24 1999 University building (new) 10 565
25 1999 Office (new) 4704
26 1999 Hospital (redevelopment) 1345
27 1999 Hospital (redevelopment) 5940
28 1998 University building (new) 2502
29 1998 Residence (new) 5223
30 1997 Hospital (new) 3649
Reliability of building embodied energy modelling 151
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
external alterations and renovations (XX) has no
relationship (p-value50.220). Refer to AIQS (2002)
for full definition of elemental classifications used in
this research.
Table 3 increases detail further to the element level,
again confined to initial embodied energy and capital
cost. More variation in the strength of the energy–cost
relationship is evident. Sanitary plumbing (PD), water
supply (WS), ventilation (VE), special services (SS)
and all site-related elements except roads, footpaths
and paved areas (XR), outbuildings and covered ways
(XB) and external electric light and power (XE) are
unreliable, and external special services (XS) has no
relationship. It is argued that the more detailed
approach, based on elemental groupings or based on
elements, is less likely to reflect actual initial embodied
energy than a single line calculation performed at the
project level.
Values for m in the regression equation (y5mx) can
be used to predict initial embodied energy based on
construction cost (expressed in fourth quarter 2004
dollars) for all elements and groups except external
alterations and renovations (XX) at varying levels of
reliability. Nevertheless, caution should be exercised
when using these values to predict site-related ele-
ments, since the basis of the relationship is linked to the
extent of work involved compared to the GFA of the
building. This relationship can vary quite significantly,
and projects that possess more extreme ratios of work
extent to GFA will lead to over- or underestimation of
Figure 1 Embodied energy vs capital cost correlation
152 Langston and Langston
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
initial embodied energy. But the values for m presented
do provide some indication of the significance of site-
related elements compared to the more usual building
elements.
The figures presented in Table 3 are important. They
underline the falling reliability of element correlations
compared to elemental group correlations, yet provide
support for the obvious link between energy and cost at
most levels of analysis. While the relationship is
undeniable, the strength of the relationship is variable.
Two elements (4.67%) show a very strong value for
adjusted r2 (.0.9), 20 elements (47.62%) show a
strong value (.0.7, but ,0.9), and five show a
moderate value (.0.5, but ,0.7). The remaining 15
elements (11.91%) show a weak value of adjusted r2
(,0.5). Therefore about half of the elements have a
strong energy–cost relationship or better. This is
compared to the 11 elemental groupings (five of these
are also elements included in the previous discussion).
Five groups (45.46%) show a very strong value of r2
(.0.9), two groups (18.18%) show a strong value
(.0.7, but ,0.9), and the remaining four groups
(36.36%) show weak values (,0.5). Bear in mind a
very strong correlation is produced at the overall
project level.
To further illustrate the declining energy–cost
relationship, elements in Building 24 are used as the
data points for regression. For example, one data point
is preliminaries, another is substructure, another is
columns, etc. It should follow that a relationship still
exists, but as can be seen from Figure 2, this relation-
ship is not strong, with an r2 of just 0.5217. Much more
‘scatter’ around the regression line is apparent.
This trend is repeated when the relationship between
energy and cost is tested for a range of common
materials used in construction (extracted from the
embodied energy model developed for this paper).
Table 4 lists these materials, their units of measure-
ment, energy/unit, cost/unit (based on the material
supply price including delivery but excluding installa-
tion) and ratio of cost to energy. There are 33 items in
the list, which provides a sufficient dataset for the
analysis. A Y-intercept of zero is again assumed.
The discovered relationship is weaker. Figure 3
shows the correlation between energy/unit and cost/
unit and determines that the derived r2 is quite low at
just 0.3560. While it is of course possible to collect
different materials and hence calculate different values
of r2, the point being made here is clearly evident from
the ratio of cost to energy shown in the last column of
Table 4.
Discussion
The focus in the hypothesis is the decreasing reliability
of the inherent energy–cost relationship as more detail
is employed. H0 is defined as the null hypothesis (i.e.
reliability does not decrease …) and H1 is defined as the
alternative hypothesis (i.e. reliability does decrease …).
Figure 1, Table 2, Table 3, Figure 2 and Figure 3
progressively demonstrate the decreasing reliability of
the relationship, and provide sufficient evidence to
conclude that H0 should be rejected in favour of H1 as
explained below.
Figure 1 indicates a strong relationship between
embodied energy and capital cost at the project level
across all 30 case studies. The derived r2 is 0.9542, but
even when a more stringent test of correlation is applied
by looking just at process analysis data, the value of r2 is
still strong at 0.8338. P-values are 1.12224 and 1.05217
respectively at 95% confidence levels.
Table 2 summarizes the correlation statistics at the
elemental group level across all case studies. Values of
r2 range down from 0.9712 (services) to 0.2188
(external alterations and renovations), and shows that
four (out of 11) elemental groups are well below the
selected test value of 0.7. The simple mean is 0.7120.
Table 2 Elemental group correlation statistics (Microsoft Excel Data Analysis Module)
Elemental
group
r r2 Adjusted r2 m p-value t-statistic
PR 0.9022 0.8140 0.7749 0.0051 5.99E-15 15.05
SB 0.9824 0.9651 0.9293 0.0200 1.27E-23 32.07
CL-ND 0.9741 0.9488 0.9125 0.0089 6.74E-24 32.83
WF-CF 0.9673 0.9357 0.9012 0.0060 7.59E-22 27.59
FT-SE 0.9717 0.9442 0.9079 0.0069 1.47E-21 26.93
SF-SS 0.9855 0.9712 0.9351 0.0024 5.39E-26 39.15
AR 0.5761 0.3319 0.1975 0.0016 1.43E-02 3.03
XP-XL 0.8645 0.7473 0.7062 0.0070 2.25E-12 12.66
XK-XS 0.4934 0.2434 0.1865 0.0041 3.02E-05 5.23
XX 0.4677 0.2188 0.0870 0.0004 2.20E-01 1.52
YY n/a n/a n/a 0.0226 4.12E-03 3.13
Reliability of building embodied energy modelling 153
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
Table 3 summarizes the correlations statistics at the
elemental level across all case studies. Here values of r2
vary between 0.9832 (external electric light and power)
and 0.0307 (water supply). Eighteen (out of 43)
elements again fall below the test value of 0.7. The
simple mean is 0.6863.
Figure 2 focuses solely on elements within a single
project (Building 24). The value of r2 is shown as 0.5217
(p-value51.3029). While a relationship still exists, it is
weaker, and below the selected test value of 0.7.
Finally, Figure 3 shows an r2 value of 0.3560 when
the energy–cost relationship is reduced to individual
materials. In this case, p-value is 2.1926.
The reason for the decreasing reliability is thought to
be a function of the level of the investigation. It is
already understood that the ratio of capital cost to
embodied energy varies widely for different materials.
Table 4 shows that this ratio ranges from 12 times
(cement) to 411 times (fabric reinforcement), with a
mean ratio of 101 times and a coefficient of variation of
Table 3 Element correlation statistics (Microsoft Excel Data Analysis Module)
Element r r2 Adjusted r2 m p-value t-statistic
PR 0.9022 0.8140 0.7749 0.0051 5.99E-15 15.05
SB 0.9824 0.9651 0.9293 0.0200 1.27E-23 32.07
CL 0.9899 0.9800 0.9398 0.0154 1.41E-24 41.49
UF 0.9491 0.9008 0.8478 0.0108 2.15E-13 18.00
SC 0.8247 0.6802 0.6279 0.0099 2.02E-09 9.72
RF 0.9179 0.8426 0.8078 0.0146 2.92E-17 18.54
EW 0.9515 0.9053 0.8688 0.0072 8.43E-19 21.23
WW 0.9660 0.9331 0.8891 0.0058 5.20E-20 28.48
ED 0.9254 0.8563 0.8083 0.0053 9.85E-15 16.14
NW 0.8856 0.7842 0.7470 0.0081 5.75E-14 13.74
NS 0.9219 0.8499 0.8170 0.0055 9.29E-16 17.26
ND 0.8862 0.7853 0.7470 0.0028 1.06E-13 13.40
WF 0.9099 0.8279 0.7923 0.0056 8.40E-15 15.27
FF 0.9440 0.8912 0.8596 0.0054 1.69E-18 20.68
CF 0.8852 0.7836 0.7438 0.0067 3.67E-14 14.36
FT 0.9631 0.9276 0.8912 0.0069 8.75E-20 23.12
SE 0.9569 0.9157 0.8552 0.0067 7.59E-12 16.38
SF 0.9486 0.8998 0.8544 0.0013 2.59E-14 19.37
PD 0.5492 0.3016 0.2141 0.0009 1.33E-03 3.99
WS 0.1752 0.0307 0.0021 0.0028 1.30E-02 3.30
AC 0.9519 0.9061 0.8653 0.0030 3.39E-18 21.73
FP 0.8649 0.7481 0.7096 0.0011 5.09E-13 13.18
LP 0.8968 0.8042 0.7634 0.0006 5.09E-16 16.59
CM 0.8004 0.6407 0.5378 0.0059 6.57E-05 6.22
GS 0.8182 0.6694 0.6625 0.0004 3.07E-05 7.16
VE 0.8062 0.6499 0.4715 0.0022 2.47E-03 4.99
TS 0.9633 0.9280 0.8008 0.0075 7.88E-07 13.67
SS 0.6223 0.3872 0.2745 0.0021 1.86E-03 4.34
AR 0.5761 0.3319 0.1975 0.0016 1.43E-02 3.03
XP 0.7314 0.5349 0.4720 0.0027 1.01E-04 5.04
XR 0.8542 0.7297 0.6812 0.0102 2.57E-10 10.59
XN 0.2585 0.0668 0.0257 0.0212 1.66E-04 5.38
XB 0.8868 0.7864 0.5954 0.0178 3.22E-03 5.29
XL 0.5425 0.2943 0.2317 0.0044 4.93E-05 5.21
XK 0.7016 0.4922 0.4389 0.0106 1.06E-05 5.83
XD 0.4822 0.2325 0.1248 0.0031 5.41E-05 5.56
XW 0.6701 0.4491 0.3671 0.0037 2.21E-05 6.23
XE 0.9916 0.9832 0.8410 0.0042 1.36E-08 29.38
XG 0.7674 0.5889 0.3308 0.0031 4.78E-03 4.82
XF 0.8305 0.6898 0.3263 0.0020 6.63E-03 4.46
XS n/a n/a n/a n/a n/a n/a
XX 0.4677 0.2188 0.0870 0.0004 2.20E-01 1.52
YY n/a n/a n/a 0.0226 4.12E-03 3.13
154 Langston and Langston
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
101.32%. Yet at higher levels these discrepancies
become less important, and the mix of materials
introduces more stability.
A simple analogy can help to explain this phenom-
enon. A typical family shopping bill at the supermarket
might be $200 per week. This amount is reasonably
predictable when the shopping trolley is full. Within
that trolley is a range of commodities that vary
significantly in price (and volume). Yet, provided the
total volume is consistent per week, the total price is
also. The effect of variability in individual unit prices is
reduced by the mix. In much the same way construc-
tion cost is predictable in terms of cost/m2 GFA despite
the detailed decisions on materials and systems that
underlie it.
The relationship between embodied energy and
capital cost is interrupted to some extent by the cost
of labour. People obviously consume goods and
services to live, and therefore any process that involves
human labour involves indirect energy use. Peet and
Baines (1986) define labour in three ways: muscular
energy expended in the performance of the task; energy
content of the foods consumed by the worker for the
time spent on the task; and total quantity of food
consumed by the worker regardless of the time spent on
the task. As explained earlier, the embodied energy of
human capital is controversial and normally excluded
from energy analysis calculations. Nevertheless valuing
labour is routine in life cycle costing and therefore cost
modelling may provide a new and simpler approach to
deal with this problem.
This matter also provides some further explanation
of the decreasing relationship between embodied
energy and capital cost as the project is broken down.
Figure 2 Building 24 correlation by element
Reliability of building embodied energy modelling 155
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
At a project level, labour accounts for on average about
30–40% of the total cost. Excluding this component
would have no effect on the correlation. But as the
analysis is refined to elemental groups, elements and
ultimately items of work, so the ratio of labour to
material becomes more volatile, and hence the correla-
tion less reliable. This situation again advocates the use
of high-level data when modelling embodied energy
from capital cost.
So embodied energy and cost have little relationship
at the level of individual materials, but as the mix
within a typical building becomes more complex the
relationship appears to strengthen. This outcome
suggests that embodied energy is more reliably pre-
dicted at the project level than any selected sub-level,
which in turn is good news for people who wish to
estimate embodied energy impact. But as cost increases
so does energy, and this relationship raises serious
questions over whether the common-held view of
spending more money to realize energy efficiencies is
at all an achievable goal.
Conclusion
It is found that initial embodied energy is reliably
modelled by capital cost, but this reliability decreases
proportionally with the level of detail at which the
model is expected to operate. In other words, as the
level at which the model operates moves from the
overall project down to individual work items, so the
correlation between energy and cost drops.
Inconsistency in the ratio of embodied energy to capital
cost for individual materials is lost in the mix of
materials that typically comprise a building. This mix
strengthens the relationship, since high and low ratios
are offset against each other.
Table 4 Material correlation data (input–output-based hybrid EE model and Rawlinsons (2006))
Material item Unit GJ/unit $2006/unit Ratio
(cost: energy)
Aluminium kg 0.25 13.40 53
Brickwork (110mm thick) m2 0.56 23.20 41
Carpet, wool m2 0.74 71.54 97
Cement kg 0.02 0.20 12
Concrete roof tiles (25mm thick) m2 0.17 19.15 115
Clear float glass (6mm thick) m2 1.91 86.29 45
Concrete, 32MPa m3 5.46 144.18 26
Concrete block, hollow (200mm thick) m2 0.56 226.73 408
Concrete pipe (300mm diameter) m 0.57 61.08 107
Copper kg 0.38 28.88 76
Fibre cement sheet (6mm thick) m2 0.21 19.15 93
Fibreglass batts, R2.5 m2 0.17 5.18 31
Lead kg 0.15 6.67 44
MDF/particleboard (25mm thick) m2 0.53 28.46 53
Membrane m2 0.24 29.72 122
Paint, water based m2 0.05 12.88 273
Plasterboard (13mm thick) m2 0.16 15.32 97
Plastic kg 0.16 19.37 119
PVC water pipe (25mm diameter) m 0.16 15.19 95
Reflective foil m2 0.14 3.07 22
Reinforcement fabric, F62 m2 0.01 3.60 411
Sand m3 0.53 23.25 44
Screenings m3 0.47 48.87 104
Slate (25mm thick) m2 0.65 99.06 151
Steel kg 0.07 1.08 15
Steel, stainless kg 0.45 6.61 15
Terracotta roof tiles (20mm thick) m2 0.59 26.42 45
Tile, ceramic m2 0.29 38.52 131
Timber, hardwood (100 6 100mm) m 0.21 6.54 31
Timber, softwood (100 6 100mm) m 0.11 9.91 91
Toughened glass (6mm thick) m2 2.55 134.72 53
UPVC pipe (100mm diameter) m 0.16 46.23 289
Vinyl (2mm thick) m2 0.66 14.31 22
156 Langston and Langston
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
The typical mix of elements is critical. The project
level equation (y50.0071x) requires all elements to be
present. Where this is not the case, such as no lifts or no
upper floors for example, the accuracy of the project-
based slope coefficient is reduced. Elemental groups
are the next best method, but the slope coefficients can
still be affected where key elements are absent.
Therefore the element-based slope coefficients provide
a more practical approach and are advocated as the
basis of a predictive model. Care must be taken,
however, with elements that have low reliability and
with external works where the ratio with building GFA
is subject to significant variation.
In all observed instances, whether at project,
elemental group or element levels, higher energy values
give rise to higher costs and vice versa. Cost is a strong
predictor of energy. While at the work item level it is
feasible to spend more capital to purchase materials or
systems with lower embodied and/or operating energy
demand, and thus introduce efficiency and value for
money, at the higher levels of aggregation this is
unlikely to be significant.
This finding leads to the conclusion that optimiza-
tion of energy and optimization of cost are not mutually
exclusive goals. The very strong correlations between
energy and cost, and particularly between embodied
energy and capital cost, suggest that this bond cannot
be upset by individual decisions made at more refined
levels of detail. It therefore may be more important to
look elsewhere for efficiencies. In the case of embodied
Figure 3 Common material item correlation
Reliability of building embodied energy modelling 157
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
energy, savings can be found by building less. This may
arise from more efficient floor plans (i.e. less non-
functional area), more efficient plan shape (i.e. lower
wall/floor ratios), more efficient internal layouts (i.e.
more open plan design), and higher floor densities (i.e.
people/m2). In the case of operating energy, savings can
be found, in addition to building less, by reducing
demand through use of natural lighting and ventilation,
proper orientation, reduced operating hours (where
possible) and intelligent control systems.
This research supports the proposition that energy
optimization and cost optimization are compatible
activities. The decisions that result from investigating
different material options do not significantly lower
total energy demand unless the cost of these options is
also proportionally reduced. Spending more initially to
save embodied energy, for example, is unlikely to be a
productive quest, although undoubtedly instances
where this might occur at a more detailed level within
a project can be imagined. A better strategy for
reducing embodied energy is simply building less.
Having said that, this study comprised case studies
that did not have significant components of recycled or
reused materials. Clearly where this is achieved, initial
embodied energy can be markedly reduced since the
upstream energy impacts would have been previously
counted on another project (i.e. double counting is not
valid). The cost of recycled and reused materials varies
widely. In some cases the cost can be higher than
comparable new materials, and in many other cases the
cost can be lower. The introduction of significant
amounts of recycled and reused materials may upset
the relationships found in this study.
This issue also has implications for embodied energy
value. In this study 73.3% of projects represented new
construction, and the remainder were redevelopment.
In many cases, redevelopment implies reuse of struc-
ture and other elements, so both embodied energy and
capital cost are reduced. There was no discernible
difference between the results for new and redeveloped
projects, indicating that the inherent energy–cost
relationship still applies.
The lack of public knowledge about embodied
energy has led to its absence from design decision
making and government policies. This situation has
arisen as a direct result of the complexity of the
calculations and the lack of reliable data upon which to
base them. Over time, embodied energy models have
become even more complex. This translates into
specialist knowledge requirements and a considerable
time commitment. The way forward is to develop
models that practitioners can use and apply routinely to
their projects. Only by putting useful tools into the
hands of building designers and managers can a wider
understanding of the importance of embodied energy
be gained. This also enables life cycle energy and GGE
calculation to be incorporated in the early design stages
to reduce unnecessary environmental degradation.
Acknowledgements
The authors of this paper would like to thank the kind
assistance of Associate Professor Graham Treloar from
the University of Melbourne for the use of his input–
output-based hybrid method for embodied energy
analyses and for his supervisory advice and guidance in
this research, Computerelation Australia Pty Limited for
making available LIFECOST TM software for operating
cost analyses, and Davis Langdon Australia for permis-
sion to use their data in the case studies. Without their
cooperation this research would not have been possible.
References
AGO (1999) Australian Commercial Building Sector Greenhouse
Gas Emissions 1990–2010, Australian Greenhouse Office,
Canberra.
AIQS (2002) Australian Cost Management Manual, Vol. 3,
The Australian Institute of Quantity Surveyors, Canberra.
Arnold, F. (1993) Life cycle doesn’t work. Environmental
Forum, 10(5), 19–23.
ASEC (2001) Australia 2001: State of the Environment,
Independent Report to the Commonwealth Minister for
the Environment and Heritage, Australian State of the
Environment Committee.
Ashworth, A. (1988) Making life cycle costing work.
Chartered Quantity Surveyor, 10(8), pp. 17–18.
Baird, G. and Chan, S. (1983) Energy Cost of Houses and Light
Construction, Report No. 76, New Zealand Energy Research
and Development Committee, November.
Beggs, C. (2002) Energy: Management, Supply and
Conservation, Oxford, Butterworth-Heinemann.
Bell, J.M. and Fawcett, A. (2000) Designing sustainability
into engineering education and practice: education for a
sustainable built environment. Presentation for Teaching
Sustainable Design Forum, 13 November.
Boustead, I. and Hancock, G.F. (1979) Handbook of Industrial
Energy Analysis, Ellis Horwood, Chichester.
Brown, R.J. and Yanuck, R.R. (1985) Introduction to Life Cycle
Costing, Fairmont Press, Atlanta.
Bull, J.W. (ed.) (1992) Life Cycle Costing for Construction,
Blackie Academic and Professional, London.
Chukwuma, C. (1996) Perspectives for a sustainable society.
Environmental Management and Health, 7(5), 5–20.
Costanza, R. (1980) Embodied energy and economic valua-
tion. Science, 210, 1219–24.
Crawford, R.H. (2004) Using input–output data in life cycle
inventory analysis, DPhil thesis, Deakin University,
Geelong, Australia.
Crawford, R.H. (2005) Validation of the use of input–output
data for embodied energy analysis of the Australian
158 Langston and Langston
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
construction industry. Journal of Construction Research, 6(1),
71–90.
Crawford, R.H., Fuller, R.J., Treloar, G.J. and Ilozor, B.D.
(2002) Embodied energy analysis of the refurbishment of a
small detached building, in Luther, M., Dawson, A.,
Ham, J., Moore, M., Rollo, J. and Treloar, G. (eds)
Proceedings of 36th Annual Conference of the Australian and
New Zealand Architectural Science Association (ANZAScA):
The Modern Practice of Architectural Science from Pedagogy to
Andragogy?, Geelong, Victoria, Australia, November,
pp. 93–100.
Dell’Isola, A.J. and Kirk, S.J. (1995) Life Cycle Cost Data,
McGraw-Hill, New York.
Department of Natural Resources and Environment (2000)
Victorian greenhouse strategy. Discussion Paper,
Department of Natural Resources and Environment.
Fay, R. (1999) Comparative life-cycle energy studies of
typical Australian suburban dwellings, DPhil thesis,
University of Melbourne, Melbourne.
Feagin, J., Orum, A. and Sjoberg, G. (eds) (1991) A Case for
Case Study. University of North Carolina Press, Chapel
Hill.
Flanagan, R. and Norman, G. (1983) Life Cycle Costing for
Construction, Surveyors Publications, London.
Fossdal, S. (1995) Energy consumption and environmental
impacts of buildings in Norway: life cycle assessment.
International Energy Agency Energy Conservation News, 22,
1–3.
Fuller, R. (1982) Life cycle costing: a comprehensive
approach, in Brandon, P.S. (ed.) Building Cost Techniques:
New Directions, E&FN Spon, London, pp. 439–46.
Hill, R.K. (1978) Gross energy requirements of building
materials, in Proceedings of Conference on Energy Conservation
in the Built Environment, Department of Environment,
Housing and Community Department, Sydney, 15–16
March, pp. 179–190.
Hoglund, I. (1992) Energy conservation in the built
environment: the past, the future, in Proceedings of World
Building Congress, Montreal, Canada, 18–22 May,
pp. 376–7.
Irurah, D.K. and Holm, D. (1999) Energy impacts of
building construction as applied to South Africa.
Construction Management and Economics, 17, 363–74.
Kirk, S.J. and Dell’Isola, A.J. (1995) Life Cycle Costing for
Design Professionals, McGraw-Hill, New York.
Lam, J., Chow, T. and Yuen, R.K. (1992) Energy for space
heating in commercial buildings in Hong Kong, in
Proceedings of World Building Congress, Montreal, Canada,
18–22 May, pp. 352–3.
Langston, C.A. (1991) The Measurement of Life-Costs, Public
Works Department of New South Wales, Sydney.
Langston, C.A. (1994) The determination of equivalent value
in life-cost studies: an intergenerational approach, DPhil
thesis, University of Technology, Sydney.
Langston, C.A. (2005) Life-Cost Approach to Building
Evaluation, Elsevier, Oxford.
Langston, C.A. and Lauge-Kristensen, R. (2002) Strategic
Management of Built Facilities, Butterworth-Heinemann,
Oxford.
Langston, Y.L. (2006) Embodied energy modelling of in-
dividual buildings in Melbourne: the inherent energy–cost
relationship, DPhil thesis, Deakin University, Geelong,
Australia.
Lawson, W.R. (1995) Embodied energy of building.
Environment Design Guide, The Royal Australian Institute
of Architects, August, pro.2, pp. 1–6.
Lenzen, M. and Lundie, S. (2002) Input–output model of the
Australian economy based on published 1996–97
Australian input–output data, unpublished paper.
Lippiatt, B.C. (1999) Selecting cost-effective green building
products: BEES approach. Journal of Construction
Engineering and Management, 125(6), 448–55.
NAEEEC (1999) Future directions for Australia’s appliance
and equipment energy efficiency program. Discussion Paper
prepared by the National Appliance and Equipment Energy
Efficiency Committee, Commonwealth of Australia.
Odum, H.T. (1971) Environment, Power and Society, Wiley-
Interscience, New York.
Peet, N.J. and Baines, J.T. (1986) Energy Analysis: A Review
of Theory and Applications, Report No. 126, New Zealand
Energy Research and Development Committee, February.
Rawlinsons (2006) Australian Construction Handbook, 24th
edn, Rawlhouse Publishing, Perth.
Robertson, G. (1991) Energy efficient commercial buildings:
a realistic market objective. Architectural Science Review, 34,
139–42.
Shen, S. (1981) Energy and Materials Flows in the Production of
Primary Aluminium, Report for the Energy and
Environmental Systems Division Special Projects Group,
October.
Stone, P.A. (1960) The economics of building design. Journal
of the Royal Society, 123(3), 237–73.
Tellis, W. (1997) Application of a case study methodology.
The Qualitative Report, 3(3), available at www.nova.edu/
ssss/QR/QR3-3/tellis2.html (accessed 15 May 2007).
Treloar, G.J. (1996) A complete model of embodied energy
‘pathways’ for residential buildings, in Treloar, G., Fay, R.
and Tucker, S. (eds) Proceedings of the Embodied Energy: The
Current State of Play Seminar, Deakin University, Geelong,
Australia, 28–29 November, pp. 51–60.
Treloar, G.J. (1997) Extracting embodied energy paths from
input–output tables: towards an input-output based hybrid
energy analysis method. Economic Systems Research, 9(4),
375–91.
Treloar, G.J. (1998) A comprehensive embodied energy
analysis framework, DPhil thesis, Deakin University,
Geelong, Australia.
Treloar, G.J., Love, P.E.D. and Holt, G.D. (2001) Using
national input–output data for embodied energy analysis of
individual residential buildings. Construction Management
and Economics, 19, 49–61.
Treloar, G.J., Ilozor, B.D. and Crawford, R.H. (2002)
Modelling energy use and greenhouse gas emissions
associated with commercial building construction, in
Luther, M., Dawson, A., Ham, J., Moore, M., Rollo, J.
and Treloar, G. (eds) Proceedings of 36th Annual Conference
of the Australian and New Zealand Architectural Science
Association (ANZAScA): The Modern Practice of
Reliability of building embodied energy modelling 159
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014
Architectural Ccience from Pedagogy to Andragogy?, Geelong,
Victoria, Australia, November, pp. 533–40.
Van Pelt, M.J.F., Kuyvenhoven, A. and Nijkamp, P. (1990)
Project appraisal and sustainability: methodological chal-
lenges. Project Appraisal, 5, 139–58.
Verbeek, I. and Wibberley, L. (1996) Data collection, in
Proceedings of 1st National Conference on LCA, 29
September–1 March, pp. 1–7.
Wainwright, W.H. and Wood, A.A.B. (1981) Practical
Builders’ Estimating, Hutchinson, London.
160 Langston and Langston
Dow
nloa
ded
by [
Rad
boud
Uni
vers
iteit
Nijm
egen
] at
05:
27 0
3 N
ovem
ber
2014