Skip to Content
SustainabilitySustainability
  • Review
  • Open Access

9 August 2012

Energy Costs of Energy Savings in Buildings: A Review

and
Industrial Research Chair in Technologies of Energy and Energy Efficiency, École de Technologie Supérieure, Université du Québec, 1100, Rue Notre-Dame Ouest, Montréal, QC H3C 1K3, Canada
*
Author to whom correspondence should be addressed.

Abstract

It is often claimed that the cheapest energy is the one you do not need to produce. Nevertheless, this claim could somehow be unsubstantiated. In this article, the authors try to shed some light on this issue by using the concept of energy return on investment (EROI) as a yardstick. This choice brings semantic issues because in this paper the EROI is used in a different context than that of energy production. Indeed, while watts and negawatts share the same physical unit, they are not the same object, which brings some ambiguities in the interpretation of EROI. These are cleared by a refined definition of EROI and an adapted nomenclature. This review studies the research in the energy efficiency of building operation, which is one of the most investigated topics in energy efficiency. This study focuses on the impact of insulation and high efficiency windows as means to exemplify the concepts that are introduced. These results were normalized for climate, life time of the building, and construction material. In many cases, energy efficiency measures imply a very high EROI. Nevertheless, in some circumstances, this is not the case and it might be more profitable to produce the required energy than to try to save it.

1. Introduction

Energy efficiency is one of the key tools to tackle two of the biggest challenge facing humanity: climate change and energy scarcity. Indeed, to avoid catastrophic climate changes, it is generally acknowledged that the world needs to reduce the CO2 emission by 50% from the current level by 2050 [1]. For developed countries, this translates into a reduction of 80%, a division by five with respect to 1990’ semissions. While, increases in renewable energy production can help to reach this goal, some authors including those of the current paper, have proposed instead to drastically reduce the energy consumption as the renewables development will never be fast enough to overcome the scarcity of fossil fuels in the current century.
Along this idea, Kesselring and Winter [2] proposed the concept of a 2000 W society which aims at consuming no more than what corresponds to an average continuous power of 2000 W per capita; the value being considered as a fair share of the world energy consumption maintained at a sustainable level. This concept was later further developed and expanded [3,4]. Since actual rates of energy consumption is about 6000 W in Europe and even 10,000 W in North America, this would certainly imply dramatic changes in day to day life for most of OECD countries.
Transportation is often singled out as the main target for energy efficiency. However, the building industry has an even larger energy and environmental footprint as it is one of the human activities with the largest environmental impact. As noted by Dixit et al. [5], the construction industry depleted two-fifths of global raw stone, gravel, and sand; one-fourth of virgin wood; and it consumes 40 percent of total energy and 16 percent of fresh water annually [6,7,8,9,10,11,12]. These figures are more or less similar in any developed country. Indeed, for OECD countries, energy consumption by buildings varies between 25% – 50% of total energy consumption [13], whereas it is closer to 50% in the European Union [14].
In these conditions, the building industry is an obvious target for energy efficiency. This is the rationale behind the European Union Directive on Energy Performance of Buildings [15]. This directive requires member states to implement energy efficiency legislations for buildings, including existing ones with floor areas over 1000 m2 that undergo significant renovations. The French legislation [16] specifies that by January 2013, any new building will have to consume less than 50 kWh/m2/yr of primary energy (this value is modulate with the building type, apartment size and local climate). By 2020, all new buildings will have to be at least net zero—that is involving a consumption of 0 kWh/m2/yr—or better, that is globally producing energy [16]. In a similar way, the Swedish government promulgated a Bill on Energy Efficiency and Smart Construction, to reduce total energy use per heated building area by 20% by 2020 and 50% by 2050, using year 1995 as the reference [17]. In addition, these energy efficiency measures offer a significant opportunity to reduce CO2 emissions [1,18].
Such ambitious goals in energy efficiency improvements raise the key issue of the efficient allocation of resources. Actions that need a large upfront investment for a minimal reduction of the energy consumption are undesirable. In some cases, the return might be so small that one might wonder if it would be better to produce the energy than trying to save it. This is true both for economic and ecological efficiencies.
This first paper of a series of two addresses this key issue from the point of view of energy savings as applied to two popular energy savings measures implemented in buildings: insulation and window optimization.

2. Energy Return on Investment: A Revised Concept

One potentially useful alternative to conventional economic analysis when it comes to evaluate the sustainability of a particular solution aimed at saving energy (and consequently greenhouse gas emissions) or producing energy is the net energy, Enet, analysis. The concept relies on the estimation of two parameters depending whether energy production or energy savings are considered.

2.1. Energy Production

In the first case, all energy required to implement a particular equipment or process (from cradle to grave) is accounted for: it is called the energy invested, Einvested. Then, all energy that this device or process will generate or produce, Eproduced, during its lifetime is evaluated. Accordingly, the net energy is simply:
In the desirable situation, Enet, is positive, that is the device or process will generate or produce more energy than it took to implement it. On contrary, it could happen that the required amount of energy required from cradle to grave could be more important than the production. This could be due to a short lifetime and most of the time driven by the economics.
The concept can be applied to non-existing solutions, project starting from scratch, for which there is no production at all at the beginning. In this context it is possible to compare several solutions to one another based on this criterion.
Or, it could be applied to solutions improvements in which case the solutions will be compared to the existing one. In this latter case, Enet, has to be defined in terms of the improvement only.

2.2. Energy Saved

In a second–opposite–case, energy savings are considered. For this case, Eproduced is replaced by Esaved. The savings, Esaved, are estimated for the difference between the amount of energy that the device, building or process would require provided nothing is done and the amount of energy it should consume with the implementation of the proposed device, building or process. On the other hand, Einvested does not account for the energy used by the device after the measures of economy are implemented. In this case, Einvested only accounts for the energy required to implement the solution or install the equipment (from resources extraction to commissioning not from cradle to grave). The energy used by the solution is already accounted for in the definition of Esaved.
In this case, a positive value of Enet accounts for savings (which are negawatts or a negative production) that are greater than the energy invested, which of course is desirable. To obtain a desirable effect associated with a positive value of Enet, the savings must be positive. On the other hand, the worst case solution is the case when the savings are negative, that is when, after an investment, the amount of energy used Econsumed,after is larger than that used previously in the original situation Econsumed,before. And this happens more often than we might think when the analysis failed to adequately predict the energy embodied into a solution and focused solely on the eventual savings over a somewhat short lifetime.
As for the case of production, Enet can be defined with respect to novel or additional measures of energy efficiency.
In both savings and production cases a positive Enet means a desirable effect and conversely.

2.3. The Energy Ratio: Energy Return on Investment

This analysis deals with the calculation of the ratio of the energy savings by a particular solution (over a given period of time) or the energy produced by some equipment or process to the energy required to implement the solution or install the equipment (from resources extraction to commissioning). This net energy analysis is sometimes called the assessment of energy surplus, the energy balance method, or the energy return on investment (EROI) [19,20,21,22,23]. In the case of energy production, the EROI is calculated from Equation (3):
The key challenge to obtain a meaningful value for this ratio is to correctly define the boundaries of the problem which is investigated and to include—or try to include—all the inputs and outputs in the process [22,23]. For instance, the production of gasoline should account for all the steps required to produce it and deliver it to the stations as in a life cycle analysis.
Of course, the higher this ratio, the lower the environmental impact per unit of energy is expected since less input is used for the same output and consequently less impact is felt by the environment [24].While several authors may argue that the energy consumption and its environment burden adequacy is not straightforward, it has still some merit as an indirect environmental impact indicator [25,26] it is likely to be linked with a better economic investment since the energy content is closely—but not necessarily linearily—related to the price of a product, a process or a service. As a result, energy sources involving a better EROI should be selected in preference to others [27,28]. This is especially true for renewable energy sources for which the environmental burden comes mostly from the extraction and transportation of the resources and manufacturing of the energy systems prior to their use. This concept is related to that of net energy, Enet, that is when Enet = 0, EROI = 1 and a negative Enet means EROI < 1.
Calculating the average EROI for an energy basket is complex. Nevertheless, there are some indications that the average EROI of the U.S. energy basket is close to 10 and that a lower EROI should induce negative economic impacts [29]. Hence, for the purpose of this discussion acceptable energy solutions should respect EROI > 10 or Enet > 9 × Einvested hence, energy solutions with a lower EROI should be discounted.
When a modification to a power plant or a device is carried out, the EROI can be evaluated. That is to determine whether or not the modifications lead to an increase level of energy production, ΔEproduced, is positive. This is always the case when a production project starts from scratch. There could nevertheless be projects for which the energy production after a modification is lower than what was previously obtained. Defined this way, the EROI is then:
with the obvious requirement that EROI > 1 to obtain a valid or sustainable modification.

2.4. Differences and Similarities in EROI

A practical problem arises when using the EROI metric in an energy savings application such as a building. There is a key difference between EROI calculated for energy sources and EROI calculated from energy saved. Hence, negajoules (J) and negawatt (W) are compared to joules (J) and watt (W) (to our knowledge no symbols exist for negawatt and negajoules. Hence, we propose to use these one).
While at first glance this change of definition might look only semantic, it involves much deeper consequences. The reason is that Esaved is an energy difference by itself whereas Eproduced is not. Moreover, savings are positive that is the desirable situation is that after implementation of the measures one looks for less consumption while the desirable situation for production after implementation calls for more production.
EROI was originally solely conceived for energy production or energy production technologies and equipment. Hence, in this scenario energy produced and energy invested are both expected to be positive. In consequence, EROI will be always positive. Even when, the net energy production, Enet, is negative, the EROI is still positive but smaller than 1. As mentioned in the above paragraph EROI could either be positive or negative.
For energy efficiency (or savings), the concept holds with minor differences. It was said that the energy saved is a positive quantity. In rare circumstances, a poorly designed intervention might increase the lifetime energy consumption, which corresponds to a negative EROI since energy saved is then negative.
This situation might also be caused by a strong rebound effect, the Jevons paradox [30], where the users adapt their energy consumption behavior in a way that they increases the consumption of a good or a service made more affordable due to the improved efficiency to a point that the new energy consumption could exceed the original one.
In this case, there cannot be a definition of EROI of gain as the energy saved is by definition a difference. However, Equation 4 corresponds to Equation 5 when the savings are negative.
There are also situation for which the definition does not hold. For instance, energy efficiency measures may cost nothing. Energy efficiency measures like changing thermostat settings, closing an interrupter or cooling by natural convection have zero or near zero costs which means that EROI→∞.
But, there is an even more favorable situation where an improvement of one aspect of a building has for consequence the optimization of the performance of others systems leading to an overall net negative energy cost. For instance, the improvements to the insulation of the building envelope produce a given EROI for the insulation addition alone, but it may also allow for the reduction of the size of the heating system and hence produce savings on its embodied energy. This could lead to an overall lower total energy cost for the whole building, compared with the version with less insulation. Nevertheless, since in practice energy must be always used to implement a project, this situation is restricted to two cases: when comparing two hypothetical situations and when embodied energy of the replaced components can be recovered to the point that the net energy invested is negative. In the following discussion, only the first situation occurs.
From the strict mathematical point of view, this would produce a negative EROI (positive energy saved over a total negative energy cost). Hence, there are two types of negative EROI, one which is negative in term of energy savings and undesirable, and one which is positive in term of energy saved and highly desirable. Actually, this situation is better than EROI = ∞ since the embodied energy is lower than that involved in the original situation! To distinguish these two cases, the symbol † is to be used instead of—for the case where the embodied energy is lower. The reader must be warned however that the value of this type EROI must be interpreted in a different way than the usual one. Indeed, a small EROI means that little operational energy is saved compared to the embodied energy, while a large EROI means that little embodied energy is saved compare to the operational. In consequence, EROI value does not provide information about the relative desirability of the technical solutions.

2.5. A Schematic Representation of the EROI Complete Concept

To complete the picture, it should be noted that there are also the situations where the investment cost is negative and where the energy return is also negative. This situation is symmetric with the classical EROI and is treated the same way. These situations are described in the following diagram (Figure 1).
Figure 1. Energy return on investment (EROI) class (classical definition is in the upper right corner).
Figure 1. Energy return on investment (EROI) class (classical definition is in the upper right corner).
In Figure 1, there are four areas: (1) in the upper right corner, the EROI is positive that is the return and the investment are positive (which is the classical case for energy production leading to positive return with a positive investment); (2) in the lower left corner, the return and the (net) investment are negative leading to a positive EROI (symmetry of case 1); (3) in the lower right corner, the EROI is negative as the return is negative (you spend more energy) after a net positive investment; and (4) in the upper left corner is the case of a positive return with a lower embodied energy after the implementation of the measures.

2.6. Additional Considerations

At last, there is another key difference between calculating EROI for energy efficiency application. The energy produced or saved is always calculated with reference to a given original condition. In both cases (production or savings), the EROI is always better when you start from scratch. For instance, adding extra insulation to a wall which is already well insulated will have a much lower EROI than adding the same insulation to a poorly insulated wall. Conversely, improving a combustion system by fine tuning the air-fuel ratio of a combustor with an added sophisticated control system will involve a lower EROI than changing and old coal-fired furnace with a modern gas combustor.
It is also important to note that EROI may stay negative for a very long time and nevertheless reaches values above 10 since the lifetime of buildings is quite long (>50 yr). Therefore, when analyzing the energy efficiency, the appropriate time scale must be used. This is why the energy payback time (EPT), which will be explained in more details in the next section, is also an important parameter to consider. Or, more generally, the context is always important and the analyst must be careful when interpreting an EROI value.
In practice, few studies have been done on an energy basis most of them have been carried out on monetary return. Since, monetary value of energy unit is sensible to the nature of the energy input, EROI calculations based on monetary inputs shall be used with care. In average, the energy content of a dollar of product and services is higher than its equivalent in energy, the EROI calculated in dollar, without correcting for this factor, is always smaller than the EROI calculated from energy units. For the data collected for these studies, this factor is typically between 6 and 10.
This is a crucial point of the discussion since most studies discuss the economical aspect of energy with respect to dollars not energy units. Almost all studies were not designed to calculate EROI, all needed information is not directly available: while the energy consumption is most of the time given in energy units, the energy invested is not. However, it is sometimes possible to gather the information on the embodied energy content from alternate sources such as the data contained in [31]. Nevertheless, this database is oriented to building analyses done in the UK context, which may create severe distortions for other countries. In few cases, numerical values of the initial investment were not explicitly given in the text and we had to rely on measurements made on published graphs to get the appropriate information.

2.7. The Energy Payback Time (EPT)

In several articles, the energy payback time (EPT) is given. The energy payback time is the period needed to recover the energy invested through energy saving or energy produced. By definition, it is the time after which the EROI reaches a value of one and the net energy is equal to zero. Hence, EROI over the life time is:
This brings the issue of the lifetime of components [32,33,34] and of the building itself, which are in general poorly defined. To handle this problem, it is often recommended to refer to the norm ISO 15686 Buildings and constructed assets service-life planning [35] or using a 50 years timeframe as a reference for major renovations, since it is acknowledged and used in many studies [36]. In the upcoming analysis, a 50 years period for the building life time and a 35 years period for the components lifetime are used.

2.8. Other Factors

There are other issues peculiar to building application. One of the key problems in building life cycle analysis arises from the long life of the buildings (30–100 yr). Over such a long period of time, the energy basket and even the climate are expected to change. This raises some concerns about the applicability of the standard life cycle analysis method for buildings [37,38,39,40,41].
Another peculiar aspect of the life cycle analysis of building is that it is possible to exhaust resources locally even if the global resource base is immense globally. This problem exists for building material since they are bulky and therefore often expensive to transport over long distances. Hence, while the depletion of bulk resources is negligible at global level [42,43] and hard to put in evidence at the scale of a country like France, depletion becomes clear in a relatively small region like Île-de-France, where depletion time scale is the same order of magnitude than quarries or buildings lifetimes [44,45]. This analysis does not convers this aspect of the problem.
Notwithstanding these weaknesses, the reader should be aware that the same formalism applies also to greenhouse gases or any other pollutants that are produced both in construction and operation of the building.

4. Conclusions

This paper shed some light on the issue of energy sobriety by using appropriate definitions of the energy return on investment (EROI). The paper first discusses the intrinsic differences between a watt and a negawatt and how savings and production of energy lead to different interpretation of the EROI. The papers stresses that while production and savings are different from a point of view of positive and negative energy, EROI for savings is always with respect to an existing situation while for production it may concern a situation for which there is nothing to compare with. The paper also introduces the concept of net negative energy investment in the context of an implementation for which the reduction of intrinsic energy in the peripheral systems is higher that the investment required by the actual solution. The paper than defines 4 types of EROI according to the signs of the numerator and denominator.
Then the paper addresses these key concepts from the point of view energy savings as applied to three popular energy savings measures implemented in buildings: insulation, window optimization, and the integration of several measures into a whole building.
Estimated EROI in energy savings strategies are high compared to most energy production strategies [24]. This illustrates the strongly positive impact of energy conservation (savings) on the environment. In consequence, the motto “The cheapest energy is the energy not used” is true in most case we have observed. Nevertheless, in few cases, such as adding an extra foot of insulation on an already well insulated building, this affirmation might be questioned.
Nevertheless, the diminishing return of the adjunction of more insulation in building walls raises the question of the existence of a threshold above which one is better to produce the energy than try to save it. This question is especially important in the light of policies that, for instance, simply copy the passivhaus standard without further optimization with respect to the local climate. The same situation arises when extreme energy consumption reduction is sought at the expense of the embodied energy.
In an upcoming study, the authors will employ the concepts developed here but from the point of view of energy production (rather than savings). Several fashionable local energy production measures advocated for residential, commercial, or institutional buildings will be considered: solar walls, photovoltaic, wind, geoexchange, etc.

Conflict of Interest

The authors declare no conflict of interest.

References

  1. IPCC, Climate Change 2007: Mitigation; Contribution of Working Group III to the Fourth Assessment Report; Cambridge University Press: Cambridge, UK, 2007.
  2. Kesselring, P.; Winter, C.J. World Energy Scenarios: A Two-kilowatt Society, Plausible Future or Illusion? In Proceedings of the Energietage 94, Villigen, Switzerland, 10-12 November 1994.
  3. Pfeiffer, A.; Koschenz, M.; Wokaum, A. Energy and building technology for the 2000 W society—Potential of residential buildings in Switzerland. Energy Build. 2005, 37, 1158–1174. [Google Scholar]
  4. Schulz, T.F.; Kypreos, S.; Barreto, L.; Wokaum, A. Intermediate steps towards the 2000 W society in Switzerland: An energy-economic scenario analysis. Energy Policy 2008, 36, 1303–1317. [Google Scholar] [CrossRef]
  5. Dixit, M.K.; Fernández-Solís, J.L.; Lavy, S.; Culp, C.H. Identification of parameters for embodied energy measurement: A literature review. Energy Build. 2010, 42, 1238–1247. [Google Scholar] [CrossRef]
  6. Arena, A.P.; de Rosa, C. Life cycle assessment of energy and environmental implications of the implementation of conservation technologies in school buildings in Mendoza-Argentina. Build. Environ. 2003, 38, 359–368. [Google Scholar] [CrossRef]
  7. Horvath, A. Construction materials and the environment. Annu. Rev. Energy Environ. 2004, 29, 181–204. [Google Scholar]
  8. Urge-Vorsatz, D.; Novikova, A. Opportunities and Costs of Carbon Dioxide Mitigation in the Worlds Domestic Sector. In Proceedings of the International Energy Efficiency in Domestic Appliances and Lighting Conference ’06, London, UK, 21-23 June 2006.
  9. Langston, Y.L.; Langston, C.A. Reliability of building embodied energy modeling: An analysis of 30 Melbourne case studies. Constr. Manag. Econ. 2008, 26, 147–160. [Google Scholar] [CrossRef]
  10. Lippiatt, B.C. Selecting cost effective green building products: BEES approach. J. Constr. Eng. Manag. 1999, 125, 448–455. [Google Scholar] [CrossRef]
  11. Tommerup, H.; Rose, J.; Svendsen, S. Energy-efficient houses built according to the energy performance requirements introduced in Denmark in 2006. Energy Build. 2007, 39, 1123–1130. [Google Scholar] [CrossRef]
  12. Ding, G. The Development of a Multi-criteria Approach for the Measurement of Sustainable Performance for Built Projects and Facilities. Ph.D. Thesis, University of Technology, Sydney, Australia, 2004. [Google Scholar]
  13. Asif, M.; Muneer, T.; Kelley, R. Life cycle assessment: A case study of a dwelling home in Scotland. Build. Environ. 2007, 42, 1391–1394. [Google Scholar] [CrossRef]
  14. Campogrande, D. The European Construction Industry—Facts and Trends. In Proceedings of the ERA Convention; European Construction Industry Federation (FIEC), Berlin, Germany: 5-6 June 2007.
  15. European Parliament, Report on the Proposal for a Directive of the European Parliament and of the Council on the Energy Performance of Buildings (Recast); COM(2008)0780-C6-0413/2008-2008/0223(COD); European Parliament: Bruxelles, Belgium, 2009 April 6.
  16. Règlementation Thermique. 2012. Available online: http://www.rt-batiment.fr/batiments-neufs/reglementation-thermique-2012/presentation.html (accessed on 4 July 2012).
  17. A National Programme for Energy Efficiency and Energy-Smart Construction. Swedish Government Bill. 2005. Available online: http://www.regeringen.se/sb/d/574/a/63635 (accessed on 4 July 2012).
  18. Harvey, L.D.D. Reducing energy use in the buildings sector: Measures, costs, and example. Energy Effic. 2009, 2, 139–163. [Google Scholar] [CrossRef]
  19. Hall, C.A.S. Migration and metabolism in a temperate stream ecosystem. Ecology 1972, 53, 585–604. [Google Scholar] [CrossRef]
  20. Hall, C.A.S.; Cleveland, C.J. Petroleum drilling and production in the U.S.: Yield per effort and net energy analysis. Science 1981, 211, 576–579. [Google Scholar]
  21. Cleveland, C.J.; Costanza, R.; Hall, C.A.S.; Kaufmann, R. Energy and the U.S. economy: A biophysical perspective. Science 1984, 225, 890–897. [Google Scholar]
  22. Hall, C.A.S.; Cleveland, C.J.; Kaufmann, R. Energy and Resource Quality: The Ecology of the Economic Process; Wiley: New York, NY, USA, 1986. [Google Scholar]
  23. Hall, C.A.S.; Powers, R.; Schoenberg, W. Peak Oil, EROI, Investments and the Economy in an Uncertain Future. In Renewable Energy Systems: Environmental and Energetic Issues; Pimentel, D., Ed.; Elsevier: London, UK, 2008; pp. 113–136. [Google Scholar]
  24. Huijbregts, M.A.; Hellweg, S.; Frischknecht, R.; Hendriks, H.W.; Hungerbühler, K.; Hendriks, A.J. Cumulative energy demand as predictor for the environmental burden of commodity production. Environ. Sci. Technol. 2010, 44, 2189–2196. [Google Scholar]
  25. Ulgiati, S.; Raugei, M.; Bargigli, S. Overcoming the inadequacy of single-criterion approaches to Life Cycle Assessment. Ecol. Model. 2006, 190, 432–442. [Google Scholar] [CrossRef]
  26. Svensson, N.; Roth, L.; Eklund, M.; Mårtensson, A. Environmental relevance and use of energy indicators in environmental management and research. J. Clean. Prod. 2006, 14, 134–145. [Google Scholar] [CrossRef]
  27. Mulder, K.; Hagens, N.J. Energy return on investment: Toward a consistent framework. AMBIO 2008, 37, 74–79. [Google Scholar] [CrossRef]
  28. Gagnon, L. Civilisation and energy payback. Energy Policy 2008, 36, 3317–3322. [Google Scholar] [CrossRef]
  29. Hall, C.A.S.; Balogh, S.; Murphy, D.J.R. What is the minimum EROI that a sustainable society must have? Energies 2009, 2, 25–47. [Google Scholar] [CrossRef]
  30. Polimeni, J.M.; Mayumi, K.; Giampietro, M.; Alacott, B. The Myth of Resource Efficiency; Earthscan: London, UK, 2009. [Google Scholar]
  31. Hammond, G.; Jones, C. Embodied Carbon - The Inventory of Carbon and Energy (ICE); Lowrie, F., Tse, P., Eds.; University of Bath with BSRIA: Bath, UK, 2011. [Google Scholar]
  32. Hernandez, P.; Kenny, P. Zero Energy Houses and Embodied Energy: Regulatory and Design Considerations. In Proceedings of the American Society of Mechanical Engineering 2nd International Conference on Energy Sustainability; Jacksonville, FL, USA: 10-14 August 2008.
  33. Hernandez, P.; Kenny, P. Defining Zero Energy Buildings—A life cycle perspective. In Proceedings of the PLEA 2008—25th Conference on Passive and Low Energy Architecture, Dublin, Ireland, 22-24 October 2008.
  34. Kellenberger, D.; Althaus, H.G. Relevance of simplifications in LCA of building components. Build. Environ. 2009, 44, 818–825. [Google Scholar] [CrossRef]
  35. ISO, Buildings and Constructed Assets—Service-Life Planning—Part 8: Reference Service Life and Service-Life Estimation; ISO 15686-8:2008; International Organization for Standardization (ISO): Geneva, Switzerland, 2008.
  36. Sartori, I.; Hestnes, A.G. Energy use in the life cycle of conventional and low-energy buildings: A review article. Energy Build. 2007, 39, 249–257. [Google Scholar] [CrossRef]
  37. Massachusetts Institute of TechnologyEnergy LaboratoryEnergy Technology Availability: Review of Longer Term Scenarios for Development and Deployment of Climate-Friendly Technologies; Massachusetts Institute of Technology, Energy Laboratory: Cambridge, MA, USA, 1997.
  38. Gregory, A.N.; Yost, P. A transparent, interactive software environment for communicating life cycle assessment results: An application to residential windows. J. Ind. Ecol. 2002, 5, 15–28. [Google Scholar]
  39. Paulsen, J.H.; Borg, M. A building sector related procedure to assess the relevance of the usage phase. Int. J. Life Cycle Assess. 2003, 8, 142–150. [Google Scholar] [CrossRef]
  40. Johnston, D. A Physically Based Energy and Carbon Dioxide Emission Model of the UK Housing Stock. Ph.D. Thesis, Leeds Metropolitan University, Leeds, UK, 2003. [Google Scholar]
  41. Khasreen, M.M.; Banfill, P.F.G.; Menzies, G.F. Life-cycle assessment and the environmental impact of buildings: A review. Sustainability 2009, 1, 674–701. [Google Scholar] [CrossRef]
  42. Guinée, J.B. Life Cycle Assessment: An Operational Guide to the ISO Standards; Kluwer Academic Publishers: Dordrecht, The Netherlands, 2002. [Google Scholar]
  43. Van Oers, L.; de Koning, A.; Guinée, J.B.; Huppes, G. Improving Characterisation Factors for Abiotic Resource Depletion as Recommended in the New Dutch LCA Handbook; Roads and Hydraulic Engineering Institute: Leiden, The Netherlands, 2002. [Google Scholar]
  44. Habert, G.; Bouzidi, Y.; Chen, C.; Jullien, A. Development of a depletion indicator for natural resources used in concrete. Resour. Conserv. Recy. 2010, 54, 364–376. [Google Scholar] [CrossRef]
  45. Habert, G.; Castillo, E.; Morel, J.C. Sustainable Indicators for Resources and Energy in Building Construction. In Proceedings of the Second International Conference on Sustainable Construction Materials and Technologies, Ancona, Italy, 28-30 June 2010.
  46. Muncey, R.W. Optimum thickness of insulation for Australian houses. Aust. J. Appl. Sci. 1955, 6, 486–495. [Google Scholar]
  47. Molnar, J.; Armitage, J.B. Determination of economic thickness of insulation. J. Inst. Engng. Ans. 1968, 40, 129. [Google Scholar]
  48. Barnhart, J.M. Economic thickness of thermal insulation. Chem. Eng. Prog. 1974, 70, 50. [Google Scholar]
  49. Brundrett, G.W. Some effects of thermal insulation on design. Appl. Energy 1975, 1, 7–30. [Google Scholar] [CrossRef]
  50. Probert, S.D.; Giani, S. Economics of thermal insulation. Appl. Energy 1976, 2, 189–204. [Google Scholar] [CrossRef]
  51. Probert, S.D.; Thirst, T.J. Thermal insulation provided by triangular sectioned attic spaces. Appl. Energy 1977, 3, 41–50. [Google Scholar] [CrossRef]
  52. Anani, A.; Jibril, Z. Role of thermal insulation in passive designs of buildings. Sol. Wind Techchnol. 1988, 5, 303–313. [Google Scholar] [CrossRef]
  53. Hasan, A. Optimizing insulation thickness for buildings using life cycle cost. Appl. Energy 1999, 63, 115–124. [Google Scholar] [CrossRef]
  54. Gustafsson, G. Optimisation of insulation measures on existing buildings. Energy Build. 2000, 33, 49–55. [Google Scholar] [CrossRef]
  55. Chaumont, D.; Angers, J.-F.; Frigon, A.; Pacher, G.; Roy, R. Évolution des Conditions Climatiques au Québec, Développement d’un Scenario Climatique Utilisé à des Fins de Prévision de la Demande d’Électricité au Québec sur l’Horizon 2030 (in French); Consortium Ouranos: Montreal, QC, Canada, 2007. [Google Scholar]
  56. Frank, T. Climate change impacts on building heating and cooling energy demand in Switzerland. Energy Build. 2005, 37, 1175–1185. [Google Scholar] [CrossRef]
  57. Gaterell, M.R.; McEvoy, M.E. The impact of energy externalities on the cost effectiveness of energy efficiency measures applied to dwellings. Energy Build. 2005, 37, 1017–1027. [Google Scholar] [CrossRef]
  58. Wang, X.; Chen, D.; Ren, Z. Assessment of climate change impact on residential building heating and cooling energy requirement in Australia. Build. Environ. 2010, 45, 1663–1682. [Google Scholar] [CrossRef]
  59. De Wilde, P. The implications of a changing climate for buildings. Build. Environ. 2012, 55, 1–7. [Google Scholar] [CrossRef]
  60. De Wilde, P.; Tian, W. Management of thermal performance risks in buildings subject to climate change. Build. Environ. 2012, 55, 167–177. [Google Scholar] [CrossRef]
  61. Feist, W. Life-Cycle Energy Balances Compared: Low-Energy House,Passiv House,Self-Sufficient House. In Proceedings of the International Symposium of CIB W67, International Council for Building Research, Vienna, Austria, 4-10 August 1996; pp. 183–190.
  62. Szalay, A.Z.-Z. What is missing from the concept of the new European Building Directive. Build. Environ. 2006, 42, 1781–1769. [Google Scholar]
  63. Comaklı, K.; Yüksel, B. Optimum insulation thickness of external walls for energy saving. Appl. Therm. Eng. 2003, 23, 473–479. [Google Scholar] [CrossRef]
  64. Bolattürk, A. Determination of optimum insulation thickness for building walls with respect to various fuels and climate zones in Turkey. Appl. Therm. Eng. 2006, 26, 1301–1309. [Google Scholar] [CrossRef]
  65. Dombaycı, Ö.A.; Gölcü, M.; Pancar, Y. Optimization of insulation thickness for external walls using different energy-sources. Appl. Energy 2006, 83, 921–928. [Google Scholar] [CrossRef]
  66. Kurt, H. The usage of air Gap in the composite wall for energy saving and air pollution. Environ. Prog. Sustain. Energy 2011, 30, 450–458. [Google Scholar] [CrossRef]
  67. Daouas, N.; Hassen, Z.; Ben Aissia, H. Analytical periodic solution for the study of thermal performance and optimum insulation thickness of building walls in Tunisia. Appl. Therm. Eng. 2010, 30, 319–326. [Google Scholar] [CrossRef]
  68. Daouas, N. A study on optimum insulation thickness in walls and energy savings in Tunisian buildings based on analytical calculation of cooling and heating transmission loads. Appl. Energy 2011, 88, 156–164. [Google Scholar] [CrossRef]
  69. Mahlia, T.M.I.; Iqbal, A. Cost benefits analysis and emission reductions of optimum thickness and air gaps for selected insulation materials for building walls in Maldives. Energy 2010, 35, 2242–2250. [Google Scholar] [CrossRef]
  70. Harvey, L.D.D. Net climatic impact of solid foam insulation produced with halocarbon and non-halocarbon blowing agents. Build. Environ. 2007, 42, 2860–2879. [Google Scholar] [CrossRef]
  71. Bribián, I.Z.; Uséon, A.A.; Scarpellini, S. Life cycle assessment in buildings: State-of-the-art and simplified LCA methodology as a complement for building certification. Build. Environ. 2009, 44, 2510–2520. [Google Scholar] [CrossRef]
  72. Masoso, O.T.; Grobler, L.J. A new and innovative look at anti-insulation behaviour in building energy consumption. Energy Build. 2008, 40, 1889–1894. [Google Scholar] [CrossRef]
  73. Huberman, N. Life Cycle Energy Costs of Building Materials: Alternatives for a Desert Environment. M.Sc. Thesis, Ben-Gurion University of the Negev, Beer-Sheva, Israel, 2007. [Google Scholar]
  74. Pulselli, R.M.; Simoncini, E.; Marchettini, N. Energy and emergy based cost-benefit evaluation of building envelopes relative to geographical location and climate. Build. Environ. 2009, 44, 920–928. [Google Scholar] [CrossRef]
  75. Utama, A.; Gheewala, S.H. Indonesian residential high rise buildings: A life cycle energy assessment. Energy Build. 2009, 41, 1263–1268. [Google Scholar] [CrossRef]
  76. Saito, M.; Shukuya, M. Energy and material use in the production of insulating glass windows. Solar Energy 1996, 58, 247–252. [Google Scholar] [CrossRef]
  77. Weir, G. Life Cycle Assessment of Multi-Glazed Windows. Ph.D. Thesis, Napier University, Napier, Australia, 1998. [Google Scholar]
  78. Weir, G.; Muneer, T. Energy and environmental impact analysis of double-glazed windows. Energy Convers. Manag. 1998, 39, 243–256. [Google Scholar] [CrossRef]
  79. Baumert, K.; Selman, M. Heating and Cooling Degree Days; World Resources Institute: Washington, DC, USA, 2003. [Google Scholar]
  80. Menzies, G.F.; Wherrett, J.R. Multiglazed windows: Potential for savings in energy, emissions and cost. Build. Serv. Eng. Res. Technol. 2005, 26, 249–258. [Google Scholar] [CrossRef]
  81. Asif, M.; Muneer, T.; Kubie, J. Sustainability analysis of window frames. Build. Serv. Eng. Res. Technol. 2005, 26, 71–87. [Google Scholar] [CrossRef]
  82. Sedovic, W.; Gorrhelf, J.H. What replacement windows can’t replace: The real cost of removing historic windows. APT Bull. J. Preserv. Technol. 2005, 36, 25–29. [Google Scholar]
  83. Recio, J.M.B.; Narvaez, R.P.; Guerrero, P.J. Estimate of energy consumption and CO2 emission associated with the production, use and final disposal of PVC, aluminium, and wooden windows. Département de Projectes d’Engineyeria, Universitat Politecnica de Catalunya, Environmental Modelling Lab., Barcelona, Spain, 2005. Available online: http://www.pvcinfo.be/bestanden/Baldasano%20study_windows.pdf (accessed on 4 July 2012).
  84. Dahlstrøm, O. Modern Highly Effective Windows; Report; NTNU: Trondheim, Sweden, 2010. [Google Scholar]
  85. Ramesh, T.; Prakash, R.; Shukla, K.K. Life cycle energy analysis of buildings: An overview. Energy Build. 2010, 42, 1592–1600. [Google Scholar] [CrossRef]
  86. Keoleian, G.A.; Blanchard, S.; Reppe, P. Life-cycle energy, costs, and strategies for improving a single-family house. J. Ind. Ecol. 2001, 4, 135–156. [Google Scholar]
  87. Uzsilaityte, L.; Martinaitis, V. Impact of the Implementation Energy Saving Measure on the Life Cycle Energy Consumption of the Building. In Proceedings of the 7th International Conference Environmental Engineering, Vilnius Gediminas Technical University, Vilnius, Lithuania, 22-23 May 2008.
  88. Yohanis, Y.G.; Norton, B. Life-cycle operational and embodied energy for a generic single-storey office building in the UK. Energy 2002, 27, 77–92. [Google Scholar] [CrossRef]
  89. Verbeeck, G.; Hens, H. Life cycle inventory of buildings: A contribution analysis. Build. Environ. 2010, 45, 964–967. [Google Scholar] [CrossRef]
  90. Gustavsson, L.; Joelsson, A. Life cycle primary energy analysis of residential buildings. Energy Build. 2010, 42, 210–220. [Google Scholar] [CrossRef]
  91. Ardente, F.; Beccali, M.; Cellura, M.; Mistretta, M. Energy and environmental benefits in public buildings as a result of retrofit actions. Renew. Sustain. Energy Rev. 2011, 15, 460–470. [Google Scholar] [CrossRef]
  92. Fay, R.; Treloar, G.; Iyer-Raniga, U. Life-cycle energy analysis of buildings: A case study. Build. Res. Inf. 2000, 28, 31–41. [Google Scholar] [CrossRef]
  93. Karlsson, J.F.; Moshfegh, B. A comprehensive investigation of a low-energy building in Sweden. Renew. Energy 2007, 32, 1830–1841. [Google Scholar] [CrossRef]
  94. Hernandez, P.; Cavanagh, S.; Brophy, V.; Futcher, J.; Szalay, Z.; Kenney, P. The Challenge of Refurbishing recentely Built Apartments: A Life Cycle Perspective. In Proceedings of the Paper Presented at the SB10mad: International Sustainable Building Conference, Madrid, Spain, 28-30 April 2010.

Article Metrics

Citations

Article Access Statistics

Multiple requests from the same IP address are counted as one view.