Embodied energy#Embodied energy in the energy field

{{Short description|Sum of all the energy required to produce any goods or services}}

{{Use dmy dates|date=November 2019}}

{{for|the related concept in relation to emissions|embedded emissions}}

{{Ecological economics|Concepts}}

Embodied energy is the sum of all the energy required to produce any goods or services, considered as if that energy were incorporated or 'embodied' in the product itself. The concept can help determine the effectiveness of energy-producing or energy saving devices, or the "real" replacement cost of a building, and, because energy-inputs usually entail greenhouse gas emissions, in deciding whether a product contributes to or mitigates global warming. One fundamental purpose for measuring this quantity is to compare the amount of energy produced or saved by the product in question to the amount of energy consumed in producing it.

Embodied energy is an accounting method that aims to find the sum total of the energy necessary for an entire product lifecycle. Determining what constitutes this lifecycle includes assessing the relevance and extent of energy in raw material extraction, transport, manufacture, assembly, installation, disassembly, deconstruction and/or decomposition, as well as human and secondary resources.

History

The history of constructing a system of accounts that records the energy flows through an environment can be traced back to the origins of accounting. As a distinct method, it is often associated with the Physiocrat's "substance" theory of value,{{cite book |first1=Philip |last1=Mirowski |title=More Heat Than Light: Economics as Social Physics, Physics as Nature's Economics |url=https://books.google.com/books?id=rmVhZnHId-oC&pg=PA154 |year=1991 |publisher=Cambridge University Press |isbn=978-0-521-42689-3 |pages=154–163}} and later the agricultural energetics of Sergei Podolinsky, a Russian physician,{{cite book |first1=J. |last1=Martinez-Alier |title=Ecological Economics: Energy Environment and Society |publisher=Basil Blackwell |year=1990 |isbn=978-0631171461 |url-access=registration |url=https://archive.org/details/ecologicaleconom0000mart }} and the ecological energetics of Vladmir Stanchinsky.{{cite book |first1=Douglas R. |last1=Weiner |title=Models of Nature: Ecology, Conservation, and Cultural Revolution in Soviet Russia |url=https://books.google.com/books?id=b8_2PvhwnO8C&pg=PA70 |year=2000 |publisher=University of Pittsburgh Press |isbn=978-0-8229-7215-0 |pages=70–71, 78–82}}

The main methods of embodied energy accounting that are used today grew out of Wassily Leontief's input-output model and are called Input-Output Embodied Energy analysis. Leontief's input-output model was in turn an adaptation of the neo-classical theory of general equilibrium with application to "the empirical study of the quantitative interdependence between interrelated economic activities".{{cite book |first1=W. |last1=Leontief |title=Input-Output Economics |publisher=Oxford University Press |year=1966 |page=134 }} According to Tennenbaum{{Cite thesis |last=Tennenbaum |first=Stephen E. |title=Network Energy Expenditures for Subsystem Production |type=MS |url=http://www.esnips.com/doc/ac5215f1-e91d-4c30-8648-2eee1f31488c/Network_Energy_Thesis.pdf |year=1988 |docket=CFW-88-08 |oclc=20211746 |url-status=dead |archive-url=https://web.archive.org/web/20070930190108/http://www.esnips.com/doc/ac5215f1-e91d-4c30-8648-2eee1f31488c/Network_Energy_Thesis.pdf |archive-date=2007-09-30 }} Leontief's Input-Output method was adapted to embodied energy analysis by Hannon{{cite journal |first1=B. |last1=Hannon |title=The Structure of ecosystems |journal=Journal of Theoretical Biology |volume=41 |issue=3 |pages=535–546 |date=October 1973 |doi=10.1016/0022-5193(73)90060-X |pmid=4758118 |bibcode=1973JThBi..41..535H |url=http://urizen-geography.nsm.du.edu/~psutton/Sutton_Courses/Geog_3890_Ecological_Economics/SeminalEEpapers/B_HannonStructureOfEcosystems.pdf }} to describe ecosystem energy flows. Hannon's adaptation tabulated the total direct and indirect energy requirements (the energy intensity) for each output made by the system. The total amount of energies, direct and indirect, for the entire amount of production was called the embodied energy.

Methodologies

Embodied energy analysis is interested in what energy goes to supporting a consumer, and so all energy depreciation is assigned to the final demand of the consumer. Different methodologies use different scales of data to calculate energy embodied in products and services of nature and human civilization. International consensus on the appropriateness of data scales and methodologies is pending. This difficulty can give a wide range in embodied energy values for any given material. In the absence of a comprehensive global embodied energy public dynamic database, embodied energy calculations may omit important data on, for example, the rural road/highway construction and maintenance needed to move a product, marketing, advertising, catering services, non-human services and the like. Such omissions can be a source of significant methodological error in embodied energy estimations.{{harvnb|Lenzen|2001}} Without an estimation and declaration of the embodied energy error, it is difficult to calibrate the sustainability index, and so the value of any given material, process or service to environmental and economic processes.

=Standards=

The SBTool, UK Code for Sustainable Homes was, and USA LEED still is, a method in which the embodied energy of a product or material is rated, along with other factors, to assess a building's environmental impact. Embodied energy is a concept for which scientists have not yet agreed absolute universal values because there are many variables to take into account, but most agree that products can be compared to each other to see which has more and which has less embodied energy. Comparative lists (for an example, see the University of Bath Embodied Energy & Carbon Material InventoryG.P.Hammond and C.I.Jones (2006) [http://www.circularecology.com/embodied-energy-and-carbon-footprint-database.html Embodied energy] and carbon footprint database, Department of Mechanical Engineering, University of Bath, United Kingdom) contain average absolute values, and explain the factors which have been taken into account when compiling the lists.

Typical embodied energy units used are MJ/kg (megajoules of energy needed to make a kilogram of product), t{{CO2}} (tonnes of carbon dioxide created by the energy needed to make a kilogram of product). Converting MJ to t{{CO2}} is not straightforward because different types of energy (oil, wind, solar, nuclear and so on) emit different amounts of carbon dioxide, so the actual amount of carbon dioxide emitted when a product is made will be dependent on the type of energy used in the manufacturing process. For example, the Australian Government[http://www.cmit.csiro.au/brochures/tech/embodied/ CSIRO on embodied energy: Australia's foremost scientific institution] {{webarchive|url=https://web.archive.org/web/20060225154902/http://www.cmit.csiro.au/brochures/tech/embodied/ |date=2006-02-25 }} gives a global average of 0.098 t{{CO2}} = 1 GJ. This is the same as 1 MJ = 0.098 kg{{CO2}} = 98 g{{CO2}} or 1 kg{{CO2}} = 10.204 MJ.

=Related methodologies=

In the 2000s, drought conditions in Australia generated interest in the application of embodied energy analysis methods to water. This has led to the use of the concept of embodied water.{{cite journal |last1=McCormack |first1=M. |last2=Treloar |first2=G.J. |last3=Palmowski |first3=L. |last4=Crawford |first4=R. |title=Modelling direct and indirect water requirements of construction |journal=Building Research and Information |volume=35 |issue=2 |pages=156–162 |year=2007 |doi=10.1080/09613210601125383 |bibcode=2007BuRI...35..156M |s2cid=109032580 }}

Data

Many databases exist to quantify the embodied energy of goods and services, including materials and products. These are based on various data sources, with geographic and temporal relevance variations and system boundary completeness. One such database is the [https://msd.unimelb.edu.au/research/projects/current/environmental-performance-in-construction Environmental Performance in Construction (EPiC) Database] developed at The University of Melbourne, which includes embodied energy data for over 250 mainly construction materials. This database also includes values for embodied water and greenhouse gas emissions.{{cite book |last1=Crawford |first1=Robert |title=EPiC database 2019 |last2=Stephan |first2=André |last3=Prideaux |first3=Fabian |publisher=The University of Melbourne |year=2019 |isbn=978-0-7340-5495-1 |publication-place=Melbourne, Australia |page= |oclc=1132202846}}

The main reason for the differences in embodied energy data between databases is the source of data and methodology used in their compilation. Bottom-up 'process' data is typically sourced from product manufacturers and suppliers. While this data is generally more reliable and specific to particular products, the methodology used to collect process data typically results in much of the embodied energy of a product being excluded, mainly due to the time, costs and complexity of data collection. Based on national statistics, top-down environmentally-extended input-output (EEIO) data can be used to fill these data gaps. While EEIO analysis of products can be useful on its own for initial scoping of embodied energy, it is generally much less reliable than process data and rarely relevant for a specific product or material. Hence, hybrid methods for quantifying embodied energy have been developed,{{cite journal |last1=Crawford |first1=R.H. |last2=Bontinck |first2=P.-A. |last3=Stephan |first3=A. |last4=Wiedmann |first4=T. |last5=Yu |first5=M. |title=Hybrid life cycle inventory methods – A review |journal=Journal of Cleaner Production |date=2018 |volume=172 |pages=1273–1288 |doi=10.1016/j.jclepro.2017.10.176|bibcode=2018JCPro.172.1273C |hdl=11343/194165 |s2cid=116770528 |url=https://unsworks.unsw.edu.au/bitstreams/05e0c708-34d3-4e54-8ad1-832fc7483270/download |hdl-access=free }} using available process data and filling any data gaps with EEIO data. Databases that rely on this hybrid approach, such as The University of Melbourne's [https://msd.unimelb.edu.au/research/projects/current/environmental-performance-in-construction EPiC Database], provide a more comprehensive assessment of the embodied energy of products and materials.

In common materials

Selected data from the Inventory of Carbon and Energy ('ICE') prepared by the University of Bath (UK)

class="wikitable sortable"
MaterialEnergy MJ/kgCarbon kg {{CO2}}/kgMaterial density kg/m3
Aggregate0.0830.00482240
Concrete (1:1.5:3)1.110.1592400
Bricks (common)30.241700
Concrete block (Medium density)0.670.0731450
Aerated block3.50.3750
Limestone block0.852180
Marble20.1162500
Cement mortar (1:3)1.330.208
Steel (general, av. recycled content)20.11.377800
Stainless steel56.76.157850
Timber (general, excludes sequestration)8.50.46480–720
Glue laminated timber120.87
Cellulose insulation (loose fill)0.94–3.343
Cork insulation26160
Glass fibre insulation (glass wool)281.3512
Flax insulation39.51.730
Rockwool (slab)16.81.0524
Expanded Polystyrene insulation88.62.5515–30
Polyurethane insulation (rigid foam)101.53.4830
Wool (recycled) insulation20.925
Straw bale0.91100–110
Mineral fibre roofing tile372.71850
Slate0.1–1.00.006–0.0581600
Clay tile6.50.451900
Aluminium (general & incl 33% recycled)1558.242700
Bitumen (general)510.38–0.43
Medium-density fibreboard110.72680–760
Plywood151.07540–700
Plasterboard6.750.38800
Gypsum plaster1.80.121120
Glass150.852500
PVC (general)77.22.411380
Vinyl flooring65.642.921200
Terrazzo tiles1.40.121750
Ceramic tiles120.742000
Wool carpet1065.53
Wallpaper36.41.93
Vitrified clay pipe (DN 500)7.90.52
Iron (general)251.917870
Copper (average incl. 37% recycled)422.68600
Lead (incl 61% recycled)25.211.5711340
Ceramic sanitary ware291.51
Paint - Water-borne592.12
Paint - Solvent-borne973.13

class="wikitable"

! Photovoltaic (PV) Cells Type !! Energy MJ per m2 !! Energy kWh per m2 !! Carbon kg {{CO2}} per m2

Monocrystalline (average)47501319.5242
Polycrystalline (average)40701130.5208
Thin film (average)1305362.567

In transportation

Theoretically, embodied energy is the energy used to extract materials from mines, manufacture vehicles, assemble, transport, maintain, transform them to transport energy, and ultimately recycle these vehicles. Besides, the energy needed to build and sustain transport networks, whether road or rail, should also be considered. The process to be implemented is so complex that no one dares to put forward a figure.

According to the Institut du développement durable et des relations internationales, in the field of transportation, "it is striking to note that we consume more embodied energy in our transportation expenditures than direct energy", and "we consume less energy to move around in our personal vehicles than we consume the energy we need to produce, sell and transport the cars, trains or buses we use".{{cite web |first1=Lucas |last1=Chancel |first2=Prabodh |last2=Pourouchottamin |title=L'énergie grise : la face cachée de nos consommations d'énergie |date=March 2013 |work=Propositions |publisher=IDDRI |url=https://www.iddri.org/en/node/21566 |language=fr}}

Jean-Marc Jancovici advocates a carbon footprint analysis of any transportation infrastructure project, before its construction.{{cite web |first=Jean-Marc |last=Jancovici |title=Pour un bilan carbone des projets d'infrastructures de transport |date=2017-12-30 |language=fr |url=https://jancovici.com/publications-et-co/articles-de-presse/pour-un-bilan-carbone-des-projets-dinfrastructures-de-transport/}}

=In automobiles=

== Manufacturing ==

According to Volkswagen, the embodied energy contents of a Golf A3 with a petrol engine amounts to 18 000 kWh (i.e. 12% of 545 GJ as shown in the report(de) [http://www.volkswagen.de/content/medialib/vwd4/de/Volkswagen/Nachhaltigkeit/service/download/umweltberichte/umweltbericht_20012002deutsch48mb/_jcr_content/renditions/rendition.file/umweltberichte_par_0009_file.pdf Volkswagen environmental report 2001/2002] {{webarchive|url=https://web.archive.org/web/20160303192010/http://www.volkswagen.de/content/medialib/vwd4/de/Volkswagen/Nachhaltigkeit/service/download/umweltberichte/umweltbericht_20012002deutsch48mb/_jcr_content/renditions/rendition.file/umweltberichte_par_0009_file.pdf |date=2016-03-03 }} see page 27). A Golf A4 (equipped with a turbocharged direct injection) will show an embodied energy amounting to 22 000 kWh (i.e. 15% of 545 GJ as shown in the report). According to the French energy and environment agency ADEME (fr) [http://www.ademe.fr/sites/default/files/assets/documents/90511_acv-comparative-ve-vt-resume.pdf Life cycle assessment] {{Webarchive|url=https://web.archive.org/web/20150726174549/http://www.ademe.fr/sites/default/files/assets/documents/90511_acv-comparative-ve-vt-resume.pdf |date=26 July 2015 }} website www.ademe.fr see page 9 a motor car has an embodied energy contents of 20 800 kWh whereas an electric vehicle shows an embodied energy contents amounting to 34 700 kWh.

An electric car has a higher embodied energy than a combustion engine one, owing to the battery and electronics. According to Science & Vie, the embodied energy of batteries is so high that rechargeable hybrid cars constitute the most appropriate solution,(fr) Science & Vie # 1213 October 2018. see pages 48 till 51. with their batteries smaller than those of an all-electric car.

== Fuel ==

As regards energy itself, the factor energy returned on energy invested (EROEI) of fuel can be estimated at 8, which means that to some amount of useful energy provided by fuel should be added 1/7 of that amount in embodied energy of the fuel. In other words, the fuel consumption should be augmented by 14.3% due to the fuel EROEI.

According to some authors, to produce 6 liters of petrol requires 42 kWh of embodied energy (which corresponds to approximately 4.2 liters of diesel in terms of energy content).(de) [https://www.springerprofessional.de/elektromobilitaet/dieselmotor/endenergiebezogene-analyse-diesel-versus-elektromobilitaet/16673694 Final energy analysis: gasoline vs. electromobility] website springerprofessional.de

== Road construction ==

We have to work here with figures, which prove still more difficult to obtain. In the case of road construction, the embodied energy would amount to 1/18 of the fuel consumption (i.e. 6%).[http://www.pavementinteractive.org/2012/02/21/energy-and-road-construction-whats-the-mileage-of-roadway/ energy-and-road-construction] website www.pavementinteractive.org

== Other figures available ==

Treloar, et al. have estimated the embodied energy in an average automobile in Australia as 0.27 terajoules (i.e. 75 000 kWh) as one component in an overall analysis of the energy involved in road transportation.{{cite journal |last1=Treloar |first1=Graham |last2=Crawford |first2=Robert |title=Hybrid Life-Cycle Inventory for Road Construction and Use |journal=Journal of Construction Engineering and Management |volume=130 |issue=1 |pages= 43–49|year=2004 |doi=10.1061/(ASCE)0733-9364(2004)130:1(43) }}

In buildings

File:建売住宅 (4355308311).jpg

Although most of the focus for improving energy efficiency in buildings has been on their operational emissions, it is estimated that about 30% of all energy consumed throughout the lifetime of a building can be in its embodied energy (this percentage varies based on factors such as age of building, climate, and materials). In the past, this percentage was much lower, but as much focus has been placed on reducing operational emissions (such as efficiency improvements in heating and cooling systems), the embodied energy contribution has come much more into play. Examples of embodied energy include: the energy used to extract raw resources, process materials, assemble product components, transport between each step, construction, maintenance and repair, deconstruction and disposal. As such, it is important to employ a whole-life carbon accounting framework to analyze the carbon emissions in buildings.{{Cite journal|last1 = Ibn-Mohammed|first1 = T.|last2 = Greenough|first2 = R.|last3 = Taylor|first3 = S.|last4 = Ozawa-Meida|first4 = L.|last5 = Acquaye|first5 = A.|date = 2013-11-01|title = Operational vs. embodied emissions in buildings—A review of current trends|journal = Energy and Buildings|volume = 66|pages = 232–245|doi = 10.1016/j.enbuild.2013.07.026| bibcode=2013EneBu..66..232I }} Studies have also shown the need to go beyond the building scale and to take into account the energy associated with mobility of occupants and the embodied energy of infrastructure requirements, in order to avoid shifting energy needs across scales of the built environment.{{Cite journal |last1=Stephan |first1=André |last2=Crawford |first2=Robert H. |last3=de Myttenaere |first3=Kristel |date=2012 |title=Towards a comprehensive life cycle energy analysis framework for residential buildings |url=https://www.sciencedirect.com/science/article/pii/S0378778812004562 |journal=Energy and Buildings |series= |volume=55 |pages=592–600 |doi=10.1016/j.enbuild.2012.09.008 |bibcode=2012EneBu..55..592S |issn=0378-7788}}{{Cite journal |last1=Stephan |first1=André |last2=Crawford |first2=Robert H. |last3=de Myttenaere |first3=Kristel |date=2013 |title=A comprehensive assessment of the life cycle energy demand of passive houses |url=https://www.doi.org/10.1016/j.apenergy.2013.05.076 |journal=Applied Energy |language=en |volume=112 |pages=23–34 |doi=10.1016/j.apenergy.2013.05.076|bibcode=2013ApEn..112...23S }}{{Cite journal |last1=Stephan |first1=André |last2=Crawford |first2=Robert H. |last3=Bunster |first3=Victor |last4=Warren-Myers |first4=Georgia |last5=Moosavi |first5=Sareh |date=2022 |title=Towards a multiscale framework for modeling and improving the life cycle environmental performance of built stocks |url=https://onlinelibrary.wiley.com/doi/10.1111/jiec.13254 |journal=Journal of Industrial Ecology |language=en |volume=26 |issue=4 |pages=1195–1217 |doi=10.1111/jiec.13254 |bibcode=2022JInEc..26.1195S |issn=1088-1980|url-access=subscription }}{{Cite journal |last1=Bastos |first1=Joana |last2=Batterman |first2=Stuart A. |last3=Freire |first3=Fausto |date=2016-05-18 |title=Significance of mobility in the life-cycle assessment of buildings |url=http://www.tandfonline.com/doi/full/10.1080/09613218.2016.1097407 |journal=Building Research & Information |language=en |volume=44 |issue=4 |pages=376–393 |doi=10.1080/09613218.2016.1097407 |bibcode=2016BuRI...44..376B |issn=0961-3218|url-access=subscription }}

In the energy field

= EROEI =

EROEI (Energy Returned On Energy Invested) provides a basis for evaluating the embodied energy due to energy.

Final energy has to be multiplied by \frac {\hbox{1}} {\hbox{EROEI-1}} in order to get the embodied energy.

Given an EROEI of eight, for example, a seventh of the final energy corresponds to the embodied energy.

Not only that, but embodied energy due to the construction and maintenance of power plants should also be taken into account to really obtain overall embodied energy. Here, figures are badly needed.

= Electricity =

In the BP Statistical Review of World Energy June 2018, toe are converted into kWh "on the basis of thermal equivalence assuming 38% conversion efficiency in a modern thermal power station".{{citation needed|date=June 2024}}

In France, by convention, the ratio between primary energy and final energy in electricity amounts to 2.58,(fr) [https://www.legifrance.gouv.fr/affichTexte.do?cidTexte=JORFTEXT000000788395 "Decree of 15th September 2006 on the energy performance diagnosis of existing buildings for sale in mainland France"], website legifrance.gouv.fr corresponding to an efficiency of 38.8%.{{citation needed|date=June 2024}}

In Germany, on the contrary, because of the swift development of the renewable energies, the ratio between primary energy and final energy in electricity amounts to only 1.8,(de) [http://www.gesetze-im-internet.de/enev_2007/BJNR151900007.html laws in Internet] {{Webarchive|url=https://web.archive.org/web/20200731002838/http://www.gesetze-im-internet.de/enev_2007/BJNR151900007.html |date=31 July 2020 }} site web gesetze-im-internet.de see section 2.1.1 corresponding to an efficiency of 55.5%.{{citation needed|date=June 2024}}

According to EcoPassenger,[http://ecopassenger.org/bin/query.exe/en?ld=uic-eco&L=vs_uic&seqnr=2&ident=7o.038511.1573535906& EcoPassenger] website ecopassenger.org, run by International Union of Railways. overall electricity efficiency would amount to 34% in the UK, 36% in Germany and 29% in France.[http://ecopassenger.hafas.de/hafas-res/download/Ecopassenger_Methodology_Data.pdf EcoPassenger Environmental Methodology and DataUpdate 2016] website ecopassenger.hafas.de; see page 15, table 2-3.

Data processing

According to association négaWatt, embodied energy related to digital services amounted to 3.5 TWh/a for networks and 10.0 TWh/a for data centres (half for the servers per se, i. e. 5 TWh/a, and the other half for the buildings in which they are housed, i. e. 5 TWh/a), figures valid in France, in 2015. The organization is optimistic about the evolution of the energy consumption in the digital field, underlining the technical progress being made.(fr) [http://decrypterlenergie.org/la-revolution-numerique-fera-t-elle-exploser-nos-consommations-denergie Will digital revolution increase our energy consumption?] website decrypterlenergie.org, website of association négaWatt. The Shift Project, chaired by Jean-Marc Jancovici, contradicts the optimistic vision of the association négaWatt, and notes that the digital energy footprint is growing at 9% per year.(fr) [https://theshiftproject.org/wp-content/uploads/2018/10/2018-10-04_Rapport_Pour-une-sobri%C3%A9t%C3%A9-num%C3%A9rique_Rapport_The-Shift-Project.pdf Lean ITC] website theshiftproject.org; see page 4.

See also

References

{{Reflist|30em}}

Bibliography

  • {{cite book |first1=D.H. |last1=Clark |first2=G.J. |last2=Treloar |first3=R. |last3=Blair |chapter=Estimating the increasing cost of commercial buildings in Australia due to greenhouse emissions trading |editor1-first=J. |editor1-last=Yang |editor2-first=P.S. |editor2-last=Brandon |editor3-first=A.C. |editor3-last=Sidwell |title=Proceedings of the CIB 2003 International Conference on Smart and Sustainable Built Environment, Brisbane, Australia |year=2003 |isbn=978-1741070415 |oclc=224896901|hdl=10536/DRO/DU:30009596 }}
  • {{Cite thesis |last=Costanza |first=R. |title=Embodied Energy Basis for Economic-Ecologic Systems |type=Ph.D. |url=http://ufdc.ufl.edu/UF00089540/00001/1 |year=1979 |publisher=University of Florida |id=UF00089540:00001 |oclc=05720193 }}
  • {{cite journal |first1=R.H. |last1=Crawford |title=Validation of the Use of Input-Output Data for Embodied Energy Analysis of the Australian Construction Industry |journal=Journal of Construction Research |volume=6 |issue=1 |pages=71–90 |year=2005 |doi=10.1142/S1609945105000250 }}
  • {{cite book |last1=Crawford |first1=R.H. |last2=Stephan |first2=A. |last3=Prideaux |first3=F. |title=Environmental Performance in Construction (EPiC) Database |publisher=The University of Melbourne |location=Melbourne, Victoria, Australia |date=2019 |doi=10.26188/5dc1e272cbedc |url=https://melbourne.figshare.com/articles/book/EPiC_Database/10257728}}
  • {{cite journal |first1=M. |last1=Lenzen |title=Errors in conventional and input-output-based life-cycle inventories |journal=Journal of Industrial Ecology |volume=4 |issue=4 |pages=127–148 |year=2001 |doi=10.1162/10881980052541981 |s2cid=154022052 }}
  • {{cite journal |first1=M. |last1=Lenzen |first2=G.J. |last2=Treloar |title=Embodied energy in buildings: wood versus concrete-reply to Börjesson and Gustavsson |journal=Energy Policy |volume=30 |issue=3 |pages=249–255 |date=February 2002 |doi=10.1016/S0301-4215(01)00142-2 |bibcode=2002EnPol..30..249L }}
  • {{cite journal |first1=G.J. |last1=Treloar |title=Extracting Embodied Energy Paths from Input-Output Tables: Towards an Input-Output-based Hybrid Energy Analysis Method |journal=Economic Systems Research |volume=9 |issue=4 |pages=375–391 |year=1997 |doi=10.1080/09535319700000032 }}
  • {{Cite thesis |last=Treloar |first=Graham J. |title=A comprehensive embodied energy analysis framework |type=Ph.D. |year=1998 |publisher=Deakin University |hdl=10536/DRO/DU:30023444 }}
  • {{cite journal |first1=G.J. |last1=Treloar |first2=C. |last2=Owen |first3=R. |last3=Fay |title=Environmental assessment of rammed earth construction systems |journal=Structural Survey |volume=19 |issue=2 |pages=99–105 |year=2001 |doi=10.1108/02630800110393680 |url=http://eprints.utas.edu.au/8221/2/Environmental_assessment_of_rammed_earth_construction_systems.pdf }}
  • {{cite journal |first1=G.J. |last1=Treloar |first2=P.E.D. |last2=Love |first3=G.D. |last3=Holt |title=Using national input-output data for embodied energy analysis of individual residential buildings |journal=Construction Management and Economics |volume=19 |issue=1 |pages=49–61 |year=2001 |doi=10.1080/014461901452076 |s2cid=110124981 }}