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Energy return on investment
View on WikipediaIn energy economics and ecological energetics, energy return on investment (EROI), also sometimes called energy returned on energy invested (ERoEI), is the ratio of the amount of usable energy (the exergy) delivered from a particular energy resource to the amount of exergy used to obtain that energy resource.[1]
Arithmetically, the EROI can be defined as:
- .[2]
When the EROI of a source of energy is less than or equal to one, that energy source becomes a net "energy sink" and can no longer be used as a source of energy. A related measure, called energy stored on energy invested (ESOEI), is used to analyse storage systems.[3][4]
To be considered viable as a prominent fuel or energy source, a fuel or energy must have an EROI ratio of at least 3:1.[5][2]
History
[edit]The energy analysis field of study is credited with being popularised by Charles A. S. Hall, a systems ecology and biophysical economics professor at the State University of New York. Hall applied the biological methodology developed at an Ecosystems Marine Biological Laboratory, and then adapted that method to research human industrial civilisation. The concept would have its greatest exposure in 1984, with a paper by Hall that appeared on the cover of the journal Science.[6][7]
Application to various technologies
[edit]Photovoltaic
[edit]The issue is still the subject of numerous studies, prompting academic argument. That's mainly because the "energy invested" critically depends on technology, methodology, and system boundary assumptions, resulting in a range from a maximum of 2000 kWh/m2 of module area down to a minimum of 300 kWh/m2 with a median value of 585 kWh/m2 according to a meta-study from 2013.[9]
Regarding output, it obviously depends on the local insolation, not just the system itself, so assumptions have to be made.
Some studies (see below) include in their analysis that photovoltaic cells produce electricity, while the invested energy may be lower grade primary energy.
A 2015 review in Renewable and Sustainable Energy Reviews assessed the energy payback time and EROI of a variety of PV module technologies. In this study, which uses an insolation of 1700 kWh/m2/yr and a system lifetime of 30 years, mean harmonised EROIs between 8.7 and 34.2 were found. Mean harmonised energy payback time varied from 1.0 to 4.1 years.[10][better source needed] In 2021, the Fraunhofer Institute for Solar Energy Systems calculated an energy payback time of around 1 year for European PV installations (0.9 years for Catania in Southern Italy, 1.1 years for Brussels) with wafer-based silicon PERC cells.[11]
Wind turbines
[edit]In the scientific literature EROIs wind turbines is around 16 unbuffered and 4 buffered.[12] Data collected in 2018 found that the EROI of operational wind turbines averaged 19.8 with high variability depending on wind conditions and wind turbine size.[13] EROIs tend to be higher for recent wind turbines compared to older technology wind turbines. Vestas reports an EROI of 31 for its V150 model wind turbine.[14]
Hydropower plants
[edit]The EROI for hydropower plants averages about 110 when it is run for about 100 years.[15]
Oil sands
[edit]Because much of the energy required for producing oil from oil sands (bitumen) comes from low value fractions separated out by the upgrading process, there are two ways to calculate EROI, the higher value given by considering only the external energy inputs and the lower by considering all energy inputs, including self generated. One study found that in 1970, oil sand net energy returns were about 1.0, but by 2010 had increased to about 5.23.[16][clarification needed]
Conventional oil
[edit]Conventional sources of oil have a rather large variation depending on various geologic factors. The EROI for refined fuel from conventional oil sources varies from around 18 to 43.[17]
Oil Shale
[edit]Due to the process heat input requirements for oil shale harvesting, the EROI is low. Typically, natural gas is used, either directly combusted for process heat or used to power an electricity-generating turbine, which then uses electrical heating elements to heat the underground layers of shale to produce oil from the kerogen. The resulting EROI is typically around 1.4–1.5.[17] Economically, oil shale might be viable due to the effectively free natural gas on site used for heating the kerogen, but opponents have debated that the natural gas could be extracted directly and used for relatively inexpensive transportation fuel rather than heating shale for a lower EROI and higher carbon emissions.
Oil liquids
[edit]The weighted average standard EROI of all oil liquids (including coal-to-liquids, gas-to-liquids, biofuels, etc.) is expected to decrease from 44.4 in 1950 to 6.7 in 2050.[18]
Natural gas
[edit]The standard EROI for natural gas is estimated to decrease from 141.5 in 1950 to an apparent plateau of 16.8 in 2050.[19]
Nuclear plants
[edit]Non-manmade energy inputs
[edit]The natural or primary energy sources are not included in the calculation of energy invested, only the human-applied sources. For example, in the case of biofuels, the solar insolation driving photosynthesis is not included, and the energy used in the stellar synthesis of fissile elements is not included for nuclear fission. The energy returned includes only human usable energy and not wastes such as waste heat.
Nevertheless, heat of any form can be counted where it is actually used for heating. However, the use of waste heat in district heating and water desalination in cogeneration plants is rare, and in practice it is often excluded in EROI analysis of energy sources.[clarification needed]
Competing methodology
[edit]In a 2010 paper by Murphy and Hall, a proposed extended ["Ext"] boundary protocol, for all future research on EROI, was detailed, to produce what they consider to be a more realistic assessment and to generate greater consistency in comparisons than what Hall and others view as the "weak points" in competing methodology.[22] In more recent years, however, a source of continued controversy is the creation of a different methodology endorsed by certain members of the IEA which for example most notably in the case of photovoltaic solar panels, controversially generates more favorable values.[23][24]
In the case of photovoltaic solar panels, the IEA method tends to focus on the energy used in the factory process alone. In 2016, Hall observed that much of the published work in this field is produced by advocates or persons with a connection to business interests among the competing technologies, and that government agencies had not yet provided adequate funding for rigorous analysis by more neutral observers.[25][26]
Relationship to net energy gain
[edit]EROI and Net energy (gain) measure the same quality of an energy source or sink in numerically different ways. Net energy describes the amounts, while EROI measures the ratio or efficiency of the process. They are related simply by
or
For example, given a process with an EROI of 5, expending 1 unit of energy yields a net energy gain of 4 units. The break-even point happens with an EROI of 1 or a net energy gain of 0. The time to reach this break-even point is called energy payback period (EPP) or energy payback time (EPBT).[27][28]
Economic influence
[edit]Although many qualities of an energy source matter (for example, oil is energy-dense and transportable, while wind is variable), when the EROI of the main sources of energy for an economy fall, that energy becomes more difficult to obtain and its relative price may increase.
With regard to fossil fuels, when oil was originally discovered, it took on average one barrel of oil to find, extract, and process about 100 barrels of oil. The ratio, for discovery of fossil fuels in the United States, has declined steadily over the last century from about 1000:1 in 1919 to only 5:1 in the 2010s.[2]
Since the invention of agriculture, humans have increasingly used exogenous sources of energy to multiply human muscle power. Some historians have attributed this largely to more easily exploited (i.e. higher EROI) energy sources, which is related to the concept of energy slaves. Thomas Homer-Dixon[29] argues that a falling EROI in the Later Roman Empire was one of the reasons for the collapse of the Western Empire in the fifth century CE. In "The Upside of Down", he suggests that EROI analysis provides a basis for the analysis of the rise and fall of civilisations. Looking at the maximum extent of the Roman Empire, (60 million) and its technological base, the agrarian base of Rome was about 1:12 per hectare for wheat and 1:27 for alfalfa (giving a 1:2.7 production for oxen). One can then use this to calculate the population of the Roman Empire required at its height, based on about 2,500–3,000 calories per day per person. It comes out roughly equal to the area of food production at its height. But ecological damage (deforestation, soil fertility loss, particularly in southern Spain, southern Italy, Sicily and especially north Africa) saw a collapse in the system beginning in the 2nd century, as EROI began to fall. It bottomed in 1084 when Rome's population, which had peaked under Trajan at 1.5 million, was only 15,000.
Evidence also fits the cycle of Mayan and Cambodian collapse too. Joseph Tainter[30] suggests that diminishing returns of the EROI is a chief cause of the collapse of complex societies, which has been suggested as caused by peak wood in early societies. Falling EROI due to depletion of high-quality fossil fuel resources also poses a difficult challenge for industrial economies, and could potentially lead to declining economic output and challenge the concept (which is very recent when considered from a historical perspective) of perpetual economic growth.[31]
Criticism of EROI
[edit]EROI is calculated by dividing the energy output by the energy input. Measuring total energy output is often easy, especially in the case of an electrical output, where some appropriate electricity meter can be used. However, researchers disagree on how to determine energy input accurately and therefore arrive at different numbers for the same source of energy.[32]
How deep should the probing in the supply chain of the tools being used to generate energy go? For example, if steel is being used to drill for oil or construct a nuclear power plant, should the energy input of the steel be taken into account? Should the energy input into building the factory being used to construct the steel be taken into account and amortised? Should the energy input of the roads which are used to ferry the goods be taken into account? What about the energy used to cook the steelworkers' breakfasts? These are complex questions evading simple answers.[33] A full accounting would require considerations of opportunity costs and comparing total energy expenditures in the presence and absence of this economic activity.
However, when comparing two energy sources, a standard practice for the supply chain energy input can be adopted. For example, consider the steel, but don't consider the energy invested in factories deeper than the first level in the supply chain. It is in part for these fully encompassed systems reasons, that in the conclusions of Murphy and Hall's paper in 2010, an EROI of 5 by their extended methodology is considered necessary to reach the minimum threshold of sustainability,[22] while a value of 12–13 by Hall's methodology is considered the minimum value necessary for technological progress and a society supporting high art.[23][24]
Richards and Watt propose an Energy Yield Ratio for photovoltaic systems as an alternative to EROI (which they refer to as Energy Return Factor). The difference is that it uses the design lifetime of the system, which is known in advance, rather than the actual lifetime. This also means that it can be adapted to multi-component systems where the components have different lifetimes.[34]
Another issue with EROI that many studies attempt to tackle is that the energy returned can be in different forms, and these forms can have different utility. For example, electricity can be converted more efficiently than thermal energy into motion, due to electricity's lower entropy. In addition, the form of energy of the input can be completely different from the output. For example, energy in the form of coal could be used in the production of ethanol. This might have an EROI of less than one, but could still be desirable due to the benefits of liquid fuels (assuming the latter are not used in the processes of extraction and transformation).
Additional EROI calculations
[edit]There are three prominent expanded EROI calculations: point of use, extended, and societal. Point of Use EROI expands the calculation to include the cost of refining and transporting the fuel during the refining process. Since this expands the bounds of the calculation to include more production processes, EROI will decrease.[2] Extended EROI provides point of use expansions, as well as the cost of creating the infrastructure needed for transportation of the energy or fuel once refined.[35] Societal EROI is the sum of all the EROIs of all the fuels used in a society or nation. A societal EROI has never been calculated, and researchers believe it may currently be impossible to know all variables necessary to complete the calculation, but attempted estimates have been made for some nations. Calculations are done by summing all of the EROIs for domestically produced and imported fuels and comparing the result to the Human Development Index (HDI), a tool often used to understand well-being in a society.[36] According to this calculation, the amount of energy a society has available to it increases the quality of life for the people living in that country, and countries with less energy available also have a harder time satisfying citizens' basic needs.[37] This is to say that societal EROI and overall quality of life are very closely linked.
EROI and payback periods of some types of power plants
[edit]The following table is a compilation of sources of energy.[38] The minimum requirement is a breakdown of the cumulative energy expenses according to material data. Frequently in literature, harvest factors are reported, for which the origin of the values is not completely transparent. These are not included in this table.
The bold numbers are those given in the respective literature source; the normal printed ones are derived (see Mathematical Description).
- (a) The cost of fuel transportation is taken into account
- (b) The values refer to the total energy output. The expense for storage power plants, seasonal reserves or conventional load balancing power plants is not taken into account.
- (c) The data for the E-82 come from the manufacturer, but are confirmed by TÜV Rheinland.[citation needed]
ESOEI
[edit]ESOEI (or ESOIe) is used when EROI is below 1. "ESOIe is the ratio of electrical energy stored over the lifetime of a storage device to the amount of embodied electrical energy required to build the device."[4]
| Storage Technology | ESOEI[4] |
|---|---|
| Lead–acid battery | 5 |
| Zinc–bromide battery | 9 |
| Vanadium redox battery | 10 |
| NaS battery | 20 |
| Lithium-ion battery | 32 |
| Pumped hydroelectric storage | 704 |
| Compressed-air energy storage | 792 |
One of the notable outcomes of the Stanford University team's assessment on ESOI was that if pumped storage was not available, the combination of wind energy and the commonly suggested pairing with battery technology, as it presently exists, would not be sufficiently worth the investment, suggesting instead curtailment.[44]
EROI under rapid growth
[edit]A related recent concern is energy cannibalism, where energy technologies can have a limited growth rate if climate neutrality is demanded. Many energy technologies are capable of replacing significant volumes of fossil fuels and concomitant greenhouse gas emissions. Unfortunately, neither the enormous scale of the current fossil fuel energy system nor the necessary growth rate of these technologies is well understood within the limits imposed by the net energy produced for a growing industry. This technical limitation is known as energy cannibalism and refers to an effect where rapid growth of an entire energy-producing or energy efficiency industry creates a need for energy that uses (or cannibalises) the energy of existing power plants or production plants.[45]
The solar breeder overcomes some of these problems. A solar breeder is a photovoltaic panel manufacturing plant which can be made energy-independent by using energy derived from its own roof using its own panels. Such a plant becomes not only energy self-sufficient but a major supplier of new energy, hence the name solar breeder. Research on the concept was conducted by Centre for Photovoltaic Engineering, University of New South Wales, Australia.[46][47] The reported investigation establishes certain mathematical relationships for the solar breeder which indicate that a vast amount of net energy is available from such a plant for the indefinite future.[48] The solar module processing plant at Frederick, Maryland[49] was originally planned as such a solar breeder. In 2009 the Sahara Solar Breeder Project was proposed by the Science Council of Japan as a cooperation between Japan and Algeria with the highly ambitious goal of creating hundreds of GW of capacity within 30 years.[50]
See also
[edit]- Cost of electricity by source – levelised cost of energy
- Embodied energy
- Emergy
- Energy balance
- Energy cannibalism
- Exergy – useful energy
- Jevons paradox – 1880s observation of the efficiency effect multiplier
- Khazzoom–Brookes postulate – 1980s updating of Jevons paradox
- Net energy gain
- Social metabolism
- Thermoeconomics
References
[edit]- ^ Murphy, D.J.; Hall, C.A.S. (2010). "Year in review EROI or energy return on (energy) invested". Annals of the New York Academy of Sciences. 1185 (1): 102–118. Bibcode:2010NYASA1185..102M. doi:10.1111/j.1749-6632.2009.05282.x. PMID 20146764. S2CID 6433639.
- ^ a b c d Hall, CA; Lambert, JG; Balogh, SB (2013). "EROI of different fuels and the implications for society". Energy Policy. 64: 141–52. doi:10.1016/j.enpol.2013.05.049.
- ^ "Why energy storage is a dead-end industry - Energy Storage Report". 15 October 2014.
- ^ a b c Barnhart, Charles J.; Dale, Michael; Brandt, Adam R.; Benson, Sally M. (2013). "The energetic implications of curtailing versus storing solar- and wind-generated electricity". Energy Environ. Sci. 6 (10): 2804–10. Bibcode:2013EnEnS...6.2804B. doi:10.1039/c3ee41973h.
- ^ Atlason, R; Unnthorsson, R (2014). "Ideal EROI (energy return on investment) deepens the understanding of energy systems". Energy. 67: 241–45. Bibcode:2014Ene....67..241A. doi:10.1016/j.energy.2014.01.096.
- ^ "Will Fossil Fuels be Able to Maintain Economic Growth? A Q&A with Charles Hall". Scientific American. April 2013.
- ^ N.Y. Times article featuring Hall Retrieved November-3-09
- ^ "Photovoltaics Report" (PDF). Fraunhofer ISE. July 28, 2014. Archived (PDF) from the original on July 25, 2014. Retrieved August 31, 2014.
- ^ Dale, M.; et al. (2013). "Energy balance of the global photovoltaic (PV) industry – is the PV industry a net electricity producer?. In". Environmental Science and Technology. 47 (7): 3482–3489. Bibcode:2013EnST...47.3482D. doi:10.1021/es3038824. PMID 23441588.
- ^ Bhandari; et al. (2015). "Energy payback time (EPBT) and energy return on energy invested (EROI) of solar photovoltaic systems: A systematic review and meta-analysis. In". Renewable and Sustainable Energy Reviews. 47: 133–141. Bibcode:2015RSERv..47..133B. doi:10.1016/j.rser.2015.02.057.
- ^ Fraunhofer Institut (2022), Photovoltaics Report, page 37, https://www.ise.fraunhofer.de/content/dam/ise/de/documents/publications/studies/Photovoltaics-Report.pdf
- ^ "Energy intensities, EROIs, and energy payback times of electricity generating power plants" (PDF). Festkoerper-kernphysik.de. Retrieved July 26, 2022.
- ^ "Meta-Analysis of Net Energy Return for Wind Power Systems". Researchgate.net.
- ^ "Archived copy" (PDF). Archived from the original (PDF) on 2020-10-21. Retrieved 2020-10-20.
{{cite web}}: CS1 maint: archived copy as title (link) [title missing] - ^ Atlason, R. S.; Unnthorsson, R. (2014-06-01). "Energy return on investment of hydroelectric power generation calculated using a standardised methodology". Renewable Energy. 66: 364–370. Bibcode:2014REne...66..364A. doi:10.1016/j.renene.2013.12.029. ISSN 0960-1481. Retrieved 2024-02-27.
- ^ Brandt, A. R.; Englander, J.; Bharadwaj, S. (2013). "The energy efficiency of oil sands extraction: Energy return ratios from 1970 to 2010". Energy. 55: 693–702. Bibcode:2013Ene....55..693B. doi:10.1016/j.energy.2013.03.080.
- ^ a b "An Assessment of Energy Return on Investment of Oil Shale". Western Resource Advocates. Retrieved 2020-04-21.
- ^ Delannoy, Louis; Longaretti, Pierre-Yves; Murphy, David J.; Prados, Emmanuel (December 2021). "Peak oil and the low-carbon energy transition: A net-energy perspective". Applied Energy. 304 117843. Bibcode:2021ApEn..30417843D. doi:10.1016/j.apenergy.2021.117843. S2CID 240530798.
- ^ Delannoy, Louis; Longaretti, Pierre-Yves; Murphy, David J.; Prados, Emmanuel (January 2021). "Assessing Global Long-Term EROI of Gas: A Net-Energy Perspective on the Energy Transition". Energies. 14 (16): 5112. doi:10.3390/en14165112.
- ^ Murphy, David J.; Raugei, Marco; Carbajales-Dale, Michael; Rubio Estrada, Brenda (2022). "Energy Return on Investment of Major Energy Carriers: Review and Harmonization". Sustainability. 14 (12): 7098. Bibcode:2022Sust...14.7098M. doi:10.3390/su14127098.
- ^ "Energy Return on Investment - World Nuclear Association". Retrieved 2024-02-27.
- ^ a b Ferroni, Ferruccio; Hopkirk, Robert J. (2016). "Energy Return on Energy Invested (ERoEI) for photovoltaic solar systems in regions of moderate insolation". Energy Policy. 94: 336–344. Bibcode:2016EnPol..94..336F. doi:10.1016/j.enpol.2016.03.034.
- ^ a b Fairley, Peter (30 August 2012). "Argument Over the Value of Solar Focuses on Spain: Analysts disagree on whether the energy returned from solar is worth the energy invested". IEEE Spectrum: Technology, Engineering, and Science News.
- ^ a b Pickard, William F. (2014). "Energy return on energy invested (EROI): A quintessential but possibly inadequate metric for sustainability in a solar-powered world? [point of view]". Proceedings of the IEEE. 102 (8): 1118–1122. doi:10.1109/JPROC.2014.2332092.
- ^ "The Real EROI of Photovoltaic Systems: Professor Hall Weighs in". Resilience. May 27, 2016.
- ^ Hall, Charles (2016-05-26). "The real EROI of photovoltaic systems: professor Hall weighs in". Cassandra's Legacy. Ugo Bardi.
- ^ Marco Raugei; Pere Fullana-i-Palmer; Vasilis Fthenakis (March 2012). "The Energy Return on Energy Investment (EROI) of Photovoltaics: Methodology and Comparisons with Fossil Fuel Life Cycles" (PDF). Brookhaven National Laboratory. Archived (PDF) from the original on 8 March 2016.
- ^ Ibon Galarraga, M. González-Eguino, Anil Markandya (1 January 2011). Handbook of Sustainable Energy. Edward Elgar Publishing. p. 37. ISBN 978-0857936387. Retrieved 9 May 2017 – via Google Books.
{{cite book}}: CS1 maint: multiple names: authors list (link) - ^ Homer-Dixon, Thomas (2007). The Upside of Down; Catastrophe, Creativity and the Renewal of Civilisation. Island Press. ISBN 978-1-59726-630-7.
- ^ Tainter, Joseph (1990). The Collapse of Complex Societies. Cambridge University Press. ISBN 978-0521386739.
- ^ Morgan, Tim (2013). Life After Growth. Petersfield, UK: Harriman House. ISBN 9780857193391.
- ^ Mason Inman. Behind the Numbers on Energy Return on Investment. Scientific American, April 1, 2013. Archive
- ^ Richards, Michael; Hall, Charles (2014). "Does a Change in Price of Fuel Affect GDP Growth? An Examination of the US Data from 1950–2013". Energies. 7 (10): 6558–6570. doi:10.3390/en7106558.
- ^ Richards, B.S.; Watt, M.E. (2006). "Permanently dispelling a myth of photovoltaics via the adoption of a new net energy indicator" (PDF). Renewable and Sustainable Energy Reviews. 11: 162–172. doi:10.1016/j.rser.2004.09.015.
- ^ Hall CA, Lambert JG, Balogh SB. 2013. EROEI of different fuels and the implications for society. Energy Policy. 141–52
- ^ Lambert JG, Hall CA, Balogh S, Gupta A, Arnold M. 2014. Energy, EROI and quality of life. Energy Policy.
- ^ Lambert JG, Hall CA, Balogh S, Gupta A, Arnold M. 2014. Energy, EROI and quality of life. Energy Policy. 153–67 & Arvesen A, Hertwich EG. 2014. More caution is needed when using life cycle assessment to determine energy return on investment (EROI). Energy Policy. 1–6
- ^ German Wikipedia.
- ^ E. Pick, Hermann-Josef Wagner: Beitrag zum kumulierten Energieaufwand ausgewählter Windenergiekonverter. Arbeitsbericht des Instituts für ökologisch verträgliche Energiewirtschaft, Universität Essen, 1998.
- ^ Mehr Windkraft an Land rückt Ökologie ins Blickfeld Archived 2011-10-09 at the Wayback Machine. In: vdi Nachrichten. 2 September 2011. Retrieved 17 September 2011.
- ^ Enercon Windblatt 4/2011 Archived 2012-01-12 at the Wayback Machine (PDF; 1,2 MB). Internetseite von Enercon. Retrieved 10 January 2012.
- ^ Rodoula Tryfonidou, Hermann-Josef Wagner: Offshore-Windkraft – Technikauswahl und aggregierte Ergebnisdarstellung. (Kurzfassung Archived 2007-02-08 at the Wayback Machine, PDF-Datei, 109 kB) Lehrstuhl für Energiesysteme und Energiewirtschaft, Ruhr-Universität, Bochum 2004.
- ^ Mariska de Wild-Scholten: Environmental profile of PV mass production: globalization. (PDF; 1,8 MB) 2011.
- ^ Report, Energy Storage (October 15, 2014). "Why energy storage is a dead-end industry". Energy Storage Report.
- ^ Pearce, J.M. (2008). "Limitations of Greenhouse Gas Mitigation Technologies Set by Rapid Growth and Energy Cannibalism". Klima. Archived from the original on 2009-08-17. Retrieved 2011-04-06.
- ^ "The Azimuth Project: Solar Breeder". Archived from the original on 2013-05-28. Retrieved 2011-04-06.
- ^ Lindmayer, Joseph (1978). The solar breeder. Proceedings, Photovoltaic Solar Energy Conference, Luxembourg, September 27–30, 1977. Dordrecht: D. Reidel Publishing. pp. 825–835. Bibcode:1978pvse.conf..825L. ISBN 9027708894. OCLC 222058767.
- ^ Lindmayer, Joseph (1977). The Solar Breeder. NASA.
- ^ "The BP Solarex Facility Tour in Frederick, MD". Sustainable Cooperative for Organic Development. 2010-03-29. Retrieved 28 February 2013.
- ^ Koinuma, H.; Kanazawa, I.; Karaki, H.; Kitazawa, K. (March 26, 2009). Sahara solar breeder plan directed toward global clean energy superhighway. G8+5 Academies' meeting in Rome. Science Council of Japan.
External links
[edit]- World-Nuclear.org Archived 2013-02-15 at the Wayback Machine, World Nuclear Association study on EROI with assumptions listed.
- Web.archive.org, Wayback Archive of OilAnalytics.org, "EROI as a Measure of Energy Availability"
- EOearth.org, Energy return on investment (EROI)
- EOearth.org, Net energy analysis
- H2-pv.us, Essay on H2-PV Breeder Synergies
Energy return on investment
View on GrokipediaFundamentals
Definition and Core Principles
Energy return on investment (EROI), also termed energy returned on energy invested (EROEI), measures the ratio of usable energy delivered by a fuel or energy technology to the total energy expended in its extraction, processing, and delivery.[3][14] This biophysical metric, pioneered by ecologist Charles A. S. Hall in the 1970s, prioritizes physical energy flows over monetary costs to assess the net productivity of energy sources.[15][16] The core principle underlying EROI is that only energy surpluses beyond production costs enable societal functions, as all human activity—from agriculture to manufacturing—derives from available net energy.[3][16] An EROI exceeding 1:1 yields a net positive return, but empirical analyses indicate that values below approximately 5:1 to 10:1 constrain complex economies by diverting disproportionate resources to energy acquisition itself.[17][15] This threshold arises because upstream investments (e.g., drilling, refining) and downstream infrastructure (e.g., transportation, conversion losses) compound energy demands, leaving less for non-energy sectors.[3] EROI embodies causal realism in energy economics by linking resource quality to thermodynamic limits: diminishing returns from depleting high-grade reserves (e.g., conventional oil fields yielding EROIs of 20:1 to 100:1 historically) versus lower-grade alternatives (e.g., tar sands at 3:1 to 5:1) directly influence scalability and substitution feasibility.[14][15] Unlike financial ROI, EROI remains invariant to price signals or subsidies, revealing inherent efficiencies grounded in physics rather than market distortions.[16] For instance, solar photovoltaics have improved from EROIs around 1:1 in early systems to 10:1 or higher in modern installations, driven by manufacturing advances, though intermittency and storage add indirect costs not always captured in basic ratios.[18][19]Societal and Economic Thresholds
Societal thresholds for energy return on investment (EROI) denote the minimum ratios necessary to produce surplus energy supporting non-subsistence activities, population expansion, and economic complexity. Below an EROI of 1:1, no net energy is gained, rendering the process dependent on external subsidies and unsustainable in isolation.[20] For practical energy carriers, such as liquid fuels for transportation, an EROI of 3:1 serves as a baseline viability threshold, below which delivery to end-users incurs net losses requiring compensation from higher-EROI sources. Hall et al. (2009) calculated this using 2005 U.S. gasoline data, where refining, distribution, and retail stages consume approximately one-third of gross output, implying that sources like corn ethanol (EROI ≈1.3:1 point-of-sale) demand fossil fuel offsets to function economically.[20] Broader societal functionality escalates these requirements. Complex civilizations allocate only a fraction of primary energy to extraction and conversion, reserving the rest for agriculture, manufacturing, and services; thus, EROIs under 5:1 to 10:1 constrain surplus, limiting specialization and growth. Lambert et al. (2014) correlated global EROI estimates with human development indices, revealing that per capita net energy above 60 GJ/year—tied to system-wide EROIs of 12:1 to 14:1—aligns with peak quality-of-life metrics, beyond which diminishing returns apply but declines risk regression to agrarian levels.[9] Economic analyses quantify this further: primary energy systems must exceed an EROI of 11:1 to enable positive GDP growth, as higher energy expenditures (e.g., >11% of U.S. GDP historically) correlate with stagnation by crowding out capital investment. Fizaine and Court (2016) derived this from 1850–2012 data, showing post-1945 U.S. growth coincided with low energy cost shares (under 5% of GDP), enabled by high-EROI fossil fuels; exceeding the threshold reverses causality, where energy scarcity hampers productivity regardless of efficiency gains. These thresholds reflect causal dependencies: low EROI elevates the energy intensity of economies, diverting labor and capital from value-adding pursuits and amplifying vulnerability to shocks, as evidenced by 1970s oil crises when conventional oil EROI began declining from 30:1 peaks. Sustaining modern infrastructure, including electrified grids and urban systems, demands EROIs above 20:1 historically, with shortfalls necessitating trade-offs in societal complexity.[20][9]Historical Development
Origins in Ecological Economics
The concept of energy return on investment (EROI) emerged from systems ecology, a foundational influence on ecological economics, where researchers sought to quantify the net benefits of energy flows in natural and human systems. Howard T. Odum, a pioneering ecologist, laid early groundwork through his development of net energy analysis, emphasizing the distinction between gross energy yields and the energy costs of extraction and transformation. In works such as Environment, Power, and Society (1971) and subsequent publications in 1972 and 1973, Odum argued that sustainable systems maximize net energy surplus after accounting for investments, applying this to ecosystems where organisms forage or migrate to achieve positive returns. This biophysical perspective challenged neoclassical economics by prioritizing thermodynamic constraints over monetary metrics, influencing the nascent field of ecological economics that integrated ecology with economic analysis to address resource limits.[21][2] Charles A.S. Hall, a student of Odum and systems ecologist, formalized EROI as a ratio of usable energy delivered to energy invested, initially deriving it from empirical studies of salmon migration in the late 1960s and early 1970s to evaluate foraging efficiency. Hall first quantified EROI for fossil fuels in the mid-1970s amid the oil crises, calculating values like 30:1 for U.S. oil in the early 20th century, highlighting how high returns historically fueled industrial growth but were declining due to depletion. This application extended Odum's principles to human energy systems, positing EROI as a universal metric for assessing viability across biological and technological processes, with thresholds below 10:1 potentially undermining complex societies. Hall's 1981 paper with Cleveland and Kaufmann explicitly framed EROI within ecological economics, critiquing overreliance on market prices that ignore embodied energy costs.[3][4][22] Within ecological economics, EROI gained traction as a tool for evaluating sustainability and limits to growth, diverging from mainstream economics by insisting on empirical energy accounting over abstract utility models. Proponents like Hall argued that declining EROI for conventional fuels, evidenced by global oil averages dropping from 100:1 in the 1930s to around 20:1 by the 2000s, signals biophysical bottlenecks that monetary policies cannot circumvent. This origins narrative underscores EROI's role in fostering causal realism about resource dependence, informing debates on transitions to lower-EROI alternatives without assuming infinite substitutability. Early adopters in the field, including the International Society for Ecological Economics (founded 1989), incorporated EROI to quantify trade-offs in energy portfolios, prioritizing sources with returns exceeding societal minimums of 3:1 to 5:1 for basic functions.[3][21][23]Key Milestones and Studies
The term "energy return on investment" (EROI) was first used in a 1979 study by Hall et al., which applied net energy analysis to ecological systems including commercial fishing, building on earlier net energy concepts from Howard Odum's work in the early 1970s.[21] A pivotal milestone came in 1981 with Hall and Cleveland's analysis of U.S. petroleum drilling and production, published in Science, which quantified EROI for oil fields and revealed a historical decline from approximately 100:1 in the 1930s to about 30:1 by the 1970s, attributing the trend to depleting reserves and increased extraction efforts.[21] [24] In 1984, Cleveland et al. extended EROI to broader economic contexts in another Science paper, examining energy's role in U.S. economic output and highlighting how declining fossil fuel EROIs could constrain growth, thus gaining wider academic traction.[21] This was followed in 1986 by Hall, Cleveland, and Kaufmann's book Energy and Resource Quality: The Ecology of the Economic Process, which synthesized EROI methodologies across resource types and emphasized quality-adjusted energy returns.[21] Subsequent studies in the 1990s and 2000s applied EROI to emerging fuels, such as Pimentel and Patzek's 2005 assessment of U.S. corn ethanol production yielding an EROI below 1:1 after accounting for agricultural inputs, underscoring challenges for biofuels.[25] Interest revived post-2005 amid rising oil prices and peak oil discussions, leading to global syntheses like Hall et al.'s 2014 review of EROI trends across fuels, which documented continued declines in conventional oil to 10-20:1 globally by the 2010s.[21] [25] These works established EROI as a core metric in biophysical economics, influencing debates on energy transitions despite methodological variations in boundary definitions.[10]Methodology
Calculation Approaches and Boundaries
The energy return on investment (EROI) is fundamentally calculated as the ratio of usable energy delivered to society divided by the total energy expended to obtain and deliver that energy, often expressed as EROI = Energy Output / Energy Input. The net energy fraction, representing the proportion of gross energy output remaining after subtracting inputs, is (EROI - 1)/EROI; for an EROI of 6.7, this is approximately 85%, whereas a 50% net energy fraction corresponds to an EROI of 2.[26] This approach employs either process analysis, which traces detailed energy flows through specific stages bottom-up, or economic input-output (IO) analysis, which allocates energy costs top-down based on monetary expenditures and sectoral averages.[26] Process methods provide granular accuracy for individual projects but require extensive data, while IO methods enable broader scalability yet introduce aggregation errors from averaged assumptions.[26] System boundaries delineate the scope of inputs and outputs, critically influencing results; narrower boundaries (e.g., at the point of extraction) yield higher EROI values by excluding downstream costs, whereas broader ones incorporate processing, transportation, and distribution, reducing the ratio.[27] [25] Boundaries are selected based on analytical objectives, data availability, and desired comparability, often framed in a two-dimensional protocol: one axis for process stages (extraction, refining, end-use) and another for input types (direct on-site energy like fuels for drilling, indirect embodied energy in equipment, or feedback loops).[26] For instance, standard EROI (EROI_st) typically encompasses direct and indirect inputs up to societal delivery, excluding consumer-side uses to focus on production efficiency.[25] Expanding boundaries progressively lowers EROI by accounting for additional costs, such as natural gas inputs in oil refining or infrastructure maintenance; oil EROI might drop from 20:1 at the wellhead to 10:1 or less when including full supply chains.[25] Variations include point-of-use EROI, which extends to final consumption and further diminishes values, and societal EROI, which embeds the resource within the broader economy to assess net contributions to human activity.[27] [18] Non-energy inputs, like materials, are converted to energy equivalents via heat content, exergy, or emergy methods to maintain consistency, though choices here can vary results by factors of 2-5.[26] Methodological protocols recommend transparent documentation of boundaries to enable replication and comparison, with life cycle assessment (LCA) increasingly integrated for renewables to standardize cradle-to-gate evaluations despite persistent boundary ambiguities.[18]Inclusion of Non-Energy Inputs
In EROI assessments, non-energy inputs encompass resources such as labor, capital equipment, raw materials (e.g., steel or concrete), land, and water that are not direct energy carriers but contribute to the production, extraction, or delivery of energy. These inputs are distinguished from energy expenditures like fuels or electricity used in operations, though their production often embeds prior energy costs via embodied energy calculations. Standard EROI methodology focuses primarily on direct and indirect energy investments in the denominator, but non-energy inputs pose challenges for boundary definition, as including them risks conflating energy efficiency with broader resource or economic accounting.[26] Two primary approaches exist for handling non-energy inputs in EROI calculations. The first, most commonly applied, excludes them from the energy denominator or lists them separately for qualitative assessment, preserving EROI as a pure measure of thermodynamic efficiency. This method facilitates cross-fuel comparisons by isolating energy returns, as non-energy factors like labor (whose metabolic energy is typically negligible, around 0.1-1% of total inputs) or material scarcity do not directly dilute the energy yield. However, critics argue this omission understates systemic costs, particularly for renewables requiring rare earth elements or extensive land, where non-energy constraints could limit scalability independently of energy ratios.[26][28] The second approach converts non-energy inputs into energy equivalents, typically by multiplying their monetary cost by the economy's energy intensity (e.g., megajoules per dollar of GDP). For instance, if steel production costs $500 per ton and the U.S. energy intensity is approximately 7.5 MJ per 2010 dollar, the implied energy cost is incorporated into the EROI denominator. This method, advocated in protocols for consistency, captures indirect energy embedded in supply chains but assumes uniform efficiency across inputs and ignores non-substitutable scarcities, such as geopolitical risks for minerals. Studies applying this to U.S. oil and gas in the 2000s found converted non-energy costs added 10-20% to total investments, lowering EROI by a similar margin compared to energy-only boundaries.[26][25][28] Researchers like Charles Hall emphasize transparent boundaries, recommending conversion for comprehensive "extended" EROI variants while cautioning against over-inclusion that blurs the metric's focus on net energy surplus. For hydroelectric projects, non-energy inputs like concrete dams are often converted, yielding EROI values of 50-200:1 after accounting, though site-specific factors like reservoir evaporation (a non-energy loss) are noted separately. In contrast, solar PV analyses sometimes highlight unconverted non-energy needs (e.g., silicon refining labor and toxic waste handling), with some studies reporting EROI around 6-7 depending on methodology and boundaries, though estimates vary widely; these could reduce effective returns below 10:1 in real-world deployments if scarcity drives up costs. This inclusion debate underscores EROI's limitations as a standalone metric, as non-energy bottlenecks—evident in declining ore grades for battery materials since 2010—may impose causal constraints on energy systems beyond caloric accounting.[25][29][30]Debates and Criticisms
Methodological Limitations
One primary methodological limitation of EROI calculations stems from inconsistent system boundaries, particularly spatial mismatches across supply chain stages such as extraction, refining, distribution, and point-of-use delivery.[6] For instance, shale gas EROI may exceed 80:1 at the wellhead but decline to approximately 5:1 after accounting for processing and grid delivery losses, rendering comparisons between fuels evaluated at different stages misleading.[6] Temporal boundary inconsistencies further exacerbate this, as conventional analyses often integrate full lifecycle inputs against outputs, while others rely on single-year data, yielding divergent results for technologies with high upfront energy costs like photovoltaics, where early-year EROI appears low before amortizing investments over decades.[6] Scale-related ambiguities compound comparability challenges, as facility-level EROI (e.g., individual wind turbine lifetimes yielding >70:1) differs fundamentally from industry-scale assessments using annual energy flows, or "power return on investment" (PROI), which for wind reached about 23:1 in regional contexts by 2018.[31] Rapid growth in renewable sectors, often exceeding 10% annually, distorts PROI downward due to disproportionate upfront investments not yet balanced by scaled outputs, assuming non-steady-state conditions unlike mature fossil fuel industries.[31] These scale mismatches prevent direct equivalence between process-specific metrics and broader societal or economic EROI variants, which incorporate wider infrastructural dependencies.[27] Data quality issues and the absence of a standardized methodology contribute to substantial variability in reported EROI values, with ranges spanning orders of magnitude for the same fuel; for example, nuclear power estimates vary from below 1:1 to over 60:1 depending on boundary choices and data sources.[10] Limited access to granular, primary data—such as proprietary energy intensities for unconventional oils—forces reliance on estimates or extrapolations, while disagreements over energy quality corrections (e.g., weighting high-density fuels higher) amplify discrepancies, as seen in geothermal EROI fluctuating between 2:1 and 39:1.[10] Such inconsistencies undermine the metric's reliability for cross-technology evaluations without harmonization protocols.[10] Additional challenges include unaddressed assumptions about steady-state operations and the exclusion of dynamic factors like technological evolution or regional grid efficiencies, which can alter EROI by factors of 2–3 across thermal-dominated versus low-loss networks.[6] Overall, these limitations necessitate cautious interpretation, as ambiguous definitions and boundary selections can inflate or deflate apparent energetic favorability, hindering robust policy or investment decisions.[31][6]Responses to Critiques from Economics
Economists have argued that energy constitutes only 5–10% of GDP in developed economies, implying that fluctuations in energy productivity, including EROI, cannot be the primary driver of economic growth, as other factors like labor and capital dominate.[3] Proponents of EROI counter that this understates energy's foundational role, as all economic activity—encompassing labor, capital formation, and goods production—ultimately depends on energy inputs governed by thermodynamic principles; historical data show that surges in high-EROI fossil fuel use from the 19th century onward correlated closely with exponential GDP growth, suggesting energy surplus enables complexity rather than merely correlating with it.[3] [25] A related critique posits that market prices efficiently allocate resources, rendering physical metrics like EROI redundant since prices incorporate scarcity, opportunity costs, and technological substitutions without needing biophysical accounting.[3] In response, EROI advocates emphasize that markets often fail to internalize full energy costs due to externalities such as environmental degradation and depletion, which are not priced equivalently to direct energy inputs; for instance, empirical analyses indicate that as global oil EROI declined from over 100:1 in the early 20th century to around 10–20:1 by the 2010s, economic growth rates slowed despite technological advances, implying biophysical constraints bind even when markets signal abundance through subsidies or delayed scarcity.[3] [32] Critics further contend that EROI overlooks energy quality differences, capital depreciation, and the potential for indefinite substitution via innovation, arguing that low-EROI sources can still support growth if economically viable.[3] Defenders reply with evidence from societal thresholds: studies estimate that modern industrialized societies require a minimum EROI of approximately 7–11:1 to sustain infrastructure and complexity, below which net energy surplus diminishes, forcing reallocation from discretionary economic activity to energy acquisition; this is evidenced by simulations showing that substituting high-EROI conventional oil (EROI ~20:1 historically) with lower-EROI alternatives like tar sands (~3–5:1) or biofuels (~1–4:1) elevates the energy share of GDP, compressing overall productivity regardless of market adaptations.[33] [25] Measurement challenges, including boundary definitions and exclusion of indirect inputs like financial overheads, are highlighted as rendering EROI incomparable to economic return-on-investment metrics that account for time value and risk.[31] Responses stress that standardized EROI protocols, such as point-of-use boundaries, provide consistent biophysical benchmarks complementary to economics; for example, peer-reviewed assessments consistently find nuclear fission achieving EROI values of 20–75:1 across lifecycle analyses, outperforming many renewables when including storage and transmission, thus informing policy where economic models undervalue long-term physical viability.[27] Multiple studies reinforce this by linking aggregate EROI declines to empirical economic drag, as seen in post-2008 stagnation periods aligning with falling oil EROI.[34]Applications to Fossil Fuels
Conventional Sources
Conventional oil extraction, particularly from large, accessible fields, has historically exhibited high EROI values, with early U.S. production reaching approximately 100:1 due to shallow wells and minimal processing requirements.[35] Over time, as fields mature and extraction shifts to smaller or deeper reservoirs, EROI has declined; for instance, combined conventional oil and gas in the U.S. fell from around 20:1 in the mid-1990s to about 12:1 by the 2010s, reflecting a 40% reduction driven by geological depletion rather than technological offsets.[25] Similar trends appear in regions like the Norwegian North Sea, where EROI dropped from 40:1 to 20:1 as production peaked and transitioned to more energy-intensive methods.[36] At the refinery stage, EROI for conventional oil-derived fuels typically ranges from 18:1 to 43:1, depending on boundary assumptions that include upstream extraction and downstream refining. These figures underscore that while conventional oil remains among the higher-EROI fossil fuels, its net energy surplus has eroded with widespread field depletion since the mid-20th century.[3] For conventional natural gas, EROI estimates vary by region but generally show a downward trajectory linked to declining reservoir quality. In Canada, production EROI decreased from 38:1 in 1993 to 15:1 by the mid-2000s, coinciding with intensified drilling in maturing basins.[37] Globally, the energy invested to produce gas—including direct extraction, indirect materials, and infrastructure—averages about 6.7% of gross output, yielding an EROI of roughly 15:1 as of recent assessments.[38] Unlike oil, natural gas benefits from relatively lower processing demands in conventional settings, such as pipeline transport from onshore or shallow offshore fields, but depletion effects dominate long-term trends, with limited evidence of sustained EROI gains from efficiency improvements.[3] These values pertain to point-of-production boundaries; extending to end-use delivery further reduces effective EROI due to compression and distribution losses. Coal from conventional surface and underground mining maintains some of the highest EROI among fossil fuels, often exceeding 50:1 at the mine mouth, owing to minimal energy inputs for excavation relative to the fuel's high calorific density.[39] In China, a major producer, coal sector EROI declined modestly from 35:1 in the mid-1990s to 27:1 by 2010, attributable to deeper shafts and thinner seams rather than systemic inefficiencies.[40] Global projections suggest peak EROI around 95:1 in the 2030s before potential declines from resource exhaustion, though coal's stability contrasts with oil and gas due to abundant reserves and straightforward combustion preparation.[39] When assessed at electricity generation boundaries, coal's EROI drops to about one-third of mine-mouth values, reflecting thermal inefficiencies, but it remains viable for baseload power in conventional contexts.[41] Across these sources, aggregate fossil fuel EROI at extraction has trended downward to approximately 30:1 in recent decades, highlighting depletion's role over technological mitigation.[27]Unconventional and Declining Fields
Unconventional fossil fuel extraction methods, including oil sands (tar sands) and oil shale, deliver markedly lower EROI than conventional crude oil due to the high energy demands of mining, heating, and processing viscous or kerogen-bound hydrocarbons. For Canadian oil sands, Poisson and Hall estimated an EROI of approximately 4.5:1, described as conservatively high by limiting analysis to upfront extraction and upgrading processes while excluding downstream refining and transport.[25] Independent assessments place surface-mined oil sands EROI at around 5:1, with in-situ methods yielding even lower returns owing to steam injection requirements.[42] Oil shale, involving pyrolysis of kerogen to produce synthetic crude, exhibits EROI values at the wellhead of roughly 2:1 when accounting for internal energy content, with net energy ratios ranging from 1.2:1 to 1.8:1 across in-situ and surface retorting techniques.[43] These figures contrast sharply with conventional oil's historical wellhead EROI of 18:1 to 23:1.[43] Shale oil from hydraulically fractured tight formations similarly underperforms, with reported EROI typically between 1.5:1 and 4:1, reflecting rapid well decline rates and repeated fracturing.[44] Unconventional natural gas from shale, accessed via fracking, fares better but remains sensitive to depletion and infrastructure costs. Analyses indicate pipeline-head EROI of 13:1 to 23:1 (mean ~17:1), though point-of-use values drop to ~5:1 after transmission and distribution energy inputs.[45][6] In declining or mature conventional fields, EROI erodes as primary recovery gives way to energy-intensive enhanced oil recovery (EOR) methods like thermal flooding or CO2 injection. Thermal EOR in heavy oil reservoirs yields net energy ratios as low as 2.5:1 to 3:1, with ultra-heavy oil fields averaging ~10.6:1.[46] Global oil production EROI has thus trended downward, from ~30:1 around 2000 to ~17:1 by the 2010s, driven by reserve depletion and the pivot to these marginal sources amid conventional field exhaustion.[32] This shift underscores thermodynamic constraints, where geological accessibility diminishes and input energies rise, even as drilling technologies advance.[32]Applications to Nuclear Energy
Fission Reactors
Fission reactors, primarily light-water designs such as pressurized water reactors (PWRs) and boiling water reactors (BWRs), exhibit high energy return on investment (EROI) due to the dense energy content of nuclear fuel and the minimal ongoing energy requirements for operation relative to construction and fuel cycle inputs. Peer-reviewed analyses typically calculate EROI by encompassing uranium mining, milling, conversion, enrichment, fuel fabrication, reactor construction, operation, and decommissioning, with boundaries at the point of electricity delivery. A comprehensive study evaluating standardized power plant systems found an EROI of approximately 75 for a 1.3 GW PWR, accounting for full lifecycle energy inputs including concrete, steel, and enrichment processes that demand gaseous diffusion or centrifugation.[47] This value reflects the reactor's capacity to deliver substantial net energy over a 40-60 year lifespan, with annual fuel requirements representing less than 1% of total energy output.[33] Variations in EROI estimates arise from methodological boundaries and assumptions about indirect inputs, such as whether to include upstream energy for labor or rare earth materials in alloys. The World Nuclear Association, drawing on updated lifecycle assessments, reports an EROI of 70 for nuclear fission when adjusting fuel cycle inputs conservatively higher than prior models, emphasizing that enrichment energy has declined with advanced centrifuge technology since the 1970s.[33] For context, this surpasses fossil fuels like coal (EROI ~30) and far exceeds intermittent renewables when buffering for grid reliability is excluded from nuclear calculations, as fission provides baseload dispatchability without storage penalties. Empirical data from operational fleets, such as France's 56 reactors averaging 70-80% capacity factors since 1980, support these high figures by demonstrating sustained output with fuel assemblies replaced every 12-24 months. Critiques of high EROI claims, often from biophysical economists like Charles Hall, propose lower values (5-16) by expanding boundaries to societal overheads or historical data from early reactors with inefficient enrichment.[10] However, such inclusions risk double-counting amortized infrastructure shared across energy sectors and overlook technological improvements; for instance, modern low-enriched uranium fuel cycles yield over 40 GWd/t burnup, reducing waste and input energy per joule output.[47] Independent reviews, including those reconciling entropy-based and empirical inventories, affirm median EROI above 50 for contemporary fission systems, underscoring their role in high-energy civilizations despite regulatory and material sourcing challenges.[2] Decommissioning energy, estimated at 1-2% of lifetime output for graphite-moderated designs, further validates net positivity when recycled materials offset inputs.[33]Advanced and Fusion Prospects
Advanced nuclear fission reactors, including Generation IV designs and small modular reactors (SMRs), promise improvements in fuel efficiency and resource utilization that could enhance EROI beyond the 50-80 range observed for light-water reactors.[33] Generation IV systems, such as molten salt reactors (MSRs) and fast breeder reactors, aim to close the fuel cycle through reprocessing and breeding fissile material from fertile isotopes like thorium or depleted uranium, potentially reducing energy inputs for fuel acquisition by up to 25% compared to open-cycle operations.[33] This efficiency stems from minimizing mining and enrichment demands, as breeders can extract over 60 times more energy from uranium than once-through cycles.[48] SMRs, often incorporating passive safety and modular construction, may achieve comparable or slightly higher EROI through standardized factory production, though initial deployment costs and scaling remain unproven at commercial levels as of 2025.[49] Nuclear fusion prospects for EROI remain speculative, as no operational power plants exist, and current experiments demonstrate only localized net energy gain in plasma ignition rather than system-wide positivity. In December 2022, the National Ignition Facility achieved a fusion yield of 3.15 MJ from 2.05 MJ laser input (Q=1.54), but total facility energy consumption exceeded output by orders of magnitude due to laser inefficiencies and infrastructure. Full EROI for fusion devices would require accounting for tritium breeding, cryogenic systems, and plant construction, with projections suggesting values exceeding 10:1 feasible if gain factors (Q) reach 20-30 in steady-state reactors like tokamaks or stellarators.[50] Abundant fuels—deuterium from seawater and lithium for tritium—imply low ongoing inputs, but high capital energy for magnets and materials poses challenges; commercial viability, targeted for the 2030s-2040s by projects like ITER and private ventures, hinges on overcoming these to surpass breakeven thresholds.[51][52]Applications to Renewables
Solar Photovoltaic Systems
Energy return on investment (EROI) for solar photovoltaic (PV) systems measures the total electricity output over the system's operational lifetime divided by the primary energy inputs required for raw material extraction, manufacturing, balance-of-system components (such as inverters and mounting structures), installation, operation, maintenance, and end-of-life processing. Recent lifecycle assessments of utility-scale monocrystalline silicon PV installations in the United States report energy payback times (EPBT) ranging from 0.5 to 1.2 years, depending on location, supply chain emissions, and recycling assumptions, with a benchmark value of 0.6 years for average conditions.[53] For a typical 30-year lifetime with 0.7% annual degradation, this translates to module-level EROI values exceeding 20:1, though actual figures vary with site-specific solar insolation and performance ratios.[53] Technological advancements have driven substantial improvements in PV EROI since the 1970s, when early systems yielded EROI below 5:1 due to low module efficiencies (around 10%) and energy-intensive production processes. By 2023, efficiencies exceeding 20% for commercial silicon panels, coupled with reduced material inputs and optimized manufacturing (e.g., lower silver and silicon use), have elevated median EROI to 10-30:1 in meta-analyses of rooftop and ground-mounted systems, with thin-film cadmium telluride (CdTe) variants occasionally reaching higher values due to shorter EPBT (under 1 year in high-insolation regions). These gains stem from scale economies in global production, where cumulative installed capacity surpassed 1 TW by 2022, enabling learning rates of 20-25% per capacity doubling. However, regional variations persist: northern latitudes with lower irradiance exhibit 20-50% longer EPBT than equatorial sites.[53] Methodological boundaries significantly influence reported EROI, with many studies limiting scope to the PV farm gate (excluding upstream mining energy or downstream grid integration), potentially overstating net yields. When expanded to system-level analyses incorporating intermittency—such as backup generation or storage to achieve dispatchable power—effective EROI declines markedly; for instance, pairing PV with lithium-ion batteries (themselves with EROI of 10-20:1) can reduce overall returns below 10:1 due to round-trip efficiencies under 90% and storage lifecycle demands.[7] In global decarbonization scenarios projecting 50-80% variable renewable penetration by 2050, systemwide EROI for electricity systems including dominant solar PV shares risks falling below 10:1 without compensatory high-EROI sources, as enabling infrastructure (transmission, curtailment mitigation) amplifies energy investments.[54] [55] Critics argue standard PV EROI metrics undervalue output quality by treating intermittent electricity as equivalent to baseload power, ignoring thermodynamic penalties for conversion and storage.[31] Supply chain dependencies further complicate assessments, as PV manufacturing relies on energy-intensive processes like polysilicon purification, which accounted for 40-60% of lifecycle energy in early 2020s analyses; reshoring production to lower-carbon grids could shorten EPBT by 10-20%, but reliance on rare earths and geopolitically concentrated refining (e.g., China-dominated) introduces vulnerabilities.[56] End-of-life recycling recovers 90-95% of materials in advanced scenarios, modestly boosting net EROI by reducing virgin inputs, though current global rates remain below 10%.[53] Despite optimistic projections of EROI surpassing 50:1 by 2030 via perovskite tandems and further efficiency gains, empirical data underscore that PV's net energy surplus supports societal thresholds only when integrated judiciously with higher-EROI dispatchable alternatives.[55]Wind Turbines
Wind turbines generate electricity from kinetic wind energy, with energy return on investment (EROI) calculated as the ratio of lifetime energy output to total energy inputs across manufacturing, installation, operation, maintenance, and decommissioning. Harmonized reviews of multiple studies report average EROI values for wind power ranging from 10:1 to 20:1 at the point of electricity generation, accounting for variations in turbine size, location-specific wind resources, and grid transmission efficiencies assumed at 30% for thermal-dominated systems.[6] Earlier life-cycle analyses of operational turbines, including 60 projects, yield an average EROI of 19.8:1, with a standard deviation of 13.7 reflecting site-specific wind speeds and turbine designs.[57] Onshore wind systems typically achieve higher EROI than offshore due to lower embodied energy in foundations, cabling, and installation; representative values for modern onshore turbines fall around 17:1 to 18:1, driven by capacity factors averaging 38% in the United States as of 2021. Offshore wind EROI is lower, estimated at 12:1 to 14:1, owing to elevated energy costs for specialized vessels, corrosion-resistant materials, and longer transmission distances, despite potentially stronger winds yielding capacity factors up to 50% in optimal sites. A 2017 analysis of New Zealand wind farms over a 20-year lifespan reported a weighted average EROI of 34.3:1, with values ranging from 20:1 to 57:1 correlated positively with average wind speeds and rotor blade diameters.[58] Key factors influencing EROI include capacity factor, which measures actual output against rated capacity and varies with hub height (averaging 90 meters for modern turbines) and local wind regimes; higher factors directly boost output relative to fixed inputs. Turbine lifetimes are typically 20 to 25 years, with energy payback times of 6 to 12 months for onshore systems under average conditions. Manufacturing dominates inputs (primarily steel, concrete, and fiberglass composites), comprising about 80-90% of total embodied energy, while operations and maintenance add 5-10% over the lifecycle. Larger turbines (e.g., 5-15 MW ratings) improve EROI by increasing output per unit of material, but scaling introduces logistical challenges, particularly offshore.[59][47] Methodological variations explain EROI discrepancies across studies; boundary definitions excluding backup storage or full grid integration yield higher point-of-edge values (e.g., 16:1 to 35:1), while including intermittency smoothing lowers them, as wind output fluctuates with weather, necessitating fossil fuel or storage supplementation not captured in farm-gate calculations. Recent advancements, such as taller towers and advanced composites, have incrementally raised EROI by 10-20% since 2010, but offshore deployments face persistent input penalties from supply chain energy demands. Empirical data from operational fleets underscore that EROI exceeds 10:1 in most cases, sufficient for net positive energy but sensitive to declining wind resources in saturated regions.[33][6]Hydropower and Biomass
Hydropower exhibits one of the highest energy return on investment (EROI) ratios among energy sources, with mean values estimated at 50:1 when accounting for variability across sites and operational factors such as reservoir evaporation losses and construction energy inputs.[25] This high EROI stems from the gravitational potential energy harnessed with minimal ongoing fuel inputs after initial infrastructure development, though upfront embodied energy for dam construction, including concrete and steel production, can represent 5-10% of lifetime output for large-scale facilities.[29] Variability arises from site-specific hydrology; large reservoir-based systems in optimal locations, like those developed mid-20th century, achieve EROIs exceeding 100:1, while run-of-river or small-scale installations yield 10:1 to 20:1 due to lower capacity factors and higher relative maintenance costs.[10] In regions like Iceland, operational data from plants such as Fljótsdalsstöð (690 MW) confirm EROIs around 50-80:1 over decades, though global averages decline as prime sites are exhausted, with new projects in developing areas facing siltation and ecological constraints that erode long-term yields.[29] Biomass energy conversion yields lower EROIs, typically ranging from 1:1 to 10:1 depending on feedstock type, harvesting methods, and processing pathways, often constrained by energy-intensive collection, drying, and transport logistics that consume 20-50% of the final output. Direct combustion of wood chips or residues in efficient combined heat and power plants can achieve 5:1 to 16:1, but liquid biofuel production, such as ethanol from corn or sugarcane, averages 1.3:1 to 4:1 after including agricultural inputs like fertilizers and distillation energy.[60] A meta-analysis of palm oil-based biofuels reports an average EROI of 3.92:1, while other biomass-derived fuels average 3.22:1, highlighting inefficiencies in photosynthetic energy capture (e.g., <1% solar-to-biomass efficiency) and soil nutrient depletion that necessitate fossil-derived subsidies, potentially inflating apparent returns if not fully boundary-accounted.[61] Advanced pathways like biomass gasification for syngas yield up to 8:1 to 24:1 for solid fuels, but scalability is limited by land competition with food production and emissions from incomplete combustion, rendering biomass marginal for baseload power compared to hydropower's reliability.| Energy Source | Typical EROI Range | Key Factors Influencing Variability |
|---|---|---|
| Large-Scale Hydropower | 20:1 to 100:1+ | Reservoir size, site hydrology, construction materials |
| Small-Scale/Mini-Hydropower | 10:1 to 20:1 | Flow intermittency, turbine efficiency, access costs |
| Biomass Combustion (Solid Fuels) | 5:1 to 16:1 | Feedstock density, moisture content, boiler efficiency |
| Biomass Biofuels (e.g., Ethanol) | 1:1 to 4:1 | Crop yields, fermentation losses, agricultural inputs |
