2019
DOI: 10.1039/c9se00427k
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A modeling framework to assess specific energy, costs and environmental impacts of Li-ion and Na-ion batteries

Abstract: Holistic assessment of Li-ion and Na-ion batteries through integration of physics-based battery model into economic and environmental analysis framework.

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Cited by 44 publications
(30 citation statements)
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“…Preliminary assessments of the potential life-cycle of NIBs have proven that NIBs already provide an ecological benefit in terms of materials compared to LIBs [337]. Finally, several works estimate that NIBs can be cost-competitive when taking into account the bill of materials, as avoidance of aluminium leads to substantial cost savings (also for cobalt and lithium, although to a much lesser extent) [7,128,338]. It should however be noted that, both for LIBs and NIBs, specific energy has the highest impact in the cell cost, as less materials are required for electrode, current collector foils, electrolyte and separator.…”
Section: Resultsmentioning
confidence: 99%
“…Preliminary assessments of the potential life-cycle of NIBs have proven that NIBs already provide an ecological benefit in terms of materials compared to LIBs [337]. Finally, several works estimate that NIBs can be cost-competitive when taking into account the bill of materials, as avoidance of aluminium leads to substantial cost savings (also for cobalt and lithium, although to a much lesser extent) [7,128,338]. It should however be noted that, both for LIBs and NIBs, specific energy has the highest impact in the cell cost, as less materials are required for electrode, current collector foils, electrolyte and separator.…”
Section: Resultsmentioning
confidence: 99%
“…[26] Thus, RO has been recognized as one of the most promising seawater desalination technologies even though it is still energy intensive compared to wastewater treatment processes for clean water production. In contrast, the two representative capacitive deionization technologies, MCDI and FCDI, have shown relatively high SEC of 83.2 kWh m −3 (MCDI) [27] and 43.0 kWh m −3 (FCDI) [28] for seawater desalination. Although MCDI and FCDI have been extensively investigated for brackish water desalination, [29][30][31] the application of these processes to seawater desalination has been limited primarily because their SECs proportionally increase with feed salinity, and the salinity of seawater is often ≈35,000 ppm (total dissolved solids; TDS).…”
Section: Seawater Battery Desalination Versus Other Seawater Desalination Technologiesmentioning
confidence: 95%
“…The material cost of LIB was reported in the range of ≈88 to ≈200 $ kWh −1 . [ 22 , 42 , 43 ] Thus, the material cost of SWBs (150.8 $ kWh −1 for SWB coin and 216.4 $ kWh −1 for SWB Rect. ) is reasonable or even cheaper compared to LIB for ESS applications.…”
Section: Feasibility Of Seawater Battery Desalination Systemmentioning
confidence: 99%
“…[130] Moreover, provided that new NIB materials exhibit increased voltage and specific capacity values similar to those of LIB materials, NIBs could become preferred to LIBs, both in terms of performance and cost, especially for high-power applications. [134] Also, as the portfolio of HCs grows, a further decrease in NIB price is very likely to occur. Even lower prices could be achieved by NIBs working with PBAs, which are based on abundant and low-cost elements.…”
Section: Cost Projectionmentioning
confidence: 99%