Cited by 111Environmental Impact and SustainabilityExtraction and Separation ProcessesPhotovoltaic Systems and Sustainability

Understanding the future of lithium: Part 2, temporally and spatially resolved life‐cycle assessment modeling

Open access
Ambrose, Hanjiro, Kendall, Alissa·2020·Journal of Industrial Ecology

Abstract

An array of emerging technologies, from electric vehicles to renewable energy systems, relies on large‐format lithium ion batteries (LIBs). LIBs are a critical enabler of clean energy technologies commonly associated with air pollution and greenhouse gas mitigation strategies. However, LIBs require lithium, and expanding the supply of lithium requires new lithium production capacity, which, in turn, changes the environmental impacts associated with lithium production since different resource types and ore qualities will be exploited. A question of interest is whether this will lead to significant changes in the environmental impacts of primary lithium over time. Part one of this two‐part article series describes the development of a novel resource production model that predicts future lithium demand and production characteristics (e.g., timing, location, and ore type). In this article, part two, the forecast is coupled with anticipatory life‐cycle assessment (LCA) modeling to estimate the environmental impacts of producing battery‐grade lithium carbonate equivalent (LCE) each year between 2018 and 2100. The result is a normalized life‐cycle impact intensity for LCE that reflects the changing resource type, quantity, and region of production. Sustained growth in lithium demands through 2100 necessitates extraction of lower grade resources and mineral deposits, especially after 2050. Despite the reliance on lower grade resources and differences in impact intensity for LCE production from each deposit, the LCA results show only small to modest increases in impact, for example, carbon intensity increases from 3.2 kg CO 2 e/kg LCE in 2020 to 3.3 kg CO 2 e/kg LCE in 2100.

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Crossref · 10.1111/jiec.12942

Cites

39 of 39 references verified0 citation errors · 0 not checkable

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  • Ambrose and Kendall's global study lacks the granularity needed to accurately assess diverse processing technologies and discuss improvements from a life cycle perspective.

    “Although Ambrose and Kendall28 present life cycle impacts of Li chemicals on a global scale, their study lacks the granularity needed to accurately assess the diverse processing technologies and to discuss improvements from a life cycle perspective.”

    From Current and Future Impacts of Lithium Carbonate from Brines: A Global Regionalized Life Cycle Assessment Model (2025) · cites this paper as [28]

    The Life-cycle inventory model (section 2.1.2; page not available) says processing varies among deposits and companies, while the Conclusions call for site-by-site assessment to capture variability. That supports a concern about granularity. But the paper does assess multiple production pathways (section 3.1) and discusses potential improvements in energy sources and efficiency (Discussion); it does not say its granularity prevents those assessments or discussions. (LLM, conf=0.83)

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  • Lithium life cycle assessments may offer insights on projected energy consumption and carbon intensity impacts yet lack social and hydrogeographic context, such as degree of water stress on the implications of water use by life cycle stage.

    “Lithium LCAs may offer insights on projected energy consumption and carbon intensity impacts yet lack social and hydrogeographic context, such as degree of water stress on the implications of water use by life cycle stage”

    From Lithium and water: Hydrosocial impacts across the life cycle of energy storage (2024) · cites this paper as Ambrose & Kendall, 2020

    The Methods and Results (§§2 and 3.1.1; page unavailable) model energy consumption and projected carbon impacts. The Conclusions (§5; page unavailable) call for site-specific assessment of socioeconomic impacts on communities, and the listed impact categories (§2.1.3) do not include water stress. The paper does not specifically discuss how local water stress changes the implications of water use at each life-cycle stage, so that example is not directly supported. (LLM, conf=0.84)

    Experimental — accuracy not yet measured
  • Existing literature uses dated LCI data for LCE production.

    “First, existing literature uses dated LCI data for LCE production.”

    From Environmental impacts of lithium supply chains from Australia to China (2024) · cites this paper as Ambrose and Kendall 2020

    The Discussion compares this study with existing LCE production inventories, supporting that prior literature uses LCI data for LCE production. Neither that section nor the Previous research section says those data are dated; the Discussion’s warning about temporally static inventories concerns this study’s own model. (LLM, conf=0.78)

    Experimental — accuracy not yet measured
  • This study's GWP values (10.7-16.7 t CO2eq/t LCE) for per ton LCE production from spodumene are lower than findings from previous studies (14-35.1 t CO2eq/t LCE).

    “Compared to findings from previous studies (14-35.1 t CO2eq/t LCE) (Khakmardan et al 2023, Ambrose and Kendall 2020, Kelly et al 2021, Haddad et al 2023), the results from this study indicated lower GWP values (10.7-16.7 t CO2eq/t LCE) for per ton LCE production from spodumene.”

    From Environmental impacts of lithium supply chains from Australia to China (2024) · cites this paper as Ambrose and Kendall 2020

    Section 3.1.1 reports GWP of 3.2–3.3 kg CO₂e/kg LCE as a production-weighted average across lithium sources, not a value for spodumene production. Sections 3.1 and 4 discuss hard-rock pathways and comparisons with other estimates, but the passages found do not give a spodumene GWP value in the cited 14–35.1 t CO₂eq/t LCE range (searched for that range and spodumene GWP). (LLM, conf=0.73)

    Experimental — accuracy not yet measured

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Cites

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Research works printed but not linked: 5

  1. Garrett, D. E. (2004). Handbook of lithium and natural calcium chloride. Amsterdam, Netherlands: Elsevier.
  2. Kawatra, S. K., & Eisele, T. C. (2002). Froth flotation-fundamental principles, pp. 1-30. Houghton, MI: Michigan Technical University.
  3. Lahsen, A., Muñoz, N., & Parada, M. A. (2010). Geothermal development in Chile (Vol. 25, p. 7). In Proceedings World Geothermal Congress, Bali, Indonesia.
  4. Menéndez, M., Vidal, J., Toraño, J., & Gent, M. (2004). Optimisation of spodumene flotation. European Journal of Mineral Processing & Environmental Protection, 4(2): 130-135.
  5. Pehlken, A., Albach, S., & Vogt, T. (2015). Is there a resource constraint related to lithium ion batteries in cars? The International Journal of Life Cycle Assessment, 22, 1-14.

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Authors
Ambrose, H., & Kendall, A.
Affiliations
University of California, Davis (US)
Corresponding author
Kendall, Alissa
Venue
Journal of Industrial Ecology
Published
2019-10-07
Volume
24
Issue
1
Pages
90-100
ISSN
  • 1088-1980 (ISSN-L)
  • 1530-9290
OpenAlex
W2977717779
Cited by
111
References
39
Citations by year
2026: 9 · 2025: 25 · 2024: 19 · 2023: 18 · 2022: 18 · 2021: 17 · 2020: 5
FWCI
4.24
Type
journal article
Language
en
Open access
Locations
Journal of Industrial Ecology (publishedVersion, cc-by)
Funders
National Science Foundation (CBET‐1337095)
Topics
  • Physical Sciences › Environmental Science › Environmental Engineering › Environmental Impact and Sustainability
  • Physical Sciences › Engineering › Mechanical Engineering › Extraction and Separation Processes
  • Physical Sciences › Environmental Science › Environmental Engineering › Photovoltaic Systems and Sustainability
Keywords
lithium, lithium-ion batteries, lithium production, ore grade, carbon intensity, mining impacts, electric vehicles, renewable energy storage

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