Battery-powered electric vehicles (BEVs) are an important part of decarbonizing the transportation sector and mitigating climate change impacts by producing lower greenhouse gas (GHG) emissions compared to conventional internal combustion engine (ICE) vehicles. However, most BEVs currently run on lithium-ion batteries (LIBs), which typically last 10 to 12 years before the battery capacity falls below 80% and can no longer propel the vehicle. Therefore, with an increasing demand for BEVs there will be a growing volume of retired LIBs with residual energy that could end up in landfills. In anticipation of a future market for used batteries, UL Solutions and UL Standards & Engagement developed and published an Outline of Investigation for Evaluation for Repurposing Batteries, UL 1974 in 2017 and later a first edition consensus safety standard in 2018. UL 1974 provides a state of health assessment for these batteries so they can be safely utilized for a second application rather than final disposal. This binational standard provides requirements for the sorting and grading processes involved in repurposing LIBs from their original first-life use, such as in BEVs, to secondary use in other applications that have lower power demands, such as stationary energy storage that can utilize the remaining energy in retired BEV LIBs. Safety standards such as UL 1974 improve the circular economy and help industries make the best use of battery technology while supporting sustainability efforts at local and global scales by reducing the need for new battery production and reducing landfill waste.
Electrification of the transportation sector has been suggested as a primary approach to reduce greenhouse gas emissions, with lithium-ion batteries (LIBs) as the key technology that will advance the transition from fossil fuel-based to electrical storage-based vehicles.
By 2030, over 1 million EV batteries will reach end of life, and with few disposal options, many may be stockpiled or landfilled — risking metal leakage, electric shock, and thermal runaway hazards.
One Oregon landfill experienced 21 LIB-related fires within a three-month period in 2023. The source of these fires ranged from cellphones to e-bikes and EVs, with a concern that the bigger the battery, the bigger the fire.
If decarbonization needs LIBs but recycling falls behind, what should be done with EV LIBs once they can’t power vehicles?
Tesla Motors is now synonymous with electric cars, but it was the Nissan Altra electric vehicle (EV), released in 1997, that was the first EV to be powered by a lithium-ion battery (LIB). 9
While only 139 Altra EVs were sold, fast forward to today’s EV market and the numbers tell a different story. Global EV sales hit one million units for the first time in 2017 6 and are predicted to surpass 300 million by 2030. 7 Such growth stems from a desire for more sustainable transportation options. Transportation accounts for over 25% of global greenhouse gas (GHG) emissions and is a well-known contributor to local air pollution issues. 15 Electrification of the transportation sector has been suggested as a primary approach to reduce GHG emissions and improve air quality. 11 As a decarbonization strategy, electrification aims to convert energy-consuming devices that traditionally run on fossil fuels to those that run on electricity or electrical storage. LIBs are the key technology advancing this process. Relative to conventional cars powered by internal combustion engines (ICEs) that run on multiple complex systems, battery-powered electric vehicles (BEVs) have a simpler internal configuration consisting of a single large battery or bank of batteries that can be charged and discharged hundreds or thousands of times during a typical battery lifetime.
When charged, an EV battery must contain a high enough energy capacity to power the propulsion system of the vehicle. Presently, common types of rechargeable batteries used in BEVs include lead-acid batteries (LABs) and LIBs. Some EV manufacturers choose LABs due to their high reliability, availability, low cost, and high recycling potential. However, they are not as widely used in EVs due to their lower energy storage capacity relative to LIBs. LIBs have significant advantages over other battery types in terms of their higher energy density and efficiency, smaller size, and lighter weight. These characteristics mean LIBs are widely used in EVs today. However, LIBs are not perfect, and current research is investigating how to improve LIB lifespan, charging rates, and driving range reliability. 10
In theory, LIBs would last forever as lithium ions move between the anode and cathode ends of a battery cell to generate a voltage and power a device. 13 However, normal aging and secondary chemical reactions cause LIBs to lose capacity over time. 8 4The point at which an EV LIB reaches end of life is determined by its remaining capacity, which is expressed as the state of health (SOH), or an estimate of the battery’s capacity to store energy compared to when it was first manufactured. 16 Currently, EV LIBs are considered to reach end of life when their SOH falls below 80%. 2 Below this, EV LIBs cannot generate enough voltage to power and accelerate the vehicle, which requires most EV LIBs to be retired after 10 to 12 years. 3
Have you ever had to figure out what to do with a lithium-ion battery, for example from an old cellphone or laptop? How did you handle it? If you haven’t, do you know what your options are for managing these batteries when they reach their end of life?
Considering today’s soaring electric vehicle sales and that lithium-ion battery-powered EVs have been on the market for nearly 30 years, more than 1 million EV LIBs are expected to be retired by 2030 with limited options for battery end-of-life management.
Recycling options for LIBs are currently limited, meaning most end up either stockpiled, sent to landfills, or in electric car “graveyards” in some countries. 1 While nearly all conventional lead-acid batteries are now recycled, few LIBs are due to the high cost and challenges associated with managing the impact of the critical elements that make up LIBs, such as lithium, nickel, and cadmium, causing most to end up in landfills where leaching releases these elements into the environment. 12 Another challenge is managing the residual energy in EV LIBs. Discarding batteries that have not been discharged leads to safety hazards such as electric shock and thermal runaway. Over 240 fires caused by LIBs were reported from 64 facilities between 2013 and 2020. 14 While most of these fires originated from smaller LIB-powered devices, the similar chemistry to EV LIBs means their larger battery packs would logically lead to larger, more dangerous fires if they continue to be discarded in landfills.
With the abundance of retired EVs, there is a market for used LIBs that still maintain 60-80% of their original energy capacity that could be met with reused LIBs from BEVs. 5 A circular economy for LIBs means that any residual power remaining in batteries when they reach the end of their first life should be fully used before the battery is finally disposed. A battery economy with a circular (e.g., take, make, reuse/repurpose, recycle) rather than a linear (e.g., take, make, use, discard) supply model will promote more resource-efficient battery use, ensuring the maximum electrical energy is harnessed from an EV battery before it reaches a final end-of-life state. A common circularity practice includes slowing resource loops by considering alternate use options before recycling. 2 For example, second use of EV LIBs could include: 1) reuse in an EV after repair or refurbishment, or 2) repurposing in a different application requiring less voltage, such as in stationary energy storage, smaller electric-powered vehicles, or power tools. The viability of whether a battery is fit for reuse or repurposing depends on the condition and state of health of the battery. To support the circular economy and improve waste management options, potential second-life LIBs need to be evaluated against a standard to ensure they are safe for their second-use applications.
Circular economy practices include closing, narrowing, and slowing resource loops. How do the waste management options of reusing, repurposing, and recycling align with these circular practices?
With an understanding that the growing number of retired EV lithium-ion batteries contain a residual, though lower, charging capacity that could be used in secondary applications, UL Solutions engineers and researchers, as well as EV original equipment manufacturers (OEMs), recyclers, and repurposing organizations supported development of a consensus safety standard that includes a health assessment for EV LIBs to determine their suitability for second-use application before final disposal.
In response, technical committee 1974 was formed in April 2017 with representatives from various interest categories, including producers, regulators, government agencies, testing and standardization organizations, supply chain members, commercial and industry representatives, and general interest members.
On October 25, 2018, the first edition of UL 1974 was published by UL Standards & Engagement as the Joint National Standard for Canada and the United States for evaluation for repurposing batteries. Over the next four years of putting UL 1974 into use, ideas for revisions to the first edition were brought forward. In 2022, proposals were received from industry with suggestions for improvements to UL 1974, including a proposal to expand the scope of the standard to incorporate remanufacturing. In November 2023, the second edition was published with a revised title: the Standard for Evaluation for Repurposing or Remanufacturing Batteries.
Considering the members of technical committee 1974, which group of stakeholders do you think would have the most interest in seeing a standard like UL 1974 published?
UL 1974, the Standard for Evaluation for Repurposing or Remanufacturing Batteries, states four main steps that are to be carried out when evaluating a battery’s potential fit for being repurposed or remanufactured: information gathering, visual inspection, testing for sorting and grading, and long-term improvement processes.
Together, these steps help determine a battery’s state of health and if it is safe for continued use in a second-life application. Test procedures carried out during the evaluation include checking the battery’s capacity, internal resistance, charge and discharge cycling, and the battery management system controls. Of particular importance during the charge and discharge cycling test is to monitor the battery’s temperature, voltage, and current to see if the battery cells function within the manufacturer’s recommended specifications. If any values are too high or too low, then the battery is rejected from moving on to being repurposed or remanufactured. Guidance like UL 110: Ensuring Mobile Phones are Sustainable | www.standardsacademy.org 8 that offered in UL 1974 helps repurposing and remanufacturing entities assess the qualities that will determine the usability of lithium-ion batteries, which supports keeping batteries within a circular economy rather than having them end up as waste, and it improves our ability to make the most efficient use of current battery technology.
Would you ever consider buying or leasing an electric vehicle that runs on a remanufactured battery system? Why or why not?
In a circular economy, products and materials are designed to be reused, remanufactured, recycled, or recovered so they can remain in the economy for as long as possible, minimizing waste and limiting further greenhouse gas emissions.
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A type of electric vehicle that is powered by a rechargeable battery.
A production model that keeps materials and products in use for as long as possible through sustainability practices such as reuse, refurbishment, remanufacture, and recycling.
A car that runs on an electric motor instead of a gasoline engine or that incorporates an electric motor in conjunction with a gasoline engine (known as hybrid EVs).
A system where resources move in one direction as raw materials are extracted from the earth to make products which then eventually end up as waste. Also known as a take-make-waste economy.
A rechargeable battery that stores energy by moving lithium ions between its anode and cathode electrodes.
A company that produces parts or products for use in other companies’ end products.
A battery pack or system that was used in one application and returned for repair and/or replacement of parts for use in the same intended application. Also known as a “refurbished battery” or a “rebuilt battery.”
A battery pack or system that was used in one application that is subject to some level of analysis, refurbishment and reconfiguration for a use in a different application. Also known as a “second-life battery.”
The remaining chemical energy in a battery when the battery can no longer power a particular device.