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LifePo4 Battery Recycling Progress and Setbacks

Solar Knowledge

LifePo4 Battery Recycling Solution Progress and Setbacks

2024-06-06 11:52:15

Abstract Introduction of LiFePO4 Battery

The Lithium Iron Phosphate (LiFePO4) battery is a type of lithium-ion battery that uses lithium iron phosphate as the positive electrode and carbon as the negative electrode. Its single cell has a rated voltage of 3.2V, with a charging cut-off voltage between 3.6V and 3.65V. Please learn more about LifePO4 battery from our other article:


Complete Knowledge about LiFePO4 Batteries (LFP Lithium Iron Phosphate Battery

LiFePO4 batteries carry the advantages as follows:
  • High operating voltage
  • High energy density
  • Long cycle life
  • Good safety performance
  • Low self-discharge rate
  • No memory effect

LiFePO4 Battery Recycling 

lifepo4 recycling and Regeneration solutions

Current Status and Problems

Rapid Growth and Large Scrap Volume

Since the development of the electric vehicle industry, China has been the world’s largest consumer market for lithium iron phosphate. In particular, from 2012 to 2013, it grew at a rate of nearly 200%, with lithium iron phosphate sales in China reaching approximately 5797t in 2013, accounting for over 50% of global sales.
In 2014, 75% of lithium iron phosphate cathode materials were sold to China. The theoretical life of lithium iron phosphate batteries is 7-8 years (calculated as 7 years), and it is estimated that by 2021, approximately 9400t of lithium iron phosphate will be scrapped. If such a large amount of waste is not properly handled, it will not only cause environmental pollution but also lead to energy waste and economic losses.

Significant Hazards

Chemicals such as LiPF6, organic carbonates, and copper contained in lithium iron phosphate batteries are listed in the national hazardous waste list. LiPF6 is highly corrosive and easily decomposes to produce HF when in contact with water. Organic solvents and their decomposition and hydrolysis products can cause serious pollution to the atmosphere, water, and soil, and pose a hazard to the ecosystem. Heavy metals such as copper accumulate in the environment and ultimately pose a threat to human health through the food chain. Once phosphorus enters bodies of water such as lakes, it can easily cause eutrophication. Therefore, if retired lithium iron phosphate batteries are not recycled and reused, they pose significant hazards to the environment and human health.

Immature Recycling Technology

Existing data indicates that the recycling of retired lithium iron phosphate batteries is divided into two types: one is metal recovery, and the other is the regeneration of lithium iron phosphate cathode materials.

(1) Wet Recovery of Lithium and Iron
This process primarily focuses on lithium recovery, and the recycling process for lithium iron phosphate is modified due to its lack of precious metals. First, the lithium iron phosphate battery is disassembled to obtain the cathode material, which is then crushed and sieved to obtain powder. Alkali solution is added to the powder to dissolve aluminum and aluminum oxides, resulting in a residue containing lithium, iron, and other elements. The residue is then leached with a mixed solution of sulfuric acid and hydrogen peroxide (reducing agent) to obtain a leachate. Iron hydroxide is precipitated by adding alkali, and the filtrate is obtained by filtration. The iron hydroxide is then calcined to obtain iron oxide, and the leachate is filtered and concentrated to crystallize lithium carbonate using solid sodium carbonate.

(2) Regeneration of Lithium Iron Phosphate
The primary method for processing retired lithium iron phosphate batteries is the solid-phase regeneration of lithium iron phosphate, which has high recycling efficiency and a high comprehensive utilization rate of resources. First, the lithium iron phosphate battery is disassembled to obtain the cathode material, which is then crushed and sieved to obtain powder. The powder is then heat-treated to remove residual graphite and binders. Alkali solution is added to the powder to dissolve aluminum and aluminum oxides. The residue containing lithium, iron, and other elements is filtered, and the molar ratio of iron, lithium, and phosphorus in the residue is analyzed. Iron, lithium, and phosphorus sources are added to adjust the molar ratio of iron, lithium, and phosphorus to 1:1:1. Carbon source is added, and after ball milling, the material is calcined in an inert atmosphere to obtain new lithium iron phosphate cathode material.

Incomplete Recycling and Utilization System
The national “863” program, “973” program, and the Eleventh Five-Year Plan for the development of high-tech industries all classify lithium iron phosphate batteries as key support areas. However, the strict production technology requirements for these batteries have led to high prices, limiting their use to electric motorcycles and a small number of cars. Therefore, there has not been a large-scale scrapping of automotive power batteries, and a professional system for the recycling and utilization of automotive power batteries has not yet been established. The existing recycling system has certain problems and low recycling efficiency.

Reasons causing the Recycling Setbacks

Inadequate Recycling Volume

A large number of waste batteries are scattered among the public, but there are no designated disposal locations for the public to deposit them. As a result, they are often handled as part of household waste, leading to almost zero individual recycling of discarded batteries. The vast majority of recovered batteries are waste generated during the production process by manufacturers or old stock materials. The number of large power batteries recovered is extremely low.

Incomplete Recycling System

A specialized system for battery recycling has not been established domestically, and the collection process is mainly carried out by small workshops in a crude manner. China is a major producer and consumer of lithium-ion batteries, but due to its large population, the per capita ownership of batteries is relatively low. For a long time, recycling companies have not been recycling individual lithium-ion batteries that do not have recycling value.

High Entry Threshold

Enterprises wishing to engage in the recycling and processing of waste batteries must apply for a Hazardous Waste Operation Permit in accordance with the provisions of the “Environmental Protection Law of the People’s Republic of China” and the “Management Measures for Hazardous Waste Operation Permits.” However, there are not many enterprises that have the qualifications for large-scale recycling, and there are numerous small-scale and low-tech companies, leading to the difficulty of centralized battery collection.

High Recycling Costs

A large amount of lithium iron phosphate material is used in the positive electrodes of power or energy storage batteries, and the demand is much higher than that of ordinary small batteries. Recycling them has high social value, but the cost of recycling is high, and lithium iron phosphate batteries do not contain precious metals, resulting in low economic value.

Weak Recycling Awareness

For a long time, there has been little public education on the recycling and utilization of waste batteries in China, leading to a lack of deep understanding of the pollution and hazards of waste batteries among citizens, and a lack of awareness of conscious recycling.

Recycling Methods of LiFePO4 Batteries

Recycling Methods of LiFePO4 Batteries

Retired lithium iron phosphate batteries that do not have value for secondary use and those that have undergone secondary use must eventually enter the disassembly and recycling stage. Unlike ternary material batteries, lithium iron phosphate batteries do not contain heavy metals. The main components for recovery are Li, P, and Fe, and the added value of the recovered products is low, necessitating the development of low-cost recycling routes. There are mainly two recycling methods: pyrometallurgical and hydrometallurgical.

Pyrometallurgical Recycling Process

Traditional pyrometallurgical recycling generally involves high-temperature incineration of electrode sheets to burn off the carbon and organic matter in the electrode fragments. The remaining ash, which cannot be burned off, is ultimately obtained through screening and contains metal and metal oxides in a fine powder form. This method is simple but has a long processing time, and the comprehensive recovery rate of valuable metals is low. An improved pyrometallurgical recycling technology involves calcining to remove organic binders, separating lithium iron phosphate powder from aluminum foil, obtaining the lithium iron phosphate material, and then adding the appropriate raw materials to achieve the required molar ratio of lithium, iron, and phosphorus, and synthesizing new lithium iron phosphate through high-temperature solid-phase methods. According to cost estimates, improved pyrometallurgical dry recycling of waste lithium iron phosphate batteries can be profitable. However, the lithium iron phosphate produced by this recycling process has high impurity levels and unstable performance.

Hydrometallurgical Recycling Process

Hydrometallurgical recycling mainly involves dissolving the metal ions in lithium iron phosphate batteries in acid-base solutions and then extracting the dissolved metal ions in the form of oxides, salts, and other compounds using precipitation and adsorption methods. The reaction process often uses reagents such as H2SO4, NaOH, and H2O2. This method is simple, requires low equipment demands, and is suitable for industrial-scale production. It is the most researched method and the mainstream route for the treatment of waste lithium-ion batteries in China.

In the hydrometallurgical recycling of lithium iron phosphate batteries, the focus is on recovering the positive electrode. When using the wet process to recover lithium iron phosphate positive electrodes, the aluminum foil collector fluid is separated from the positive electrode active material. One method involves using an alkaline solution to dissolve the collector fluid, while the active material does not react with the alkaline solution and can be obtained through filtration. Another method involves using an organic solvent to dissolve the binder PVDF, separating the lithium iron phosphate positive electrode material from the aluminum foil, and reusing the aluminum foil. The active material can then undergo subsequent processing, and the organic solvent can be recycled through distillation for reuse. Of the two methods, the second is more environmentally friendly and safe. One method for recovering lithium iron phosphate from the positive electrode is to produce lithium carbonate. This low-cost recovery method is adopted by most waste lithium iron phosphate recycling companies, but the main component of lithium iron phosphate, iron phosphate (with a content of 95%), is not recovered, leading to resource waste.

An ideal hydrometallurgical recycling method involves converting waste lithium iron phosphate positive electrode materials into lithium salt and iron phosphate to achieve full elemental recovery of Li, Fe, and P. To transform lithium iron phosphate into lithium salt and iron phosphate, the ferrous iron must be oxidized to ferric iron, and the lithium must be leached using acid or alkali. Researchers have used oxidation and calcination to separate aluminum foil and lithium iron phosphate, followed by sulfuric acid leaching and separation to obtain crude iron phosphate. The solution is purified using sodium carbonate precipitation to obtain lithium carbonate. The crude iron phosphate is further refined to obtain battery-grade iron phosphate, which can be used in the preparation of lithium iron phosphate materials. After years of research, this process has become relatively mature.

Application Achievement of LiFePO4 Battery 

World Yielding of Lithium Batteries

Firstly, the market share of lithium iron phosphate batteries reached a new high in 2023. Data shows that in the installed capacity of power batteries in 2023, the cumulative installed capacity of ternary batteries was 126.2GWh, accounting for 32.6% of the total installed capacity, with a year-on-year growth of 14.3%; the cumulative installed capacity of lithium iron phosphate batteries was 261.0GWh, accounting for 67.3% of the total installed capacity, with a year-on-year growth of 42.1%. Since 2021, due to its lower cost and higher safety, lithium iron phosphate batteries have continuously surpassed ternary lithium batteries in market share, and by 2023, their share had exceeded two-thirds.

In terms of the main product structure, the proportion of lithium iron phosphate positive electrode materials accounts for nearly 70% of the total positive electrode material shipments, while the proportion of ternary positive electrode materials is less than 26%; the market shipment volume of lithium manganese iron phosphate materials will exceed 30,000 tons, with a year-on-year growth of over 500%. Driven by the demand for lithium manganese oxide materials, the shipment growth of lithium-rich manganese-based materials in China will exceed 50% (mainly doped for use). Driven by the growth of lithium iron phosphate batteries, the demand for LiFSI in China will exceed 30,000 tons in 2024, with a market growth rate of over 100%. In 2024, the domestic shipment volume of lithium iron phosphate materials and other lithium iron materials will see a growth of over 30% (used in conjunction with phosphate-based batteries).

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